microsoft word hostin nb 9-2.doc nova biotechnologica 9-2 (2009) 205 chlorine production for water disinfection by the means of photovoltaic panels stanislav hostin 1, peter benedikovič2, anna michalíková2 1department of biotechnology, university of ss. cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic (stanislav.hostin@ucm.sk) 2slovak university of technology in bratislava, faculty of materials science and technology in trnava, institute of safety and environmental engineering, department of environmental engineering, botanická 49, trnava, sk-917 08, slovak republic (anna.michalikova@stuba.sk) abstract: in this contribution a possibility of electrochemical production of chlorine for water disinfection, by using photovoltaic panels from solar energy, is described. a simple way of chloride production by means of a photovoltaic panel, comparable with classical electrical power source was performed on an experimental device. by using photovoltaic panel with nominal output 50 w and solar irrigation 380 – 550 w/m2 chlorine production was 0.3 mg/min, which represents amount of chlorine sufficient for disinfections of approximately 4000 l water per day. key words: chlorine production, disinfection of water, solar energy, photovoltaic panel 1. introduction water disinfection is important to provide for a hygienic quality of water. it is not only a concern of drinking, service, heating and cooling waters in industry but also waters for public and private pools. in all these cases a potential infection with pathogenic micro-organism legionella pneumophilla must be prevented. water disinfection must be acceptable from point of view of environmental impacts, efficiency and costs (verčimáková et al., 2008). a broad scale of disinfection agents and techniques are available. each of them have advantages and disadvantages. for disinfection of drinking water chlorine, chlordioxide, ozone, cationic silver particles, uv light and ultrafiltration are the most frequently used. to prepare service water, for example for pools, chlorine, calcium hypochlorite (pellets, solution), sodium hypochlorite (solution produced by electrolysis of sodium chloride), bromine, peroxide, iodine, silver, trichlorisocyuronic acid can be used (bartram et al., 2005). a frequent way of chlorine production is electrolysis of sodium/potassium chloride solutions. during this process sodium/potassium hydroxide are also produced. the main technologies are mercury, diaphragmatic and membrane electrolysis. in these procedures the base material is mainly sodium chloride or less frequently potassium chloride. each of the mentioned technologies represents a different way of chlorine 206 hostin, s. et al. accumulation that is produced in the space near anode and hydrogen and hydroxide accumulation produced nearby cathode (reed, 2004). for the diaphragmatic method, which was used in this work, a summary chemical reaction of electrolysis of sodium chloride can be written as follows: 222 222 hnaohclohnacl ++→+ photovoltaic panels (pv panels) represent nowadays modern and available devices for a direct production of electric energy from the solar source. principles, materials, properties, types of pv panels are described in many foreign and native publications where various applications in industry and household are presented (appleyard, 2009; ďuricová et al., 2008). in this work we describe an application of pv panels for electrochemical production of chlorine which is subsequently used for disinfection, preferably service water. 2. material and methods 2.1 chlorine production a hermetic cell (electrolyzer) containing a carbon (6 cm2 area) and an iron (15 cm2 area) with a final volume 750 ml was constructed (fig. 1). an asbestine diaphragm was localized inside of the cell, 500 ml of a brine containing 7% nacl was used as an electrolyte. the hermetic cell contained two outlets provided with plastic tubes. one outlet served for releasing of hydrogen into atmosphere, chlorine was collected into a beaker containing 500 ml water using a second outlet. electrolyser was connected to electric circuit according to a scheme presented in fig. 2. in the first series of experiments a variable laboratory source of unidirectional current type uhs 401-1 (ac 220 v, 2 a / dc 1....15 v, 4 a) was used. a photovoltaic (pv) panel, model str 36×50, produced by solatec, ltd., czech republic was used as a provider of solar energy. pv panel was localized on a south-west oriented flat roof under 35° angle. the panel of 1005 × 453 × 34 mm size, 5.9 kg mass was constructed from a monocrystalline silicium, contained 36 primary cells, working temperature -35 -85 °c. electric parameters for solar irradiation: 1000w/m2, spectrum am 1.56, temperature 25 °c, nominal output 50 w, optimal output 50 w, nominal voltage 12 v, optimal voltage 17.4 v, off-load voltage 21.4 v, short circuit current 3.27 a, optimal current 2.97 a. electric characteristics of electrolysis (voltage, current) were monitored using wattmeter lutron dw 6090 connected via a serial boundary to pc. in case of pv panel, a rheostat with cylindrical coil, total resistance 100 ω for maximum voltage 500v and current 3a, was used. 2.2 determination of chlorine concentration in water concentration of chlorine soluble in water during chlorination was determined spectrophotometrically according to (jonson and overby, 1969). a yellownova biotechnologica 9-2 (2009) 207 orange color of a reaction product of chlorine and o-tholuidine was measured at 440 nm on a digital spectrophotometer genesystm 8 connected to pc. a mixture of k2cr2o7 and k2cro4 was used as a calibration curve. fig. 1. a hermetic electrolytic cell for chlorine production. fig. 2. a scheme of connection of a hermetic cell for chlorine production. 2.3 determination of solar irradiation this was done by an indicator of intensity of solar irradiation, type fl a613-gs, localized nearby the pv panel connected to the data logger almeno 5690-1m (ahlborn). 208 hostin, s. et al. 3. results and discussion 3.1 study of chlorine production using a laboratory electric power source in the first series of experiments a hermetic electrolytic cell was connected to a regulated laboratory electric power source and an electro-chemical production of chlorine was tested. optimal electric characteristics of electrolysis were determined as a constant voltage 6 v and current 0.6 a. fig. 3 presents results of water chlorination. it was found that maximal concentration of chlorine in water was 4.2 mg/dm3 and this was achieved after 25 minutes of electrochemical chlorine production. 0.5 1 1.5 2 2.5 3 3.5 4 4.5 0 5 10 15 20 25 30 electrolysis time [ min ] c hl or in e co nc en tr at io n [ m g/ l ] fig. 3. electrolytic production of chlorine using a laboratory electric power source. 3.2 study of chlorine production using a photovoltaic panel in a next series of experiments a hermetic electrolytic cell was connected to a photovoltaic panel which served as a source of electric energy. irregularities of this energy source (dependence on intensity of solar irradiation) were compensated by rheostat. the constant voltage 6 v and 0.6 a current were used similarly as in the case of laboratory electric power source. results of water chlorination are presented in fig. 4. it was found that maximal concentration of chlorine in water was 4.2 mg/dm3 which was achieved after 25 minutes of electrochemical chlorine production. both energy sources provide the maximal concentration of chlorine in water 4.2 mg/dm3 after 25 minutes of electrolysis. however, in case of pv panel the initial chlorine concentration is about 2.5 times higher. measurement of intensity of solar irradiation represents figure 5. from the kinetics of chlorine production it was calculated that the tested hermetic cell connected to the photovoltaic panel ( nominal output 50 w and solar irradiation nova biotechnologica 9-2 (2009) 209 380 -550 w/m2 ) can provide 0.3 mg of chlorine per minute what represents amount of chlorine sufficient for disinfection of approximately 4000 l water per day. 2 2.5 3 3.5 4 4.5 0 5 10 15 20 25 30 electrolysis time [ min ] c hl or in e co nc en tr at io n [ m g/ l ] fig. 4. electrolytic production of chlorine using a photovoltaic panel. 200 250 300 350 400 450 500 550 600 14:45 14:52 15:00 15:07 15:14 15:21 15:28 15:36 15:43 15:50 15:57 time [ h ] s ol ar ir ri ga tio n [ w /m 2 ] fig. 5. solar irradiation during chlorination of water using a photovoltaic panel. 4. conclusion it was found that pv panel can be used as an alternative of a laboratory electric power source to provide electric energy for an electrolytic chlorine production in a hermetic cell. pv panel can be recommended, after some improvements and economic calculations, for practical application. 210 hostin, s. et al. acknowledgement: this work was supported by projects under the contract no. vega 1/0798/08, development and utilization of small hydroenergetic power source combined with solar systems in machine technologies. references appleyard, s.: assessing the use of simple dye-sensitized solar cells for drinking water chlorination by communities with limited resources. renew. energ., 34, 2009, 1651-1654 bartram, j., mia, k. l., lenton, r., wright, a.: focusing on improved water and sanitation for health. lancet, 365, 2005, 810-812 ďuricová, i., hostin, s., ondruška, m., michalíková, a., gerulová, k.: the catalogue of projects, solar laboratory, mtf stu trnava, 2008, 58 pp., isbn 978-80-969443-8-5 jonson, j. d., overby, r.: stabilized neutral orthotolidine, snort, colorimetric method for chlorine. anal. chem., 41, 1969, 1744-1750 reed, r.h.: the inactivation of microbes by sunlight, solar disinfection as a water treatment process. adv. appl. microbiol., 54, 2004, 333-365 verčimáková, k., rybár, r., trojan, p.: utilization of uv radiation for water disinfection in solar reservoirs. acta mont. slov., 13, 2008, 343-349 microsoft word vranovicova nbc 12-2.doc nova biotechnologica et chimica 12-2 (2013) 70 doi 10.2478/nbec-2013-0008 © university of ss. cyril and methodius in trnava magnetostructural j-correlations in fe(iii) complexes – a revision beata vranovičová1, roman boča1,2 1department of chemistry, faculty of natural sciences university of ss. cyril and methodius, sk-917 01 trnava, slovak republic (roman.boca@stuba.sk) 2institute of inorganic chemistry, faculty of chemical and food technology, slovak university of technology, bratislava, sk-812 37, slovak republic abstract: the magnetostructural correlations in fe(iii) complexes, originally outlined by gorun and lippard has been revised. other correlation variants have been tested and the dataset enlarged for more recent entries possessing the fe-o-fe bridge including dinuclear, tetranuclear and hexanuclear fe(iii) complexes. the resulting relationships confirm that instead of the original suggestions, the correlation could stay as a linear relationship which covers the possibilities of positive values of exchange coupling constants. key words: exchange coupling, x-ray structure, magnetostructural correlation, fe(iii) complexes 1. introduction relationships between structural and magnetic parameters attract attention of scientists for a long time. invented by hatfield (crawford et al., 1976; hatfield et al., 1985), the exchange coupling constant occurring in the heisenberg form of the spin hamiltonian ˆ ˆˆ ( )ab ab a bh j= − ⋅s s (1) depends upon certain structural parameters such as bond lengths and bond angles. in the series of dinuclear cu(ii) complexes of the [cu(oh)2cu] type the values of j correlate with the bonding angle α = cu-o-cu along a straight line with the negative slope as shown in fig. 1. (notice, the original definition of the j-constant utilizes a numerical prefactor −2, so that all the data below are rescaled to the definition that matches eq. (1)). the critical angle when the positive coupling constant alters to the negative value is close to 98 deg. thus the ground state s = 1 (j > 0) and/or s = 0 (j < 0) can be controlled by the bonding angle α. the correlations of the above type have been extended also to some other types of dinuclear cu(ii) complexes, such as alkoxidoor phenoxido-bridged complexes (thompson et al., 1996). a further progress has been achieved by proposing the magnetostructural correlations in dinuclear cr(iii) complexes of the [cr(oh)2cr] type by hodgson et al. (glerup et al., 1983; hodgson et al., 1985). in dinuclear mn(iv) complexes of the [mn(o)2mn] type a magnetostructural correlation has been outlined by law et al. (2000). contrary to the previous cases, gorun and lippard (1991) proposed a magnetostructural correlation in fe(iii) oxido-bridged complexes in a different form: the value of –j has been found to correlate with the shortest fe-o contact (abbr. p) bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:00 utc nova biotechnologica et chimica 12-2(2013) 71 along a decreasing exponential function: 1[cm ] exp( )j a bp−− = ⋅ with the constants a = 8.763 × 1011 and b = −12.663. cu-o-cu /o 94 96 98 100 102 104 106 j/ cm -1 -600 -400 -200 0 200 400 fig. 1. magnetostructural correlation in [cuii(oh)2cuii] complexes by hatfield et al. (crawford et al., 1976) regression line: 1 o[cm ] 78.33 [ ] 7653j α− = − ⋅ + , r2 = 0.98. 2. results and discussion the dataset compiled by gorun and lippard (1991) has been subjected to a non-linear regression using contemporary software. to this end the correlation displayed in fig. 2 has been reconstructed; the regression line is 1[cm ] exp( )j a bp−− = ⋅ − with parameters a = 2.360 × 1010 and b = 10.661 and it is drawn by bold-solid line. the outer bands refer to the confidence and prediction intervals (95 %), respectively. p(fe-o)/10−10 m 1.75 1.80 1.85 1.90 1.95 2.00 2.05 2.10 − j /c m -1 0 20 40 60 80 100 120 140 fig. 2. magnetostructural correlation for [feiii(o)feiii] complexes by gorun and lippard (1991). regression line: 1 10 10[cm ] (2.360 × 10 ) exp( 10.661 [10 m])j p− −− = ⋅ − ⋅ , r2 = 0.95. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:00 utc 72 vranovičová, b. and boča, r. in can be seen that the data is aggregated to two clusters: one for short p ~ 1.8 å referring to a strongly negative j; the second cluster is around “normal” p ~ 1.95 – 2.00 å and it is associated with weakly negative j. the correlation of the above type excludes the occurrence of positive j (no such a data has been reported so far). there is a clear difference between the j-α correlations proposed for cu(ii) complexes and j-p correlations proposed for fe(iii) ones. therefore we tested some other variants of the magnetostructural correlations for fe(iii) complexes. p(fe-o)/10−10 m 1.75 1.80 1.85 1.90 1.95 2.00 2.05 2.10 j/ cm -1 -140 -120 -100 -80 -60 -40 -20 0 fig. 3. redrawn magnetostructural j-p correlation for fe(iii) complexes in a linear mode. first, the original (−j)-p correlation has been redrawn to the usual (+j)-p picture and subjected to the linear regression (fig. 3). the resulting regression line is 1 10[cm ] 525.7 [10 m] 1055j p− −= ⋅ − , r2 = 0.92, and it can be concluded that the correlation coefficient adopts the acceptable value. moreover, the linear relationship allows passing to the region of positive j. there are three datapoints in the intermediate region (p = 1.85 – 1.95) that do not fall the straight line (highlighted by a dot). however, a detailed inspection to the dataset reveals that these data refer to triangulo-[μ3-o-fe3] complexes where the bond angles are fixed to 120 deg so that the bond lengths are more constrained. there is another datapoint that does not match the linear correlation referring to the [fe(salen)cl]2 complex (marked by a cross). omission of these four points improves the regression to r2 = 0.958 that is a better value relative to the original exponential regression. second, the correlation j-α has also been tested for fe(iii) oxido-bridged complexes and the results are displayed in fig. 4. the problematic datapoint is marked by a cross and excluded from the correlation: 1 o[cm ] 3.98 [ ] 396j α− = − ⋅ + , r2 = 0.70. having some more datapoints at the disposal from recent structural and magnetic investigations (nesterov et al., 2012; chygorin et al., 2012; nesterova et al., 2013), the original dataset has been enlarged and subjected the linear regression (fig. 5). finally, the regression line is 1 10[cm ] 520.9 [10 m] 1047j p− −= ⋅ − , r2 = 0.93. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:00 utc nova biotechnologica et chimica 12-2(2013) 73 α(fe-o-fe) /o 90 100 110 120 130 140 150 160 170 j/ cm -1 -140 -120 -100 -80 -60 -40 -20 0 fig. 4. probing of magnetostructural correlation j-α in fe(iii) complexes using original dataset. a point excluded from the correlation is marked by a cross. p(fe-o)/10−10 m 1.75 1.80 1.85 1.90 1.95 2.00 2.05 2.10 j/ cm -1 -200 -150 -100 -50 0 fig. 5. magnetostructural correlation in fe(iii) complexes using enlarged dataset. two points excluded from the correlation are marked by cross. 3. conclusions it has been demonstrated that the original (exponential) magnetostructural jcorrelation for fe(iii) complexes with μ-oxido bridge suffers of a number of weaknesses. it can be substituted by a linear dependence that is approximately of the same quality. the original dataset can be enlarged by points obtained from recent magnetic and structural studies. the data need be filtered for the quality of the x-ray structure determination, different structural motif, and also the quality of experimental magnetic data-taking and theoretical analysis. acknowledgements: slovak grant agencies (vega 1/0233/12, apvv-0014-11) are acknowledged for the financial support. this article was created with the support of the ministry of education, science, research and sport of the slovak republic within the research and development operational programme for the bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:00 utc 74 vranovičová, b. and boča, r. project "university science park of stu bratislava", itms 26240220084, co-funded by the european regional development fund. references crawford, v. h., richardson, h. w. , wasson, j. r., hodgson, d. j., hatfield, w. e.: relation between the singlet-triplet splitting and the copperoxygen-copper bridge angle in hydroxo-bridged copper dimers. inorg. chem., 15 (9), 1976, 2107-2110. glerup, j., hodgson, d. j., pedersen, e.: a novel correlation between magnetism and structural parameters in superexchange coupled chromium(iii) dimers. acta. chem. scand., 37, 1983, 161-164. gorun, m. s., lippard, j. s.: magnetostructural correlations in magnetically coupled (μ-oxo)diiron (ii) complexes. inorg. chem.,, 30, 1991, 1625-1630. hatfield, w. e. in: willett, r. d., gatteschi, d., kahn, o. (eds.), magneto-structural correlations in exchange coupled systems, nato asi series. reidel, dordrecht, 1985, p. 555. hodgson, d. j. in: willet, r. d., gatteschi, d., kahn, o. (eds.), magnetostructural correlations in exchange coupled systems, nato asi series. reidel, dordrecht, 1985, p. 501. chygorin, e. n., nesterova, o. v., rusanova j. a., kokozay, v. n., bon, v. v., boča, r., ozarowski, a.: novel heterometallic schiff base complexes featuring unusual tetranuclear {coiii2fe iii 2(μ-o)6} and octanuclear {coiii4fe iii 4(μ-o)14} cores: direct synthesis, crystal structures, and magnetic properties. inorg. chem., 51, 2012, 386-396. law, n. a., kampf, j. w., pecoraro, v. l.: a magneto-structural correlation between the heisenberg constant, j adn the mn-o-mn angle in [mniv(μ-o)]2 dimers. inorg. chim. acta, 297, 2000, 252-264. nesterov, d. s., chygorin, e. n., kokozay, v. n., bon, v. v., boča, r., kozlov, y. n., shuľpina, l. s., jezierska, j., ozarowski, a., pombeiro, a. j. l., shuľpin, g. b.: heterometallic coiii4fe iii 2 schiff base complex: structure, electron paramagnetic resonance, and alkane oxidation catalytic activity. inorg. chem., 51 (16), 2012, 9110-9122. nesterova, o. v., chygorin, e. n., kokozay, v. n., bon, v. v., omelchenko, i. v., shishkin, o. v., titiš, j., boča, r., pombeiro, a. j. l., ozarowski, a.: magnetic, high-field epr studies and catalytic activity of schiff base tetranuclear cuii2fe iii 2 complexes obtained by direct synthesis. dalton trans., 42, 2013, 16909. thompson, l. k., mandal, s. k., tandon, s. s., bridson, j. n., park, m. k.: magnetostructural correlations in bis(μ2-phenoxide)-bridged macrocyclic dinuclear copper(ii) complexes. influence of electron-withdrawing substituents on exchange coupling. inorg. chem., 35, 1996, 3117-3125. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:00 utc microsoft word mikulasova nb 9-2.doc nova biotechnologica 9-2 (2009) 161 antimicrobial effects of essential oils from tanacetum vulgare l. and salvia officinalis l., growing in slovakia mária mikulášová1, štefánia vaverková2 1institute of cell biology, faculty of natural sciences, comenius university, mlynská dolina, bratislava, sk-842 15, slovak republic (mikulasovam@fns.uniba.sk) 2department of pharmacognosy and botany, faculty of pharmacy, comenius university, odbojárov 10, bratislava, sk83232, slovak republic (vaverkova@fpharm.uniba.sk) abstract: possible antimicrobial properties of essential oils isolated from tanacetum vulgare l., and salvia officinalis l., harvested from five different locations in slovakia, were examined using the disc agar diffusion method and by the microdilution method. gc/ms analysis of the essential oil from tanacetum vulgare l. resulted in the identification of 16 compounds constituting 82.1% of the total oil. gram-positive bacteria, mainly bacillus subtilis, were more susceptible to essential oils from both plants than were gramnegative species. tested essential oils posses also anti-yeast activity. the shares of the constituents in the essential oils as well as their antimicrobial activity differed in dependence on the locality. key words: essential oils, tanacetum, salvia, antimicrobial 1. introduction essential oils are volatile compounds of plant secondary metabolism, and may act as phytoprotective or insecticide agents. these compounds also have antibacterial and antifungal activity, which is important both for food preservation and control of human and plant diseases of microbial origin. the quality and yield of essential oils is influenced by many factors, such as fertilizer and ph of soil (alvarezcastelianos and pascual-villalobos, 2003), chemotype or subspecies (goren et al., 2001), choice of plant part (keskitalo et al., 2001), harvesting season (cornu et al., 2001), the choice and stage of drying conditions (tateo and riva, 1991) and extraction method (scalia et al., 1999). the content of some components of essential oils varies according to the geographic location. thus, 1,8cineole was the most abundant in the oil of sage from the usa (18.0%), camphor in the oil of romania (26.5%), caryophallene in the oil from the usa (10.0%), alphathujone in the oil from italy (45.8%), beta-thujone in the oil from romania (23.1%) (boelens and boelens, 1997). the composition of the essential oils from various chemotypes of tanacetum vulgare was studied in detail on populations of wild growing species in finland (keskitalo et al., 2001), norway (dragland et al., 2005), hungary, poland, italy, and others. in our previous work (vaverková et al., 2006) we examined qualitative properties of the essential oil obtained from tanacetum vulgare l. and we confirmed that the shares of the constituents in the essential oils differ in dependence on the location. the purpose of this work was to estimated and compared antimicrobial activity of extracts from tanacetum vulgare and salvia sp. from some geographic locations in slovakia. 162 mikulášová, m. and vaverková, s. 2. material and methods 2.1 plant material and gc/ms analyses of essential oils tanacetum vulgare l. and salvia officinalis l. were used as a testing material. collection of the plant has been carried in the phase of full flowering flower heads. twenty grams of dry flower heads were subjected to hydrodistilation for 3.5 hours in accordance to the european pharmacopoea. isolated oil was diluted in n-hexane and dried over anhydrous sodium sulphate. oil samples were analyzed using a hewlett packard hp 5971. a mass selective detector directly coupled to a gas chromtaograph hp 5890 series ii fid was used. a capillary column db-wax/26m x 0.20 mm, 0.2 mm film thickness (hewlett packard, usa) was used. detailed agro-ecological characteristics of individual locations are archived at the workplace of authors. 2.2 microbial strains bacterial strains escherichia coli ccm 3988, proteus mirabilis ccm 1941, staphylococcus aureus ccm 3953, micrococcus luteus ccm 732, bacillus subtilis ccm 1718 and the yeasts saccharomyces cerevisiae, candida albicans, candida parapsiloides and rhodotorula glutinis were obtained from the czech collection of microorganisms, brno, czech republic. 2.3 antimicrobial activity disc diffusion method nutrient agar plates were swabbed with the respective broth culture of the organisms (diluted to 0.5 mcfarland standard with saline). filter paper discs (6 mm in diameter) were impregnated with 5 μl of the extract and placed on the inoculated plates. these plates, after staying at 4°c for 2 h, were incubated at 37°c for 24 h for bacteria and at 28°c for 48 h for the yeasts. the diameters of the inhibition zones were measured in millimeters. determination of minimum inhibitory concentration was performed using broth microdilution method. the overnight growing culture of bacteria was filtered and 2% suspension of bacteria was prepared. 180 µl of this suspension and 20 µl of double diluted solutions of eo were placed into the wells of 96 well microtitre plates and cultivated for 24 h on reciprocal shaker at 37°c. the time course of absorbance (a630) was determined at 120 min intervals in triplicates. 3. results and discussion 3.1 chemical composition of the essential oil the following compounds were identified using gc/ms analysis in essential oil from tanacetum vulgare l., which constituted 82.1 % of total oil: α-pinene, camphene, sabinene, β-pinene, myrcene, 1,8-cineole, artemisia ketone, β-tujone, nova biotechnologica 9-2 (2009) 163 camphor, borneol, umbellulone, d-carvone, chrysantenyl-acetate, bornyl-acetate, thymol, germacrene and carvacrol. comparison of these results with those mentioned in literature indicates that these compounds are in the most cases the main components of tanacetum essential oils. the shares of the constituents in the essential oils differed in dependence on the location. 3.2 antimicrobial activity as seen in fig. 1, tested oils from tanacetum vulgare l., and salvia officinalis l. showed better activity against gram-positive bacteria than against gram-negative ones. a 0 5 10 15 20 25 t1 t2 t3 t4 t5 zo ne o f i nh ib it io n (m m ) b 0 5 10 15 20 25 s1 s2 s3 zo ne o f i nh ib it io n (m m ) e.coli p.mirabilis s.aureus m.luteus b.subtilis fig. 1. antibacterial activity of essential oils from tanacetum vulgare l. (a) and salvia officinalis l. (b) from different locations. 164 mikulášová, m. and vaverková, s. among the bacteria tested bacillus subtilis was the most sensitive to all eos. other gram-posititve bacteria show lower susceptibility to the essential oils. from gramnegative bacteria only escherichia coli was more susceptible to eo from salvia officinalis l. oil from one chemotype of tanacetum vulgare l. (t3) had very strong effect on both gram-negative bacteria, but oils from another chemotypes had only very slightly effect. according to kalodera et al. (1997), oils from tanacetum are effective on gram-negative bacteria. however, most studies investigating the antibacterial effects of essential oils confirmed, that they are more active against grampositive than gram-negative bacteria (randrianarivelo et al., 2009). our results indicate that this effect differs due to different chemotype of plant, as is state later. the comparative evaluation of essential oils from two distinct species of plants (tanacetum vulgare l., and salvia officinalis l.) showed variations in the level of activity against bacteria. these variations were evident from zones of inhibition as well from mic values. mic of essential oils from tanacetum ranged in all bacteria from <0.6 % to >>2.5 %. three essential oils from salvia had strong effect on micrococcus luteus and bacillus subtilis (mic <0.6 %). in gbacteria escherichia coli and proteus mirabilis mics of salvia essential oils ranged from <0.6 % to 2.5 %. samples of essential oils t1-t5 originated from the same plant species, were isolated using the same procedures and differ only by the geographic location of plants. as is evident from the comparison of inhibition zones (fig. 1) and mic values their antibacterial properties are different. t4 and t5 possess the lowest antibacterial effect and sample t3 posses the best one. mic of this eo in e. coli, proteus mirabilis and bacillus subtilis is <0.6%, only in micrococcus luteus is 2.5 %. essential oils were tested also for their effects on the yeasts. as is evident from the values of inhibition zones in fig. 2, the more susceptible to eo is candida albicans. also on this yeast, the most effective essential oils are t3 from tanacetum and s1 from salvia. a 0 2 4 6 8 10 12 14 16 t1 t2 t3 t4 t5 zo ne o f i nh ib it io n (m m ) nova biotechnologica 9-2 (2009) 165 b 0 2 4 6 8 10 12 14 16 18 s1 s2 s3 zo ne o f i nh ib it io n (m m ) s.cerevisiae c.albicans c.parapsilosis r.glutinis fig. 2. the effect of essential oils from tanacetum vulgare l. (a) and salvia officinalis l. (b) from different locations on the growth of yeasts. 4. conclusions from this study it can be concluded, that essential oils from tanacetum vulgare l. and salvia officinalis l. posse antibacterial and anti-yeast activity. it is known, that the chemical composition of essential oils from plants species can vary according to the geographical origin and harvesting period. individual components of essential oils exhibit different degrees of antimicrobial activity; therefore variation in composition between batches of essential oils from plants from different locations can be sufficient to cause variability in their antimicrobial effects. references alvarez-castelianos, p.p., pascual-villalobos, m.j.: effect of fertilizer on yield and composition of flowerhead essential oil of chrysanthemum coronarium (asteraceae) cultivated in spain. ind. crop prod., 17, 2003, 77-81. boelens, m. h., boelens, h.: chemical and sensory evaluation of three sage oils. perfum. flavor., 22, 1997, 9-39. cornu, a., camat, a.p, martin, b., coulon, j.p., lamaison, j.l., berdagué, j.l.: solid-phase micro-extraction of volatile components from natural grassland plants. j. agric. food chem., 49, 2001, 203-209. dragland, s., rohloff, j., mordal, r., iversen, t.h.: harvest optimization and essential oil production in five tansy (tanacetum vulgare l.) genotypes under a northern climate. j. agric. food chem., 53, 2005, 4946-53. goren, n., demirci, b., baser, k.h.c.: composition of the essential oils of tanacetum spp. from turkey. flavour frag. j., 16, 2001, 191-194. 166 mikulášová, m. and vaverková, s. kalodera, z., pepeljnak, s., blaževič, n., petrak, t.: chemical composition and antimicrobial activity of tanacetum parthenium essential oil. pharmazie, 52, 1997, 885-886. keskitalo, m., pehu, e., simon, j.e.: variation in volatile compounds from tansy (tanacetum vulgare l.) related to genetic and morphological differences of genotypes. biochem. system. ecol., 29, 2001, 267-285. randrianarivelo, r., sarter, s., odoux, e., brat, p., lebrun, m., romestand, b., menut, c., andrianoelisoa, h.s., raherimandimby, m., danthu, p.: composition and antimicrobial activity of essential oils from cinnamosma fragrans. food chem., 114, 2009, 680-684. scalia, s., giuffireda, l., pallado, p.: analytical and preparative supercritical fluid extraction of chamonile flowers and its comparison with conventional methods. j. pharm. biomed. anal., 21, 1999, 549-558. tateo, f., riva, g.: influence of the drying process on the quality of essential oils in artemisia absinthum. mitt.geb. leven. hyg., 82, 1991, 607-614. vaverková, š., mikulášová, m., habán, m., sloboda, p.: a study of qualitative properties of the essential oils of tanacetum vulgare l. čes. slov. farm., 55, 2006, 181-185. microsoft word kavsek nb 9-3.doc nova biotechnologica 9-3 (2009) 265 multivariate statistical methods for characterization of waste water quality darja kavšek1, darinka brodnjak vončina2 1regional technological centre zasavje, chemical-technological laboratory, nasipi 48, 1420 trbovlje, slovenia (darjakavsek@gmail.com) 2faculty of chemistry and chemical engineering, university of maribor, smetanova 17, 2000 maribor, slovenia (darinka.brodnjak@uni-mb.si) abstract: the aim of this work is focused on water quality classification of the waste waters and evaluation of pollution by the monitoring measurements during period 2006-2008. environmental monitoring was performed in the region of trbovlje, slovenia, with two sampling sites and 15 chemical and physicochemical water quality parameters (ph, temperature, suspended solids, settling matter, chemical oxygen demand, biochemical oxygen demand, aox (adsorbable organic halogens), total phosphorus, ammonium, nitrite, sulphate, chloride, fluoride, sulphide and mineral oil content) monitored in monthly periods (total of 60 objects x 15 variables). for handling the results different chemometric methods were employed, such as basic statistical methods for the determination of mean and median values, standard deviations, minimal and maximal values of measured parameters and their mutual correlation coefficients, the principal component analysis (pca), cluster analysis (ca), and linear discriminant analysis (lda). monitoring of general pollution of waste waters and following measuring parameters which are above permitted concentration level can be used for searching of pollution source and for planning prevention measures from pollution, as well. the study allows drawing new information from the data sets such as patterns of similarity between sampling locations, sources of pollution in the environment, seasonal behavior of chemical contents and time trends. key words: waste waters, water quality, chemometrics, principal component analysis, classification. 1. introduction the experimental data set, carried out throughout the years 2006-2008, was composed of analytical parameters from 2 waste water sources, first is the cave water from savski rov and the second is the industrial wastewater. through this period the quality of the water was followed and the classification has been made according to sampling sites. from 28 variables 15 variables, carrying the most useful information, were selected and investigated. the aim of this work is to find the correlation between sampling sites and the variables obtained by chemical measurements, which can be used to construct a fast decision model for separating different waste water quality samples. chemometric methods have been often used for the classification and comparison of different water samples (simeonova and simeonov, 2007; massart et al., 1997). some examples are, for instance, the differentiation of water sources in a vast southwest area of paris by principal component analysis (pca) (de luca et al., 2008), application of chemometric techniques to the analysis of suquia river water quality (alberto et al., 2001), identification of sources of bottom waters in the weddel sea by pca and target estimation (lindegren and josefson, 1998), 266 kavšek, d. and brodnjak-vončina, d. determination of correlation of chemical and sensory data in drinking waters by factor analysis (meng et al., 1997), to name just a few. chemometric methods have been used also for evaluating environmental data of lagoon water (carrer and leardi, 2006), san francisco bay and estuary (jarman et al., 1997), and muggia bay in northern adriatic sea (barbieri et al., 1998). the quality of the waste waters was studied through the years 2006-2008. altogether 15 preselected characteristic features were measured for 60 samples collected and analysed during this period. several chemometric methods were applied in order to visualize multivariate data and to enable a quick classification of samples, regarding the source location within the studied time period. 2. materials and methods a standard method was used for sampling (iso 5667-01:1996 (e)). water was collected in polyethylene bottles 0.5 m below the surface. all glass and plastic ware used for sampling and analyses were rinsed with milli-q water. standard analytical methods (water quality, 1980, 1996, 1998, 2000, 2002, 2004, 2005) were used for the determination of 15 physico-chemical variables. all reagents were analytical grade. the milli-q system was used for purifying the water. the 60 samples are characterized by 15 physico-chemical variables: (1) ph, (2) water temperature, (3) suspended solids, (4) settling matter, (5) chemical oxygen demand (6) biochemical oxygen demand, (7) adsorbable organic halogens (aox), (8) total phosphorus, (9) ammonium, (10) nitrite, (11) sulphate, (12) chloride, (13) fluoride, (14) sulphide, and (15) mineral oil content. the results of all measurements have been investigated by different chemometric methods (massart et al., 1997): the basic statistical methods for the determination of mean and median values, standard deviations, minimal and maximal values of measured variables and their mutual correlation coefficients. the pca was applied for grouping of water samples due to measured variables. all the calculations and plots in the following (pca) section were done with the teach/me software (teach/me datalab 2.002, 1999) using teach/me data analysis option. 3. results and discussion 3.1 statistical screening of data first the mean and median values and standard deviation were determined. after excluding 2 samples, which were discovered as outliers, namely, first sample with very high content of sulphate (more ten times higher than in all other samples, but still under the legislation permitted level) and the second one with high content of suspended solids. the mutual correlation was sought for all measured variables. the maximal correlation coefficient of the data was found between measurements of sulphate content and ph (r = -0.82) and between suspended solids and settling matter (r = 0.77). the correlation between suspended solids and settling matter is expected to be high. the negative correlation between sulphate content and ph shows that samples from two sampling sites are mainly differentiated according to these two parameters. nova biotechnologica 9-3 (2009) 267 fig. 1. dendrogram of 58 samples at 2 different sampling sites (classes). cluster analysis resulted in a dendrogram shown in fig. 1, where all 58 samples are divided into a number of clusters, depending on the level of similarity. clustering is based on ward distance. first group of samples, namely sampling site “savski rov” (the right-most cluster) is well distinguished from second sampling site. clusters of samples from sampling sites 1 and 2 are well defined. according to the content of pollution parameters from the previous mentioned sampling sites it can be concluded that sample 13 from sampling site 1 is different from all others and is clustered in cluster 2. 3.2 principal component analysis (pca) pca was performed in order to get an overall impression about the correlation of 58 water samples, described with physical and chemical variables, with the quality of water in different sampling sites. pca was applied on the matrix composed of 58x15 elements. 58 rows represent waste water samples composed of 15 variables. data were additionally pre-processed in two different ways. first the "column centering" of the data was used and second, the autoscaling of individual variables was performed, called "column standardization". the pca with column standardized data were further analysed for formed clusters. it was found from the score plots of the first and the second pcs that samples are well separated according to sampling sites. clusters of samples from sampling sites 1 and 2 are well defined. the scores and loadings plots of pca of the waste water samples represented with 15 variables are shown in figure 2. it is evident from figure 2 that samples from two sampling sites are well separated. the inspection of particular parameters shows that the content of sulphate is much higher for all samples from sampling site 1, while ph for all samples from sampling site 1 is always lower than for the sampling site 2 (fig. 4). 268 kavšek, d. and brodnjak-vončina, d. fig. 2. pca for all waste water samples from 2 different sampling sites denoted by class numbers 1 and 2. fig. 3. pca for 58 waste water samples from 2 different sampling sites; loadings in 15 pc axes are shown. fig. 4. ph value for all samples from two different sampling sites. nova biotechnologica 9-3 (2009) 269 separation of the two classes is obtained by pc1 (labels 1, 11 and 9, see fig. 3) which is accounted for the ph value and content of ammonium and sulphate, while the second principal component pc2 is accounted for suspended solids, settling matter and mineral oil content (labels 3, 4 and 15, see fig. 3). 3.3 linear discriminant analysis (lda) linear discriminant analysis confirms the predetermined classes. it was found from lda that samples are well separated according to sampling sites (fig. 5). plot of discriminant functions -6 -3 0 3 6 9 function 1 -2,3 -1,3 -0,3 0,7 1,7 2,7 f un ct io n 2 variety 0 1 2 centroids fig. 5. discriminant function for waste waters. 4. conclusions the study gives the opportunity to follow quality of waste waters at different sampling sites. monitoring of general pollution of waste waters and following measuring parameters which are above permitted concentration level can be used for searching of pollution source, for planning of prevention action and for the protection from pollution. references alberto, w.d., del pilar, d.m., valeria, a.m., fabiana, p.s., cecilia, h.a., de los angeles, b.m.: pattern recognition techniques for the evaluation of spatial and temporal variations in water quality, a case study: suquia river basin (cordoba-argentina). water res., 35, 2001, 2881-2894. barbieri, p., adami, g., favretto, a., reisenhofer, e., a chemometric survey of three sites in muggia bay (northern adriatic sea): meteorological effects on heavy metal patterns in surface coastal waters. fresenius j. anal. chem., 361, 1998, 349-352. carrer, s., leardi, r.: characterizing the pollution produced by an industrial area: chemometric methods applied to the lagoon of venice. sci. total environ., 370, 2006, 99-116. de luca, m., oliverio, f., ioele, d., husson, g. p., ragno, g.: monitoring of water quality in south paris district by clustering and simca classification. int. j. environ. anal. chem., 88, 2008, 1087-1105. 270 kavšek, d. and brodnjak-vončina, d. deutsche einheisverfahren zur wasser-, abwasserund schlammuntersuchung bestimmung des volumenanteils der absetzbaren stoffe im wasser und abwasser (h9), din 38409-h9-2:1980. deutsche einheitsverfahren zur wasser-, abwasserund schlammuntersuchung physikalische unf physikalisch-chemische bestimmung der temperatur (c4), din 38404:c4:2000. jarman, w.m., johnson, g.w., bacon, c.e., davis, j.a., risebrough, r.w., ramer, r.: levels and patterns of polychlorinated biphenyls in water collected from the san francisco bay and estuary, 1993-1995. fresenius j. anal. chem., 359, 1997, 254-260. massart, d.l., vandeginste, b.g.m., buydens, l.m.c., de jong, s. lewi, p.j., verbeke, j.s.: handbook of chemometrics and qualimetrics: part a, elsevier, amsterdam, 1997. meng, a.k., suffet, i.h.: a procedure for correlation of chemical and sensory data in drinking water samples by principal component factor analysis. environ, sci. technol., 31, 1997, 337-345. simeonova, p., simeonov, v.: chemometrics to evaluate the quality of water sources for human consumption. microchim. acta, 156, 2007, 315-320. teach/me, sdl software development lohninger; teach/me datalab 2.002, 1999, springer, berlin, developed by h. lohninger and the teach/me people. soil qualitydetermination of oil contentmethod by infrared spectrometry and gas chromatographic method, iso tr 11046 (e). water quality-samplingpart 10: guidance on sampling of waste water iso 5667-01: 1996 (e). water qualitydetermination of ph, iso 10523:1996 (e). water qualitydetermination of suspended solids by filtration through glass fibre filters, iso 11923:1998 (e). water qualitydetermination of chemical oxygen demand, iso 6060:1996 (e). water qualitydetermination of biochemical oxygen demand after n days (bodn)part 2: method for undiluted samples, iso 5815-2:2002 (e). water qualitydetermination of adsorbable organically bound halogens (aox), iso 9562:2005 (e). water qualitydetermination of phosphorusammonium molybdate spectrometric method, iso 6878:2004 (e). water qualitydetermination of ammoniumdistillation and titration method, iso 5664:1996 (e). water qualitydetermination of dissolved anions by liquid chromatography of ionspart 2: determination of bromide, chloride, nitrate, nitrite, orthophosphate and sulfate in waste water, iso 10304-2:1998(e). microsoft word nadaska nb 9-3.doc nova biotechnologica 9-3 (2009) 295 manganese fractionation analysis in specific soil and sediment samples gabriela nádaská, kristína polčová, juraj lesný department of biotechnology, university of ss cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic (pisarcig@ucm.sk) abstract: manganese has been determined in soiland sediment samples taken from selected regions with high manganese concentrations anthropogenic and/or geogenic. the total content of manganese in chosen sedimentand soil samples has been determined applying faas after microwave digestion and the manganese fractions after sequential extraction procedures using galvanostatic stripping chronopotentiometry. the highest content of manganese has been determined in sediment from hôrka (6243.6 ± 56.2 mg kg-1), while the lowest value has been obtained in the sediment from kráľová (278.6 ± 3.9 mg kg-1). using a modified tessier’s procedure it was found, that manganese in sediments from kráľová is associated mainly with the carbonate fraction (>50%), while in sediments from lozorno and hôrka it is associated primarily with the mn and fe oxide fraction (80% and 42% respectively). key words: manganese, galvanostatic stripping chronopotentiometry, fractionation analysis 1. introduction manganese is an essential micronutrient for all organisms, playing an important role in tissue and bone formation, in reproductive functions and in carbohydrate and lipid metabolisms (anjos et al., 2007), but at higher levels it can be toxic. in man, chronic manganese poisoning affects the central nervous system, with symptoms resembling those of parkinson’s disease. manganese toxicity is a serious constraint to crop cultivation since manganese is taken-up by plants and can easily be passed into the food chain (khoo et al., 1996; banks et al., 2005; pearson and greenway, 2005). therefore, the determination of manganese in several matrices samples is very important for some areas, such as environmental chemistry and food control (lemos et al., 2008). measurement of total metal concentrations is useful to evaluate the heavy metal burden but their mobility depends strongly on their specific chemical forms or ways of binding. however, the determination of specific chemical species or binding forms is as a rule very complex and often hardly possible. for this reason, sequential extraction procedures are commonly applied because they provide information about the fractionation of metals in the different lattices of the solid sample which is a good compromise to give information on environmental contamination risk (marguí et al., 2004). for manganese determination highly sensitive methods are required. various techniques have been used for the determination of trace manganese in biological and environmental samples, such as spectrophotometry and atomic absorption spectrometry. however the electronalytical techniques such as stripping analysis, which incorporate a preconcentration step, e.g. stripping voltammetry and stripping 296 nádaská, g. et al. chronopotentiometry are the most used in trace metal determination in complex samples. these techniques have been shown to be suitable, versatile and rapid for multicomponent analysis, having good selectivity and adequate sensitivity (town and leeuwen, 2001; filipe et al., 2003). 2. materials and methods 2.1 samples soils and sediments analyzed in this study were collected from regions with high concentrations of anthropogenic and/or geogenic manganese at five sampling sites: kráľová (n 48°12'35''; e 17°48'02''), lozorno (n 48°32'83''; e 17°05'85''), kišovce (n 49°01'18''; e 20°37'95''), primovce (n 49°01'18''; e 20°37'95'') and hôrka (n 49°01'18''; e 20°39'06''). soil samples were taken from top layer (horizon a; 0-15 cm) and subsurface substrate (35-45 cm). the samples were air-dried, homogenized, screened through a 0.3 mm sieve, and stored for subsequent analysis. 2.2 mineralization soil and sediment samples (0.25 g) have been transferred into ptfe digestion vessels and digested with 2 ml of conc. hcl and 5 ml of conc. hno3 in a microwave oven multiwave mw 3000 (anton paar gmbh, austria) according to the following working conditions: 210°c; 30 min; 40 bars. the acid solution was diluted to 25 ml and the metal content was determined by faas using the atomic absorption spectrometer varian spectraa-200 (varian inc., australia). 2.3 sequential extraction procedure the sequential extractions have been performed using the modified tessier’s procedure on 1 g of soil and sediment samples. the relevant procedure is described in table 1. table 1. sequential extraction procedure. extracted fraction procedure f1exchangeable 1.0 g sample; 8 ml 1 m mgcl2 (ph=7), 1 h agitation; room temperature, centrifugation 4000 rpm, 5 min; rinsing of solid residue with 3 ml deionized h2o; centrifugation 4000 rpm, 5 min f2bound to carbonates solid residue from step 1; 8 ml 1 m naoac (ph=5), 5 h agitation; room temperature, centrifugation 4000 rpm, 5 min; rinsing of solid residue with 3 ml deionized h2o; centrifugation 4000 rpm, 5 min f3bound to fe-mn oxides/reducible solid residue from step 2; 8 ml 0.1 m nh2oh.hcl (ph=2), 16 h agitation; room temperature, centrifugation 4000 rpm, 5 min; rinsing of solid residue with 3 ml deionized h2o; centrifugation 4000 rpm, 5 min f4oxidisable solid residue from step 2; 8 ml 30% h2o2, 5 h agitation; room temperature, centrifugation 4000 rpm, 5 min; rinsing of solid residue with 3 ml deionized h2o; centrifugation 4000 rpm, 5 min nova biotechnologica 9-3 (2009) 297 2.4 galvanostatic stripping chronopotentiometry (scp) the amount of mn in obtained fractions after evaporation and dissolving in electrolyte has been determined by galvanostatic stripping chronopotentiometry using the flow-through system ecaflow model glp 150 (istran ltd., slovakia). for the determination, stripping chronopotentiometry on a macroporous electrode has been applied. at suitable positive potential mn(ii) is deposited from a slightly acidic solution on the electrode surface as a hydrate oxide: −+ − + ++→ ehohohmnohmn xx 3)()()( 332 2 2 in the next step the deposit is stripped applying a constant negative current. during this step the signal (chronopotentiogram) is recorded and the concentration of mn in the sample is evaluated. the compact flow-through electrochemical cell ecacell 104, ag/agcl reference electrode and carbon porous working electrode e-104 has been used. basic (carrier) electrolyt solution of 0.1 mol dm-3 na2so4 + 0.01 mol dm -3 nah2po4 and reagent solution of 0.1 mol dm-3 hcl has been used. standard solutions 50 μg dm-3, 100 μg dm-3 and 200 μg dm-3 mn(ii) were prepared from certified reference material (merck). deionised water (conductivity of 0.054 μs cm-1) has been used for all solutions. in all experiments analytical grade reagents were used. table 2 shows the applied experimental parameters for mn determination using scp. table 2. experimental conditions for the determination of mn (www.istran.sk). d e p o s i t i o n p o t e n t i a l 1 1 0 0 m v d e p o s i t i o n t i m e 6 0 s i n i t i a l p o t e n t i a l 1 1 0 0 m v f i n a l p o t e n t i a l 5 0 0 m v d i s s o l u t i o n c u r r e n t 2 5 μa t i m e o f s t a b i l i z a t i o n 1 0 s m a x . t i m e o f s t r i p p i n g 1 2 0 s r e g e n e r a t i o n p o t e n t i a l 4 0 0 m v t i m e o f r e g e n e r a t i o n 1 0 s v o l u m e o f s a m p l e 1 m l „ s t a n d b y “ p o t e n t i a l 6 5 0 m v 3. results and discussion the total mn concentrations and the manganese fractions obtained by the chosen sequential extraction procedures are shown in tables 3-5. samples from kráľová contain anthropogenic manganese markedly derived from waste dump of a former nickel smelter in sereď. manganese in sediments has been found only in carbonate fraction. this is caused evidently by higher ph values of the water reaching 8.2. manganese in soil samples from the same site has been bound to fe-mn oxides in higher proportion, while significant differences of its abundance in different soil horizons have not been observed. 298 nádaská, g. et al. the total mn concentrations of investigated soil samples show similar values as well. our results show for manganese concentrations in soils in comparison with the ones in sediments higher values. we assume that for soils floods may act as a not negligible source of mn. in the same time by lower ph values caused by acid rains the soluble mn species reach the deeper soil horizons. table 3. concentrations of mn in samples of stream sediments after modified tessier’s extraction procedure. concentration of mn ± sd in fractions [mg kg-1] sample f1 f2 f3 f4 total concentration of mn ± sd [mg kg-1] kráľová 141.4 ± 2.9 278.6 ± 3.9 lozorno 48.2 ± 3.6 645.8 ± 22.1 779.9 ± 10.9 hôrka 594.9 ± 2.1 2586.8 ± 56.1 219.5 ± 0.2 6243.6 ± 56.2 kišovce 209.9 ± 12.8 50.3 ± 6.7 2.4 ±0 .8 617.3 ± 13.6 primovce 969.1 ± 5.2 516.6 ± 11.3 45.2 ± 0.4 3219.8 ± 61.2 0 10 20 30 40 50 60 70 80 90 primovce (3219.8) kišovce (617.3) hôrka (6243.6) lozorno (779.9) kráľová (278.6) f1-exchangeable fraction f2-fraction bound to carbonates f3-fraction bound to fe-mn oxides f4-oxidisable fraction m n fr ac tio n [% ] fig. 1. percentual abundance of mn in particular fractions using modified tessier’s extraction procedure in sediment samples (data under the graph represent total manganese concentrations [mg kg-1] determined by faas). table 4. concentrations of mn in soil samples taken from horizon a after modified tessier’s extraction procedure. concentration of mn ± sd in fractions [mg kg-1] sample f1 f2 f3 f4 total concentration of mn ± sd [mg kg-1] kráľová 101.2 ± 4.0 145.9 ± 1.8 14.7 ± 0.6 733.2 ± 10.9 lozorno 27.4 ± 0.9 471.6 ± 3.3 590.1 ± 7.08 kišovce 145.4 ± 9.2 309.6 ± 5.4 85.7 ± 27.9 1339.7 ± 26.8 primovce 498.9 ± 6.4 620.9 ± 23.9 167.6 ± 4.1 2426.6 ± 16.9 nova biotechnologica 9-3 (2009) 299 0 10 20 30 40 50 60 70 80 m n fr ac tio n [% ] f1-exchangeable fraction f2-fraction bound to carbonates f3-fraction bound to fe-mn oxides f4-oxidisable fraction primovce (2426.6) kišovce (1339.7) lozorno (590.1) kráľová (733.2) fig. 2. percentual abundance of mn in particular fractions of the modified tessier’s extraction procedure in soil samples taken from horizon a (data under the graph represent total manganese concentrations [mg kg-1] determined by faas). table 5. concentrations of mn in soil samples taken from subsurface substrate after modified tessier’s extraction procedure. concentration of mn ± sd in fractions [mg kg-1] sample f1 f2 f3 f4 total concentration of mn±sd [mg kg-1] kráľová 79.9 ± 5.4 198.3 ± 6.1 32.3 ± 0.6 757.7±12.1 lozorno 4.5 ± 0.4 343.2 ± 5.3 446.6±15.2 kišovce 81.8 ± 6.6 65.5 ± 1.2 8.9 ± 0.5 488.1±8.3 primovce 298.9 ± 32.3 952.8 ± 126.6 248.3 ± 15.2 2620.8±28.8 0 10 20 30 40 50 60 70 80 m n fr ac tio n [% ] f1-exchangeable fraction f2-fraction bound to carbonates f3-fraction bound to fe-mn oxides f4-oxidisable fraction primovce (2620.8) kišovce (488.1) lozorno (446.6) kráľová (757.7) fig. 3. percentual abundance of mn in particular fractions of the modified tessier’s extraction procedure in soil samples taken from subsurface substrate (data under the graph represent total manganese concentrations [mg kg-1] determined by faas). 300 nádaská, g. et al. acidic soils are typical for zahorie region. this is evidently caused by chemically inactive soil constituents. both, iron and manganese as well, are at oxidizing conditions in higher oxidation states and so they are present in precipitated chemical forms. in such conditions major proportions of iron and manganese in sediments as well as in investigated soil horizons are bound to fe and mn oxides. the highest contents of total manganese have been measured in samples taken from hôrka, kišovce and primovce. this region is known as one with high geogenic manganese concentrations. at lower ph values the carbonate system consists of hydrogen carbonates predominantly and manganese is in such conditions soluble. according to our observation sediments near hôrka contain extremely high manganese concentrations. this fact is avowedly caused by former mining activity. we found that manganese is in this region predominantly bound to mn-fe oxides caused apparently by oxidation of manganese originated from mining activity. fig. 4. typical chronopotentiograms obtained by manganese determination using scp. 4. conclusions results of fractionation experiments prove that the type of manganese coupling to the sedimentand soil matrix is strongly affected by factors connected to geological bedrock as well as to relevant ph values. in regions with low ph values the carbonate system consists mostly from hydrogen carbonates and at such conditions manganese is soluble. for this reason manganese in sediments from lozorno and hôrka is present in fraction bound to fe-mn oxides, namely 80% and 42% respectively. in regions with higher ph values the solubility of carbonates is low. manganese in sediment from kráľová is bound to carbonates, namely >50%. standard 100 μg dm-3 standard 200 μg dm-3 standard 50 μg dm-3 sample nova biotechnologica 9-3 (2009) 301 references anjos, a.p, ponce, l.c., cadore, s., baccan, n.: determination of manganese by flame atomic absorption spectrometry after its adsorption onto naphthalene modified with 1-(2-pyridylazo)-2-naphtol (pan). talanta, 71, 2007, 1252-1256. banks, c.g., kruusma, j., moore, r.r., tomčík, p., peters, j., davis, j., lovrić, š.k., compton, r.g.: manganese detection in marine sediments: anodic vs. cathodic stripping voltammetry. talanta, 65, 2005, 423-429. beinrohr, e.: determination of mn in clean as well as turbid water samples, application list no.74. istran ltd., slovakia. http://www.istran.sk/en/ download/start-download/english/application-lists/33-application-listno.74.html filipe, o.m.s, brett, c.m.a.: cathodic stripping voltammetry of trace mn(ii) at carbon film electrodes. talanta, 61, 2003, 643-650. khoo, s.b., soh, m.k., cai, q., khan, m.r., guo, s.x.: differential pulse cathodic stripping voltammetric determination of manganese(ii) and manganese(vii) at the 1-(2-pyridylazo)-2-naphtol-modified carbon paste electrode. electroanalysis, 9, 1997, 45-51. lemos, v.a., baliza, p.x., carvalho, a.l., oliveira, r.v., teixeira, l.s.g., bezerra, m.a.: development of a new sequential injection in-line cloud point extraction system for flame atomic absorption spectrometric determination of manganese in food samples. talanta, 77, 2008, 388-393. marguí, e., salvadó, v., queralt, i., hidalgo, m.: comparison of threestage sequential extraction and toxicity characteristic leaching tests to evaluate metal mobility in mining wastes. anal. chim. acta, 524, 2004, 151-159. pearson, g.p, greenway, g.m.: recent developments in manganese speciation. trends anal. chem., 24, 2005, 803-809. town, r.m., leeuwen, h.p.: fundamental features of metal ion determination by stripping chronopotentiometry. j. electroanal. chem., 509, 2001, 58-65. microsoft word fargasova nb 9-2.doc nova biotechnologica 9-2 (2009) 107 cr and ni simultaneous phytotoxicity and mutagenicity assay agáta fargašová, jana lištiaková department of ecosozology and physiotactics, faculty of natural sciences, comenius university in bratislava, mlynská dolina, sk-842 15 bratislava, slovak republic (fargasova@fns.uniba.sk) abstract: for genotoxicity study simultaneous phytotoxicity and mutagenicity assay with vicia sativa l. var. klára was used. for phytotoxicity the following rank orders of growth inhibition can be arranged: for roots: ni(ii) > cr(vi) > cr(iii); for shoots: ni(ii) > cr(vi) ≥ cr (iii). for mutagenicity assay root tips of v. sativa were used and chromosome aberrations were determined at least in 500-anatelophases. all tested metals exerted in v. sativa a significant increase of chromosomal aberration rate in applied concentrations. maximum of aberrations invoked cr(vi) and the rank order of aberrations fall was: cr(vi) > ni(ii) > cr(iii). genotoxic effects of metals were determined by analysis of micronuclei frequency in the pollen tetrads of tradescantia plants. none of tested metal significantly stimulated micronuclei frequency and genotoxic effect was decreased in order: cr(vi) ≥ ni(ii) > cr(iii). key words: chromium, nickel, vicia sativa, phytotoxicity, chromosomal aberation assay, tradescantia micronucleus assay 1. introduction vascular plants have been found to be highly effective for recognizing and predicting metal stress in the environment (growth inhibition, reduction of biomass production, changes in water absorption and translocation) (shanker et al., 2005; szárazová et al., 2008). for genotoxicity studies are plants highly responsible and sensitive. their beneficial interest is that seeds and pollen grains can be easy storage away and offer cheap, relative easy and accurate toxicological assessment (kristen, 1997). by their ability to accumulate toxic substances, they indicate metal presence in the environment even in very low concentration (chandra, 2004). contamination of soil and water by cr and ni are of particular recent concern. the impact of cr contamination on the physiology of plants depends on the metallic species responsible for its mobilization, uptake and toxicity in the plant system (bennicelli et al., 2004). while cr is not considered an essential element for plant nutrition (sharma et al., 1995), ni is classified an essential trace element (brown et al., 1987); and although it is found everywhere in the environment, it usually occurs only in trace amounts. 2. materials and methods simultaneous phytotoxicity and mutagenicity assay was carried out on plant species vicia sativa l. var. klára according to miadoková et al. (2005). after 24 h of soaking at 25 °c in distilled water or solution with metal concentration equal to ic50 value the seeds of v. sativa were allowed to germinate in petri dishes (diameter = 18.5 108 fargašová, a. and lištiaková, j. cm) with filter paper soaked with the same concentration of tested metal as that used for soaking. phytotoxicity was assayed after 72 h of the dark cultivation in the thermostat at 25 °c by the same way as described previously svetková and fargašová (2007) for s. alba. the roots and shoots of v. sativa seedlings were measured and the growth inhibition percentage was assessed. the seedling roots used for chromosome and genome mutability evaluation were fixed and permanent slides were prepared by the feulgen method. chromosome aberrations were determined at least in 500-anatelophases. for statistic analysis the student’s t-test was used. the procedures for maintaining the tradescantia plants and for analyzing micronuclei frequency in the tetrads have been described by mišík et al. (2006; 2007). tradescancia paludosa clone 03 was standardly cultivated at the department of botany, faculty of natural sciences, comenius university in bratislava. inflorescence were harvested at the 8-10-buds stage and immersed into 500 ml of tested metal solutions (100 mg/l cro3 and nicl2, 1000 mg/l cr(no3)3) for 12 h. as control tap water was used. the 24 h reconvalescence, during which inflorescence peduncles were dipped in 500 ml of tap water, succeeded to 12 h exposure. then the buds were fixed for 24 h in ethanol : acetic acid (3 : 1). the fixed material was stored in 70% ethanol. slides were prepared from the fixed material using the aceto-carmine squash technique. micronuclei were scored in the early tetrad stages of pollen mother cells. in the present study, 15 to 20 inflorescences comprised a sample. three hundred tetrads were scored from each of five slides prepared from a treatment sample for a total of 1,500 tetrads per plot. data were recorded as the number of micronuclei (mcn) per 100 tetrads. a change of frequency of mcn/100 tetrads was considered statistically significant (at p < 0.05) if the difference between the mean of the control population and the mean of the treated population was at least twice as large as the standard error of the difference between the two means (ma et al., 1994; mišík et al., 2007). for samples of tested metals nicl2.6h2o, cr(no3)3.9h2o and crco3 of analytical grade p.a. were obtained from lachema, brno, czech republic. all experiments for growth inhibition were set up in a completely randomized design with three replicates. chronic toxicity was assessed as inhibition of roots and shoots growth and results were evaluated by gryck-haustein method and ic25, ic50 and ic75 concentrations were determined. the results were statistically evaluated by using toxicity program. 3. results and discussion toxic effects of heavy metals, mainly during chronic exposure, are not visible immediately hence ecotoxicological studies request also assessment of genotoxicity. genotoxicological effect is developed then the concentration is low order than that for fytotoxicity effect (mičieta and murín, 1998). for phytotoxicity and clastogenicity study v. sativa seedlings were used. phytotoxicity was determined through ic25, ic50 and ic75 values and for roots and shoots the strongest inhibitory effect had ni(ii) (fig. 1). no significant differences were confirmed between cr(iii) and cr(vi) adverse effects on v. sativa shoot growth. on the basis of these values, and their statistical evaluation, metals can be arranged in the following rank orders of inhibition: for roots: ni(ii) > cr(vi) > cr(iii); for shoots: ni(ii) > cr(vi) ≥ cr (iii). nova biotechnologica 9-2 (2009) 109 fig. 1. ic25, ic50 and ic75 values and their 95% confidence intervals (ci) (ml/l) for vicia sativa l. after 72 h application; the mean of three determinations with a standard deviation 6% or less for mutagenicity assay root tips of v. sativa were used and chromosome aberrations were determined at least in 500-anatelophases. all tested metals exerted in v. sativa a significant increase of chromosomal aberration rate in applied concentrations (table 1). from all tested metals cr(vi) invoked maximum of aberrations in anatelophase cells. the rank order of aberrations fall was: cr(vi) > ni(ii) > cr(iii). table 1. potential clastogenicity evaluation of cr and ni in vicia sativa l. (n = 500) metal concentration (mg/l) metal ni cr number of aberrations ± sd percentage of aberrations ± sd control <0.07 <0.01 7 ± 0.69 2.33 ± 0.23 ni(ii) 16.46 ± 2.16 10 ± 0.75 ** 3.33 ± 0.25 ** cr(iii 114.41 ± 13.36 8 ± 0.75 * 2.67 ± 0.25 * cr(vi) 69.69 ± 8.66 13 ± 0.69 ** 4.33 ± 0.23 ** sd – standard deviation; ** significant differences in comparison with control at p <0.01; * significant differences in comparison with control at p <0.05; control – sterile distilled water genetic variation in susceptibility to environmental agents and metals can be considered as differences in metabolism of these agents in various organisms (omenn, 1991). in addition, dna target size and dna content are also important in determining genotoxic hazard of metals. as described kovalchuk et al. (1998) and chauhan et al. (1998) genotoxicity can be obtained as a result of multipolar anaphase and c-mitose or damage of protein synthesis in the presence of dna 110 fargašová, a. and lištiaková, j. toxicant. simultaneous toxicity and clastogenity of wastes with cr and ni content was also confirmed for v. sativa by miadoková et al. (1999) and for v. faba and allium cepa by chandra et al. (2004; 2005). chromozomal fragments and bridges created in cr(vi) presence indicated as introduced quian (2004) that cro3 affecting dna structure and conformation. table 2. micronuclei frequency in the tradescantia pollen tetrads after treatment with cr and ni solutions (n = 1,500) metal concentration (mg/l) metal ni cr number of micronuclues ± sd percentage of micronucleus ± sd control <0.07 <0.01 43 ± 13.74 2.89 ± 0.92 ni(ii) 24.71 ± 0.25 59 ± 17.48 3.93 ± 1.17 cr(iii 130.00 ± 1.30 47 ± 16.61 3.13 ± 1.11 cr(vi) 52.00 ± 0.52 60 ± 15.98 4.00 ± 1.07 sd – standard deviation for determination of cr and ni genotoxic effects was also used analysis of micronuclei frequency in the pollen tetrads of tradescantia plants. as it is evident from table 2 none of tested metal significantly stimulated, in comparison with the control, micronuclei frequency and genotoxic effect was decreased in order: cr(vi) ≥ ni(ii) > cr(iii). tradescantia micronucleus test (trad-mcn) belongs together with allium cepa l. and vicia faba l. tests with root tips to most frequently used genotoxicity tests on plants (majer et al., 2005) and it is very popular now for in situ biomonitoring of air pollution (mišík et al., 2006; 2007). results obtained during our genotoxicity tests are in good agreement with those introduced by knasmüller et al. (1998) when cro3, crcl3 and nicl2 up to concentration 10 mm did not evoke genotoxic effects. the same conclusion also introduced majer et al. (2005) for cr(iii). higher genotoxicity of cr(vi) than cr(iii) determined during our experiments also described němeček et al. (2002). rossman (1995) introduced that molecular mechanism of dna damage by cr(vi) involve induction of dna-dna and dnaprotein cross-links and genotoxic effect can be also increased by reactive oxygen produced during intracellular reduction. for ni(ii) no genotoxic effects confirmed for bacteria rossman (1995) and patierno and costa (1987) introduced that mutations after ni applications are also the result of dna damage and dna-protein cross-links formation. acknowledgements this study was supported by grants vega 1/4361/07, vega 1/0238/08 and apvv – 0231-07. references bennicelli, r., stepniewska, z., banach, a., szajnocha, k., ostrowski, j.: the ability of azolla caroliniana to remove heavy metals (hg(ii), cr(iii), cr(vi)) from municipal waste water. chemosphere, 55, 2004, 141146. nova biotechnologica 9-2 (2009) 111 brown, p.h., welch, r.m., cary, e.e.: nickel: a micronutrient essential for higher plants. plant physiol., 85, 1987, 801−803 chandra, s., chauhan, l.k.s., pande, p.n., gupta, s.k.: cytogenetic effects of leachates from tannery solid waste on the somatic cells of vicia faba. environ. toxicol., 19, 2004, 129-133. chandra, s., chauhan, l.k.s., murthy, r.c., saxena, p.n., pande, p.n., gupta, s.k.: comparative biomonitoring of leachates from hazardous solid waste of two industries using allium test. sci. total environ., 347, 2005, 46-52. chauhan, l.k.s., saxena, p.n., sundararaman, v., gupta, s.k.: diuron-induced cytological and ultrastructural alterations in the root meristem cells of allium cepa. pestic. biochem. physiol., 62, 1998, 152-163. knasmüller, s., gottmann, e., steinkellner, h., fomin, a., pickl, c., paschke, a., god, r., kundi, m.: detection of genotoxic effects of heavy metal contaminated soils with plant bioassays. mutat. res., 420, 1998, 37-48. kovalchuk, o., kovalchuk, i., arkhipov, a., telyuk, p., hohn, b., kovalchuk, l.: the allium cepa chromosome aberration test reliably measures genotoxicity of soils of inhabited areas in the ukraine contaminated by the chernobyl accident. mutat. res., 415, 1998, 47-57. kristen, u.: use of higher plants as screens for toxicity assessment. toxicol. vitro, 11, 1997, 181-191. ma, t.h., cabrera, g.l., chen, r., gill, b.s., sandhu, s.s., vanderberg, a.l., salamone, m.f.: tradescantia micronucleus bioassay. environ. health perspect., 95, 1994, 157-189. majer, b.j., grummt, t., uhl, m., knasmüller, s.: use of plant bioassays for the detection of genotoxins in the aquatic environment. acta hydrochim. hydrobiol., 33, 2005, 45-55. miadoková, e., dúhová, v., vlčková, v., sládková, l., suchá, v., vlček, d.: genetic risk assessment of acid waste water containing heavy metals. gen. physiol. biophys., 18, 1999, 92-98. miadoková, e., svidová, s., vlčková, v., dúhová, v., pražmáriová, e., tothová, k., naďová, s., kogan, g., rauko, p.: the role of natural biopolymers in genotoxicity of mutagens/carcinogens elimination. biomed. pap. med. fac. univ. palacky olomouc czech rep., 149, 2005, 493-496. mičieta, k., murín, g.: tree species of genus pinus suitable as bioindicators of polluted environment. water air soil pollut., 104, 1998, 413-422. mišík, m., solenská, m., mičieta, k., mišíková, k., knasmüller, s.: in situ monitoring of clastogenicity of ambient air in bratislava, slovakia using the tradescantia micronucleus assay and pollen abortion assays. mutat. res./genet. toxicol. environ. mutagen., 605, 2006, 1-6. mišík, m., mičieta, k., solenská, m., mišíková, k., pisarčíková, h., knasmüller, s.: in situ biomonitoring of the genotoxic effects of mixed industrial emissions using the tradescantia micronucleus and pollen abortion tests with wild life plants: demonstration of the efficacy of emission controls in an eastern european city. environ. pollut., 145, 2007, 459-466. 112 fargašová, a. and lištiaková, j. němeček, j., podlešáková, e., vácha, r.: transfer of trace elements with low soil mobility into plants. rostl. výr., 48, 2002, 45-50. omenn, g.s.: future research direction in cancer ecogenetics. mutat. res., 247, 1991, 283-291. patierno, s.r., costa, m.: effect of nickel ii on nuclear protein binding in intact mammalian cells. cancer biochem. biophys., 9, 1987, 113-126. quian, x.: mutagenic effects of chromium trioxide on root tip cells of vicia faba. j. zhejiang univ. sci., 5, 2004, 1570-1576. rossman, t.g.: metal mutagenesis. in: r.a. goyer, g.c. cherian (eds.) toxicology of metals. springer, new york, 1995, 373-430. shanker, a.k., cervantes, c., loza-tavera, h., avudainayagam, s.: chromium toxicity in plants. environ. int., 31, 2005, 739-753. sharma, d.c., chatterjee, c., sharma, c.p.: chromium accumulation and its effects on wheat (triticum aestivum l. c.v. dh 2204) metabolism. plant sci., 111, 1995, 145−151 svetková, k., fargašová, a.: phytotoxicity of washing waste waters from cutlery production line. bull. environ. contam. toxicol., 79, 2007, 109-113. szárazová, k., fargašová, a., hiller, e., velická, z., pastierová, j.: phytotoxic effects and translocation of cr and ni in washing wastewaters from cutlery production line to mustard (sinapis alba l.) seedlings. fresenius environ. bull., 17, 2008, 58-65. microsoft word uhrovcik et al nbc12-2.doc nova biotechnologica et chimica 12-2 (2013) 93 doi 10.2478/nbec-2013-0011 © university of ss. cyril and methodius in trnava possibility of the spectrophotometric determination of europium by means of arsenazo iii jozef uhrovčík, monika gyeváthová, juraj lesný department of ecochemistry and radioecology, university of ss. cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic (jozef.uhrovcik@ucm.sk) abstract: the concentration of eu(iii) cations in model aqueous solutions can be quantified by means of arsenazo iii reagent. absorbance of the solution was measured at the wavelength λmax = 655 nm. molar absorptivity reached the value ε655 = 5.5±0.2 · 104 cm-1 mol-1 · dm3. beer's law was obeyed in the range from 0 to 2 mg · dm-3 eu(iii). the value of limit of detection was established by application of 3σ approach and reached the value of 20.9 μg · dm-3. repeatability of analysis expressed by relative standard deviation does not exceed the value of ± 8% and apparent recovery lay in acceptable range from 91 to 106 %. stoichiometry between eu(iii) and arsenazo iii in media of relevant solution was 1:1. the absorbance of the solutions within the linear range of the proposed method maintained a constant value for 60 minutes. described procedure can be utilized to determination of eu(iii) concentration in real samples, but it is necessary eliminate interfering ions. cations like la(iii), sm(iii), th(iv), u(vi) and complexing agent edta cause significant error at the determination of eu(iii) in model solution. presented spectrophotometric method could be applied for the determination of europium in the minerals and water samples, however after a suitable separation and preconcentration of target analyte. key words: europium, arsenazo iii, spectrophotometry, limit of detection. 1. introduction europium is a soft silvery white metal which belongs to the lanthanide family. it was discovered in 1896 and isolated in 1901 by eugène-anatole demarçay (heiserman, 1992); its atomic number is 63 and atomic weight is 151.96. europium can exist in two oxidation states, namely eu(ii) and eu(iii) and the latter represents its most stable oxidation form. majority of europium is obtained from monazite sand, which is a mixture of phosphates of calcium, thorium, cerium and most of the other rare earth metals. europium can be separated from the rare earth metals first of all by precipitation (blazejak-ditges, 1970). the result of this process is formation of europium oxide, eu2o3. europium in metal state can be prepared by mixing with powdered lanthanum metal in a tantalum crucible. various methods have been developed for the determination of rare earth metals including europium. they include spectrofluorimetry (takatatsu and sato, 1979; yamada et al., 1982), polarography (fu et al., 1993), voltammetry (mlakar and branica, 1991), atomic emission spectroscopy with inductively coupled plasma (daskalova et al., 1996) and mass spectrometry with inductively coupled plasma (zang et al., 1995). however, all these procedures are troublesome or the instruments are not readily available. therefore, there is the need for suitable laboratories equipped with inexpensive instrumentation, which allows the determination of europium to be carried bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:08 utc 94 uhrovčík, j. et al. out in a fast and cheap way without sacrificing precision. spectrophotometric method is an alternative that satisfies these requirements and can be afforded by most laboratories. in the present time exists some spectrophotometric methods suggested for the determination of traces of europium in different types of samples, for example (fang et al., 1999; poluektov et al., 1971; stoyanov et al., 2011). arsenazo iii is reported to be suitable primarily for the photometric determination of lanthanides and actinides (savvin, 1961; savvin 1964). it is commercially available and soluble in water and diluted acids. the reagent has ability to form stable chelates and can work in strongly acidic medium eliminating the chances of partial hydrolysis of metal ions to be determined. its sensitivity due to color reaction is quite high (0.05–0.01 μg cm-3 of the element). the high sensitivity and stability is coupled with a well-defined contrast in color transition from pinkish (reagent) to blue-green or raspberry-red (complex with arsenazo iii) (basargin et al., 2000). in this paper is described the spectrophotometric method for determination of europium using arsenazo iii as chromogenic reagent in buffer medium. 2. material and methods 2.1 chemicals and reagents all used reagents were of analytical grade and were prepared in deionized water. stock solution of eu(iii) with mass concentration m = 10.0±0.1 mg · dm-3 was prepared by appropriate dilution of standard solution (fluka analaytical, austria). 100 cm3 of given solution was stabilized by addition of 0.5 cm3 concentrated nitric acid (merck, germany). stock solution of arsenazo iii (fluka analytical, austria) with concentration 0.05% (w./v) was prepared by weighting and dissolution of appropriate amount of complexing agent in deionized water. buffer solutions in the ph range from 2.20 to 4.00 were prepared by suitable mixing of diluted hydrochloric acid with molar concentration c = 1 mol · dm-3 (mikrochem, slovakia) and solution of potassium hydrogen phthalate with molar concentration c = 0.1 mol · dm-3 (merck millipore, germany). stock solutions of interfering cations and anions with given mass concentrations were prepared by appropriate dilution of their standard solutions (merck, germany). 2.2 apparatus a double wavelength/double beam spectrophotometer cary winuv 50 with 10 mm quartz rectangular cuvette (varian inc., australia) was employed for the absorbance measurements. the ph of studied solutions and buffer solutions was measured and adjusted by ph-meter inolab 730 (wtw gmbh, germany). for the production of deionized water with specific conductivity < 0.054 μs · cm-1 was used ultrapure water system simplicity 185 (millipore, germany). 2.3 recommended procedure place the appropriate amount of pretreated sample containing < 20 μg eu(iii) into 10 cm3 volumetric flask, add 2 cm3 of buffer solution with ph = 2.60 and 0.8 cm3 bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:08 utc nova biotechnologica et chimica 12-2 (2013) 95 of arsenazo iii solution; then fill with deionized water to mark and mix thoroughly. measure the absorbance of this solution against the reagent blank at the wavelength 655 nm. obtain the europium quantity from a calibration curve, which has been prepared with known amounts (0-20 μg) of europium. it is necessary to use technique of standard additions or technique of external calibration with matrix-matched standards in the case of existence of matrix effect. 3. results and discussion the absorption maximum of the complex between eu(iii) and arsenazo iii was observed at the wavelength 610 and 655 nm, respectively. the latter wavelength was used for the determination due to the lower absorbance of background and higher value of analytical signal of formed complex. the position of measured peak (λ = 655 nm) was not affected by the value of ph in the range from 2.20 to 4.00 as shown in fig. 1. 600 625 650 675 700 725 750 775 800 0.00 0.05 0.10 0.15 0.20 0.25 0.30 0.35 a bs or ba nc e λ [nm] ph = 2.20 ph = 2.60 ph = 3.00 ph = 3.40 ph = 3.80 ph = 4.00 fig. 1. absorption spectra of eu(iii)-arsenazo iii complex at the ph value of solutions; blank corrected. c eu(iii) = 1 mg · dm-3; buffer solution v = 2 cm3, arsenazo iii solution v = 1 cm3. the effect of buffer solution ph on the absorbance of relevant complex in the range from 2.20 to 4.00 has been investigated. it has been found out that the maximum absorbance for eu(iii)-arsenazo iii complex was occurred at ph = 2.60. on the basis of this finding, ph of measured solutions was adjusted to this value and used for subsequent measurements. the optimum volume of arsenazo iii, necessary for maximum absorbance, is represented by 0.8 cm3. the raspberry-red colour of formed complex develops instantaneously. the validity of beer’s law was verified in the concentration range from 0 to 2 mg dm-3 eu(iii) (fig. 2). however, beyond that, a deviation from the linearity was observed. the molar extinction coefficient and sandell's sensitivity of the complex were calculated from the regression equation and reached the value ε655 = 5.5±0.2 10 4 cm-1 ·mol-1 ·dm3 and 0.02 μg cm-2, respectively. coefficient of determination r2 was equal to 0.9952. upper boundary of beer’s law validity was bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:08 utc 96 uhrovčík, j. et al. established by application of qc parameter (van loco et al., 2002). results for determination of repeatability of measurement and trueness of measurement are given in table 1. trueness of measurement was verified by spike-recovery procedure. 0.0 0.5 1.0 1.5 2.0 2.5 3.0 0.0 0.2 0.4 0.6 0.8 a bs or ba nc e at λ = 6 55 n m m eu(iii) [mg . dm-3] fig. 2. absorbance of eu(iii)-arsenazo iii complex as a function of europium mass concentration; blank corrected. table 1. determination of repeatability and trueness for studied analytical procedure (n = 10). m eu(iii) [mg · dm-3] apparent recovery [%] relative standard deviation [%] 0.5 91.1 ±7.8 1.0 100.7 ±3.0 1.5 106.1 ±2.3 0 20 40 60 80 100 120 0.10 0.15 0.20 0.25 0.30 0.35 0.40 0.45 0.50 0.55 a bs or ba nc e at λ = 6 55 n m t [min.] fig. 2. time dependence of absorbance for eu(iii)-arsenazo iii complex; blank corrected. (●) – 0.5 mg dm3; (●) – 1.0 mg dm-3; (●) – 1.5 mg dm-3. the intercept of calibration line has proven to be statistically negligible against the hypothetical value 0 (significance level α = 0.05). the student t-test was used for this bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:08 utc nova biotechnologica et chimica 12-2 (2013) 97 purpose. limit of detection calculated according to 3σ criterion reached the value 20.9 μg · dm-3. the optical density was found constant within the linear range for 60 minutes under normal laboratory conditions (fig. 2). a gradual decrease in the absorbance was then observed. composition of eu(iii)-arsenazo iii complex under presented experimental design, equal to 1:1, was established by mole ratio method (fig. 3). same results gained rohwer and hosten (1997). 0.0 0.2 0.4 0.6 0.8 1.0 1.2 1.4 1.6 1.8 2.0 0.00 0.05 0.10 0.15 0.20 0.25 0.30 0.35 0.40 a bs or bn ac e at λ = 6 55 n m n arsenazo iii / n eu(iii) fig. 3. determination of eu(iii)-arsenazo iii composition by mole ratio method; blank corrected. c eu(iii) = 6.85 μmol · dm-3. the effect of selected ions on europium determination has been checked. the results are listed in table 2. the mass concentration of eu(iii) was maintained at the level m = 1 mg ·dm-3. the mass ratio between eu(iii) and studied cations and anions is given in relevant table. a ±5 % variation in the absorbance is taken as tolerable limit within experimental error. table 2. impact of selected cations and anions on the eu(iii) determination in model solutions. anion mass ratio deviation [%] cation mass ratio deviation [%] cation mass ratio deviation [%] edtac 1:15 −21.9 ca(ii)a 10:1 +0.1 sr(iii)b 10:1 +0.2 fluoridec 1:10 +0.8 cu(ii)b 10:1  +0.8 th(iv)b 2:1  +26.0 phosphatec 1:10  +2.0 fe(iii)a 10:1  +2.5 u(vi)b 2:1  +24.1 sulphatec 1:10  +2.2 la(iii)b 10:1  +13.2   oxalatee 1:10  −2.7 mg(ii)a 2:1 +1.1 tartrated 1:10  +1.4 sm(iii)a 10:1 +11.0 a as chloride, b as nitrate, c as sodium salt, d as acid, e as ammonium salt. results indicate that la(iii), sm(iii), th(iv), u(vi) cations and edta anion interfere seriously. all interfering ions, except edta, have increased the absorbance. cation-exchange resin, for example ag50w-x8 (strelow, 1980) should be applied for removal of above mentioned interfering ions from matrix of real sample containing analyte of interest. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:08 utc 98 uhrovčík, j. et al. 4. conclusions simple, sensitive and fast spectrophotometric procedure has been developed for determining eu(iii) using arsenazo iii as chromogenic reagent. a calibration curve was linear over the range up to 2.0 mg · dm-3 eu(iii) and the limit of detection reached the value 20.9 μg · dm-3. elements from the lanthanide and actinide family interfere seriously and should be removed. the method is applicable for europium determination in ores and water with reasonable accuracy, but it is necessary to use proper type of cation-exchange resins or another type of separation technique. references basargin, n. n., ivanov, v. m., kuznetsov, v. v., mikhailova, a. v.: 40 years since the discovery of the arsenazo iii reagent. j. anal. chem., 55, 2000, 204-210. blazejak-ditges, d.: über die photometrische bestimmung des cergehaltes legierter stähle. z. anal. chem., 251, 1970, 11-15. daskalova, n., velichkov, s., slavova, p.: spectral interferences in the determination of traces of scandium, yttrium and rare earth elements in “pure” rare earth matrices by inductively coupled plasma atomic emission spectrometry part iii. europium. spectrochim. acta, 51b, 1996, 733-768. fang, g. z., pan, j. m., zhou, w. l., xu, b. l.: study on the spectrophotometric determination of rare earths with a new chromogenic reagent dibromo-pmethyl-chlorosulfonazo (dbmcsa). chinese chem. lett., 10, 1999, 851-854. fu, x. t., wang, c. m., zhang, y. s.: polarographic study of the eu(iii)triethylenetetraaminehexaacetic acid complex and determination of europium by oscillopolarography. anal. chim. acta, 272, 1993, 221-225. heiserman, d. l.: exploring chemical elements and their compounds, mcgrawhill, new york, 1992, 371 pp. mlakar, m., branica, m.: voltammetric study of europium(iii) in the presence of 2-thenoyltrifluoroacetone. anal. chim. acta, 247, 1991, 89-95. poluektov, n. s., kirilov, a. i., makarenko, o. p., vlasov, n. a.: determination of total rare earth content in natural waters by extraction – spectrophotometric method (english translation). zavod. lab., 37, 1971, 536-537. rohwer, h., hosten, e.: ph dependence of the reactions of arsenazo iii with the lanthanides. anal. chim. acta. 339, 1997, 271-277. savvin, s. b.: analytical use of arsenazo iii. determination of thorium, zirconium, uranium and rare earth elements. talanta, 8, 1961, 673-685. savvin, s. b.: analytical applications of arsenazo iii–ii* determination of thorium, uranium, protactinium, neptunium, hafnium and scandium. talanta, 11, 1964, 1-6. stoyanov, a., chivireva, n. a., stoyanova, i. v., timukhin, e. v., antonovich, v. p.: indirect photometric determination of europium(ii) in some inorganic materials containing aliovalent europium species. j. anal. chem., 66, 2011, 470-475. strelow, f. w. e.: quantitative separation of lanthanides and scandium from barium, strontium and other elements by cation-exchange chromatography in nitric acid. anal. chim. acta. 120, 1980, 249-254. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:08 utc nova biotechnologica et chimica 12-2 (2013) 99 takatatsu, t., sato, a.: spectrofluorimetric determination of europium and samarium with mixtures of 2-thenoyltrifluoroacetone and tri-n-octylphosphine oxide in aqueous solutions containing triton x-100. anal. chim. acta, 108, 1979, 429-432. van loco, j., elskens, m., croux, ch., beernaert, h.: linearity of calibration curves: use and misuse of the correlation coefficient. accredit. qual. assur., 7, 2002, 281-285. yamada, s., kano, k., ogawa, t.: time discrimination in the laser fluorimetry and ultratrace determination of europium(iii) and samarium(iii) with 4,4,4trifluoro-1-(2-thienyl)-1,3-butanedione. anal. chim. acta, 134, 1982, 21-29. zang, s., murachi, s., imasak, t., wataabe, m.: determination of rare earth impurities in ultrapure europium oxide by inductively-coupled plasma mass spectrometry. anal. chim. acta, 314, 1995, 193-201. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:08 utc microsoft word lehotay nb 9-3.doc nova biotechnologica 9-3 (2009) 341 imprinted polymers in analytical chemistry jozef lehotay1, miroslava lachová1, ján mocák2 1institute of analytical chemistry, faculty of chemical and food technology, slovak university of technology, radlinského 9, bratislava, sk-812 37, slovak republic (jozef.lehotay@stuba.sk) 2department of chemistry, university of ss. cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic abstract: molecularly imprinted polymers were prepared and tested in different way. 1-methyl-2piperidinoethylester of 4-decyloxyphenylcarbamic acid was used as template for imprints formation. acrylamide, 4-vinylpyridine and methacrylic acid as monomers and methanol and acetonitrile as a porogene were used. non-imprinted polymers (nip) were prepared for each imprinted polymer by the same procedure. polymers were employed as sorbents for solid-phase extraction (spe). in this work the influence of polymerization mixture composition on polymer properties, such as capacity and selectivity, was investigated. the influence of alkoxy-chain length and position on benzene ring on the selectivity of polymers was also investigated. key words: hplc, molecularly imprinted polymer, spe. 1. introduction molecular imprinting is a technique for preparing chemically selective binding sites, which recognize a particular molecule, in a macroporous polymer matrix. the producing of molecularly imprinted polymers (mips) involves polymerization in solution of a target molecule (template) with functional and crosslinking monomers. removal of the template molecule from a resultant polymer leaves behind specific recognition sites that are complementary to the template and enable the polymer to selectively rebind the imprint molecule from a mixture of closely related compounds. the mips can be produced in a covalent or non-covalent manner. in the case of covalent approach of molecular imprinting covalent bonds between the template and polymerizable monomers are formed. in order to remove the template from the polymer to liberate the binding sites, these covalent bonds have to be chemically cleaved. non-covalent approaches are based on the formation of a prepolymerization complex between monomers and the template trough noncovalent bonds such as ionic interactions or hydrogen bonding. this enables the removal of the template simply by solvent extraction. because mips have outstanding advantages such as predetermined selectivity, simple and convenient preparation, robustness in organic solvents and acidic or basic reagents, and durability to high temperature, molecular imprinting has drawn extensive attention in recent years (zhang et al., 2001). the advantages, applications and developments in molecular imprinting were mentioned in several reviews (kandimalla and ju, 2004 chapuis, 2006; ramström et al., 2001, andersson, 2000; ensing and de boer, 1999; haupt and mosbach, 1998). 342 lehotay, j. et al. a technology, using selective solid phases based on mips in mispe (molecularly imprinted spe), is still investigated by research groups. analysts can use two approaches to obtain the required selectivity: non-selective and selective adsorption of mips for spe. if the analyte can be trapped on the mip by ionic or hydrophobic interactions, users can load an aqueous sample directly and retain it by using nonselective interactions. if the trapping is performed in water, the non-selectively bound components will be removed by washing with organic solvent, and the analyte of interest retained on the mip will switch from non-selective to selective binding (ensing and majors, 2002). mips have been already applied in biological, pharmaceutical (bereczki et al., 2001; theodoridis and manesiotis, 2002; xie et al., 2003; feng et al., 2004; caro et al., 2004) and environmental analysis (baggiani et al., 2001; mena et al., 2002; chapuis et al., 2003; zhon and lai, 2004). there are also some works where mispe was used for sample preparation of herb or tea (xie et al., 2001; blahova et al., 2004). in this study, the influence of functional monomer and porogen, respectively, on the sorptive properties was investigated. the structurally related compounds (analytes with alkoxy-chain with in different position or with different length) were utilized to study the selectivity of mips. all mips were prepared by non-covalent approach by bulk polymerization and used as the sorbent for solid-phase extraction. 2. material and methods 2.1 chemicals 1-methyl-2-piperidinoethylesters of alkoxyphenylcarbamic acid (fig. 1) were synthesized on pharmaceutical faculty in bratislava. acetonitrile, methanol, toluene, methacrylic acid and diethylamine were purchased from merck, 4-vinylpyridine was obtained from aldrich, acrylamide and azobisizobutylonitrile were obtained from fluka, and acetic acid was purchased from lachema. (a) nh coo or ch ch3 ch2 n h cl + (b) nh coo or ch ch3 ch2 n fig. 1. structure of compounds used in research, free base (a) and hydrochloride (b). template molecule: r= c10h21 in 4position (4-dpca). other analytes used in research: r= c10h21 in 2position (2-dpca). 2.2 hplc analysis an hp 1100 system (hewlett-packard, germany), consisting of a pump with a degasser, a diode-array detector (dad) a 50 μl injector and a hp chemstation were used. analyses were carried out on the analytical column separon sgx c18 (125 x 4 mm, 7 μm) (watrex, usa) at laboratory temperature. mobile phase consisted of methanol, acetonitrile, acetic acid and diethylamine (80:20:0.1:0.1) at a flow rate of nova biotechnologica 9-3 (2009) 343 0.5 ml/min. izokratic elution was used. diode-array detector worked in the range of 190 – 400 nm and the chromatograms were acquired at wavelength of 240 nm. 2.3 polymer preparation the molecularly imprinted polymer was prepared according to zhang et al. (2001) method. for synthesis of mips template (1-methyl-2-piperidinoethylester of 4decyloxyphenylcarbamic acid – 4-dpca) was applied as hydrochloride and base, respectively. the base was used mainly for polymers prepared in acetonitrile and toluene because of better solubility of base template in these solvents. the composition of polymerization mixtures is shown in table 1. table 1. composition of polymerization mixtures. polymer form of template molecule porogene monomer mip1 base methanol acrylamide mip2 hydrochloride methanol acrylamide nip1,2 methanol acrylamide mip3 base acetonitrile acrylamide nip3 acetonitrile acrylamide mip4 base toluene acrylamide nip4 toluene acrylamide mip5 hydrochloride methanol 4-vinylpyridine nip5 methanol 4-vinylpyridine mip6 base acetonitrile 4-vinylpyridine nip6 acetonitrile 4-vinylpyridine mip7 base toluene 4-vinylpyridine nip7 toluene 4-vinylpyridine mip8 hydrochloride methanol methacrylic acid mip9 base methanol methacrylic acid nip8,9 methanol methacrylic acid mip10 base acetonitrile methacrylic acid nip10 acetonitrile methacrylic acid mip11 base toluene methacrylic acid nip11 toluene methacrylic acid 2.4 evaluation of mip the cartridge capacity of each mip and nip was tested in methanol, acetonitrile, water and toluene. prior to applying the solution of derivative of 4-dpca, the polymer was pre-equilibrated with 5 ml of methanol and then with 5 ml of solvent in which the capacity was studied. 4-dpca solution (0.5 μg/ml) was applied onto the cartridge (effluent was collected in 1 ml fractions) until a release was detected. each fraction was measured by hplc. in the case of toluene, 5 ml of 4-dpca solution dissolved in toluene (0.5 μg/ml in the case of mip4, mip7, nip4 and nip7;) was applied. in the case of mip11 and nip11, 20 ml of 4-dpca (5 μg/ml) was applied onto the 344 lehotay, j. et al. cartridges. then the cartridges were dried and the adsorbed analyte was desorbed by methanol acetic acid mixture (95:5). effluent was dried, resolved in methanol and measured by hplc. for polymers´capacity, the template was used in the same form (free base or hydrochloride) as it was used during polymerization. the selelectivity of mip3, mip 9, mip10 and mip11 for 1-methyl-2piperidinoethylester of 4-methoxyphenylcarbamic acid (4-mpca) and 2decyloxyphenylcarbamic acid (2-dpca) was tested. the selectivity of mip3 and mip11 in acetonitrile and mip9 and mip10 in methanol was determined. the procedure and the solution concentration were the same as described for 4-dpca. 3. results and discussion 3.1 capacity of polymers as it was described above, the capacities of mips were evaluated in different solvents. the same procedure was performed on mips and nips, respectively, and the resultant values of polymer capacities for template molecules are shown in table 2. table 2. binding capacities of prepared polymers. rsd = 4.5 – 13.5 %, n = 3. capacity (µg of analyte/100 mg of polymer) polymer acetonitrile methanol toluene mip1 (aa-meoh) 0.1 0 mip2 0 0 nip1,2 0.1 0.1 mip3 (aa-acn) 2.5 0.5 nip3 0.4 0.4 mip4 (aa-tol) 0.7 0.1 1.2 nip4 0.5 0 0.9 mip5 (4vp-meoh) 0.2 0.1 nip5 0.3 0 mip6 (4vp-acn) 0.5 0.2 nip6 0.6 0 mip7 (4vp-tol) 0.7 0.1 0.4 nip7 0.8 0.1 0.4 mip8 (maa-meoh) 3.8 2.0 mip9 28.0 8.0 nip8,9 4.0 1.9 mip10 (maa-acn) 20.4 20.2 nip10 10.7 5.9 mip11 (maa-tol) 76.0 32.0 61.1 nip11 9.7 6.2 6.6 rsd = 4.5 – 9.5 %, n = 3. polymers prepared with hydrochloride form as a template were tested for both forms (hydrochloride and base, respectively) and the values of capacities of each polymer (mip1, 5, 8) were similar for both forms of template. nova biotechnologica 9-3 (2009) 345 as it was mentioned in the introduction, the type of functional monomer and porogen plays important role during the formation of pre-polymerization complex. it is obvious from table 2, that the specific capacity of polymers prepared with 4vinylpyridine as a functional monomer is very low. therefore 4-vinylpyridine is not suitable monomer for this type of template. methacrylic acid seems to be the most convenient monomer for our template. all mips, with the exception of mip8, prove the ability to bind the template molecule specifically. different capacity of mip8 in comparison to mip9 demonstrates the influence of the template form on the ability to form the pre-polymerization complex. the mip9 was prepared using by the base form and the mip8 was prepared with hydrochloride form. when we compare the mips prepared with acrylamide, only mip3 is able to bind the template specifically. it indicates the influence of porogene on the formation of pre-polymerization complex. acetonitrile is less polar solvent in comparison to methanol. in this case less polar solvents optimize the interactions between monomer and template. more polar solvents such as methanol and water cancel the hydrogen bonding between monomer and template. the difference between acetonitrile and methanol is also in the way of creation of the hydrogen bonds – donor and acceptor. the solvent used in the process of capacity determination is also very important. the nature of solvent employed for this step influences the relative swelling of the polymer. swelling of the polymer causes changes in the binding site cavities. solvent is also responsible to solvatation process. it means that the size and shape of template molecule depends on the solvent. combination of these factors affects the change of capacity of mip. the highest values of binding capacities were obtained using water (not presented in table) for sample loading for all mips and also for nips. the whole amount of loaded template (100 µg) was sorbed onto the sorbents. in aquaeous environments, hydrogen-bonding and electrostatic interactions could be disrupted, and hydrophobic interactions, which are non-specific, could govern analyte retention (haginaka 2005) this allows to use water samples for extraction, of course, after sample loading, the cartridge should be dried and washed with selective organic solvent able to disrupt the non-specific interaction of analyte with polymer. 3.2 capacity of mips for structurally related compounds the procedure of determination of capacity of mip3, mip9, mip10 and mip11 for structurally related compounds was the same as for template. the influence of length of alkoxychain on benzene ring was tested using by 4-mpca. the influence of position of alkoxy-chain was investigated by measuring of mips´ capacity for 2dpca. the polymer capacities of mips and relevant nips are shown in table 3. as it is obvious from table 3, the capacity of mip3 is lower for analyte with shorter alkoxy-chain (4-mpca) than for template. therefore the length of alkoxychain impacts the capacity of analyte and mip3 can recognize template molecule from structurally related compounds. the influence of alkoxy chain position on benzene ring was also tested. the difference between capacity values of the template (4-dpca) and the analyte with 346 lehotay, j. et al. table 3. binding capacities of prepared polymers. capacity (µg of analyte/100 mg of polymer) ester of pdecyloxyphenylcarb. acid (template) – 4dpca ester of pmethoxyphenylcarb. acid – 4mpca ester of odecyloxyphenylcarb. acid – 2dpca mip3 (aa-acn) 2.5 1.3 1.9 nip3 0.4 0.3 0.4 mip9 (maa-meoh) 8.0 9.2 4.8 nip8,9 1.9 1.9 1.8 mip10 (maa-acn) 20.2 18.1 10.2 nip10 5.9 3.2 6.2 mip11 (maa-tol) 76.0 75.1 76.2 nip11 9.7 10.2 8,0 rsd = 4.5 – 9.1 %, n = 3. alkoxy chain in ortoposition (2-dpca) is not very leap. but in the case of mip9 and mip10, the capacity of mips is two times higher for template than for the analyte with alkoxy-chain in orto-position. it demonstrates that mip9 and mip10 have the different selectivity for compounds with decyloxy-group in other position on benzene ring. references andersson, l.i.: molecular imprinting for drug bioanalysis: a review on the application of imprinted polymers to solid-phase extraction and binding assay. j. chromatogr. b 2000, 739, 163-173. baggiani, c., giovannoli, c., anfossi, l., tozzi, c.: molecularly imprinted solid-phase extraction sorbent for the clean-up of chlorinated phenoxyacids from aqueous samples. j. chromatogr. a, 938, 2001, 35-44. bereczki, a., tolokán, a., horvai, g., horváth, v., lanza, f., hall, a.j., sellergren, b.: determination of phenytoin in plasma by molecularly imprinted solid-phase extraction. j. chromatogr. a, 930, 2001, 31-38. blahová, e., lehotay, j., skačáni, i.: the use of molecularly imprinted polymer for selective extraction of (+)-catechin. j. liq. chromatogr. rel. tech., 27, 2004, 2715-2731. caro, e., marcé, r.m., cormack, p.a.g., sherrington, d.c., borrul, f.: a new molecularly imprinted polymer for the selective extraction of naproxen from urine samples by solid-phase extraction. j. chromatogr. b, 813, 2004, 137143. chapuis, f., dichon, v., lanza, f., sellerfgre, s., hennon, m.c.: optimization of the class-selective extraction of triazines from aqueous samples using a molecularly imprinted polymer by a comprehensive approach of the retention mechanism. j. chromatogr. a, 999, 2003, 23-33. ensing, k., de boer, t.: tailor-made materials for tailor-made applications: application of molecular imprints in chemical analysis. trends anal. chem., 18, 1999, 138-145. nova biotechnologica 9-3 (2009) 347 ensing, k., majors, r.e.: selective sorbents for solid-phase extraction based on molecularly imprinted polymers. lc-gc europe, 15, 2002, 16-25. feng, s.y., lai, e.p.c., dabak-zlotorzynska, e., sadeghi, s.: molecularly imprinted solid-phase extraction for the screening of antihyperglycemic biguanides. j. chromatogr. a, 1027, 2004, 155-160. haginaka, j., selectivity of affinity media in solid-phase extraction of analytes. trends anal. chem. 2005, 24, 407-415. haupt, k., mosbach, k.: plastic antibodies: developments and applications. trends biotech., 16, 1998, 468-475. kandimalla, v.b., ju, h.: molecular imprinting: a dynamic technique for diverse applications in analytical chemistry. anal. bioanal. chem., 380, 2004, 587-605. mena, m.l., martínez-ruiz, p., reviejo, a.j., pizarrón, j.m.: molecularly imprinted polymers for on-line preconcentration by solid phase extraction of pirimicarb in water samples. anal. chim. acta, 451, 2002, 297-304. ramström, o., skudar, k., haines, j., patel, p., brüggemann, o.: food analyses using molecularly imprinted polymers. j. agric. food chem., 49, 2001, 2105-2114. theodoridis, g., manesiotis, p.: selective solid-phase extraction sorbent for caffeine made by molecular imprinting. j. chromatogr. a, 948, 2002, 163-169. xie, j., chen, l., li, ch., xu, x.: selective extraction of functional components derived from herb in plasma by using a molecularly imprinted polymer based on 2,2-bis(hydroxymethyl)butanol trimethacrylate. j. chromatogr. b, 788, 2003, 233242. xie, j., zlu, l., luo, h., zhon, l., li, ch., xu, x.: direct extraction of specific pharmacophoric flavonoids from gingko leaves using a molecularly imprinted polymer for quercetin. j. chromatogr. a, 934, 2001, 1-11. zhang, t., liu, f., chen, w. wang, j., li, k.: influence of intramolecular hydrogen bond of templates on molecular recognition of molecularly imprinted polymers. anal. chim. acta, 450, 2001, 53-61. zhon, s.n., lai, e.p.c., miller, j.d.: analysis of wheat extracts for ochratoxin a by molecularly imprinted solid-phase extraction and pulsed elution. anal. bioanal. chem., 378, 2004, 1903-1906. microsoft word ondas nb 9-2.doc nova biotechnologica 9-2 (2009) 183 conversion of corn fiber into fuel ethanol vladimír ondáš, hana novanská, viera horváthová department of biotechnology, university of ss. cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic (vladimir.ondas@gmail.com) abstract: corn fiber due to its chemical composition (up to 20% starch, 50 60% non-starch polysaccharides) and availability has potential to serve as a substrate for manufacture of various products, including fuel ethanol. this paper deals with assessment of fiber-to-ethanol conversion. the water/dry fiber ratio in suspensions was 10/1. enzyme liquefaction and saccharification of residual starch in corn fiber was carried out in two steps with thermostable α-amylase (20 min, 120°c) and mixture of pullulanase and glucomalyse (24 hours, 60°c). procedures resulted in release of 57.7±1.6 mg of glucose per gram of dry fiber basis. it responds to the dextrose equivalent expression to 96.7±2.2%. by fermentation of the starch hydrolysates by yeasts saccharomyces cerevisiae ccy-11-3 (5% v/v inoculum, 28°c, 72 hours) 0.48 g of ethanol per gram of glucose in hydrolysates was obtained. the solids after starch hydrolysis were separated by filtration and processed by acid pretreatment (0.1 g of conc. hcl/g of biomass/5 ml of water, 120°c, 20 min) with subsequent enzyme hydrolysis (24 hours, 60°c) by the multienzyme preparations containing cellulases and hemicellulases. overall yield of reducing sugars after these two steps was 740.7±3.9 mg/gram of dry corn fiber basis. fermentation of lignocellulosic hydrolysates by yeasts pichia stipitis ccy-39-50-1 and candida shehatea ccy-29-68-4 (in both cases 5% v/v inoculum, 28°c, 72 hours) resulted in 0.38 and 0.12 g of ethanol per gram of reducing sugars. the results indicate that applied pretreatment methods and used microorganisms are able to produce ethanol from corn fiber. key words: corn fiber, enzyme hydrolysis, acid pretreatment, pentoseand hexose-fermenting yeasts 1. introduction corn fiber is a potential raw material for the production of various products, including fuel ethanol, because it is available in countries in which corn grains are processed (mosier et al., 2005; atkin, et al., 2008; noureddini et al., 2009). it is obtained in the process of wet milling of corn. corn fiber, similar to other lignocellulosic materials is the complex of polysaccharides (35% hemicelluloses, 20% cellulose, up to 20% starch) and lignin. the main component of corn fiber is the outer corn grain layer – pericarp and residual part of starchy endosperm (gáspár et al., 2007). the first step of bioethanol production is enzymatic saccharification, in which polysaccharides are converted to monomeric sugars. in contrast to starch or cellulose, containing only hexose – glucose, hemicelluloses contain also pentoses, like xylose and arabinose. in the second step yeasts are used for the fermentation of these sugars (réczey et al., 1996, ballesteros et al., 2004; palmarola-adrados et al., 2005). the most used pentose-fermenting microorganisms are various yeasts like pichia stipitis, candida shehatea, pachysolen tannophilus, but also other strains of this species are able to ferment xylose (zhao et al., 2005; maris et al., 2006). beside naturally occurring pentose-ferment yeasts, also genetically improved e. coli strains or zymomonas mobilis strains are able to convert pentose to ethanol (jarboe et al., 2007). 184 ondáš, v. et al. conversion of the starch along with the lignocellulosic components in the corn fiber would increase ethanol yields from corn wet mill by 13% (grohmann and bothast, 1997) and is promising if the value of the corn fiber as an animal feed product is not severely affected (schell et al., 2004). the aim of this study was to investigate the possibility of corn fiber to ethanol conversion by traditional methods of lignocellulose substrate processing. 2. materials and methods 2.1 materials microbial strains saccharomyces cerevisiae ccy-11-3, pichia stipitis ccy 39-50-1 and candida shehatea ccy 29-68-4 were obtained from the culture collection of yeasts at institute of chemistry (slovak academy of sciences, slovakia), subcultured on slant agar media and stored in a refrigerator at a temperature about 4 °c. corn fiber was received from amylum slovakia s.r.o (boleráz, slovakia) and stored at – 20°c. the following commercial enzymes were used: thermostable αamylase (termamyl 120l), glucoamylase (amg 300l), thermostable pullulanase (promozyme d2), cellulose (celluclast 1,5l) and β-glucosidase (viscozyme l). all enzymes were obtained from novozymes (denmark). 2.2 corn fiber destarching a 10% (w/w) non-ground corn fiber dry matter aqueous solution was prepared. thermostable α-amylase for starch liquefaction (0.3 µl/g starch) was added in two steps and the mixture was boiled at up to 120°c for 20 min. after cooling to about 60°c was glucoamylase (0.8 µl/g starch) and thermostable pullulanase (7.2 µl/ g starch) added and incubated at 60°c for 24 hours. the solids were recovered by filtration. schematic view of this process in the context of other processes is depicted in fig. 1. 2.3 pretreating of destarched corn fiber with hydrochloric acid solids after destarching were mixed with 5 ml of water and 0.1 g of concentrated hydrochloric acid. mixture was heated in a pressure device at 120°c for 20 minutes. after cooling to room temperature, the solids were recovered by filtration. schematic view of this process in the context of other processes is illustrated in fig. 1. 2.4 enzymatic hydrolysis of cellulose in pretreated corn fiber the mixture of cellulolytic enzymes (119 µl/g dry matter of lignocellulose) and βglucosidase (595 µl/g dry matter of lignocellulose) was inoculated to 5% acetate buffer solution of destarched and pretreated solids of corn fiber. the reaction was allowed to proceed for 24 hours at 60°c and stirring at speed rate 120 rpm. schematic view of this process in the context of other processes is shown in fig. 1. nova biotechnologica 9-2 (2009) 185 fig. 1. schematic view of processes involved in the processing of corn fiber to ethanol. 2.5 fermentation liquid hydrolysate from corn fiber destarching was inoculated with 5% inoculum of yeasts saccharomyces cerevisiae, fermentation medium components were added and ph was adjusted to 5.0. liquid hydrolysate from enzyme hydrolysis of destarched and pretreated corn fiber was inoculated with 5% inoculum of yeasts pichia stipitis or candida shehatea, fermentation medium components were added and ph was adjusted to 5.0. fermentation was carried out at 28°c and lasts 72 hours. schematic view of this process in the context of other processes is depicted in fig. 1. 2.6 analytical procedures the dry matter content of corn fiber, destarched corn fiber and pretreated corn fiber was determined by drying of the sample at 105°c. glucose content was determined 186 ondáš, v. et al. using biola test glukosa god 1500 (lachema, czech republic) and reducing sugars were determined using dinitrosalicylic acid (dns). analyses of glucose, maltose, maltotriose and oligosaccharides were performed by high performance liquid chromatography (hplc) with an hpx-87c column (bio-rad laboratories, hercules, usa) at 80°c with water as the mobile phase at a flow rate of 0.5 ml/min. 3. results and discussion destarching of corn fiber with enzymes was carried out in two steps using thermostable α-amylase for liquefaction and mixture of pullulanase and glucoamylase for saccharification. kinetics of saccharification is shown in table 1. results are averages of three determinations table 1. saccharification kinetics of liquefied starch in suspension with 10% content of corn fiber dry matter. reducing sugars glucose hour mg/ml hydrolysate mg/g dry matter mg/ml hydrolysate mg/g dry matter de (%) 0 3.0±0.2 24.4±1.6 0.6±0.05 5.2±0.4 8.7±0.3 2 5.1±0.1 41.8±0.8 4.4±0.1 35.8±0.8 59.9±1.5 4 5.8±0.2 47.2±1.6 4.6±0.1 37.8±0.8 63.3±1.6 6 6.1±0.1 50.0±0.8 5.5±0.2 44.5±1.6 74.5±1.6 8 6.6±0.1 53.8±0.8 6.4±0.1 52.3±0.8 90.0±1.9 24 9.6±0.1 78.5±0.8 7.1±0.2 57.7±1.6 96.7±2.2 de (%) = dextrose equivalent in the first eight hours the dextrose equivalent achieved 90%, and in the next sixteen hours it rose to almost 97%. similar time course of saccharification is described in the work of leathers (2003). glucose represents about 64.6% of all sugars in hydrolysate, maltotriose 17.2% and last 18% other oligosaccharides. we supposed that lower proportion of glucose was caused by reduced availability of starch as a result of the particle size of substrate. destarching of corn fiber leads to better access of pretreatment or hydrolysing agents to non-starch polysaccharides or other substrates. because corn fiber contains about 35% of hemicelluloses, 18% of cellulose and 8% of lignin, it is necessary to pretreat it before enzymatic hydrolysis of polysaccharides to achieve the maximum release of fermentable sugars. acid hydrolysis is one of the possible pretreatment ways (shibanuma et al., 1999; saha, 2003; noureddini et al., 2009). in our experiments 1 g of destarched corn fiber was supplemented with 0.1 g of concentrate hydrochloric acid and 5 ml of water. the mixture was heated in a pressure device at up to 120°c for 20 minutes. after heating the device was nova biotechnologica 9-2 (2009) 187 allowed to cool to room temperature and solids were separated from liquid hydrolysate by filtration. obtained results are listed in table 2. results are averages of three determinations. table 2. concentration of reducing sugars and glucose after pretreatment of destarched corn fiber with hydrochloric acid. reducing sugars glucose mg/ml hydrolysates mg/ml hydrolysates mg/ml hydrolysates mg/g dry matter hydrochloric acid 35.2 ± 1.3 587 ± 3 7.0 ± 0.4 117 ± 1 because most of the pretreatment strategies do not lead to complete hydrolysis of polysaccharides, an important step in processing any lignocellulosic material is the enzymatic hydrolysis of cellulose or hemicelluloses or both polysaccharides. in addition, enzymatic processes are carried out under mild conditions and thus lower consumption of energy. the risk of fermentation inhibitors creation is also minimal. processing of destarched corn fiber with cellulytic and hemicellulytic enzymes in our experiments lasts 24 hours and temperature was maintained at 60°c. the results are summarized in table 3 and are averages of three determinations. table 3. concentration of reducing sugars and glucose after enzymatic hydrolysis of destarched corn fiber and destarched and pretreated corn fiber. reducing sugars glucose substrate mg/ml hydrolysates mg/ml hydrolysates mg/ml hydrolysates mg/g dry matter destarched corn fiber 3.7 ± 0.1 61.7 ± 2.2 1.5 ± 0.1 25.8 ± 0.9 destarched and pretreated corn fiber 8.2 ± 0.3 154 ± 1 2.81 ± 0.1 52.9 ± 0.3 by hplc (results provided by amylum slovakia s.r.o., boleráz) was determined that oligosaccharides represent more than 60% of all sugars in enzyme hydrolysates of destarched and pretreated corn fiber. other saccharides were maltose and maltotriose. in next part of the research fermentation of starch and lignocellulosic hydrolysates prepared from corn fiber was carried out. for the fermentation of starch hydrolysates yeasts saccharomyces cerevisiae were used and for lignocellulosic hydrolysates yeasts pichia stipitis and candida shehatea were used. fermentation conditions were the same for all three yeast strains – ph 5.0, 5% inoculum, 28°c, 72 hours. results are shown in table 4 (starch hydrolysates), table 5 and table 6 (lignocellulosic hydrolysates). 188 ondáš, v. et al. table 4. yield of ethanol after fermentation by saccharomyces cerevisiae of starch hydrolysates with 10% content of corn fiber dry matter. amount of waterless ethanol substrate g/ 100 ml fermentation medium g/g glucose g/g dry matter conversion [%]* corn fiber 0.56 0.48 0.03 94.2 * the degree of conversion is value relative to the maximum theoretical yield of ethanol (0.51 g ethanol from 1 g of glucose) (ballesteros et al., 2004). bura et al. (2002), for the fermentation of starch from corn fiber also used yeasts saccharomyces cerevisiae, but with substrate pretreated by so2 steam explosion. in those conditions yeasts saccharomyces cerevisiae converted saccharides in hydrolysates with efficiency from 90 to 96%. also our conversion efficiency falls within this range. table 5. yield of ethanol after fermentation by pichia stipitis and candida shehatae of lignocellulosic hydrolysate of destarched corn fiber pretreated with hydrochloric acid. amount of waterless ethanol conversion [%]* microorganism g/ 100 ml fermentation medium g/g reducing sugars g/g dry matter pichia stipitis 0.16 0.44 0.02 84.2 candida shehatae 0.05 0.14 0.01 28.4 * the degree of conversion is value relative to the maximum theoretical yield of ethanol (0.51 g ethanol from 1 g of glucose) (ballesteros et al., 2004). table 6. yield of ethanol after fermentation by pichia stipitis and candida shehatea of hydrolysate of corn fiber pretreated by acid prehydrolysis and enzymatic hydrolysis. amount of waterless ethanol conversion [%]* microorganism g/ 100 ml fermentation medium g/g reducing sugars g/g dry matter pichia stipitis 0.85 0.38 0.09 73.9 candida shehatea 0.27 0.12 0.03 22.9 * the degree of conversion is value relative to the maximum theoretical yield of ethanol (0.51 g ethanol from 1 g of glucose) (ballesteros et al., 2004). nova biotechnologica 9-2 (2009) 189 we have to state that fermentation of destarched corn fiber hydrolysates by candida shehatea was efficient not enough. one of the problems causing such low values may also be poor adaptation of yeast strain candida shehatea ccy 29-68-4 to the fermentation conditions such as temperature, ph, presence of inhibitors, the composition of the fermentation medium or the need for aeration. to define optimal conditions for the strain of candida shehatea ccy 29-68-4 undertaking of further experiments is needed. 4. conclusions although agricultural residues are plentiful and readily accessible, improved methods are needed for their conversion to fermentable sugars and subsequently to ethanol or other value-added products. this is also a case of pretreatment method based on acid hydrolysis at lower temperature (under 150°c). also using of pentosefermenting yeasts, like pichia stipitis and candida shehatea needs very careful determination of fermentation conditions. acknowledgments: this research was supported by the slovak research and development agency within the project apvv lpp-0251-07. references atkin, d.e., rigsby, l.l.: corn fiber: structure, composition, and response to enzymes for fermentable sugars and coproducts. appl. biochem. biotechnol., 144, 2008, 59-68. ballesteros, m., olive, j.m., negro, m.j., manzanares, p., ballesteros, i.: ethanol from lignocellulosic materials by a simultaneous saccharification and fermentation process (sfs) with kluyveromyvces marxianus cect 10875. process biochem., 39, 2004, 1843-1848. bura, r., mansfield, s.d., saddler, j.n., bothast, r.j.: so2-catalyzed steam explosion of corn fiber to ethanol production. appl. biochem. biotechnol., 98, 2002, 59-66. gáspár, m., kálmán, g., réczey, k.: corn fiber as a raw material for hemicellulose and ethanol production. process biochem., 42, 2007, 1135-1139. grohmann, k., bothast, r.: saccharification of corn fiber by combined treatment with dilute sulphuric acid and enzymes. process biochem., 32, 1997, 405-415. jarboe, l.r., grabar, t.b., yomano, l.p., shanmugan, k.t., ingram, l.o.: development of ethanologenic bacteria. adv. biochem. engin/biotechnol., 108, 2007, 237-261. leathers, t.d.: bioconversion of maize residues to value-added coproducts using yeast – like fungi. fems yeast res., 3, 2003, 133-140. mosier, s.n., hendrickson, r., brewer, m., ho, n., sedlak, m., dreshel, r., welch, g., dien, b.s., aden, a., ladisch, r.m.: industrial 190 ondáš, v. et al. scale-up of ph-controlled liquid hot water pretreatment of corn fiber for fuel ethanol production. appl. biochem. biotechnol., 125, 2005, 77-85. noureddini, h., byun, j., yu, t.: stagewise dilute-acid pretreatment and enzyme hydrolysis of distillers' grains and corn fiber. appl. biochem. biotechnol., 2009 (in press). palmarola-adrados, b., chotěborská, p., galbe, m., zacchi, g.: ethanol production from non-starch carbohydrates of wheat bran. bioresour. technol., 96, 2005, 843-850. réczey, k., szengyel, z., eklund, r., zacchi, g.: cellulase production by trichoderma reesei. bioresour. technol., 57, 1996, 20-25. saha, b.c.: hemicellulose bioconversion. ind. microbiol. biotechnol., 30, 2003, 279-291. schell, d.j., riley, c.j., dowe, n., farmer, j., ibsen, k.n., ruth, m.f., toon, s.t., lumpkin, r.e.: a bioethanol process development unit: initial operating experiences and results with corn fiber feedstock. bioresour. technol., 91, 2004, 179-188. shibanuma, k., takamine, k., maseda, s., osaki, s., abe, j., hizukuri, s.: partial acid hydrolysis of corn fiber for the ethanol production of l-arabinose. j. appl. glycosci., 46, 1999, 249-256. van maris, a.j.a., abbott, d.a., bellissimi, e., brink, j., kuyper, m., luttik, m.a.h., wisselink, h.w., scheffers, w.a., dijken, j.p., pronk, j.t.: alcoholic fermentation of carbon sources in biomass hydrolysates by saccharomyces cerevisiae: current status. antonie van leeuwenhoek, 90, 2006, 391-418. zhao, j., wang, m., yang, z.: measurement of inhibitory effect of furfural and furfural alcohol using coupled redox mediators. enzym. microb. tech., 37, 2005, 246-253. microsoft word mocak nb 9-3.doc nova biotechnologica 9-3 (2009) 319 current calculation of irreversible electrode reaction mechanisms in linear sweep voltammetry ján mocák, estera rábarová department of chemistry, university of ss. cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic (jan.mocak@ucm.sk, estera.rabarova@ucm.sk) abstract: application of exponential infinite series gives highly accurate analytical solution contributing to the theory of linear sweep voltammetry for single scan experiments. we have calculated theoretical dimensionless current function (usually denoted as π1/2χ(bt)) at relevant potentials for irreversible charge transfer without a coupled chemical reaction. for this purpose several transformation techniques were used, which convert the derived infinite series into summable sequences. since infinite series of further electrochemical mechanisms with irreversible electrode reaction have similar features (particularly those comprising preceding and catalytic chemical reaction), the same approach can be successfully applied also for further electrochemical mechanisms. the respective infinite series are divergent in the most important potential region at and after voltammetric peak therefore their transformation by epsilon and levin transform techniques was used. necessary arbitrary precision arithmetic (apa) was implemented by ubasic. the results were compared to the customary solution of nicholson and shain, who computed the current-potential curves by means of numerical solution of the integral equations but with a much lower precision. our results were obtained in a broad potential range including the potential regions where the series are divergent. obtained current functions are precise to 12 valid decimal numbers, which is utilizable for evaluation of the results achieved by various faster but less precise digital simulation techniques. key words: linear sweep voltammetry, irreversible charge transfer, dimensionless current function, infinite series, arbitrary precision mathematics. 1. introduction mathematical description of current – potential curves, which create an essential analytical signal in linear sweep voltammetry, is complex end still not sufficiently treated in electrochemical literature, in spite of its value. the relevant calculations originate from a system of parabolic differential equations describing the concentrations of the reduced r and oxidized o forms of the studied electrochemical system as well as concentrations of further species eventually taking part in the overall electrochemical mechanism. different mechanisms differ in the detailed composition of initial and boundary conditions. an effective way of calculation submitted nicholson and shain (nicholson and shain, 1964) who solved eight electrochemical mechanisms by converting the boundary value problem into integral equations, which may be further solved either by the derived infinite series or directly using a numerical solution. of them only the series solution is considered analytical from the mathematical point of view since it provides an arbitrary precise result in the region where the series converge. the main problem with the series solution is that they are generally not convergent in the most desired potential region close to the maximum current (peak), which is basic for quantitative analysis. therefore very 320 mocák, j. and rábarová, e. many numerical ways of calculation have been described in electrochemical literature, mostly indicated as and belonging to digital simulation (britz, 2005; britz, 2009; rudolph et al., 1994; mocak and feldberg, 1994). this work is focussed to the uncomplicated irreversible electrode reaction (mechanism ii denoted by nicholson and shain (1964). severe problems with the series convergence can be overcome (at least in a sufficient extent) by transformation of divergent series into summable sequences. 2. theory, problem formulation and tools 2.1 convergence acceleration and resummation in applied mathematics, natural and technical sciences, various methods are used for the convergence acceleration of slowly convergent sequences or series and for the summation of divergent series. their basic idea is to extract hidden information contained in partial sums of a specific slowly convergent or divergent series, and to use that information in order to make a qualified estimate about new (usually higherorder) partial sums which eventually converge to some limit. in many cases, this “qualified estimate” leads to spectacular numerical results which represent a drastic improvement over a term-by-term summation of the original series, even if the series is formally convergent. for further discussion it is useful to consider a sequence {{sn}} = {{s0, s1, . . .}} with elements sn or the terms an = sn − sn−1 of an infinite series. sequence transformations are important tools for the convergence acceleration of slowly convergent sequences or series and also for the summation of divergent series (brezinski, 2000). the basic idea is to construct from a given sequence {{sn}} a new sequence {{s′n}} = t({{sn}}) where each s′n depends on a finite number of elements sn1, . . . , snm. often, the sn are the partial sums of an infinite series. the aim is to find a transformation t such that {{s′n}} converges faster than sn or, after all, it is capable to sum {{sn}}. a common approach is to rewrite sn as sn = s + rn (1) where s is the limit (or antilimit in the case of divergence) and rn is the remainder. the aim then is to find a new sequence {{s′n}} such that s′n = s + r′n , r′n /rn → 0 for n → ∞ (2) thus, the sequence {{s′n}} converges faster to the limit s (or diverges less violently) than {{sn}}. 2.2 employed ways of series transformation a large number of mainly nonlinear sequence transformations for the acceleration of convergence and the summation of divergent series are discussed in review (brezinski, 2000). some of the sequence transformations are well established nova biotechnologica 9-3 (2009) 321 in mathematical literature; among them wynn’s epsilon algorithm (wynn, 1956; wynn, 1966) and levin’s sequence transformations (levin, 1973; smith and ford, 1979; 1982), which were used in this work. wynn's epsilon algorithm or epsilon (ε-) transformation is the nonlinear recursive scheme utilising the partial sums of the original series (0)0ε = s0, (1) 0ε = s1, …, ( ) 0 nε = sn, and defined by the following equations (wynn, 1956): ( ) 1 nε − = 0, ( ) 0 nε = sn , n ≥ 0 (3) ( )n kε = ( 1) 2 n kε + − + 1 / ( ) 1 n kε −δ , k > 0 (4) where the forward difference operator δ is applied to superscripts: ( ) 1 n kε −δ = ( 1) 1 n kε + − − ( )1 n kε − (5) wynn found out that only the elements of the ε table with even subscripts (2n) are applicable for the results calculation (they give so-called shanks transformation) whereas the elements of the ε table with odd subscripts (2n+1) are only auxiliary quantities. each calculation element has a rhombus structure containing four terms and a recursive calculation using a single 1-dimensional array is possible (wynn, 1965). epsilon algorithm allows a simple and efficient series transformation and stimulated an enormous amount of research in this field. transformations t({{sn}}, {{rn}}) that depend not only on the sequence elements or partial sums sn but also on an auxiliary sequence containing the estimates of the remainder rn are of levin-type if they are linear in the sn, and nonlinear in the rn. remainder estimates are usually denoted ωn and provide an easy-to-use possibility to utilize asymptotic information on the problem sequence for the construction of highly efficient sequence transformations. levin transformations are based on the ratio of two series. the first series (in numerator) is a function of sn values of the original sentence divided by ωn, the second series (in denominator) depends on 1/ωn (figure 1). several variants of levin transformation differ in the way how ωn is estimated. in this work two variants were found most useful, particularly levin u and levin d transformations. they all can be solved recursively by using only a 3-term recurrence formulas, which are separately expressed for numerator as well as denominator and the final result is achieved as the ratio of the lastly calculated numerator and denominator terms. ( ) ( ) ( ) ( ) ( ) ( ) ( ) ( ) 1 1 0 1 1 0 1 1 1 1 1 1 1 kk j n j k j n jn k n n kk j k j n j sk n j j n k l s , k n j j n k ω ω ω − + − = + − − = + + +⎛ ⎞ − ⎜ ⎟ + +⎝ ⎠ = + +⎛ ⎞ − ⎜ ⎟ + +⎝ ⎠ ∑ ∑ l fig. 1. general calculation scheme of levin transformations; remainder estimates ωn = (n+1)an and ωn = an+1 for the u and d transformations, respectively. 322 mocák, j. and rábarová, e. 2.3 solved problems and corresponding series investigated irreversible electrochemical reaction is identical to the mechanisms ii defined by nicholson and shain (nicholson and shain, 1964) where all employed symbols, common in voltammetry, are defined. the corresponding reaction scheme and the derived series are: r – z e− k ⇒ o (6, 7) ( ) ( ) ( ) 1 00 ii =1 * ( ) 1 exp ln 1 ( ) ( ) j j a j a s d bj n f rt i bt e e rt n f kj π πβ π χ β ∞ + ⎡ ⎤ = = − − +⎢ ⎥ − ⎢ ⎥⎣ ⎦ ∑ ! the summation of the series was performed by epsilon and levin u transformations (more suitable at larger potential values). computer program for recursive calculation of this mechanism was written in ubasic programming language, which allows implementation of arbitrary precision arithmetic (apa) and uses all numbers with very many decimal places (koyama, 2000). the potential scale utilized by nicholson and shain and their successors is defined as: e*(n-s) = (e – e0)αza + (rt/f) ln [(πdo b)1/2/ ks ] (8) however, oldham and coworkers in several important papers concerning irreversible electrode reaction used a simpler potential scale (e.g. in dalrymplealford, 1977) where π1/2 was omitted from the argument of logarithm: e*(oldh) = (e – e0)αza + (rt/f) ln [(do b)1/2/ ks ] (9) so that this scale is shifted by (rt/f) ln(π)1/2 = 14.705546966777 mv or by 0.572364943 when the dimensionless potential scale is used as another alternative, frequently utilized in electrochemistry. 3. results and discussion 3.1 current – potential dependence for irreversible electrode reaction using real unit potential scale for the sake of space the obtained results are demonstrated in a tabulated form. table 1 brings the calculated values of the current function π1/2χ(bt) designated here also as the dimensionless current i*, which was used in our previous papers (mocak, 2002; mocak and bond, 2004) and in the pioneer works of reinmuth. potential scales of nicholson-shain (n-s) as well as oldham (oldh) are implemented using real millivolt units. our precise values located in the third and seventh column (using n-s scale) can be compared to the values shown in the columns two and six, which were nova biotechnologica 9-3 (2009) 323 calculated numerically 45 years ago by nicholson and shain (1964). one should highly appreciate them (especially considering the computer level that time) since the deviation on the third rounded decimal place is observed only in four cases (emphasized in italics). it is surprising that the results of sivakumar and basha (2005), who investigated the same problem and used four decimal figures for the tabulated current function, were less precise behind the peak potential than the results of nicholson and shain and their potential range was even smaller than that of nicholson and shain. table 1. calculated dimensionless current for irreversible electrode oxidation using nicholson-shain and oldham potential scales expressed in real millivolt units. e*, mv π1/2χ(bt) (n-s) i* (n-s) i* (oldh) e*, mv π1/2χ(bt) (n-s) i* (n-s) i* (oldh) -300 0.00001505 0.00000849 -10 0.462 0.46201793 0.37464546 -250 0.00010536 0.00005944 -5 0.480 0.48053005 0.40852572 -200 0.00073716 0.00041603 0 0.492 0.49178853 0.43859990 -160 0.003 0.00348738 0.00197054 5 0.496 0.49574697 0.46329925 -150 0.00513823 0.00290546 10 0.493 0.49301358 0.48139777 -140 0.008 0.00756454 0.00428200 15 0.485 0.48470520 0.49222092 -120 0.016 0.01632951 0.00927948 20 0.472 0.47221381 0.49576253 -110 0.024 0.02391140 0.01363423 25 0.457 0.45696130 0.49266598 -100 0.035 0.03488516 0.01999080 30 0.441 0.44020946 0.48407130 -90 0.050 0.05062198 0.02922079 35 0.423 0.42295691 0.47137873 -80 0.073 0.07288591 0.04252075 40 0.406 0.40591713 0.45600522 -70 0.104 0.10376342 0.06146949 45 0.38955001 0.43919904 -60 0.145 0.14535833 0.08802158 50 0.374 0.37411700 0.42194196 -50 0.199 0.19905868 0.12433319 60 0.34644141 0.38861355 -45 0.23037469 0.14676318 70 0.323 0.32294382 0.35892542 -40 0.264 0.26422510 0.17225545 80 0.30310390 0.33350738 -35 0.300 0.29992874 0.20082435 100 0.27192236 0.29386329 -30 0.337 0.33648220 0.23230306 120 0.24872422 0.26514046 -25 0.372 0.37256762 0.26628454 150 0.22320466 0.23462457 -20 0.406 0.40661969 0.30206924 200 0.19446262 0.20168254 -15 0.437 0.43696362 0.33863453 250 0.17485343 0.17997456 3.2 current – potential dependence for irreversible electrode reaction using dimensionless potential scale in principle the same calculation approach was used for obtaining the dimensionless current i* related to the dimensionless potential e* defined again in two potential scales, those introduced by nicholson-shain (n-s) and oldham (oldh), respectively. tabulated results are exhibited in table 2. assuming t = 298.15 k, one dimensionless potential unit corresponds to the value rt / f = 25.692606 mv (mocak, 2002). it is worth mentioning that assuming temperature t = 298.15 k, one dimensionless potential unit corresponds to the value rt / f = 25.692606 mv (mocak, 2002). 324 mocák, j. and rábarová, e. table 2. calculated dimensionless current for irreversible electrode oxidation using dimensionless nicholson-shain and oldham potential scales. e* i* (oldh) i* (n-s) e* i* (oldh) i* (n-s) -10.0 0.00004540 0.00008046 0.5 0.48846716 0.48888145 -9.0 0.00012339 0.00021869 1.0 0.49177335 0.45470458 -8.0 0.00033535 0.00059424 1.5 0.46069675 0.37002530 -7.0 0.00091105 0.00161366 2.0 0.41718128 0.30856070 -6.0 0.00247262 0.00437423 3.0 0.34050384 0.26830872 -5.0 0.00669276 0.01180127 4.0 0.28933513 0.24060300 -4.0 0.01798448 0.03143348 5.0 0.25529883 0.22028455 -3.0 0.04739313 0.08092026 6.0 0.23121011 0.20457946 -2.0 0.11864417 0.19088973 7.0 0.21311328 0.19194529 -1.0 0.26145051 0.36765286 8.0 0.19886406 0.18147266 -0.5 0.35430163 0.44848739 9.0 0.18724114 0.17259233 0.0 0.43859990 0.49178853 10.0 0.17750549 0.17750549 4. conclusions the infinite series solution represents at present time the only alternative of analytical solution (from mathematical standpoint) of the corresponding set of differential equations pertinent to irreversible charge transfer (6) in stationary electrode voltammetry and facilitates very precise calculation of voltammetric current even in the potential region far after the peak. even though the corresponding infinite series (7) behaves very badly at large positive potentials, levin transformations and the use of arbitrary precision arithmetic prevents catastrophic loss of precision in calculation and enables very accurate calculation even at 250 mv (using n-s scale). in the indicated potential region all calculated dimensionless current values were precise at minimum to 12 decimal places even though the tables exhibited above contain only the numbers with 8 decimal places to be sufficiently lucid. for practical comparison with the calculations obtained in other mathematical ways even a smaller number of decimal places is needed. in any case, the resulting current – potential data obtained in this work may serve as the standard values utilizable for precision assessment of other, perhaps faster computational tools like digital simulation. acknowledgement: the support of this work by slovak grant agencies by means of grants vega 1/1005/09 and 1/0066/09, and vvce-0004-07 is highly acknowledged. references brezinski, c.: convergence acceleration during 20th century. j. comput. appl. math., 122, 2000, 1-21. britz, d.: digital simulation in electrochemistry. lect. notes phys., 666, 3rd edition, springer-verlag, berlin, 2005, 338 pp. nova biotechnologica 9-3 (2009) 325 britz, d.: digital simulation in electrochemistry, 3rd ed. electronic version: http://www.scribd.com/doc/17687737/digital-simulation-in-electrochemistry-3rded-dieter-britz, 2009. koyama, y.: ubasic. kanazawa univ. japan, ftp://rkmath/rikkyolac.jp/pub/ubibm; ubasic ver. 8.8f, download: http://www.rkmath.rikkyo.ac.jp/~kida/ubasic.htm, 2000. levin, d.: development of non-linear transformations for improving convergence of sequences. int. j. comput. math., b 3, 1973, 371-388. mocak, j., feldberg, s.w.: the richtmyer modification of the fully implicit finite-difference algorithm for simulations of electrochemical problems. j. electroanal. chem., 378, 1994, 31-37. mocak, j.: voltammetric current-potential calculations using infinite series solution. electrochem. comm., 4, 2002, 803-807. mocak, j., bond, a.m.: use of mathematica software for theoretical analysis of linear sweep voltammograms. j. electroanal. chem., 561, 2004, 191-202. nicholson, r.s., shain, i.: single scan and cyclic methods applied to reversible, irreversible, and kinetic systems. anal. chem., 36, 1964, 706-723. dalrymple-alford, p., goto, m., oldham, k.b.: shapes of derivative neopolarogram. j. electroanal. chem., 55, 1977, 1-15. rudolph, m., reddy, d.p., feldberg, s.w.: a simulator for cyclic voltammetric responses. anal. chem., 66, 1994, a589-a600. sivakumar, s., basha, c.a.: evaluation of the current function in linear sweep voltammetry by pade approximation and epsilon convergence. russian j. electrochem., 41, 2005, 421-438. smith, d.a., ford, w.f.: acceleration of linear and logarithmic convergence. siam j. numer. anal., 16, 1979, 223-240. smith, d.a., ford, w.f.: numerical comparisons of nonlinear convergence accelerators. math. comput., 38, 1982, 481-499. wynn, p.: on a device for computing the em(sn) transformation. math. tables aids comput., 10, 1956, 91-96. wynn, p.: a note on programming repeated applications of the ε-algorithm. rev. franc. trait. inf. – chiffres, 8, 1965, 23-62. wynn, p.: on the convergence and the stability of the epsilon algorithm. siam j. numer. anal., 3, 1966, 91-122. microsoft word hegedusova nb 9-2.doc nova biotechnologica 9-2 (2009) 125 use of phytoremediation techniques for elimination of lead from polluted soils alžbeta hegedűsová1, silvia jakabová1, andrea vargová1, ondrej hegedűs2, tímea judit pernyeszi3 1department of chemistry, constantine the philosopher university in nitra, tr. a. hlinku 1, nitra, sk949 01, slovak republic (ahegedusova@ukf.sk, sjakabova@ukf.sk, avargova@ukf.sk) 2regional authority of public health in nitra, štefánikova 58, nitra, sk949 63, slovak republic (nr.hegedus@uvzsr.sk) 3department of analytical and environmental chemistry university of pécs, ifjúság u. 6, pécs, hu-7624, hungary (ptimea@ttk.pte.hu) abstract: the effect of chelating agent – edta (ethylene-diamine-tetra-acetic acid) was used for induced phytoextraction to increase intensity of lead transfer from roots to aboveground parts of garden pea. pot experiments with contaminated soil substrata (50 mg pb.kg-1 and 100 mg pb.kg-1) were established for experimental purposes in growth chamber. the results showed that application of 5 and 10 mmol edta.kg-1 to experimental variants with 100 mg pb.kg-1 doubled the increase of lead uptake by pea roots in comparison with variants without edta addition, which was statistically confirmed. intensive lead transfer was observed from roots to aboveground parts of pea after application of 5 and 10 mmol edta.kg-1 in variant with 50 mg pb.kg-1 (40-fold increase), as well as in variant with 100 mg pb.kg-1 (17-fold increase). the results showed that induced phytoextraction can improve the mobility of lead from soil to plant roots. application of 5 mmol edta.kg-1 resulted to 40-fold increase of lead transfer to green plant parts, despite the fact, that garden pea does not belong to conventional metal hyperaccumulating plant species. following the results, pea could be used for decontamination of arable soil. the optimal edta concentration seems to be 5 mmol.kg-1. therefore, application of 10 mmol edta.kg-1 decreased root mass about 55%, which resulted to decrease the intensity of lead uptake. key words: induced phytoextraction, edta, lead, garden pea 1. introduction the territory of slovakia belongs to long term polluting areas with transfer of contaminants from large industrial and power plant complexes with regional effects. these negative effects affect an extraordinary heterogenous soil cover and increase the content of risk elements to amounts exceeding their limits. accumulation of risk elements in soils affects its ability to produce hygienically unobjectionable foodstuffs, which applies especially for the content of heavy metals with a high degree of biotoxicity from various sources (hegedűsová et al., 2000). decontamination of areas, polluted with toxic metals, presents one of very important research topics and cleaning of the areas by conventionally used physico-chemical methods is financially very expensive and often non-ecologic. modern decontamination technologies, generally called phytoremediation offer possibilities of removing heavy metals from soils (huang and cunningham, 1996; lasat, 2002; simon et al., 2003). the most often used phytoremediation techniques are especially phytoextraction and phytostabilitation. 126 hegedűsová a. et al. during the process of phytoextraction, plants absorb contaminants from soil through the root system and store them mainly in the green biomass and partially in root biomass. application of chelating agents increases the bioavailability of the elements, which is known as an induced phytoextraction process. the most effective is using the plant species with larger biomass production (mcgrath et al., 2002). obtained biomass is processed by several different techniques including microbiological (composting), thermic (ashing or combustion), or chemical (extraction) ones. some of plants species, called hyperaccumulators, bind the metals in high amounts, and therefore, they are used in phytoremediation. tolerance of plants to heavy metals can be explained by binding of metal to cell wall, membrane tolerance to metals, active transport of metals in plant cells, presence of metal-tolerant enzymes, accumulation of metals in vacuole and chelatation of metals with organic or inorganic ligands. lead does not belong to essential elements; moreover, it is highly toxic for animals and humans. similarly to other heavy metals, ions of lead are also potential cancerogenic agents. lead disturbs intermediate metabolism, inhibits the exchange of saccharides in nerve tissue, affects the changes in metabolism of porphyrins and influences the inhibition of homeostasis. it mainly interferes with enzymes on their sulfhydryl groups. the highest risk of intake and retention of this xenobiotic element is from foodstuff intake, therefore approximately 60 % of lead in human organism is ingested and 30 % comes from inhalation (kafka and punčochářová, 2002). common source of lead is soil. the content of lead in main soil types in slovakia varies in wide interval between 10 and 60 mgpb.kg-1. natural values of pb in soil rise after accumulation of dust around roads and from wet deposition after rainfalls. in soil, degradation by microorganisms does not occur, because contact with oxygen leads to oxidation (fodor, 2003; fodor et al., 1996; grčman et al., 2003). the aim of this work was to follow the effect of selected chelating agent – edta (ethylene-diamine-tetra-acetic acid) within decontamination of soil to increase transfer of lead from model contamined soil to aboveground parts of garden pea (pisum sativum l.) using the technique of induced phytoextraction. 2. materials and methods 2.1 plant material pot experiment was established with garden pea (pisum sativum l., variety oskar, very early, marrowfat). from nutritional aspect, peas are well known for being a rich source of highly bioavailable protein. composition of the proteins is similar to proteins of animal origin. ions of heavy metals usually attack tiol-groups, and also binding on carboxyl or amino groups of amino acids occurs in pea proteins. this could explain why pea has higher uptake of metals than cereals. n-compounds exceed 90 % in pea; moreover, main fraction present globulins (45 – 60 %) and other fractions (albumins, insoluble proteins and non-protein fraction) present approximately 15 – 20 % of all nitrogen. content of proteins varies in dependence on variety properties, soil, nutrition, climatic conditions and level of maturity. pea seeds are important source of vitamins nova biotechnologica 9-2 (2009) 127 c, e and b group, derivatives of folic acid, called folates, and macro elements like phosphorus, potassium, magnesium, and calcium. pea is also interesting from the aspect of water soluble or non soluble fibre. 2.2 pot experiments with induced phytoextraction model pot experiments were realized in nine experimental variants in growth chamber with controlled condition at the department of botany and genetics constantine the philosopher university in nitra. growing medium was clean soil substrata in an amount 1000g in each pot. lead solution was applied in two concentrations (50 and 100 mg pb.kg-1) by spraying of soil 4 weeks before sowing. garden pea was sowed directly to pots in amount 20 seeds per pot. growing conditions were following: air temperature 20 ºc, air humidity 60 – 70 %, soil humidity 75 %. light was set to12 h of light and 12 h of darkness, intensity of radiation was max. 50 000 lx). in the sixth and seventh week of growth, chelating agent edta was applied as the solutions with the total addition 5 and 10 mmol.kg-1. after eight weeks of growth all experimental plants were harvested and submitted to analysis. 2.3 sample preparation and determination of lead by et-aas technique dry and homogenized plant samples in amount 1 g were wet digested in vessels za-1 with digesting mixture 1 cm3 deionized water, 2 cm3 h2o2 and 5 cm 3 hno3. soil extracts in were prepared according to standard stn iso 11466:2001. solutions of roots, aboveground plant parts and soil extracts were submitted to quantitative determination of lead using the method et-aas. determination was done on atomic absorption spectrometer spectraa240fs (varian, mulgrave virginia, australia). the technique requires lead hollow cathode lamp to operate at a wavelength of 217.0 nm with a slit width set to 1.0 nm and an electrodeless discharge lamp set at 5 ma current. injected sample volume was 10 μl and palladium matrix modifier pb(no3)2 with concentration 0.1 mol.dm -3 digested in 0.1% hno3 and ascorbic acid (1%) were used as modifiers. 2.4 evaluation of results evaluation of the results was done with the method of calibration curve. the results were statistically evaluated using the single-factor analysis of variance and tukey b test in spss program. 3. results and discussion effect of chelating agent edta to enhance lead uptake from soil to plant and metal transfer in the plant was followed. model concentrations of lead were proposed according to results of soil monitoring on southern slovakia (hegedűsová et al., 2000). in variants with pb addition 50 mg pb.kg-1 and 100 mg pb.kg-1 without edta treatment pea roots accumulated lead in amount 0.22 mg pb.kg-1 and 0.27 mg pb.kg-1 128 hegedűsová a. et al. respectively. transfer of lead did not continue from roots to aboveground parts of plant in variant without application of edta. on the other hand, addition of chelating agent (edta) enhanced the content of the metal in all plant tissues in comparison to variant without edta treatment. pb content in pea roots from pots with 50 mg pb.kg-1 increased about 30% (1.3-fold) after application 5 mmol edta.kg-1. non-significant enhancement of pb was found after application of 10 mmol edta.kg-1 in comparison with edta-nontreated variant (table 1, fig.1). additions of edta resulted to statistically significant increase of lead transfer from soil to pea roots within the soil treatment with 100 mg pb.kg-1 and 5 mmol edta.kg-1. the increase presented 150 % in comparison with edta non treated variant. 100% increase of pb content was found in variant with application 100 mg pb.kg-1 and 10 mmol edta.kg-1 compared with variant without chelate (table 1, fig. 2). statistically significant increase of lead in aboveground plant parts of pea was also found in variants with 50 mg. pb kg-1 in combination with edta treatment. application of 5 and 10 mmol edta.kg-1 resulted to 44-fold and 36-fold increase of pb respectively. lead content in aboveground parts rised approximately 18-times in variant with 100 mg pb.kg-1 in combination with two applied concentrations of chelate (table 1, fig.1, fig.2). there is an assumption that root exudes in a mixture of selected plant species played an important role in the process of metal dissolving in soil and make easier the uptake of metals by pea roots. luo et al. (2008) experimentally proved enhancement of metal uptake (in pea, placed in mixed culture with barley. concentrations of pb, cu, zn, cd and fe in the shoots were higher than in the case of growing pea in isolation. these results presented the evidence that natural chelates, produced by plants themselves, enhance the bioavailability of heavy metals in soil solution and support their uptake by plants. table 1. content of lead in roots and aboveground parts of garden pea in dependence on soil treatment by lead and edta (pot experiments in growth chamber, nitra, 2008). content of pb [mg.kg-1] roots aboveground parts variant pb/edta xmin xm xmax xmin xm xmax c 0.042 0.05a 0.05 0.02 0.03a 0.04 50/0 0.15 0.22ab 0.33 0.02 0.03a 0.03 50/5 0.16 0.29b 0.43 0.8 1.33c 0.18 50/10 0.31 0.33b 0.39 0.96 1.08bc 1.19 100/0 0.21 0.27b 0.40 0.28 0.04a 0.58 100/5 0.59 0.67c 0.78 0.55 0.73b 1.02 100/10 0.32 0.54c 0.79 0.51 0.71b 0.97 legend: c – control variant without application of pb and edta, xmin – minimum value, xmax – maximum value, xm– mean value, a, b, c, d, e – single-factor analysis of variance, tukey b test – statistically significant difference is between the mean values which have different index in the same group, significance level p<0.05, n (number of duplicates) = 9. nova biotechnologica 9-2 (2009) 129 fig. 1. transfer of lead to roots and aboveground parts of garden pea in soil with addition 50 mg pb.kg-1 in dependence on applied amounts of edta (pot experiments in growth chamber, nitra, 2008) fig. 2. transfer of lead to roots and aboveground parts of garden pea in soil with addition 100 mg pb.kg-1 in dependence on applied amounts of edta (pot experiments in growth chamber, nitra, 2008) many studies dealt with increase of heavy metal accumulation in plants within the process of induced phytoextraction. result of experiment of huang and co-workers (1997) confirmed that application of 1g edta.kg-1 to soil contamined with 2500 mg pb.kg-1 enhanced lead transfer to roots and aboveground plant parts about 120-times. five synthetic chelating agents (edta, hedta, dtpa, egta, eddha) were examined and just edta showed the most intensive desorption properties. 3.1 biomass production the biomass production and content of dry mass was followed in all experimental variants. the results showed the statistically significant difference only in variants 130 hegedűsová a. et al. treated with 10 mmol edta.kg-1 (table 2). this amount of chelating agent affected 24 to 33 % decrease of root biomass production (calculations were done with dry mass values). therefore we also supposed decrease of lead uptake intensity by root system. table 2. dry mass of roots and aboveground plant parts of pea in all variants (pot experiments in growth chamber, nitra, 2008). dry mass (g/pot) variant pb/edta roots aboveground parts c 0.73a 3.33a 50/0 0.70a 3.33a 50/5 0.68a 2.99a 50/10 0.53b 3.09a 100/0 0.67a 3.33a 100/5 0.57a 3.33a 100/10 0.45b 2.95a note: single-factor analysis of variance, tukey b test (p<0.05). 3.2 transport indexti transport index (table 3) was calculated as a ratio between pb content in aboveground part and its content in root. table 3. transport index. variant ti 50/0 14.00 50/5 4.59 50/10 3.27 100/0 0.15 100/5 1.09 100/10 1.31 note: ti – transport index (aboveground parts /roots) the results showed that concentration of 5 mmol edta.kg-1 enhanced pb transport from roots to aboveground parts 33-times in variant with 50 mg pb.kg-1. lower transport indexes (1.09 and 1.31) were calculated in variants with addition 100 mg pb.kg-1, which were probably connected with decrease of weight of root system. 3.3 lead balance in plant lead balance in pea plant showed 56 to 62% accumulation of the metal in roots in variants without edta treatment. induced phytoextraction was activated after additions 5 and 10 mmol edta.kg-1, which resulted in enhanced of the metal mobility nova biotechnologica 9-2 (2009) 131 from roots. moreover, 95% and 88 % of metal content was translocated to aboveground parts in variants with application 50 and 100 mg pb.kg-1 respectively (table 4). table 4. lead balance in pea plant (pot experiments in growth chamber, nitra, 2008). withdrawn amount of pb /pot/dry mass roots aboveground parts variant [μg] [%] [μg] [%] c 0.03 23.07 0.10 76.93 50/0 0.15 62.05 0.09 37.50 50/5 0.18 5.02 3.41 94.98 50/10 0.18 4.78 3.59 95.22 100/0 0.19 55.88 0.15 44.12 100/5 0.39 13.00 2.61 87.00 100/10 0.27 11.74 2.03 88.26 the lowest transfer of lead from roots to aboveground parts of pea in variant with addition 100 mg pb.kg-1 could be caused by lower production of root biomass after application of chelate. 4. conclusions despite the fact that in the recent years decreased the amount of emissions in slovakia as a result of certain system precautions, the problem of heavy metal pollution of the environment still exist. hygienic safety of agricultural soils was the basic assumption for growth of hygienic safety foodstuffs. the results from the study of induced phytoextraction process on garden pea plants (pisum sativum l.) using the chelating agent edta allowed us to conclude the following: 1. content of lead in plants in experimental variants with pb addition increased after application of chelating agent. uptake of lead to aboveground parts of pea increased using edta concentrations 5 and 10 mmol edta. kg-1 in the range from 36 to 44fold (in variant with 50 mg pb.kg-1) and to 18-fold (in variant with 100 mg pb.kg-1). 2. statistical significant enhancement of lead transfer from soil to roots was observed only in variant with 100 mg.kg-1 pb addition and present 2 to 2.4 fold increase. 3. efficiency of pb translocation from roots to aboveground parts of pea was evaluated from the calculations of transport indexes. the highest values of transport indexes were observed in pea plants, grown on soil with addition 50 mg pb.kg-1 in both variants treated with edta. 4. the balance of lead content showed enhancement of metal mobility from roots after treatment with edta. moreover, 95% of absorbed metal was translocated to aboveground parts. 132 hegedűsová a. et al. 5. decrease of dry mass production was observed only on root biomass after treatment with 10 mmol edta.kg-1, which resulted to decrease of lead uptake from soil. we can conclude that the most effective continual phytoextraction of lead using garden pea was in variant with 50 mg pb.kg-1 after application 5 mmol edta.kg-1. theoretical calculations showed that garden pea is able to absorb 45-times more lead after chelate treatment than in the case without treatment. pea biomass could be used as an fuel and lead could be obtained back in metal form. another manner how to manage with the biomass is composting, which can reduce its volume. ackowledgment: the work was supported by the project vega 1/4370/07. references fodor, f.: ólom és kadmiumstressz növényekben. bot. közlem., 90, 2003, 107-120. fodor, f., sárvári, é., láng, f., sziget, z., cseh, e.: effects of pb and cd on cucumber depending on the fe-complex in the culture solution. j. plant. physiol., 148, 1996, 434-439. grčman, h., vodník, d., velikonja-bolta, š., leštan, d.: heavy metals in the environment. j. environ. qual., 32, 2003, 500-506. hegedűsová, a., hegedűs, o., vollmannová, a.: kontaminácia poľnohospodárskych pôd a zelenín ťažkými kovmi na južnom slovensku. hort. sci., 27, 2000, 57-64. huang, j.w., cunningham, s.d.: lead phytoextraction: species variation in lead uptake and translocation. new phytol., 134, 1996, 75-84. huang, j.w., chen, j., berti, w. r., cunningham, s.d.: phytoremediation of lead-contaminated soils: role of synthetic chelates in lead phytoextraction. environ. sci. technol., 31, 1997, 800-805. kafka, z., punčochářová, j.: těžké kovy v přírodě a jejich toxicita. chem. listy, 96, 2002, 611 617. lasat, m.: phytoextraction of toxic metals. j. environ. qual., 31, 2002, 109-120. luo, ch., shen, z., li, x.: root exudates increase metal accumulation in mixed cultures: implications for naturally enhanced phytoextraction. water air soil pollut., 193, 2008, 147 – 154. mcgrath, s.p. zhao, f.j., lombi, e.: phytoremediation of metals, metalloids, and radionuclides. adv. agron., 75, 2002, 1-56. simon, l., szegvári, i., csillag j.: impact of picolinic acid on the chromium accumulation in fodder radish and komatsuna. plant soil, 254, 2003, 337-348 microsoft word gasparova revision.doc nova biotechnologica 8-1 (2008) 79 synthesis and plant growth activity of 2-(4-oxochromen-3-yl)benzothiazolium and benzoxazolium bromides mária henselová1, renata gašparová2, margita lácová3 1department of plant physiology, faculty of natural sciences, comenius university, mlynská dolina b-2, sk-842 15 bratislava, slovak republic 2department of chemistry, faculty of natural sciences, university of ss. cyril and methodius, námestie jozefa herdu 2, sk-917 01 trnava, slovak republic 3department of organic chemistry, faculty of natural sciences, comenius university, mlynská dolina ch-2, sk-842 15 bratislava, slovak republic abstract: a facile synthesis of novel 2-(4-oxochromen-3-yl) benzothiazolium bromides 4 and benzoxazolium bromide 5 using the one-pot condensation of substituted 4-oxochromene-3-carboxaldehydes 1 with 2-methylbenzothiazole (2a) or 2-methylbenzoxazole (2b) and benzyl bromide is described. the effects of benzothiazolium bromides 4 on the growth stimulation of the cucumber and retardant activity on corn seedlings were investigated. they inhibited growth of cucumber (root and hypocotyl) and shoots of corn at the range of 10 – 100 ppm and stimulated at 0.1 – 1 ppm concentrations. keywords: plant growth activity, benzothiazolium, benzoxazolium salts, 4-oxochromene-3-carboxaldehydes 1. introduction benzothiazole derivatives represent a large group of heterocyclic substances, which were tested for a different biological activity (sutoris et al., 1988; kráľová et al., 1994; el-shaaer et al., 1998). 2-r substituted benzotiazole derivatives manifested antibacterial and antifungal activities (afsah and nayer 1996; magdolen et al., 2000; buffa et al., 2001) and are reported also to be active as antineoplastics agent (krieg and billitz 1996). according šimonová et al., (2005) ones were characterized as biologically active substances with dominant auxin-like growth promoting activity. 3-r substituted benzothiazole derivatives influenced the prolongation of growth, stimulated the plant regeneration, activity of peroxidase, and may induce the dedifferentiation and morphogenesis of plants in in vitro conditions (sutoris et al., 1993; havel et al., 1994). benzothiazole derivatives were also observed as protective agents against uv-induced mutagenesis in euglena gracilis foltínová et al., (2003) and also against of cadmium stress henselová et al., (2007); klecová šimonová et al. (2008) in phytollaca dioica, vigna radiata and brassica juncea plants. a large number of 4-oxochromene derivatives occur in nature and exhibit variety of biological activities, e.g. antialgal (kráľová et al., 1998), antifungal, antimycobacterial and antiparasitic (caujolle et al., 1993; lácová et al., 1995; gašparová et al., 1997; nawrot-modranka et al., 2006), however, none of 80 henselová, m. et al. them have been reported to have plant growth regulation activity. this paper described the auxin and retardant-like growth activity of newly synthesized oxochromene benzothiazole compounds. 2. materials and methods 2.1 chemistry scheme 1 shows the synthetic pathway to benzothiazolium and benzoxazolium salts. more synthetic details as well as the characteristic data of synthesized compounds are described (kleštinec et al., 2008). general procedure for synthesis 4a-5 a stirred mixture of 4-oxochromene-3-carboxaldehyde 1a (1 mmol), 2methylbenzothiazole 2a (1 mmol) (or 2-methyloxazole 2b) and benzylbromide (1 mmol) in anhydrous nitromethane (2 dm3) was irradiated in microwave oven at 270 w for 10 min. after cooling, the solid product was filtered off, washed with warm acetone and crystallized from acetonitrile to give 45 – 81% yields of products. o o cho r1 x n ch3 c6h5 o or 1 n x br c6h5br + 1 3a x = s 3b x = o 4a-4f x = s 5 x = o x n ch3 scheme 1 c6h5ch2br ch3no2 ch3no2 2a x = s 2b x = o r1 = h, 6-ch3, 6-cl, 6-br, 6-no2, 6-oh, 7-oh 2.2 study of the plant growth activity the solutions of salts 4 5 were prepared in dimethylsulfoxide (dmso). the final concentration of dmso in experiments, including the control, was held constant at 1% by volume. this concentration of dmso had no detectable effect on the growth of plants under experimental conditions. for determination of stimulated growth activity like indole-3-acetic acid (iaa) we used the bioassay as described by merrill (1989) in this modification: twenty seeds of cucumber (cucumis sativus l. cv. regina) were placed in 12 cm petri-dishes on two layers of filter paper whatman № 2, wetted with 15 ml of distilled water (control), or of the indicated benzothiazole nova biotechnologica 8-1 (2008) 81 solution at 0.1, 1 and 10 ppm concentrations. the petri-dishes were placed to a dark box and incubated at 28 °c. the length of the root and hypocotyl seedlings was measured to the nearest milimeter after 7 days. the stimulated effect of tested compounds was evaluated and compared with the control and standard iaa in the range from 0.001 to 10 ppm concentrations. for corn bioassay in nutrient culture the seeds of corn (zea mays l. cv. greta) were pregerminated by soaking them in water for 24 hours. twenty-five seeds were placed on wet filter paper in the petri-dishes of 20 cm diameter for 48 hours at 25 °c to the dark box. seeds selected for treatment had a coleoptile emergence of 10 to15 mm. for determination of retardant activity-like abscisic acid (aba) we used the seedlings bioassay as described by dathe et al., (1978): twenty seedlings were chosen per every variant and placed after two seedlings in glass flasks containing 4 ml of half nutrient solution prepared according brown and dalton (1970) with application of testing compounds in 1, 10 and 100 ppm concentrations. the treated and untreated corn plants were cultivated under glass cover in climatic box (temperature 25/15 °c during 16 hours photoperiod and light intensity of 60 μmol·m-2·s-1 with a relative humidity of 80%). the level of the solutions in the flasks was maintained daily by adding nutrient solution. the length of the corn shoots was measured after 7 days and compared with the control and standard aba. the standards iaa and aba come from sigma, st. louis, mo, usa. all dates are presented as arithmetic averages of the individual experiments. bioassay results were statistically evaluated using the student’s t-test. 3. results and discussion 3.1 study of inhibition of germination and early growth of cucumber and corn seedlings it is obvious from our experimental data that the biological growth effects depend on concentrations of tested compounds. the cucumber growth test and corn bioassay have been used as a specific and sensitive tests for verification of auxin and retardant activities of tested benzothiazole compounds. the differences in auxin (iaa) and retardant (aba) like growth activities between tested derivatives are evident from tables 1 and 2. in general, the inhibition activity was observed at higher (10-100 ppm), and the stimulation activity at lower (0.1-1 ppm) concentrations. all tested compounds showed concentration-dependent stimulation activity in growth elongation of cucumber hypocotyl and root (table 1). growth elongation of hypocotyls was increased from 6% (compound no.5) to 42% (no. 4a). in the case of root growth, maximum stimulation was achieved following the application of 0.1ppm concentration from 14.3% (no. 4e) to 45% (no. 4c). their effects were similar not only to those of synthetic auxin iaa, but also 2,4-dichlorophenoxyacetic acid (york et al., 1984; sutoris et al., 1993) which stimulated elongation of pea stem and wheat coleoptile segments. the highest significant growth stimulation was achieved following application-tested substances in a concentration range of 0.1 to 1 ppm for both hypocotyl and root. compounds no. 4b and 5 have no stimulation effect on root growth (table 1). however, all the compounds were weaker, than iaa, which 82 henselová, m. et al. exhibited maximum effect (6165%) at a concentration one hundred times lower (0.001 ppm). similar effects achieved sutoris et al., (1993) at testing of 3– phenoxycarbonyl-methyland 3-aryloxycarbonyl-methyl-2-benzothiazolinones and (šimonová et al., (2005) at 2-r substituted benzothiazole derivatives. in the range of 10-3 10-7 m concentrations the compounds showed different auxin-like effects on elongation growth of wheat coleoptile segments and the formation and number of adventitious roots and the length of hypocotyl in mung bean. tab. 1. effect of 4a-5 benzothiazole compounds and indole-3-acetic acid (iaa) on root and hypocotyl length in cucumber cv. regina. compound r1 concentration [ppm] mean length [mm] % of control root hypocotyl root hypocotyl control –– 63.5 36.6 100.0 100.0 4a h 0.1 1.0 10.0 83.0 77.0 63.0 52.0 48.5 44.7 130.7a 121.2a 99.2 142.1a 132.5a 122.1 4b 6-ch3 0.1 1.0 10.0 59.0 52.2 40.0 44.7 38.2 26.2 92.9 82.2a 63.0a 122.1a 104.4 71.6a 4c 6-cl 0.1 1.0 10.0 92.0 71.8 45.8 46.2 39.8 26.8 144.9a 113.1b 72.1a 126.2a 108.7 73.2a 4d 6-br 0.1 1.0 10.0 80.0 63.0 61.0 50.5 47.0 10.7 126.0a 99.2 96.1 137.9a 128.4a 111.2 b 4e 6-no2 0.1 1.0 10.0 72.6 51.8 48.6 47.0 44.2 35.2 114.3b 81.6a 76.5a 128.4a 120.8a 96.2 4f 6-oh 0.1 1.0 10.0 89.7 79.7 64.0 49.2 47.5 43.2 141.2a 125.5a 100.8 134.4a 129.8a 118.0a 4g 7-oh 0.1 1.0 10.0 74.6 70.4 48.8 41.2 35.8 33.7 117.5b 110.9 b 76.8 b 112.6a 97.8 92.1 5 6-ch3 0.1 1.0 10.0 61.2 39.0 31.2 38.8 25.4 19.2 96.4 61.4a 49.1a 106.0 69.4a 52.4a iaa standard 0.001 0.01 0.1 1.0 10.0 104.8 94.8 86.4 79.8 32.2 58.9 51.2 44.6 43.1 27.9 165.0a 149.3a 136.1a 125.7a 50.7a 160.9a 139.9a 121.8a 117.7a 76.2a a values are significantly different at the 1%; b values are significantly different at the 5% level against the control as determined by student’s t-test. present studies thus show that the compounds retarded shoot growth of corn, although not necessarily at the same rate (table 2). the majority of tested compounds showed retardation activity in elongation shoot growth of corn seedlings in the range nova biotechnologica 8-1 (2008) 83 of 10 -100 ppm concentrations. this effect, in dependence on the compound structure, amounted up to 82% at no.5 (table 2). at the highest concentration (100 ppm) the compounds exhibited a morfogenic effect evident in the dwarfing of corn coleoptile and cucumber hypocotyle. it is known that the synthetic auxins at higher concentrations causes inhibition of growth, stem twisting, and other formative effects in susceptible plants (chang and foy 1983; fargašová 1994). on the other hand however, stimulates both root and shoot growth of many plants at rates lower, what confirmed also our results. the effect of tested substances was comparable with that of aba (table 2) with exception of compounds no. 4b and 5 that exhibited higher retardant activity (63-82%) in compare to the standard (42.8%) at the same concentration of 100 ppm. three compounds (4a, 4e and 4f) had no retardant effect on corn shoot growth in the range of tested concentrations (table. 2). tab. 2. effect of 4a – 5 benzothiazole compounds and abscisic acid (aba) on shoot length of corn cv. greta. compound concentration (ppm) mean length of the shoot (mm) % of control control –— 121.4 100.0 4a 1 10 100 155.5 143.0 142.0 128.1a 117.8a 116.9a 4b 1 10 100 113.0 65.0 45.0 93.1 53.5a 37.1a 4c 1 10 100 185.0 141.0 98.5 152.4a 116.1a 81.1a 4d 1 10 100 125.0 142.0 93.0 102.9 116.9a 76.6a 4e 1 10 100 135.0 145.0 121.5 111.2 b 119.4a 100.1 4f 1 10 100 132.0 146.0 143.5 108.7 120.3a 118.2a 5 1 10 100 126.0 101.0 22.0 103.8 83.2a 18.1a aba standard 1 10 100 95.4 77.4 45.2 78.6a 63.7a 57.2a a values are significantly different at the 1%; b values are significantly different at the 0.5% level against the control as determined by student’s t-test. the enhancement of growth of cucumber and corn seedlings at the lower concentrations and, on the other hand, their inhibition effect at higher concentrations 84 henselová, m. et al. observed in tested of benzothiazole derivatives are according to merrill’s characteristic growth pattern for auxins. auxins generally showed the best induction of adventitious roots and stimulated the elongation growth on various plants (müller 2000; wang et al., 2003; kollárová et al., 2005). mode(s) of action of growth stimulators, especially auxin-like substances as were tested compounds, have often been hypothesized as being involved in the regulation of synthesis or degradation of endogenous auxin indole-3-acetic acid (iaa) in plants (davies 1995). 4. conclusions the effects of 3-benzyl-2-[(6-r-4-oxochromen-3-yl)ethenyl]benzothiazolium bromides 4a – 4g and 3-benzyl-2-[(6-r-4-oxochromen-3-yl)ethenyl]benzoxazolium bromide and 5 were tested on the germination and early growth of cucumber and corn seedlings. the tested oxochromene benzothiazole derivatives may be characterized as biologically active substances with auxin and retardant growth promoting activity. they inhibited growth of cucumber (root and hypocotyl) and shoots of corn at the range of 10 – 100 ppm and stimulated at 0.1 – 1 ppm concentrations. the most effective compounds with stimulating activity on cucumber seedlings was 4a (r = h), 4f (r = oh) and the best retardant activity on corn seedlings showed 5 (r = ch3) and 4b (r = ch3). acknowledgement: the authors are grateful for financial support to the slovak research and development agency by way of project no. apvt-20-005204 and to the vega grant agency of slovak ministry of education by way of project no. 1/3584/06. references afsah, s.a., nayer, s.a.: synthesis of some styryl chain substituted benzothiazolium asymmetric cyanines: spectra and antimicrobial studies. asian j. chem., 8, 1996, 419-424. brown, b.t., dalton, l.k.: morphactin–like activity of benzilate esters in arabidopsis thaliana.“ in: d.j. carr (ed.), plant growth substances. springerverlag, berlin-heidelberg-new york. 1970, 318-323. buffa, r., zahradník, p., foltínová, p.: computer aided benzothiazole derivativess. synthesis, structure and biological study of new push-pull conjugated benzothiazolium salts. heterocyclic commun., 7, 2001, 331-336. caujolle, r., baziard-mouysset, g., favrot, j. d., payard, m., loiseau, p. r., amarouch, h., linas, m. d., seguela, j. p., loiseau, p. m.: synthesis, antiparasitic and antifungal activities of arylalkyl and arylvinylthiazolines. eur. j. med. chem., 28, 1993, 29 35. dathe, w., schneider, g., sembdner, g.: endogenous gibberellins and inhibitors in caryopses of rye. phytochemistry, 17, 1978, 963-966. davies, p.j.: plant hormones, physiology, biochemistry and molecular biology. kluwer academic publishers, dordrecht-boston-london 1995, 833 p. el-shaaer, h.m., foltínová, p., lácová, m., chovancová, j., stankovičová, h.: synthesis, antimicrobial activity and bleaching effect of nova biotechnologica 8-1 (2008) 85 some reaction products of 4-oxo-4h-benzopyran-3-carboxaldehydes with aminobenzothiazoles and hydrazides. il farmaco, 53, 1998, 224-232. fargašová, a.: toxicity determination of selected plant growth hormones on germination and root growth of sinapis alba seeds. biologia (bratislava), 49, 1994, 109-112. foltínová, p., magdolen, p. zahradník, p.: inhibition of uv-induced mutagenesis in euglena gracilis by benzothiazole derivatives. pharmazie, 58, 2003, 4. gašparová, r., lácová, m., el-shaaer, h.m., olderová, ž.: synthesis and antimycobacterial activity of some new 3-heterocyclic substituted chromones. farmaco, 52, 1997, 251-253. havel, l., konečná, h., snášelová, v., procházka, s., blažková, j.: regeneration and peroxidases activity in cabbage tissue culture under the influence of benzolinon and auxins. rost. výr., 40, 1994, 783 791. henselová, m., machlicová, a., bujdoš, m.: benzolinone – induced tolerance of phytolacca dioica l. plants to cadmium stress. proceedings of 27th international symposium „industrial toxicology ´07“ stu bratislava, 2007, 174179. chang, i.k., foy, c.l.: rapid growth responses of dwarf corn coleoptile sections to picloram. pestic. biochem. physiol.,19, 1983, 203-209. klecová-šimonová, e., henselová, m., masarovičová, e., zahradník, p.: resistance increasing of vigna radiata and brassica juncea plants to cd-stress after application of benzothiazole derivative. sborník z konference „vliv abiotických a biotických stresorů na vlastnosti rostlin 2008“. vúrv praha, 2008, 234-238. (in slovak). kleštinec, m., gašparová, r., lácová, m.: in preparing kollárová, k., henselová, m., lišková, d.: effect of auxins and plant oligosaccharides on the root formation and elongation growth of mung bean hypocotyls. plant growth reg., 46, 2005, 1-9. kráľová, k., mitterhauszerová, l., halgaš, j.: effect of some benzothiazolium salts on chlorophyl production in chlorella vulgaris. biol. plant., 36, 1994, 477 – 479. kráľová, k., šeršeň, f., gašparová, r., lácová, m.: effect of 3-r2ch22-[2-(6-r1-chromon-3-yl)ethenyl]benzothiazolium halides on photosynthetic processes. chem. pap., 52, 1998, 776 779. krieg, m., billitz, j.: structurally modified trimethyne thiacarbocyanine dyes. effect of n-alkyl substituents on antineoplastic behavior. mol. biochem. pharmacol., 51, 1996, 1461-1467. lácová, m., stankovičová, h., odlerová, ž.: chromonyl-aminosalicylic acid derivatives as possible antimycobacterial agents. farmaco, 50, 1995, 885-888. magdolen, p., zahradník, p., foltínova, p.: synthesis, antimicrobial testing and qsar study of new 2-phenylethenylbenzothiazolium salts substituted by cyclic amines. pharmazie, 55, 2000, 803-810. merrill, g.b.: eupatoriochromene and encecalin, plant-growth regulators from yellow starthistle (centaurea solstitialis l). j. chem. ecol., 15, 1989, 2073-2087. 86 henselová, m. et al. müller, j.l.: indole-3-butyric acid in plant growth and development. plant growth reg., 32, 2000, 219-230. nawrot-modranka, j., nawrot, e., graczyk, j.: in vivo antitumor, in vivo antibacterial activity and alkylating properties of phosphorohydrazine derivatives of coumarin and chromone. eur. j. med. chem., 41, 2006, 1301-1309. šimonová, e., henselová, m., zahradník, p.: benzothiazole derivatives substituted in position 2 as biologically active substances with plant growth regulation activity. plant soil environ., 51, 2005, 496-505. sutoris, v., bajči, p., sekerka, v., halgaš, j.: benzothiazolium salts which increase sugar and chlorophyl contents in plants. chem. pap., 42, 1988, 249 261. sutoris, v., gáplovský, a., sekerka, v.: benzothiazole compounds. xlvi. 3,4-disubstitued 2-benzothiazolinones with plant growth regulation activity. chem. pap., 47, 1993, 260-263. wang, s., taketa, s., ichii, m., xu, l., xia, k., zhou, x.: lateral root formation in rice (oryza sativa l.): differential effects of indole-3-acetic acid and indole 3-butyric acid. plant growth reg., 41, 2003, 41-47. york, w.s., darvill, a.g., albersheim, p.: inhibition of 2,4dichlorophenoxyacetic acid-stimulated elongation of pea stem segments by a xyloglucan oligosaccharide. plant physiol., 75, 1984, 295-297. microsoft word chmelova nbc 12-2.doc nova biotechnologica et chimica 12-2 (2013) 120 doi 10.2478/nbec-2013-0014 © university of ss. cyril and methodius in trnava repeated-batch production of laccase by ceriporiopsis subvermispora daniela chmelová1, miroslav ondrejovič2 1department of biochemistry and biotechnology, faculty of biotechnology and food sciences, slovak university of agriculture in nitra, tr. a. hlinku 2, 949 76 nitra, slovak republic (daniela.chmelova@gmail.com) 2department of biotechnology, faculty of natural sciences, university of ss. cyril and methodius in trnava, nám. j. herdu 2, 917 01 trnava, slovak republic abstract: the aim of this study was to set parameters of repeated-batch cultivation of ceriporiopsis subvermispora for laccase production and evaluate the efficiency of this type of cultivation for production of selected enzyme. the suitable conditions for repeated-batch cultivation were designed on the base of study of batch cultivation of white-rot fungus c. subvermispora. c. subvermispora was cultivated in media with different concentration of casein hydrolysate as nitrogen source and glucose as carbon source. a suitable concentration of casein hydrolysate to stimulate the laccase production was 1.5 and 2.5 g/l. laccase production was started at certain critical concentration of glucose (5 g/l). in order to improve laccase production by repeated-batch cultivation of c. subvermispora, glucose was tested in concentration 10 g/l and casein hydrolysate in concentration 1.5 g/l. during a repeated-batch cultivation was measured increase laccase activities from 177.8 to 266 u/l. it was also observed, the cultivation time needed to reach maximum laccase production was shortened to 10 days. keywords: ceriporiopsis subvermispora, laccases, repeated-batch cultivation. 1. introduction laccase is key enzyme participating in the breakdown of lignin during degradation lignocellulose in the nature. in comparison with other ligninolytic enzymes, laccase has wide substrate specificity for oxidation of various phenolic compounds, are more stable and not require the presence of cofactors (hammel and cullen, 2008). therefore, laccase founds more applications in various sectors. laccase activity is essential for biodegradation of organic pollutants with phenyl ring such as polyamines, aminophenols, aryldiamines, polycyclic aromatic hydrocarbons (pozdnyakova et al., 2004), organophosphorus pesticides and synthetic dyes (torres et al., 2003). laccase can be produced by various organisms, but significant producers of this enzyme are white-rot fungi such as ceriporiopsis subvermispora (rűttimann et al., 1992). laccase production by c. subvermispora is affected by various factors such as temperature, ph, medium composition and presence of elicitors in cultivation medium (chmelová et al., 2011). because laccase production starts in negative environmental conditions, parameters of fermentation process designed for laccase production are essential for achievement of sufficient yields. significant factor influenced the production of laccase is an availability of carbon and nitrogen sources. although easily utilizable carbon or nitrogen source allow an increase in laccase production, its production occurs only after exhaustion of the source (galhaup et bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:16 utc nova biotechnologica et chimica 12-2 (2013) 121 al., 2002; thiruchelvam and ramsay, 2007). in the literature, laccase was produced mostly by batch fermentation. this process does not allow sufficient using of sources for laccase production because most sources are used for biomass production. repeated-batch cultivation was reported as a promising method for high laccase production (birhanli and yesilada, 2010). fungal biomass can be reused for a long time in this cultivation (birhanli et al., 2013). the present study was carried out to investigate the laccase production by white-rot fungus c. subvermispora in batch cultivation media with different concentration of nitrogen or carbon sources, then the parameter selection of repeated-batch cultivation of c. subvermispora for laccase production and the evaluation of its effectiveness compared to batch cultivation. 2. materials and methods 2.1 chemicals 3,5-dinitrosalicylic acid 98 % (acros organics, usa), malt agar (biomark, india), k2hpo4. 12 h2o p.a., kh2po4 p.a., nacl p.a., cacl2. 2 h2o p.a., zncl2 p.a., glucose p.a., feso4. 7 h2o p.a., mgso4. 7 h2o p.a., cuso4. 5 h2o p.a., casein hydrolysate, 2,2'-azino-bis(3-ethylbenzothiazoline-6-sulphonic acid) 98 % (sigma aldrich, g), mnso4. 4 h2o p.a. (slavus, sk). 2.2 microorganism culture of ceriporiopsis subvermispora attc 90467 was provided from the centraalburea voor schimmelcultures (netherlands). the culture was maintained on malt agar and stored at 4 °c. in all cases, the suspension of fungal mycelium was prepared by scraping of plaque (1 cm2) of the growth culture from agar plate using microbiological loop in sterile deionized water (10 ml). 2.3 medium composition for batch cultivation, 50 ml of basic mineral medium (table 1) containing glucose as carbon source (5, 10, 25, 50, 75 and 100 g/l) and casein hydrolysate as nitrogen source (0.5, 1.5, 2.5 and 5.0 g/l) was inoculated with 5 ml of fungal mycelium suspension. inoculated cultivation medium was shaken (min. 200 rpm) at 30 °c. table 1. composition of basic mineral medium (aguiar et al., 2006). components of medium concentration mgso4. 7 h2o 0.5 g/l nacl 0.1 g/l cacl2. 2 h2o 0.1 g/l cuso4. 5 h2o 0.1 mg/l feso4. 7 h2o 0.2 mg/l mnso4. 4 h2o 0.02 mg/l zncl2 0.15 mg/l bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:16 utc 122 chmelová, d. and ondrejovič, m. for repeated-batch cultivation, 200 ml of basic mineral medium (table 1) containing glucose (10 g/l) and casein hydrolysate (1.5 g/l) was inoculated with 20 ml of fungal mycelium suspension. inoculated cultivation medium was maintained shaken (min. 200 rpm) at 30 °c. after achieving of maximal laccase activity, cultivation medium was replaced by fresh cultivation medium and biomass in fresh cultivation medium was cultivated at 30 °c with shaking (min. 200 rpm). replacement of cultivation medium was repeated two times. 2.4 concentration of glucose residual glucose was determined in cultivation media using dns (3,5dinitrosalicylic acid) method (miller, 1959). 0.8 ml of dns reagent was added to 0.1 ml of supernatant. reaction mixture was incubated in boiling water batch for 5 minutes. the mixture was cooled down to room temperature and 8 ml of distilled water was added. the absorbance of the reaction mixture (200 µl) was measured at 540 nm using a microplate reader (biotek el 800, fisher, ge). 2.5 activity of laccase activity of laccase was determined with abts (2,2'-azino-bis(3ethylbenzothiazoline-6-sulphonic acid) as the substrate. the assay mixture contained 150 µl of 50 mmol/l phosphate buffer (ph 5.0) with 1 mm abts and 50 µl of enzyme extracts. oxidation of abts was monitored by measuring of absorbance at 405 nm (shin et al., 1987). activity of laccase was expressed in unit (u) as the amount of enzymes able to convert 1 mg of abts per minute. 3. results and discussion composition and availability of nutrients play a significant role in laccase production (galhaup et al., 2002). production of laccase is a part of secondary metabolism of white-rot fungi (howard et al., 2003). secondary metabolism starts in response to negative environmental conditions as a lack of nutrients (carbon or nitrogen sources), the presence of specific organic compounds (catechol, syringaldazine, 2,5-xylidine, veratrylalcohol) (chmelova et al., 2011) or growth conditions (ph, temperature, pressure, ionic strength) (howard et al., 2003). in our study, we tested laccase production ability of white-rot fungus c. subvermispora under various concentrations of carbon and nitrogen sources. c. subvermispora was cultivated in medium intended for the production of biomass (aguiar et al., 2006). cultivation medium was composed from basic mineral medium (table 1), carbon source and nitrogen source. glucose was selected as a readily consumed carbon source, because it is a cheap and easily available substrate (galhaup et al., 2002). for efficient laccase production by fungi, the selection of suitable nitrogen source is essential (galhaup et al., 2002; thiruchelvam and ramsay, 2007). the organic nitrogen substrates such as peptone, casein hydrolysate or malt-extract supported better fungal biomass production and enzyme activities as bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:16 utc nova biotechnologica et chimica 12-2 (2013) 123 compared to the inorganic nitrogen substrates (levin et al., 2008; chmelová et al., 2011). therefore, casein hydrolysate was used as nitrogen source. for determination of effect of carbon and nitrogen sources on laccase production, c. subvermispora was cultivated in medium with glucose (10 g/l) and variable concentrations of casein hydrolysate (0.5, 1.5, 2.5 and 5.0 g/l). during cultivation, glucose concentration as indicator of metabolic activity and laccase activity were determined (fig. 1). fig. 1. concentration of glucose and activity of laccase during growth of white-rot fungus c. subvermispora in cultivation medium with glucose as carbon source (10 g/l) and casein hydrolysate as nitrogen source in a concentration a – 0.5 g/l, b – 1.5 g/l, c – 2.5 g/l and d – 5.0 g/l; ♦ concentration of glucose and ■ – activity of laccase. from fig. 1, laccase activity in cultivation media with different concentrations of casein hydrolysate varied considerably (from 21.1 to 169 u/l). the highest laccase activity (169 u/l) was determined in medium with 2.5 g/l of casein hydrolysate (fig. 1-c). in medium with higher concentration of casein hydrolysate (5.0 g/l), laccase bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:16 utc 124 chmelová, d. and ondrejovič, m. production was lower (fig. 1-d). time for maximum laccase production increased with increasing of casein hydrolysate concentration. laccase production achieved maximum enzyme activity in 13th (159 u/l), 17th (169 u/l) and 19th (62 u/l) day of cultivation at casein hydrolysate concentration 1.5, 2.5 and 5 g/l, respectively. production of laccase was observed when a glucose concentration in the medium declined to critical level (approximately 5 g/l) with the exception of the medium with the lowest concentration of casein hydrolysate (0.5 g/l). in this medium, the laccase activity was achieved the maximum after 16th day of cultivation, while the glucose concentration did not decrease to critical level (5 g/l) and maximum laccase activity was only 21 u/l. low casein concentration led to deficient laccase production. in this case, laccase production was started probably due to lack of nitrogen not carbon source. similar results were described in other studies (galhaup et al., 2002; levin et al., 2010), when laccase activity was mainly detectable in the phase when glucose in culture medium was almost exhausted. these results suggest that suitable a carbon:nitrogen ratio for an effective laccase production is 6.7:1. carbon:nitrogen ratio depend on fungal species, for example phanerochaete flavido-alba requires low carbon:nitrogen ratio (pérez et al., 1996) and pycnoporus cinnabarinus high c/n ratio (eggert et al., 1996). the effect of carbon source concentration on laccase production was studied in media with variable glucose concentrations (5; 10; 25; 50; 75 and 100 g/l) and with maintained carbon:nitrogen ratio (6.7:1). during cultivation of c. subvermispora, glucose concentration and laccase activity were determined. results are shown in fig. 2. activity of laccase was increased with increasing glucose concentration until a glucose concentration 50 g/l. activity of laccase reached a maximum at 15th (50.6 u/l), 12th (221 u/l), 26th (239.1 u/l) and 35th (352 u/l) days in cultivation media with glucose concentration 5, 10, 25 and 50 g/l, respectively (fig. 2a-d). laccase activity was not measured throughout the cultivation in media with 75 and 100 g/l of glucose (fig. 2e,f). this could be caused by an excessive concentration of glucose which prevents the start of secondary metabolism of c. subvermispora (lee et al., 2004). in these media, it was not observed decreasing of glucose concentration under critical level neither after 50 days. this could be due to the exhaustion of nitrogen source and stopping the growth of white-rot fungus c. subvermispora. we found that, although laccase production increased with increasing glucose also cultivation time required to maximum laccase production was extended. therefore, in repeated-batch process, cultivation media were composed of glucose in concentration 10 g/l and casein hydrolysate in concentration 1.5 g/l. repeated-batch cultivation represents a potential alternative mode of cultivation, in which medium or some part of the medium is drawn and fresh medium is refilled periodically without changing fungal biomass (wesenberg et al., 2003). this process allows the use of fungal biomass repeatedly and achieves better results, compared with batch cultivation (birhanli and yesilada, 2006). the best selected conditions were used for the following repeated-batch cultivation of fugal biomass. in order to improve laccase production by c. subvermispora, glucose was tested as a carbon source (10 g/l) and casein hydrolysate as nitrogen source (1.5 g/l). this medium was added to biomass of c. subvermispora. during cultivation was bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:16 utc nova biotechnologica et chimica 12-2 (2013) 125 determined glucose concentration as indicator of metabolic activity and laccase activity. after achieving of maximal laccase activity, the cultivation medium was replace by fresh medium with starting concentration of glucose and casein hydrolysate. the results of repeated-batch cultivation of c. subvermispora are shown in fig. 3. fig. 2. concentration of glucose and activity of laccase during growth of white-rot fungus c. subvermispora in cultivation medium with casein hydrolysate as nitrogen source and glucose as carbon source in carbon:nitrogen ratio (6.7:1; w/w) with glucose concentration a – 5 g/l, b – 10 g/l, c – 25 g/l, d – 50 g/l; e – 75 g/l and f – 100 g/l; ♦ concentration of glucose; ■ – activity of laccase. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:16 utc 126 chmelová, d. and ondrejovič, m. fig. 3. repeated-batch cultivation of c. subvermispora in cultivation medium with 10 g/l of glucose and 1.5 g/l of casein hydrolysate at 30 °c and ph 5.0; ♦ concentration of glucose and ■ – activity of laccase. from fig. 3, the laccase production can be periodically increased during long-term cultivation by periodical replacing the cultivation medium for medium with started concentration of glucose and casein hydrolysate. maximum laccase activity obtained by repeated-batch cultures of c. subvermispora was 177.8 u/l during first cultivation phase after 15 days, 233.5 u/l during second cultivation phase after 13 days and 266 u/l during third cultivation phase after 10 days. it was also observed, the cultivation time needed to reach maximum laccase production during repeated-batch cultivation was shortened and maximum laccase activity was increased. the advantage of this process is the reuse of fungal biomass for laccase production. similar results were observed in other studies (birhanli and yesilada, 2006; birhanli and yesilada, 2010). 4. conclusions the stimulatory effect of some components of cultivation medium on laccase production during batch cultivation was described. high amount of laccase could be obtained with repeated-batch cultivation by selecting the most appropriate culture conditions for laccase production (glucose concentration 10 g/l, casein hydrolysate concentration 1.5 g/l). our results show that repeated-batch cultivation is an easy and suitable process for high amount of laccase without a need for a new fungal biomass. acknowledgement: this work was supported by the grant no. fppv-08-2012. references aquiar, a., souza-cruz, p. b., ferraz, a.: oxalic acid, fe3+ reduction activity and oxidative enzymes detected in culture extracts recovered from pinus bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:16 utc nova biotechnologica et chimica 12-2 (2013) 127 taeda wood chips biotreated by ceriporiopsis subvermispora. enzyme microb. tech., 38, 2006, 873-878. birhanli, e., yesilada, o.: increased production of laccase by pellets of funalia trogii atcc 2008000 and trametes versicolor atcc 200801 in repeatedbatch mode. enzyme microb. tech., 39, 2006, 1286-1293. birhanli, e., yesilada, o.: enhanced production of laccase in repeated-batch cultures of funalia trogii and trametes versicolor. biochem. eng. j., 52, 2010, 3337. chmelová, d., ondrejovič, m., ondáš, v., šturdík, e.: influence of cultivation conditions on production of lignocellulolytic enzymes by ceriporiopsis subvermispora. biologia, 66, 2011, 748-754. eggert, c., temp, u., eriksson, k. e.: the ligninolytic system of the white rot fungus pycnoporus cinnabarinus: purification and characterization of the laccase. appl. environ. microbiol., 62, 1996, 1151-1158. ferraz, a., córdova, a. m., machuca, a.: wood biodegradation and enzyme production by ceriporiopsis subvermispora during solid-state fermentation of eucalyptus grandis. enzyme microb. tech., 32, 2003, 59-65. galhaup, c., wagner, h., hinterstoisser, b., haltrich, d.: increased production of laccase by the wood-degrading basidiomycete trametes pubescens. enzyme microb. tech., 30, 2002, 529-536. hammel, k. e., cullen, d.: role of fungal peroxidases in biological ligninolysis. curr. opin. plant biol., 11, 2008, 349-355. howard, r. l., abotsi, e., jansen van rensburg, e. l., howard. s.: lignocellulose biotechnology: issues of bioconversion and enzyme production. afr. j. biotechnol., 2, 2003, 602-619. kaal, e. e. j., field, j. a., joyce, t. w.: increasing ligninolytic enzyme activities in several white-rot basidiomycetes by nitrogen-sufficient media. bioresour. technol., 53, 1995, 133-139. lee, k. h., wi, s. g., singh, a. p., kim, y. s.: micromorphological characteristics of decayed wood and laccase produced by the brown-rot fungus coniophora puteana. j. wood sci., 50, 2004, 281-284. levin, l., herrmann, c., papinutti, v. l.: optimization of lignocellulolytic enzyme production by the white-rot fungus trametes trogii in solid-state fermentation using response surface methodology. biochem. eng. j., 39, 2008, 207-214. levin, l., melignani, e., ramos, a. m.: effect of nitrogen sources and vitamins on lignolytic enzyme production by some white-rot fungi. dye decolorization by selected culture filtrates. bioresour. technol., 101, 2010, 45544563. miller, g. l.: use of dinitrosalicylic reagent for the determination of reducing sugar. anal. chem., 31, 1959, 426-428. pérez, j., martínez, j., la rubia, t.: purification and partial characterization of a laccase from white rot fungus phanerochaete flavido-alba. appl. environ. microbiol., 62, 1996, 4263-4267. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:16 utc 128 chmelová, d. and ondrejovič, m. pozdnyakova, n. n., rodakiewicz-nowak, j., turkovskaya, o. v.: catalytic properties of yellow laccase from pleurotus ostreatus d1. j. mol. catal. b. enzym., 30, 2004, 19-24. rüttimann, c., schwember, e., salas, l., cullen, d., vicuna, r.: ligninolytic enzymes of the white rot basidiomycetes phlebia brevispora and ceriporiopsis subvermispora. biotechnol. appl. biochem., 16,1992, 64-76. shin, t., murao, s., matsumura, e.: a chromogenic oxidative coupling reaction of laccase: application for laccase and angiotensin i converting enzyme assay. anal. biochem., 166, 1987, 380-388. thiruchelvam, a. t., ramsay, j. a.: growth and laccase production kinetics of trametes versicolor in a stirred tank reactor. appl. environ. microbiol., 74, 2007, 547-554. torres, e., bustos-jaimes, i., le borgne, s.: potential use of oxidative enzymes for the detoxification of organic pollutants. appl. catal., b., 46, 2003, 115. wesenberg, d., kyriakides, i., agathos, n.: white-rot fungi and their enzymes for the treatment of industrial dye effluents. biotechnol. adv., 22, 2003, 161-187. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:16 utc microsoft word remenarova nb 9-3.doc nova biotechnologica 9-3 (2009) 239 biosorption of cationic dyes by1, by2 and bg4 by moss rhytidiadelphus squarrosus from binary solutions lucia remenárová1, martin pipíška1,2, miroslav horník1,2, jozef augustín1,2 1department of biotechnology, university of ss. cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic (pipiskam@ucm.sk) 2consortium for environmental biotechnology and environmental chemistry, hlavná 418, špačince, sk-919 51, slovak republic abstract: a biosorbent prepared from moss rhytidiadelphus squarrosus biomass was used for biosorption of cationic dyes – malachite green (bg4), auramine o (by2) and thioflavine t (by1) from binary aqueous solutions. sorption data obtained at non-equilibrium conditions were analyzed by sheindorfrebuhn-sheintuch (srs) equation (competitive model for binary systems derived from freundlich isotherm) and extended model of freundlich isotherm. following the comparison of coefficient of determination values (r2) as well as values of root mean squared error (rmse), the extended model of freundlich isotherm was more suitable for description of investigated binary systems bg4-by1 (r2bg4 = 0.983, r2by1 = 0.993) and bg4-by2 (r2bg4 = 0.976, r2by2 = 0.995). the competition coefficients aij, obtained from srs model can be considered as a way to quantify mutual competitive interactions. the competition coefficients indicated that the presence of by1 in binary system decreased the sorption of bg4 (aby1,bg4 = 0.835) while presence of bg4 (abg4,by1 = 0.208) has less pronounced competitive effect on the sorption of by1 onto biosorbent. competition coefficients obtained for binary system by1-bg4 indicate that bg4 (abg4,by2 = 0.186) was more significantly affected by the presence of by2 (aby2,bg4 = 1.167). finally, equations used in this work were represented by the three-dimensional biosorption isotherm surfaces. key words: cationic dyes, r. squarrosus, binary biosorption, equilibrium, isotherms 1. introduction pollution of water sources by many organic contaminants over the past decades has become an issue of growing importance. biosorption has become a well-established separation technique to remove diluted pollutants, offering the potential for regeneration, recovery and recycling of the adsorbed materials (mckay et al., 2004). most of the research is engaged in biosorption of cationic dyes in single systems, but as wastewater from the dye manufacturing and textile finishing contains usually mixture of dye components, bigger accent on multicomponent adsorption systems should be put. when more than one species is present in the sorption system, the evaluation, interpretation and representation of sorption data become much more complicated (see e.g. lee et al., 2004). but to provide additional information on the nature of biosortpion process, such as the fraction of adsorption sites being shared with each species, their relative affinities toward these sites, and the mutual interaction between the adsorbed species, is necessary to investigate the simultaneous sorption of two or more species (aksu et al., 2009). 240 remenárová, l. et al. our previous study concerned with the sorption of cationic dyes thioflavine t (by1), auramine o (by2) and malachite green (bg4) from single aqueous solutions onto moss biosorbent and freundlich and langmuir isotherm models were used to describe the equilibrium characteristics of monocomponent adsorption. the freundlich isotherm was found to represent the measured sorption data of bg4, by1 and by2 well (remenárová et al., 2009). within this context, the aim of our work was to study the sorption of cationic dyes from binary aqueous solutions by moss rhytidiadelphus squarrosus. on the basis of the results obtained from single systems, sheindorf-rebuhn-sheintuch (srs) equation and extended model of freundlich isotherm were chosen for analyzing equilibrium data and describing competitive effect of bg4, by1 and by2 in binary systems. 2. materials and methods 2.1 biosorbent preparation a biomass of moss r. squarrosus used in this work was collected in high tatras mountains, slovak republic. to remove the impurities, the biomass was washed twice in deionized water, then oven-dried for 72 h at a maximum of 45°c to avoid the degradation of binding sites. after drying, the moss biomass was milled and sieved for particle size <300 µm. 2.2 dyes cationic dyes malachite green (bg4, basic green 4 – malachite green oxalate, mr 927, c.i. 42 000, merck, d); auramine o (by2, basic yellow 2, mr 304, c.i. 41 000, aldrich, d) and thioflavine t (by1, basic yellow 1, mr 319, c.i. 49 005, fluka, d) were used in sorption experiments (fig. 1). the stock solutions of dyes were prepared in deionized water. working solutions of desired concentrations were obtained by successive dilutions. fig. 1. structure of the basic dyes: (a) malachite green, (b) auramine o and (c) thioflavine t. c a b nova biotechnologica 9-3 (2009) 241 2.3 batch equilibrium sorption experiments in binary systems batch biosorption experiments in binary systems bg4-by1 and bg4-by2 were carried out in series of solutions containing both dyes at initial concentrations within the range from 25 to 300 mg/l in the concentration ratio 2:1, 1:1 or 1:2. the ph was adjusted to 4.0 with 0.1 m hcl. biomass (1 g/l, dw) was added, and the mixture in flasks was agitated on a reciprocal shaker (120 rpm) for 4 h at 25°c. the dye concentrations (ceqbg4, ceqby1, ceqby2) in the solutions were determined spectrophotometrically (uv-vis spectrophotometer varian cary 50). all experiments were performed in duplicate. 2.4 equilibrium modeling for description of sorption equilibrium in binary systems sheindorf-rebuhnsheintuch (srs) equation (competitive model derived from freundlich isotherm) and extended model of freundlich isotherm were used. to calculate the corresponding parameters of adsorption isotherms, non-linear regression analysis was performed by the nlsf (origin´s nonlinear least square fitter) using program microcal origin 8.0 professional (originlab corporation, northampton, usa) with automatic initialization of parameters and graphpad prism 5.0 (graphpad software inc., usa). the 3d sorption surfaces for each binary system were obtained by plotting the experimental dye equilibrium concentrations ceq on the x and y axes, against the dye uptake qeq on the z axis. the tablecurve 3d 4.0 (systat software, inc., chicago, usa) software was used for this purpose. the coefficient of determination (r2) and root mean squared error (rmse) were used to assess the goodness of the fit. 2.5 scanning electron microscopy (sem) the surface structure of moss biosorbent was analyzing by scanning electron microscopy (sem) using vega tescan microscope and software quantax qx2 (version 1.6). 3. results and discussion moss biomass, washed with water, dried at 45°c and milled, represents easily fractionable, well sedimenting material with a large specific surface area, suitable for biosorption of dissolved solutes. the surface of the particles 300 – 600 μm fraction is shown in fig. 2a and 2b. biosorption in multicomponent systems is rather complicated due to the possible interactions among the solutes. the behavior of each species in a multicomponent system depends strongly on the number and properties of other species present. also the solution ph, the physical and chemical properties of both the sorbent and sorbate significantly influenced the sorption process (aksu and akpinar, 2000). 242 remenárová, l. et al. fig. 2. sem micrographs of biosorbent prepared from moss r. squarrosus. a) magnification 500×, b) magnification 2500×. sorption of dyes by r. squarrosus from binary system bg4-by1 and bg4-by2 at ph 4.0 is depicted in fig. 3 and fig. 4. 0 50 100 150 200 250 0 50 100 150 200 250 300 350 400 q eq b g 4 (μ m ol /g ) c eq bg4 (μmol/l) molar ratio by1 : bg4 0 : 1 2 : 1 3 : 1 5 : 1 0 100 200 300 400 500 600 700 0 50 100 150 200 250 300 350 molar ratio by1:bg4 1 : 0 1 : 2 1 : 3 1 : 5 q eq b y 1 (μ m ol /g ) c eq by1 (μmol/l) fig. 3. isotherms of the bg4 (a) and by1 (b) biosorption by r. squarrosus (1.0 g/l, d.w.) at 25°c and ph 4.0 from binary system at different initial molar [bg4]:[by1] ratios. it is evident that sorption of dyes increased with the increasing of dyes concentration in solution. sorption of bg4 from binary systems bg4-by1 and bg4by2 decreased with increasing concentration of by1 (fig. 3a) and by2 (fig. 4b) in solution. on the contrary, the presence of bg4 caused less pronounced decrease of both by1 (fig. 3b) and by2 (fig. 4a) sorption. this can be mainly attributed to the interactions between the basic dyes molecules on the biosorbent surface as reported turabik (2008). based on the literature review it is known that the most appropriate form to describe sorption equilibrium in binary systems is to adjust the experimental data to a b b a nova biotechnologica 9-3 (2009) 243 a mathematical model from which number of parameters can be obtained for quantitative interpretation of sorption equilibrium uptake (see e.g. srivastava et al., 2009; romera et al., 2008, turabik, 2008; teng et al., 2009). in our previous study we determined that the sorption of dyes bg4, by1 and by2 from single systems by r. squarrosus was well described by freundlich isotherm. therefore we used the extended freundlich model (fritz and schluender, 1974) and sheindorf-rebuhn-sheintuch (srs) equation (sheindorf et al., 1981) (competitive model for binary systems derived from freundlich isotherm) for description of equilibrium in binary systems. parameters of freundlich isotherm ki and ni are known from single system (remenárová et al., 2009). 0 200 400 600 800 1000 1200 0 50 100 150 200 250 300 350 400 q eq b y 2 (μ m ol /g ) c eq by2 (μmol/l) molar ratio by2:bg4 1 : 0 2 : 1 3 : 1 6 : 1 0 50 100 150 200 250 0 50 100 150 200 250 300 350 400 q eq b g 4 (μ m ol /g ) c eq bg4 (μmol/l) molar ratio by2 : bg4 0 : 1 2 : 1 3 : 1 6 : 1 fig. 4. isotherms of the by2 (a) and bg4 (b) biosorption by r. squarrosus (1.0 g/l, d.w.) at 25°c and ph 4.0 from binary system at different initial molar [bg4]:[by2] ratios. in 1974 fritz and schluender have discussed the extended form of the monocomponent freundlich isotherm for defining sorption from the binary mixtures which can be written as follows: 11 11 2,11, )/1( 1,1 1, z eq x eq xn eq eq cyc ck q + = + (1) 22 22 1,22, )/1( ,2 2, z eq x eq xn ieq eq cyc ck q + = + (2) where k1, k2, n1 and n2 are derived with the help of the mono-component isotherm. the rest of the parameters are determined using the non-linear regression analysis. the parameters q1 and q2 represent the amount of sorbed species 1 and 2 at equilibrium. also sheindorf et al. (1981) extended the freundlich isotherm to multi-solute systems to derive a freundlich-type multicomponent adsorption isotherm named sheindorf-rebuhn-sheintuch (srs) equation. the assumptions incorporated in the derivation are (1) each component individually follows the freundlich isotherm and (2) for each component in the multi-component adsorption, an exponential distribution of adsorption energies exists, the distribution which is equivalent to the distribution in the single-component system. b a 244 remenárová, l. et al. the srs equations for component 1 and 2 in binary system are written: 1 2121111 1)( −+= ncacckq (3) 12121222 2)( −+= nccackq (4) where α12 is the competition coefficient for the adsorption of component 1 in the presence of component 2. the values for competition coefficient α12 range from zero (complete lack of competition) to values greater than zero for a high degree of competition. wu et al. (2002) and wei and nakato (2006) laboured and successfully used this model to describe sorption of various contaminants from multisolute systems. both freundlich-type isotherms were used to fit the experimental data. 3-d sorption isotherm surfaces of bg4-by1 binary system predicted by the extended freundlich model and srs equation are shown in fig. 5 and 6. similar 3-d sorption isotherm surfaces of bg4-by2 binary system predicted by the extended freundlich model and srs equation were obtained (not shown). 0 50 100 150 200 ceq bg 4 (µ mo l/l) 010 020 030 040 050 060 0 ceq by1 (µmol/l) 0 0 100 100 200 200 300 300 400 400 q eq b g 4 (µ m ol /g ) q eq b g 4 (µ m ol /g ) 0 100 200 300 400 500 600 ceq by 1 (µ mo l/l) 0 50 100 150 200 ceq bg4 (µmol/l) 0 0 100 100 200 200 300 300 400 400 q eq b y 1 (µ m ol /g ) q eq b y 1 (µ m ol /g ) fig. 5. 3-d sorption isotherm surfaces of bg4-by1 binary system: (a) bg4 sorption (μmol/g), (b) by1 sorption (μmol/g). the surfaces are predicted by the extended freundlich model (eq 1 and 2), the symbols represent experimental data obtained at ph 4.0 and 25°c. the vertical bars represent 95% confidence interval. 0 50 100 150 200 ceq bg 4 (µ mo l/l) 010 020 030 040 050 060 0 ceq by1 (µmol/l) 0 0 100 100 200 200 300 300 400 400 q eq b g 4 (µ m ol /g ) q eq b g 4 (µ m ol /g ) 0 100 200 300 400 500 600 ceq by 1 (µ mo l/l) 0 50 100 150 200 ceq bg4 (µmol/l) 0 0 100 100 200 200 300 300 400 400 q eq b y 1 (µ m ol /g ) q eq b y 1 (µ m ol /g ) fig. 6. 3-d sorption isotherm surfaces of bg4-by1 binary system: (a) bg4 sorption (μmol/g), (b) by1 sorption (μmol/g). the surfaces are predicted by the srs equation (eq 3 and 4), the symbols represent experimental data obtained at ph 4.0 and 25°c. the vertical bars represent 95% confidence interval. a b a b nova biotechnologica 9-3 (2009) 245 parameters specified by the application of freundlich-type models are presented in table 1 and 2. by using of srs model the competition coefficients αij were obtained. higher competition coefficients values were estimated for sorption of by1 (aby1bg4 = 0.835 ± 0.111, table 1) and by2 (aby2bg4 = 1.167 ± 0.139, table 2) in the presence of bg4, indicating that both by1 and by2 affect adsorption of bg4 markedly. on the other hand, values of competition coefficients obtained for sorption of bg4 in the presence of by1 (abg4by1 = 0.208 ± 0.015, table 1) and in the presence of by2 (abg4by2 = 0.186 ± 0.015, table 2) were smaller and indicate that sorption of by1 and by2 would be least affected by competitive interactions of bg4. values of r2 and rmse are regarded as a measure of the goodness of fit of experimental data on the isotherms models. as can be seen from table 1 a 2 high coefficients of determination r2 and small values of rmse were obtained for both used models. this indicates that both models well describe the experimental biosorption data. to determine the model better describing experimental data we compared obtained experimental data (qeq exp) with data calculated from models (qeq cal). the analysis of the obtained scatter diagrams shows that experimental values were in a good agreement with values calculated from the extended freundlich model (diagrams not shown). agreement in case of the srs equation was lower. table 1. equilibrium parameters for bg4 and by1 biosorption from the binary mixtures bg4-by1 by moss r. squarrosus calculated from the extended freundlich model and srs model by non-linear regression analysis. extended freundlich model dye xi yi zi r2 rmse* (μmol/g) by1 0.858 ± 0.179 4.214 ± 1.960 0.304 ± 0.141 0.993 9.76 bg4 1.012 ± 0.137 0.025 ± 0.013 1.292 ± 0.169 0.983 13.22 srs model aby1bg4 abg4by1 by1 0.835 ± 0.111 1 0.972 18.75 bg4 1 0.208 ± 0.015 0.977 14.98 *root mean squared error table 2. equilibrium parameters for bg4 and by2 biosorption from the binary mixtures bg4-by2 by moss r. squarrosus calculated from the extended freundlich model and srs model by non-linear regression analysis. extended freundlich model dye xi yi zi r2 rmse* (μmol/g) by2 0.727 ± 0.095 4.126 ± 1.227 0.221 ± 0.069 0.995 8.94 bg4 1.140 ± 0.150 0.027 ± 0.016 1.340 ± 0.179 0.976 15.76 srs model aby2bg4 abg4by2 by2 1.167 ± 0.139 1 0.971 21.32 bg4 1 0.186 ± 0.015 0.973 16.57 *root mean squared error 246 remenárová, l. et al. 4. conclusions in this work the biosorption of cationic dyes from binary solutions onto moss rhytidiadelphus squarrosus was studied. sorption data obtained from binary systems by1-bg4 and by2-bg4 were analyzed by sheindorf-rebuhn-sheintuch (srs) equation and extended model of freundlich isotherm and presented in the form of 3d sorption isotherm surfaces. based on the r2 and rmse values both isotherms well described sorption of cationic dyes from binary systems. higher competition coefficients values were estimated for sorption of by1 and by2 in the presence of bg4, indicating that both by1 and by2 affect adsorption of bg4 markedly. the influence of bg4 on sorption of by1 and by2 from binary systems was less pronounced. it can be concluded that srs equation and extended freundlich model provide a suitable description of the experimental binary data. prepared moss biosorbent may be used for individual and simultaneous removal of basic dyes from effluents. references aksu, z., ertugrul, s., dönmez, g.: single and binary chromium (vi) and remazol black biosorption properties of phormidium sp. j. hazard. mat., 1168, 2009, 310-318. aksu, z. akpinar, d.: modelling of simultaneous biosorption of phenol and nickel(ii) onto dried aerobic activated sludge. sep. purif. technol., 21, 2000, 8799. fritz, w., schluender, e.u.: simultaneous adsorption equilibria of organic solutes in dilute aqueous solutions on activated carbon. chem. eng. sci., 29, 1974, 1279-1282. lee, h.s., suh, j.h., kim, i.b., yoon, t.: effect of aluminum in two-metal biosorption by an algal biosorbent. minerals eng., 17, 2004, 487-493. mckay, g., allen, s.j., porter, j.f.: adsorption isotherm models for basic dye adsorption by peat in single and binary component systems. j. colloid interface sci., 280, 2004, 322-33. remenárová, l., pipíška, m., horník, m., augustín, j.: sorption of cationic dyes from aqueous solutions by moss rhytidiadeplhus squarrosus: kinetics and equilibrium studies. nova biotechnol., 9, 2009, 53-61. romera, e., gonzález, f., ballester, a., blázquez, m.l., muñoz, j.a.: biosorption of heavy metals by fucus spiralis. bioresour. technol., 99, 2008, 684-4693. sheindorf, ch., rebhun, m., sheintuch, m.: a freundlich-type multicomponent isotherm. j. colloid interface sci., 79, 1981, s.136-142. srivastava, v.ch., mall, i.d., mishra. i.m.: competitive adsorption of cadmium(ii) and nickel(ii) metal ions from aqueous solution onto rice husk ash. chem. eng. process., 48, 2009, 370-379. teng, s.-x., wang, s.-g., liu, x.-w., gong, w.-x., sun, x.-f., cui, j.-j., gao, b.-y.: interaction between congo red and copper in a binary adsorption nova biotechnologica 9-3 (2009) 247 system: spectroscopic and kinetic studies. colloid. surface. a: physicochem. eng. aspects, 340, 2009, 86-92. turabik, m: adsorption of basic dyes from single and binary component systems onto bentonite: simultaneous analysis of basic red 46 and basic yellow 28 by first order derivative spectrophotometric analysis method. j. hazard. mat., 158, 2008, 52-64. wei, q., nakato, t.: competitive adsorption of phenols on organically modified layered hexaniobate k4nb6o17. miscropor. mesopor. mat., 96, 2006, 84-92. wu, ch.-h., kuo, ch.-y., lin, ch.-f., lo, s.-l.: modeling competitive adsorption of molybdate, sulfate, selenate, and selenite using a freundlich-type multicomponent isotherm. chemosphere, 47, 2002, 283-292. microsoft word maresova et al 2010-1.doc nova biotechnologica 10-1 (2010) 53 sorption of co2+, zn2+, cd2+ and cs+ ions by activated sludge of sewage treatment plant jana marešová, miroslav horník, martin pipíška, jozef augustín department of biotechnology, faculty of natural sciences, university of ss. cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic (jana.maresova@ucm.sk) abstract: sludges are byproducts of sewage treatment process. land application of sewage sludge is one of the final steps of waste water treatment, but solubilization of toxic metals restricts this method of sludge disposal. in our paper cobalt, zinc, cadmium and cesium sorption by suspension of non-treated activated sewage sludge (14 g/dm3, dry wt.) from waste water spiked with 60cocl2, 65zncl2, 109cdcl2 or 137cscl were determined in laboratory experiments at 20°c. activated sludge supplied by the municipal sewage treatment plant in zeleneč (trnava region, slovakia) showed high efficiency to sorb co2+, zn2+, cd2+ and cs+ ions from waste water ph 6-7. the process can be characterized by the concentration equilibrium (csolid/cliquid) typical for sorption processes. efficiency of the sorption increased in the order cs < co < zn < cd. metal sorption process was not inhibited by pretreatment of the sludge with 0.2% formaldehyde or thermal inactivation at 60°c, what confirms that the process was not dependent on metabolic activity of the sludge. cobalt, zinc, cadmium and cesium were easily removable from the sludge by washing with diluted hcl, edta or water solutions of the corresponding metal ions, but with low efficiency by deionized water. key words: activated sludge, sorption, cobalt, zinc, cadmium, cesium, radiotracer analysis 1. introduction several physico-chemical methods were used for removal of heavy metals from industrial liquid wastes, such as ion-exchange, chemical precipitation, chemical reduction and adsorption. there are still some problems associated with these methods since these are cost-expensive and they themselves can produce other wastes, which will limit their industrial applications. among the available treatment processes, the application of biological sorbents is the most promising due to the following reasons: requirement of chemicals for the treatment process is reduced, low operation costs, eco-friendly and cost-effective alternative of conventional techniques and high efficiency at low levels of contaminations. sludge of municipal waste water treatment plants are produced in huge amounts and generally represent one of the main problems of european countries (fytili and zabaniotou, 2008). many experimental studies are applied worldwide to determine the extractable trace metals in sludge to assess the bio-available metal fraction and the potential mobility of trace metals from polluted sludge (alvarez et al., 2002; fuentez et al., 2004; iaquinta et al., 2006). however, the activated sludge can be considered also as a biosorbent capable to bind toxic metals from liquid wastes of industrial origin. 54 marešová, j. et al. in our previous papers we described sorption characteristics of co, zn and cd binded by dry biomass of lichen e. prunastri (pipíška et al., 2008) and moss r. squarrosus (pipíška et al., 2010) biomass. the objective of this study was to obtain quantitative data of cobalt, zinc, cadmium and cesium sorption by nontreated activated sludge of the municipal wastewater treatment plant. 2. materials and methods 2.1 sorption and desorption experiments activated sludge supplied by a municipal sewage treatment plant in zeleneč (trnava region, slovakia) was kept in refrigerator at 4°c for 30 d and used for experiments. suspension of activated sludge ph 6.9 pre-concentrated by centrifugation contained 14.0 g/dm3 biomass (dry wt.). in batch experiments, the test tubes with 1 ml of activated sludge suspensions in waste water were spiked with 60cocl2, 65zncl2, 109cdcl2 or 137cscl (0.5-50 mmol/dm3) and shaken at 20°c. in time intervals, the biomass was separated by centrifugation (20 min at 12 000 × g), supernatant was removed and sediment was used for radiometric determination of sorbed metals. in desorption experiments, the biomass after metal sorption was separated (20 min at 12 000 × g) and resuspended by wortexing for 30 min in 1.0 ml deionized water, 0.1 m edta, 0.1 m hcl, 0.5 mm cocl2, 0.5 mm zncl2, 0.5 mm cdcl2 or 0.5 mm cscl. concentration of metals in biomass was estimated by similar way as in the sorption experiments. biomass dry weight was estimated by drying for 24 h at 60 °c. the prediction of co, zn, cd and cs speciation in the solution as a function of ph was performed using the visual minteq (version 2.53) program. 2.2 radiometric analysis the gamma spectrometric assembly using the well type scintillation detector 54bp54/2-x, nai(tl) (scionix, the netherlands) and the data processing software scintivision 32 (ortec, usa) were used for 60co, 65zn, 109cd and 137cs determination in sediment of sludge and supernatant fluids at the energy of γphotons [kev]: 60co1173.24, 65zn – 1115.52, 109cd – 88.04, 137cs – 661.62. counting time 600 s allowed obtaining data with measurement error <2 %, which do not reflect other sources of errors. standardized solutions of 65zncl2 (50 mg/dm 3 zncl2 in 3 g/dm 3 hcl), 60cocl2 (20 mg/dm 3 cocl2 in 3 g/dm 3 hcl), 109cdcl2 (50 mg/dm 3 cdcl2 in 3 g/dm3 hcl), 137cscl (20 mg/dm3 cscl in 3 g/dm3 hcl) were obtained from the czech institute of metrology (prague, czech republic). 3. results and discussion 3.1 metal sorption sorption experiments showed that non-treated activated sludge is able to bind high amounts of cobalt, zinc, cadmium and cesium (fig. 1). at c0 = 50 mmol/dm 3, nova biotechnologica 10-1 (2010) 55 sorptions q (μmol/g; dry wt.) 611, 995, 1076 and 374 for cobalt, zinc, cadmium and cesium respectively, were observed. however, at the initial concentration c0 = 50 mmol/dm3, the system was not saturated, and higher qmax values can be expected. 10 100 1000 10000 100000 0,01 0,1 1 10 100 1000 co zn cd cs q [μ m ol /g ] c0 [μmol/dm 3] fig. 1. cobalt (-), zinc (-o-o-o-), cadmium (-) and cesium (-) uptake q (μmol/g; dry wt.) by non-treated activated sludge in dependence on the initial cocl2, zncl2, cdcl2 and cscl concentration. specific radioactivity in solutions [bq/ml]: 60co – 195; 65zn – 156; 109cd – 192 and 137cs – 172. data after 1h reaction at 20°c. biomass concentration 14.0 g/dm3 (dry wt.). data are the arithmetic mean of three replicates. 3.2 the role of metabolic activity broad consortium of vital aerobic microbial population in activated sludge can participate in metal uptake driven by metabolic processes. on the other hand, dead microbial biomass and polymers such as proteins and polysaccharides can also bind metals on the basis of sorption processes or complexing. experiments showed that treatment of activated sludge by formaldehyde or thermal inactivation at 60°c had minimal effect on cobalt, zinc, cadmium and cesium uptake (fig. 2). it means, that metal uptake is not dependent on metabolic activity and physico-chemical processes play decisive role in cobalt, zinc and cadmium binding by non-treated activated sludge. the sorption of metals is attributed to the bacterial cell wall (fein 2006; vullo et al., 2008) and to the exopolymeric substances (pal and paul, 2008), which contain a large number of negatively charged functional groups such as carboxyl, phosphate and sulphate (wingender et al., 1999). exopolymers can be expected 56 marešová, j. et al. to buffer metal ion concentrations over wide ranges of concentrations and ph (bhaskar and bhosle, 2006). comprehensive data dealing with metal binding by activated sludge can be found in papers (milne et al., 2003; guibaud et al., 2009). 0 10 20 30 co zn cd cs q [μ m ol /g ] fig. 2. uptake of cobalt, zinc, cadmium and cesium q (μmol/g; dry wt.) by non-treated activated sludge ---, formaldehyde-treated sludge (0.5%, 30 min at 20°c, under wortexing) ---, and thermally treated sludge (30 min at 60°c) ---. specific radioactivity in solutions [bq/ml]: 60co – 198; 65zn – 150; 109cd – 167 and 137cs – 162. sorption 1 h under agitation at 20°c. reaction conditions see fig. 1. 3.3 the role of ph acidic ph region is not typical for municipal waste waters as well as activated sludges. it is generally known, that metal cation biosorption is diminished below ph 4 (pipíška et al., 2010). in acidic ph region species of cobalt and zinc exist as me2+ cations, and cesium as me+ cation (fig. 3). in the case of cadmium the main ionic form within ph 4 -8 beside cd2+ is cdcl+ with the ratio approx 60 to 40 (fig. 4). above ph 7 more complex ionic equilibrium takes place, in dependence of the concentration of anion such as chloride, carbonate and phosphate. the concentration of cd(oh)3 – anion is increasing above ph 9. during the sorption of metals by sludges from alkaline liquid wastes besides sorption of me2+ cations, also the existence of other than ionic metal forms with different solubility in water have to be taken into consideration. this fact is in agreement with our observations that sorption efficiency of activated sludge increases above ph 8 (not shown). strong sigmoidal ph dependence of cd2+ sorption by polysaccharides of activated sludge with inflection point at ph 8.6 was described by guibaud et al. (2009). nova biotechnologica 10-1 (2010) 57 3 4 5 6 7 8 9 10 11 12 0 20 40 60 80 100 (m en + / m e t ot al ) x 10 0 ph co2+ zn2+ cd2+ cs+ fig. 3. molar fraction of co2+, zn2+, cd2+ and cs+ in dependence on ph of synthetic waste water (iaquinta et al., 2006) at 25°c and c0 1.0 mmol/dm3. calculated by speciation program visual minteq ver. 2.53. 3 4 5 6 7 8 9 10 11 12 0 10 20 30 60 70 80 cdcl+ cdcl 2 cdso 4 cd(so4) 2 2 cdoh+ cd(oh) 2 cd 2 oh3+ cd(oh) 3 (m ex / m e t ot al ) x 10 0 ph fig. 4. speciation forms of cadmium in dependence on ph of synthetic waste water (iaquinta et al., 2006) at 25°c and c0 1.0 mmol//dm3. calculated by speciation program visual minteq ver. 2.53. 3.4 desorption high percentage of co, zn, cd and cs can be desorbed from the sludge by one step washing with cocl2, zncl2, cdcl2 and cscl solutions respectively, as well as with edta and hcl solutions (tab. 1; fig. 5b). at the same time only 6, 2 and 7 per cent of sorbed cobalt, zinc and cadmium, respectively, can be solubilized by washing the activated sludge with deionized water. it means that for releasing of the above mentioned metals certain, ionic force is necessary for replacing metal ions from binding sites. cesium was easily removable from the sludge even with deionized water. generally, cs+ ions show the highest mobility in biological systems resembling behavior of k+ ions. cadmium showed the highest affinity to the sludge and the lowest extractability with mineral acids and salt solutions (fig. 5a, b). the explanation of this 58 marešová, j. et al. phenomenon will require a more detailed study oriented toward speciation of cadmium in individual components of the sludge flocks. table 1. removable portion of metals from activated sludge by single step washing of sludge with 0.1 m hcl, 0.1 m edta or 0.5 mm cocl2, zncl2, cdcl2 or cscl. specific radioactivity in solutions [bq/ml]: 60co – 205; 65zn – 158; 109cd – 160 and 137cs – 146. calculations based on volume radioactivity of supernatant washing liquid. parameter co zn cd cs sorbed q (μmol/g; dry wt.) * 26±0.7 30±0.9 31±1.1 11±0.2 removed with water [%] 6 2 7 36 removed with 0.5 mm salt [%] 46 50 15 72 removed with 0.1 m hcl [%] 81 91 30 83 removed with 0.1 m edta [%] 90 92 73 81 * biosorption from c0 = 0.5 mmol/dm3 solutions at biomass concentration 14.0 g/ dm3 (dry wt.). 0,01 0,1 1 10 100 1000 10000 q [μ m ol /g ] c 0 [mmol/l] 5,0 50,00,5 0,1 1 10 100 1000 10000 q [μ m ol /g ] c 0 [mmol/l] 5,0 50,00,5 fig. 5a. cobalt (-), zinc (-), cadmium (-) and cesium (-) uptake q (μmol/g; dry wt.) by nontreated activated sludge in dependence on the initial cocl2, zncl2, cdcl2 and cscl concentration. specific radioactivity in solutions [bq/ml]: 60co – 195; 65zn – 156; 109cd – 192 and 137cs – 172. data after 1h reaction at 20 °c. biomass concentration 14.0 g/dm3 (dry wt.). fig. 5b. remaining metal uptake after 30 min washing of the sludge with cocl2, zn cl2, cd cl2 or cscl solution. data are the arithmetic mean of three replicates. according to hsiau and lo (1998), sequential extraction revealed that the percentages of the heavy metals of organically bound form and exchangeable form in chemically fixed sludge samples were in the order of cu > pb > cr > zn. however, mobility of cesium can be diminished by supplementing of activated sludge with clay materials or bentonites. in that case, cesium released from activated sludge will be bound irreversibly on clay minerals and will not be bio-available or leachable under natural conditions and even under more drastic conditions such as with alkali or acid solutions. clays (dyer et al., 2000) and bentonites (see e.g. a b nova biotechnologica 10-1 (2010) 59 galamboš et al., 2010; závodská and lesný, 2006) are well known sorbents for irreversible cesium binding, as well as for binding many heavy metals and metalloids. activated sludge disposes much higher capacity for metal sorption calculated for unit biomass, than the content of metals contained in municipal waste waters. it means that the sludge biomass is not saturated and can be used as sorbent for reversibly sorption of the metals from other liquid wastes. table 2. sorption capacities (mg/g, dry wt.) of naturally occurring sorbents. according to bailey et al. (1999), modified. sorbent cs co zn cd pb hg bark 32 182 400 modified cotton 1000 chitin 100 chitosan 558 796 1123 clay 16.5 58 microbial biomass 28 116 lignin 95 1865 150 modified wool 87 135 632 moss 46.7 peat 5.1 230 16.2 seaweed 215 344 33.3 18 1.2 xanthate zeolite 84.3 155.4 150.4 lichen biomass (1) 5.7 7.3 moss biomass (2) 7.2 12.2 19.4 green algae (3) 14.5 activated sludge(4) 24.5 activated sludge (5) 50 36 65 121 (1) pipíška et al. 2008; (2) pipíška et al., 2010; (3) horník et al., 2008; (4) choi and yun, 2006; (5) this paper. in tab. 2, the sorption capacity (q) values of activated sludge obtained in this paper are compared with q values of other sorbents published. as we can see, activated sludge showed the sorption capacity comparable with other low-cost sorbents and therefore the sludge could be used for lowering concentration of toxic metals originating from industrial effluents, subsequently dewatered or incinerated. 4. conclusions the non-treated activated sludge from aerobic phase of municipal waste water treatment plant contains the whole spectrum of metals. however, the sorption capacity of the sludge is much higher than actual concentration of heavy metals in treated waste waters. sludge can be used as an efficient sorbent for the removal of heavy metals from industrial liquid wastes. sorption capacity of activated sludge studied for co, cd, 60 marešová, j. et al. zn and cs from 0.5 mmol/dm3 solution was 36, 65, 121 and 50 mg/g (dry wt.), respectively. the ability of non-treated activated sludge to sorb co2+, zn2+, cd2+ and cs+ metal ions is based mainly on physical processes not dependent on the metabolic activity of the sludge microflora. recovery of the metals by washing with diluted hcl, edta and salt solutions decreases in the order: cs > co = zn > cd. the obtained data stress the potential of surplus production of activated sludge as a sorbent for binding of toxic and radiotoxic metals and metaloides from liquid industrial wastes. the next treatment of the sludge will depend on the concentration of sorbed metals and their toxicity. incineration will be one of the ways for final treatment. acknowledgement: we would like to thank juraj miština, m.a. for proofreading. department of english language, faculty of natural sciences, university of ss. cyril and methodius in trnava, slovak republic. references alvarez, e.a., mochon, m.c., sanchez, j.j., rodriguez, m.t.: heavy metal extractable forms in sludge from wastewater treatment plants. chemosphere, 47, 2002, 765-775. bailey, s.e., olin, t.j., bricka, r.m., adrian, d.d.: a review of potentially low-cost sorbents for heavy metals. wat. res., 33, 1999, 2469-2479. bhaskar, p.v., bhosle, n.b.: bacterial extracellular polymeric substance (eps): a carrier of heavy metals in the marine food-chain. environ. int., 32, 2006, 191-198. costley, s.c., wallis, f.m.: bioremediation of heavy metals in a synthetic wastewater using a rotating biological contactor. wat. res., 35, 2001, 3715-3723. choi, s.b., yun, y.s.: biosorption of cadmium by various types of dried sludge: an equilibrium study and investigation of mechanisms. j. hazard. mater. b, 138, 2006, 378–383. dyer, a., chow, j.k.k., umar, i.m.: the uptake of cesium and strontium radioisotopes onto clays. j. mater. chem., 10 (12), 2000, 2734-2740. fein, j.b.: thermodynamic modeling of metal adsorption onto bacterial cell walls: current challenges. adv. agron. 90, 2006, 179-202. fuentes, a., llorens, m., saez, j., aguilar, m., ortuno, f., meseguer, v.f.: phytotoxicity and heavy metals speciation of stabilised sewage sludges. j. hazard. mater., 108, 2004, 161-169. fytili, d., zabaniotou, a.: utilization of sewage sludge in eu. application of old and new methods a review. renew. sust. energ. rev., 12, 2008, 116-140. galamboš, m., kurčáková, j., rosskopfová, o., rajec, p.: adsorption of cesium and strontium on natrified bentonites. j. radioanal. nucl. chem., 2010, (in press). guibaud, g., van hullebusch, e., bordas, f., d´abzac, p., joussein, e.: sorption of cd (ii) and pb (ii) by exopolymeric substances (eps) extracted from activated sludges and pure bacterial strains: modelling of the metal/ligand ratio effect and role of the mineral fraction. bioresource technol., 100, 2009, 2959-2968. nova biotechnologica 10-1 (2010) 61 horník, m., pipíška, m., kočiová, m., augustín, j., lesný, j.: influence of chelating agents on 60co uptake by fresh water algae. cereal res. commun., 36, 2008, 419-422. hsiau, p., lo, s.: extractabilities of heavy metals in chemically-fixed sewage sludges. j. hazard. mater., 58, 1998, 73-82. iaquinta, m., stoller, m., merli, c.: development of synthetic wastewater from the tomato industry for membrane processing purposes. desalination, 200, 2006, 739-741. milne, c.j., kinniburgh, d.g., van riemsdijk, w.h., tipping, e.: generic nicadonnan model arameters for metal-ion binding by humic substances. environ. sci. technol., 37, 2003, 958-971. pal, a., paul, a.k.: microbial extracellular polymeric substances: central elements in heavy metal bioremediation. indian j. microbiol. 48, 2008, 49-64. pipíška, m., horník, m., remenárová, l., augustín, j., lesný, j.: biosorption of cadmium, cobalt and zinc by moss rhytidiadelphus squarrosus in the single and binary component systems. acta chim. slov., 2010 (in press). pipíška, m., horník, m., vrtoch, ľ., augustín, j., lesný, j.: biosorption of zn and co ions by evernia prunastri from single and binary metal solutions. chem. ecol., 24, 2008, 181-190. vullo, d.l., ceretti, h.m., daniel, m.a., ramirez, s.a.m., zalts, a.: cadmium, zinc and copper biosorption mediated by pseudomonas veronii 2e. bioresour. technol., 99, 2008, 5574-5581. wingender, j., neu, t.r., flemming, h.c.: what are bacterial extracellular polymeric substances? springer-verlag, heidelberg, germany, 1999, 171-200. závodská, l., lesný, j.: comparison of zn2+, cd2+ and sr2+ sorption characteristics for clinoptilolite and mordenite. in: szilágyi, m., szentmihályi, k. (eds.), trace elements in the food chain: proceedings: international symposium on trace elements in the food chain: budapest, 2006, 135-139. microsoft word maresova et al. nb 2010-2.doc nova biotechnologica 10-2 (2010) 157 cadmium sorption by dried plant biomass – reversibility studies kristína muráňová, jana marešová, miroslav horník, jozef augustín department of ecochemistry and radioecology, university of ss. cyril and methodius in trnava, j. herdu 2, trnava, sk-917 01, slovak republic (jana.maresova@ucm.sk) abstract: heavy metals such as cadmium are hazardous to biosystems and present possible human health risk. thus, the removal of cadmium from liquid wastes is of great importance from an environmental and industrial point of view. there is a tendency to use agricultural wastes for the sorption of toxic metals as an alternative to the existing conventional technologies. the aim of this work was to describe cd sorption and desorption equilibria by dried leaf biomass of tobacco (nicotiana tabacum l.), hop (humulus lupulus l.), pumpkin (cucurbita pepo l.), sunflower (helianthus annuus l.), cucumber (cucumis sativus l.), pepper (capsidum annuum l.), tomato (solanum lycopersicum l.) and vine-grape (vitis vinifera l.) using radiotracer technique with 109cdcl2. cadmium sorption q values (mg/g, d.w.) of all of plant biomass studied increased proportionally with the initial cdcl2 concentration within the range 0.01 – 10 mmol/l cdcl2. mean sorption capacity of dried leaf biomasses of eight plants for cd from the solution with the initial concentration c0 = 10 mmol/l cdcl2 in deionized water was q = 213 µmol/g (d.w.). by single step desorption of cd from leaf biomass for 30 minat 20 °c with deionized water, 0.1 mmol/l edta or 0.1 mmol/l hcl, up to 30 %, 85 % and 98 % of sorbed cd, respectively, was removed. obtained data can serve as a model for the prediction of sorption-desorption equilibria of biomass used for removing of cd from polluted waters and cd releasing back into waters containing other inorganic solutes. formation of cd2+, cdcl+, cdcl20, cdso40, cdoh+, cd2oh3+, cd(oh)20 and cd(oh)3species in dependence on ph values and the presence of clanions is also discussed. key words: cadmium, 109cdcl2, sorption, desorption, plant biomass 1. introduction cadmium is one of the most toxic metals found in effluents discharged from industries involved in metal plating, metallurgical alloying, mining, ceramics and other industrial activities. also, there is growing environmental concern about cd as being one of the most ecotoxic metals that exhibit highly adverse effects on soil biological activity, plant metabolism and the health of humans. usepa has also classified cadmium as group b1 carcinogen (usepa, 1999). the behaviour of cd in the environment and related health aspects has been reviewed by kabata-pendias and pendias (2001). broad spectrum of sorbents has received increased attention for heavy metal removal. data were published in numerous original papers and patents. for reviews see e.g. singh and tripathi (2007), sud et al. (2008). several physical and chemical methods have been used for removal of heavy metals from industrial liquid wastes, such as ion-exchange, chemical precipitation, chemical reduction and 158 muráňová, k. et al. adsorption. there are still problems associated with these methods mainly these are cost-expensive and can themselves produce other wastes, which has limited their industrial applications. among the available treatment processes, the application of biological sorbents is the most promising due to the following reasons: requirement of chemicals for the treatment process is reduced, lower operating costs, eco-friendly, higher efficiency at low levels of contaminations and cost-effective alternative of conventional techniques. in our previous papers we described sorption characteristics of co, zn and cd binding by dry biomass of lichen e. prunastri (pipíška et al., 2008) and moss r. squarrosus (pipíška et al., 2010) and by biomass of activated sludge of waste water treatment plant (marešová et al., 2010). the objective of this study was to obtain quantitative data of cadmium sorption by dried leaf biomass of common agricultural plants and reversibility of the sorption-desorption processes. 2. materials and methods 2.1 plant biomass leaves of sunflower (helianthus annuus l.), pumpkin (cucurbita pepo l.), cucumber (cucumis sativus l.), pepper (capsidum annuum l.), tomato (solanum lycopersicum l.) collected from plants growing in garden (trnava region) and leaves of vine-grape (vitis vinifera l.) from vineyard (malé karpaty region) in the middle of summer period. tobacco (nicotiana tabacum l.) and hop (humulus lupulus l.) leaves were obtained from plants cultivated in laboratory at 22 °c at light/dark period 12/12 h (2 000 lx). seeds of tobacco were germinated and grown in pots filled with granulated perlite watered with diluted hoagland medium ph 7.0 (hoagland, 1920). hop plants (variety osvald clone 72, genotype k-72/6/13) were obtained from the research institute of plant production in piešťany (sk). detached leaves were dried for 3 days at 60 °c, pulverized by rotatory knife blender and sieved by normalized sieves. fractions < 0.45 mm were used for experiments. 2.2 sorption experiments a batch equilibrium method was used to determine sorption of cd by dried leaf biomass of 8 plants. in plastic test tubes (10 ml) 0.05 g of dried biomass was mixed with 2 ml cdcl2 solution in deionized water (0.01 – 10 mmol/l), spiked with 109cdcl2 and placed on reciprocal shaker (200 min -1) at 20 °c. preliminary experiments showed that 10 min reaction time is sufficient for reaching of sorption equilibrium. for sorption experiments the initial ph value of solutions was adjusted to ph 5.0 with 1.0 m naoh. biomass was separated by centrifugation for 20 min at 2 800 × g and both sediments and liquid phase were analysed by gamma spectrometry. the experiments were conducted in triplicate. the amount of sorbed cd (μmol cd/g d.w.) was calculated according to the following equation: nova biotechnologica 10-2 (2010) 159 m ccv q eq )(* 0 −= (1) where q is the specific cd uptake (μmol cd/g biomass d.w.); v is the volume of cd solution (l); c0 is the initial concentration of cd in the solution (mmol/l); ceq is the concentration of cd in the solution in equilibrium (mmol/l) and m is mass of the dried biosorbent (g). 2.3 desorption experiments biomass (0.05 g, d.w.) after sorption experiments was separated by centrifugation for 20 min at 2 800 × g and resuspended by wortexing for 30 min in 5.0 ml deionized water, 1.0 ml 0.1 m edta or 1.0 ml 0.1 m hcl. cd concentrations in biomass and in extracts were estimated by similar way as in the sorption experiments. 2.4 radiometric and speciation analysis a gamma spectrometric assembly using the well type scintillation detector 54bp54/2-x, nai(tl) (scionix, nl) and data processing software scintivision-32 (ortec, usa) were used for cd determination in biomass and supernatants. a library of radionuclides was built by selecting characteristic γ-ray peaks (88.04 kev for 109cd, 661.66 kev for 137cs, 834.81 kev for 54mn and 1115.52 kev for 65zn) for energy and efficiency calibration. counting time 600 s allowed obtaining data with measurement error < 2 %, which do not reflect other source of errors. standardized solution of 109cdcl2 (3.94 mbq/ml, 50 mg/l cdcl2 in 3 g/l hcl) was obtained from the czech institute of metrology (prague, cr). cd speciation in the solution as a function of ph and concentration of clanions was performed using the visual minteq (ver. 3.0) modelling software. 3. results and discussions 3.1 cadmium sorption sorption experiments showed that dried leaf biomass is able to bind remarkable amounts of cadmium. q values (μmol/g, d.w.) at biomass concentration 25 g/l (d.w.) are proportional to the initial cdcl2 concentration within the range studied 0.01 – 10 mmol/l cdcl2. however as can be seen from the data in fig. 1 even at initial concentration c0 = 10 mmol/l cdcl2 plant sorbents were not saturated under given conditions and higher qmax values at saturation of sorbent can be expected. sorption capacity q of the dried leaf biomass of studied plants differs within the same order, ranging from 145 to 289 μmol/g (d.w.), despite of different taxonomic classification (tab. 1). in table 2, the value sorption capacities q (mg/g cd, d.w.) for naturally occurring sorbents are presented. we can conclude that studied plant biomasses showed similar results in comparison with others inorganic, organic and biological sorbents origin. 160 muráňová, k. et al. 1e-3 0,01 0,1 1 10 100 1e-3 0,01 0,1 1 10 100 0,1 1 10 100 1000 0,1 1 10 100 1000 tobacco hop pumpkin sunflower cucumber* cucumber** pepper tomato vine-grape q [μ m ol /g ] c 0 [mmol/l] fig. 1. cadmium sorption q (μmol/g; d.w.) by dried leaf biomass of different plants (25 g/l, d.w.) in dependence on initial cdcl2 concentration. data after 10 min reaction at 20 °c, ph 5.0 are the mean of three replicates. *c. sativus l. convar. longus,**c. sativus l. convar. viridis table 1. cadmium sorption q (μmol/g; d.w.) by dried leaf biomass (25 g/l, d.w.) of different plants after 10 min reaction in 10 mmol/l cdcl2 in deionized water at 20 °c, ph 5.0. data are the mean of three replicates. plant family q [μmol/g] humulus lupulus l. cannabaceae 288.8 ± 3.8 cucurbita pepo l. cucurbitaceae 283.1 ± 8.7 helianthus annuus l. asteraceae 268.4 ± 5.6 cucumis sativus l. convar. longus cucurbitaceae 228.4 ± 7.6 cucumis sativus l. convar. viridis cucurbitaceae 209.7 ± 6.1 capsicum annuum l. solanaceae 196.9 ± 4.3 nicotiana tabacum l. solanaceae 148.8 ± 4.0 solanum lycopersicum l. solanaceae 147.2 ± 4.0 vitis vinifera l. vitaceae 145.0 ± 2.0 table 2. sorption capacities q (mg/g cd; d.w.) of naturally occuring sorbents. (1) pipíška et al., 2010; (2) marešová et al., 2010; (3 ) bailey et al., 1999; (4) this paper. *c. sativus l. convar. longus,**c. sativus l. convar. viridis sorbent q [mg/g] ref. sorbent q [mg/g] ref. bark 32 3 activated sludge 121 2 chitosan 558 3 hop leaves 32.5 4 clay 16.5 3 pumpkin leaves 31.8 4 microbial biomass 28 3 sunflower leaves 30.2 4 modified wool 87 3 cucumber leaves* 25.7 4 peat 5.1 3 cucumber leaves** 23.6 4 seaweed 215 3 pepper leaves 22.1 4 xanthate 33.3 3 tobacco leaves 16.7 4 zeolite 84.3 3 tomato leaves 16.5 4 moss biomass 19.4 1 vine leaves 16.3 4 nova biotechnologica 10-2 (2010) 161 3.2 the influence of ph it is generally accepted that the ph optimum of biosorption for bivalent metal cations is within ph 4 – 6. in strong acid media the efficiency of cation sorption is minimal due to competitive effect of h+ ions. in alkaline region the situation is more complicated due to the existence of multiple cd species. data obtained by speciation program visual minteq shows that eight cd species can exist in alkaline solutions. molar fractions of cationic, anionic and nonionic forms of cd expressed in molar fraction x in dependence on ph value are shown in fig. 2. 2 3 4 5 6 7 8 9 10 11 12 0,0 0,2 0,4 0,6 0,8 cd2+ cdcl+ cdcl 2 0 cdso 4 0 cdoh+ cd 2 oh3+ cd(oh) 2 0 cd(oh) 3 m ol ar fr ac tio n x = [c dn + ] / [c dς n ] ph fig. 2. molar fraction x of cadmium species in dependence on solution ph at concentration 10 mmol/l cdcl20 and 20 °c. solution of inorganic salts corresponding to synthetic waste water according to iaquinta et al. (2006) (ppm): cl– 455; so42– 87; na+ 418; k+ 78; mg2+ 45; ca2+ 138. calculated by visual minteq ver. 3.0. as can be seen from the data in fig. 2, prevailing part of cd is present in cd2+ form (42 %) and cdcl+ form (51 %) and this proportion stay the same within ph range from ph 3.0 to ph 8.5. concentration of cd(oh)2 0 increases above ph 9. during the sorption of metals by sorbents from alkaline liquid wastes besides sorption of cd2+ cations also the existence of other than ionic metal forms with different solubility in water have to be taken into consideration. similar data was obtained also by guibaud et al. (2009), where sigmoidal ph dependence of cd2+ sorption by polysaccharides of activated sludge with inflection point at ph 8.6 was observed. 3.3 the influence of cl ions as can be seen from the data in fig. 3, molar fraction x of cd2+ significantly decreases in the presence of clions up to 10-1 mol/l nacl, as a result of the increase of cdcl+ molar fraction. at 1.0 mol/l nacl (5.8 %, w/v) concentration of cd2+ is minimal and prevailing cd species are non dissociated cdcl2 0 or cdcl+. in interactions of biosorbents with cd(ii) in the presence of clanions, what is typical for many kinds of liquid wastes, the existence of complex mixture of different cd species can be expected. mechanism of cd biosorption will then depend both on the ph values of liquid phase, as well as on the concentration of other solutes, mainly 162 muráňová, k. et al. clsalts, but also on the presence of other solutes able to form complexes with high values of stability constants log k. 1e-3 0,01 0,1 1 0,0 0,2 0,4 0,6 0,8 1,0 m ol ar fr ac tio n x = [c dn + ] / [c dς n ] cl[mol/l] cd2+ cdcl+ cdcl 2 0 fig. 3. molar fraction x of cd2+, cdcl+ and cdcl20 species in dependence on nacl concentration in 1.0 mol/l cdcl2 in deionized water and 20 °c. calculated by visual minteq ver. 3.0. 2 3 4 5 6 7 8 9 10 11 0,0 0,2 0,4 0,6 m ol ar fr ac tio n x = [c dn + ] / [c dς n ] 0.1 mmol/l ph cd2+ cdcl+ 2 3 4 5 6 7 8 9 10 11 0,0 0,2 0,4 0,6 ph cd2+ cdcl+ 1.0 mmol/l 2 3 4 5 6 7 8 9 10 11 0,0 0,2 0,4 0,6 m ol ar fr ac tio n x = [c dn + ] / [c dς n ] ph cd2+ cdcl+ 10.0 mmol/l 2 3 4 5 6 7 8 9 10 11 0,0 0,2 0,4 0,6 ph cd2+ cdcl+ 100.0 mmol/l fig. 4. ph dependence of molar fraction x of cd2+ and cdcl+ ions at different cdcl2 concentration and 20 °c in solution of inorganic salts simulating waste water according to iaquinta et al. (2006) (ppm): cl– 455; so42– 87; na+ 418; k+ 78; mg2+ 45; ca2+ 138. calculated by visual minteq ver. 3.0. nova biotechnologica 10-2 (2010) 163 3.4 desorption in dependence on the [biomass]: [extractant] ratio, different percentage of cadmium can be removed. by extracting with deionized water at the [biomass]: [extractant] = 1: 100 (w/v) ratio and in dependence on plant species up to 30 % of cd was removed by single step extraction at 20 °c. by extraction with 0.1 mol/l edta at [biomass]: [extractant] = 1: 20 (w/v) ratio, up to 85 % and with 0.1 m hcl up to 98 % was removed under identical conditions. by desorption with water, new concentration equilibrium expressed as p = [cd]sorbent: [cd]solution is formed. cadmium is released with higher efficiency from the binding sites of lower stability constants log k. stability constant of the metal complex can be described by the equation (2): log k = [ml] / [m]* [l] (2) where k is the stability constant, [m] is the concentration of cd2+ ions and [l] is the concentration of a ligand such as carboxylic or amino acids. 0,01 0,1 1 10 1 10 100 1000 10000 desorption with edta desorption with water p = [c d] bi om as s/ [c d] so lu tio n c0 [mmol/l] sorption fig. 5. sorbent to solution concentration ratio (mmol/kg)/(mmol/l) for cadmium in dependence on initial concentration of cdcl2. sorption process (–■–■–); desorption with deionized water (–o–o–) and desorption with 0.1 mol/l edta (–δ–δ–). experimental points are the mean values obtained from sorption experiments of 8 plants shown in fig. 1 (–■–■–); and of data obtained by desorption of biomass with deionized water (–o–o–) and 0.1 mol/l edta as described in materials and methods. metal ions can form more or less stable complexes with many biomolecules differing in stability constants log k. cd complexes with organic compounds can be divided into four groups. a: log k ~ 1 2 (carboxylic acids); b: log k ~ 5 6 (amino acids and citric acid); c: log k ~ 9 – 10 (cysteine, glutathione and other –sh compounds); d: log k ~ 16 18 (complexing ligands such as edta). classification is based on published data of cd and other bivalent metal complexes (martell and smith, 1964; srivastava et al., 1993; gunther and kastenholz, 2005). we can suppose that by extracting with deionized water only cd atoms bind into complexes of low log k values are released. characterization of the mode of cadmium 164 muráňová, k. et al. binding not extractable with the strongest ligands such as edta will require more detailed study. however differences in the efficiency of cd desorption with water and edta reflects the fact that broad spectrum of reactive groups differing in stability constants is taking place. 4. conclusions dried leaf biomass of eight vascular plants shows the sorption capacity for cadmium binding from cdcl2 water solution depending on the initial concentration of the solute, and is comparable with the sorption capacity of other sorbents of plant origin. sorbed cadmium is partially leachable with deionized water and with high efficiency by edta solution and diluted mineral acids. this supports the idea that in sorption processes cd complexes with different stability constants log k are formed. calculation by speciation program visual minteq showed, that both alkaline ph values and concentration of chloride anions determines the existence at least seven cd species with cationic, anionic and neutral charge. obtained data can serve for the prediction of cadmium transport in biosphere and at penetration into food chain from contaminated vegetable crops. references bailey, s.e., olin, t.j., bricka, r.m., adrian, d.d.: a review of potentially low-cost sorbents for heavy metals. water res., 33, 1999, 2469-2479. guibaud, g., van hullebusch, e., bordas, f., d´abzac, p., joussein, e.: sorption of cd (ii) and pb (ii) by exopolymeric substances (eps) extracted from activated sludges and pure bacterial strains: modelling of the metal/ligand ratio effect and role of the mineral fraction. bioresour. technol., 100, 2009, 29592968. gunther, k., kastenholz, b.: speciation of cadmium in the environment and food. in: cornelis, r., crews, h., caruso, j., heuman, k.g. (eds.), handbook of elemental speciation ii: species in the environment food, medicine and occupational health. john wiley and sons, ltd. 2005, 745 pp. hoagland, d.r.: optimum nutrient solutions for plants. science, 52, 1920, 562-564. iaquinta, m., stoller, m., merli, c.: development of synthetic wastewater from the tomato industry for membrane processing purposes. desalination, 200, 2006, 739-741. kabata-pendias, a., pendias, h.: trace elements in soils and plants. 3rd edition, crc press, boca raton, florida, usa, 2001, 403 pp. marešová, j., horník, m., pipíška, m., augustín, j.: sorption of co2+, zn2+, cd2+ and cs+ ions by activated sludge of sewage treatment plant. nova biotechnol., 10, 2010, 53-61. martell, a.e., smith, r.m.: stability constants of metal ion complexes. (special supplement no. 17). chemical society, london, 1964, 754 pp. nova biotechnologica 10-2 (2010) 165 pipíška, m., horník, m., remenárová, l., augustín, j., lesný, j.: biosorption of cadmium, cobalt and zinc by moss rhytidiadelphus squarrosus in the single and binary component systems. acta chim. slov., 57, 2010, 163-172. pipíška, m., horník, m., vrtoch, ľ., augustín, j., lesný, j.: biosorption of zn and co ions by evernia prunastri from single and binary metal solutions. chem. ecol., 24, 2008, 181-190. singh, s., tripathi, r.d. (eds.): environmental bioremediation technologies. springer-verlag, berlin 2007, 518 pp. srivastava, s.k., gupta, v.k., tiwari, b.b., ali, i.: electrophoretic determination of stability constants of zn(ii)and cd(ii)nitrilotriacetatepenicillamine mixed complexes. j. chromatogr., 635, 1993, 171175. sud, d., mahajan, g., kaur, m.p.: agricultural waste material as potential adsorbent for sequestering heavy metal ions from aqueous solutions – a review. bioresour. technol., 99, 2008, 6017-6027. usepa: us environmental protection agency, integrated risk information system (iris) on cadmium, national centre for environmental assessment, office of research and development, washington, dc, 1999. microsoft word melcakova 2010-1.doc nova biotechnologica 10-1 (2010) 33 biosorption of zinc from aqueous solution using algae and plant biomass iva melčáková, tomáš růžovič všb tu-ostrava, institute of environmental engineering, faculty of mining and geology, ostrava, czech republic (iva.melcakova@ vsb.cz, tomas.ruzovic.st@vsb.cz) abstract: in the present study, the sorption capacity of plant biomass has been studied; particularly the ability of biomass algae chlorella vulgaris, filamentous green algae spirogyra sp. and roots, stems and leaves of an invasive plant reynoutria japonica to bind up zn2+ ions. the results of this biosorption study revealed that the rate and extent of uptake were affected by ph level, contact time and initial metal concentration. the maximum uptake of metal ions was obtained at ph 6.0. the equilibrium sorption data for metal system at ph 6 were described by the langmuir isotherms model. for zn2+, sorption capacity qmax of 17 mg/g was achieved using biomass from leaves. removal of zn2+ with 1g of biosorbent from leaves was almost 77% when present in low concentrations, whereas it is lower at higher concentrations. keywords: chlorella vulgaris, spirogyra sp., reynoutria japonica, biosorption, zinc, isotherm 1. introduction metal pollution is one of the most important environmental problem today. three kinds of metals are of concern, including toxic metals (such as hg, cr, pb, zn, cu, ni, cd, as, co, sn etc.), precious metals (such as pd, pt, ag, au, ru etc.) and radionuclides (such as u, th, ra, am, etc.) (wang and chen, 2009). metals can be distinguished from other toxic pollutants, since are non-biodegradable and can accumulate in the living tissues, thus becoming concentrated throughout the food chain (williams et al., 1998). by far the greatest demand for metal sequestration comes from the need for immobilizing the metals “mobilized” by and partially lost through growing and everintensifying human technological activities. pollution of the environment by toxic metals arises as a result of many human activities like mining, metallurgy, electroplating, leather tanning, metal finishing, textile industry, and paper industry. effects of these metals on ecosystems are of large economic and public-health significance (volesky, 2001). biosorption and bioaccumulation belong to the group of biological methods suitable for heavy metal removal from wastewater (kaduková and virčíková, 2005). the biosorption is relatively new technology and could be considered for its economic edge as a possible alternative technique for metal recovery. in recent years, biosorption has been widely studied for the removal of metal ions, especially at the concentrations ranging from 1 to 100 mg/l, due to its lower costs and higher effectiveness than the conventional methods such as chemical precipitation and ion exchange (han et al., 2008). different biomass have been used to adsorb metal ions from the environment. bacteria, fungi, yeast, algae, and plants have proved to be 34 melčáková, i . and růžovič, t. potential metal sorbents (gupta et al., 2000; romera et al., 2007). while choosing biomaterial for metal sorption, its origin is a major factor to be taken into account; it can come from a) microorganisms as a by-product of fermentation industry, b) organisms naturally available in large quantities in nature and c) organisms cultivated or propagated for biosorption purposes using inexpensive media (ahluwalia and goyal, 2007). understanding the sorption of metal ions from aqueous solution is important for apllication in industrial water treatment. in this study we wanted to compare biosorption of zinc by laboratorly cultivated species chlorella vulgaris with ubiquitous and in large quantities in nature found species spirogyra sp. and reynoutria japonica. chlorella vulgaris is fast–growing edible algae, cultivated on large scale, and used as a food or feed supplement (chojnacka, 2007). several studies (bishnoi et al., 2007; gupta et al., 2006; gupta and sharma, 2008) has been reported about spirogyra sp., harvested from natural populations, which have exhibited its excellent ability to remove chromium, copper and lead from aqueous solutions. the cell wall of spirogyra sp. is very similar to that of terrestrial plants because its main components are cellulose and pectin. last species reynoutria japonica is an invasive ubiquitous plant investigated currently as a possible energetic plant. it is also known that the species of this genus are able to accumulate heavy metals from soil. zinc is the fourth among metals of the world in annual consumption. it is extensively used in the automobile industry, for the production of protective coatings for iron and steel, in cosmetics, powders, ointments, antiseptics, paints, varnishes, rubber and linoleum. zinc is also needed for manufacturing of parchment papers, glass, automobile tires, television screens, dry cell batteries and electrical equipment. the main sources of zn in the environment are zinc fertilizers, sewage sludges and mining and smelting (bradl et al., 2005). the average human body contains about 2 grams of zinc, which is essential for the normal activity of dna polymerization and for protein synthesis. soluble and astringent acid salts, such as znso4 in large doses (about 10 g), have caused internal organ damage and death (gupta and sharma, 2003). 2. materials and methods the culture of unicellular algae species, chlorella vulgaris (fig.1), the culture of filamentous green algae spirogyra sp. (fig. 2 and 3) and plant reynoutria japonica (fig.4) were used for laboratory experiments. 2.1 chlorella vulgaris cultivation chlorella vulgaris in log phase used in the experiments was inoculated in medium milieu bristol, modification 3n, at ph 7. the medium was sterilized by autoclaving at 121°c for 15 minute. medium was stored at 4°c until inoculated. cultures were grown in liquid media in 2 l glass erlenmeyer flasks, aerated with filtered air, and incubated at 25°c on a light table. samples were taken every 24 h using sterile glass pipettes. in the samples the cell counts were obtained using the thoma cellula, and the content of nova biotechnologica 10-1 (2010) 35 pigment chlorophyll a was determined by du®-64 spectrophotometer (beckman, memory pac +m). 2.2 preparation of biosorbents when chlorella vulgaris cultures reached the stationary phase, they were harvested and used for metal ion biosorption experiments. chlorella vulgaris was first cooled down in order to ease following centrifugation (10 minutes at 3000 rpm), and obtained biomass was extensively washed two times with water (1 l of de-ionized water per 1 g of biomass) to get rid of medium remnants. then it was dried in the oven (at 60°c) overnight and pulverized in a grinding mortar. acid pre-treatment was then done by washing the sorbent with 0.2 m solution of h2so4 (1 l of acid per 1 g of biomass for 90 minutes), washing twice again by de-ionized water, centrifuged once more and dried 24 hours at constant temperature of 60°c. filamentous green algae spirogyra sp. was collected from a fresh water pond. the sorbent was then prepared using the same procedure as described above. fig. 1. chlorella vulgaris fig. 2. spirogyra sp. fig. 3. spirogyra sp. fig. 4. reynoutria japonica 36 melčáková, i . and růžovič, t. all samples of reynoutria japonica used were collected from the same non-urban area in foothills of the lysá hora mountain, in the area of the moravskoslezské beskydy. this sampling area does not have any prior history of contamination by heavy metals. roots, stems and leaves of this plant were air-dried at room temperature. dried samples were ground and screened using a sieve shaker; uniform particle size fraction 1-2 mm was obtained. ion exchange resins manufactured for the same purpose generally feature particle sizes between 0.7 and 1.5 mm. biosorbent granule size usually ranges between 1 to 2 mm. particles of roots, stems and leaves were twice washed with 0.01 m of hcl (1 l of acid per 10 g of biomass), then with extensive volume of de-ionized water in order to remove soil or debris, and finally washed with distilled water. the biomass samples were then oven-dried at 90°c for one day. 2.3 chemicals zn2+ ions (znso4.7 h2o) were used in this study. test solutions containing this single ion were prepared by diluting proper amount of 1g/l stock solution of zinc ion in order to obtain desired concentrations. chemicals used were of analytical reagent grade and therefore used without further purification. 2.4 procedure of experiments 2.4.1 time course time course of zn2+ uptake by chlorella vulgaris, spirogyra sp. and reynoutria japonica was investigated. the sorbent with the final concentration 0.5 g/l of dried biomass of algae and 1 g/l of reynoutria japonica (leaves, stems, roots) was suspended in 200 ml or 500 ml of zinc ion solution. the flasks were placed on a shaker at 120 rpm at a room temperature (around 25°c) for 24 hours for algae and 6 hours for reynoutria japonica. the ph value of the solutions tended to drop during the equilibration and during the sorption experiments it was adjusted with 0.1 m solution of naoh. the temperature and ph were measured by a microcomputer meter. samples were taken from the solution at desired intervals and were filtered through membrane filter millipore 0.45 μm or, in the case of r. japonica, through filter paper ak-01 blue, dry. all samples were duplicated with the average presented in the results. the heavy metal concentrations in the resulting supernatant were measured by the atomic absorption spectrophotometry (aas) unicam 969, wavelength 213.9 nm. 2.4.2 effect of ph the experiment was conducted at concentration 100 mg/l of zinc ions for chlorella vulgaris and 10 mg/l for spirogyra sp. and reynoutria japonica, 1 g/l biosorbent dose in 50 ml and 500 ml zinc solution for six hours with ph varying from 4.0-6.0. ph of the solution was adjusted using 0.1 m naoh. nova biotechnologica 10-1 (2010) 37 2.4.3 adsorption isotherm in the present experiment we have determinate adsorption isotherms for zinc. amounts of 2 g/l dry acid-pre-treated biomass of algae and 1 g/l dry acid-pre-treated plant biomass (all three types: roots, stems and leaves) were suspended in samples of various concentrations (10-100 mg/l) of zn2+ solutions. the ph of solutions before and during equilibration was adjusted with 0.1 m and 0.01 m solutions of naoh. after 60 minutes of incubation, zinc samples were filtered in order to remove the biomass and metal concentration in supernatant was measured with aas. sorption capacity of the substrate (q) expressed in terms of metal amount sorbed on the unitary biosorbent mass (mg/g). this parameter has been calculated as indicated below (cimino et al., 2000). ( ) sccvq fi /−= (1) where: v – the volume of metal-bearing solution contacted with the sorbent some [l], ci – initial and residual concentrations of metal in the solution [mg/l], cf – residual concentrations of metal in the solution [mg/l], s – the amount of the added biosorbent [g]. 3. results and discussion 3.1 time course the kinetics experiments of zinc ions removal from solutions showed that biosorption is the equilibrium process, in which the equilibrium is reached after about 10 minutes. the ions are bound with the biomass steadily, and the final concentration of metal ions remained unchanged for 100 hours (chojnacka et al., 2005). to determine time course of biosorption of chlorella sp. biomass we have chosen zinc concentration of 100mg/l, based on our experience with previous experiments with chromium (chovancová, 2001). as zinc displayed different behaviour and the efficiency of its removal in high concentration was not sufficient, for following experiments with spirogyra sp. and reynoutria japonica we decreased concentrations to 10 mg/l. nevertheless, for both concentrations (100 mg/l and 10 mg/l) it can be concluded that at optimal ph value 6 (fig. 5 and 6) zinc binding onto algal and plant biomass is rapid (in the first 10 minutes). during the process, concentration of a metal ion gradually decreases and the equilibrium is reached; the concentration remains almost constant after approximately 100 minutes. adsorption slowed down in later stages because initially a large number of vacant surface sites may be available for adsorption and after some time, the remaining vacant surface sites may be difficult to occupy due to forces between the solute molecules of the solid and bulk phase (bishnoi et al., 2007). it is, however, necessary to say that in the case of higher concentration (100 mg/l) the equilibrium status has not been reached and after about 300 minutes zinc started to be separated out back into the solution (fig. 5). 38 melčáková, i . and růžovič, t. 0 2 4 6 8 10 12 14 0 200 400 600 800 1000 1200 1400 1600 time (minute) q (m g/ g) chlorella vulgaris fig. 5. time course of metal sorption of divalent zinc by chlorella vulgaris, ph 6.0, initial metal concentration 100 mg/l, room temperature 25°c. 0 1 2 3 4 5 6 7 8 9 0 50 100 150 200 250 300 350 400 time (minute ) q ( m g /g ) roots stems leaves spirogyra fig. 6. time course of metal sorption of divalent zinc by roots, stems and leaves of reynoutria japonica and spirogyra sp., ph 6.0, initial metal concentration 10 mg/l, room temperature 25°c. 3.2 effect of ph ph is one of the most important environmental factors influencing not only site dissociation, but also the solution chemistry of the heavy metals: hydrolysis, complexation by organic and/or inorganic ligands, redox reactions, and precipitation are strongly influenced by ph and, on the other side, strongly influence the speciation and the biosorption availability of the heavy metals (esposito et al., 2002). the effect of ph on the zinc biosorption capacity of biomass has been shown in fig. 7. the increase of sorption of zinc ions corresponds to ph values growing from 4.0 to 6.0, the latter being the optimum ph for biosorption of zinc ions by all types of biomass. acid-washed biosorbents can be viewed as natural ion-exchange materials that primary contain weak acid and basic groups (kratochvil and volesky, 1998). number of negatively charged active sites (functional groups such as carboxyl, amine, hydroxyl and phosphate groups) at higher ph increases, facilitating a higher electrical attraction to positively charged metal ions (klimmek et al., 2001; romera et al., 2007). chojnacka et al. (2005) identified in cyanobacteria spirulina sp. different functional groups at different ph values. in ph value range 5.0-9.0, which covers ph nova biotechnologica 10-1 (2010) 39 value used in our experiments, she identified with use of potentiometric titration carboxyl and phosphate group to be the main functional groups. our results of optimum ph value are in agreement with studies of romera et al. (2001), who studied untreated algae biomass of spirogyra insignis, and salehizadeh et al. (2003) and norton et al. (2004) studying bacteria. 0 2 4 6 8 10 12 14 16 0 1 2 3 4 5 6 7 ph q (m g/ g) roots stems leaves spirogyra sp. fig. 7. effect of ph on the sorption of zn2+ by roots, stems and leaves of r. japonica and spirogyra sp., ph 4.0-6.0, initial metal concentration 10 mg/l, room temperature 25°c. 3.3 determination of adsorption isotherms the fig. 8 displays metal uptake isotherms for zn2+ ions plotted against final metal concentration cf in aqueous solutions. when the initial zn 2+ concentration increased from 10 to 50 mg/l, uptake by chlorella vulgaris increased, and reached 15.9 mg/g. 0 5 10 15 20 25 0 20 40 60 80 100 120 final metal concentration in solution (mg/l) m et al u pt ak e (m g/ g) chlorella vulgaris spirogyra sp. reynoutria japonica roots reynoutria japonica stems reynoutria japonica leaves fig. 8 sorption isotherms for the sorption of zn2+ onto chlorella vulgaris, spirogyra sp. and roots, stems and leaves of reynoutria japonica biomass, ph 6.0, room temperature 25.0 o c. similar results were obtained with leaves of reynoutria japonica (uptake 19.5 mg/g), and spirogyra sp. biomass (uptake 14.5 mg/g), both at initial zinc concentration 75 mg/l. it is possible to conclude that in both low and high concentrations, leaves showed the best results. at initial zn2+ concentration 100 mg/l, decrease of sorption in 40 melčáková, i . and růžovič, t. all biomass types was recorded, with the exception of roots and stems of reynoutria japonica; however these two types of biomass displayed generally the lowest zinc uptake ability among all biomass investigated. the process of zinc sorption on the biosorbent was described by the langmuir adsorption model, which is widely used to analyze data for water and wastewater treatment applications. the langmuir model represents one of the first theoretical descriptions of nonlinear sorption and suggests that uptake occurs on a homogeneous surface by monolayer sorption without interaction between adsorbed molecules. in addition, the model assumes uniform energies of adsorption onto the surface and no transmigration of the adsorbate (sahmoune et al., 2008). the langmuir equation is given by eq. (2) ff bcbcqq += 1/max (2) where: qmax – maximal metal uptake [mg/g], b – a constant related to the affinity of the binding sites [l/mg], q – experimental metal uptake [mg/g], cf – residual concentrations of metal in the solution [mg/l]. q and b can be determined from the linear plot of cf:/q vs. cf (donmez et al., 1999). the main advantage of this model is the possibility of evaluation of qmax maximum possible quantity of a metal ion adsorbed per gram of adsorbent, and b – parameter related to the affinity of binding sites for a metal ion (michalak et al., 2007). in general, for good biosorbents, high qmax and high b are desirable (davis et al., 2003). the langmuir constants r2 for the zinc biosorption onto biomass of chlorella vulgaris, spirogyra sp. and reynoutria japonica are showed in fig. 9 and 10. the results indicate the highest applicability of the langmuir model for two biosorbents: spirogyra sp. with the best regression coefficient r2 = 0.9834, and leaves of reynoutria japonica r2 = 0.9807. based on qmax, it can be concluded that spirogyra sp. (qmax = 17.8 mg/g) has slightly higher adsorption capacity for zinc than leaves of reynoutria japonica (qmax =17.0 mg/g). as for parameter b, however, spirogyra sp. has significantly lower (b = 0.06) than leaves of reynoutria japonica (b = 0.26). hashim and chu (2004) suggest that a biosorbent with low qmax and high b could outperform a biosorbent with high qmax and low b, especially in cases where the metal ion to be removed is present at trace amounts. therefore, higher b value of leaves of reynoutria japonica indicates its higher affinity for zinc. ranking of sorptions of all sorbents studied, based on qmax, can be set up as follows: spirogyra sp. > leaves > stems > chlorella vulgaris > roots of reynoutria japonica. very similar results for spirogyra sp. were obtained by romea et al. (2007). in his experiments with untreated spirogyra sp. biomass maximum capacity for zinc was found to be 21.6 mg/g, and parameter b = 0.04. adsorption capacity for zinc by waste tea leaves biomass (similar type of biomass as leaves of reynoutria japonica) was found to be 11.8 mg/g (tee and khan, 1988). nova biotechnologica 10-1 (2010) 41 r2 = 0,9834 r2 = 0,9223 -2 0 2 4 6 8 10 12 0 10 20 30 40 50 60 70 80 90 cf c f/q chlorella spirogyra sp. fig. 9. sorption isotherms for the sorption of zn2+ onto chlorella vulgaris and spirogyra sp., ph 6.0, room temperature 25°c. r2 = 0,9128 r2 = 0,9807 r2 = 0,9779 0 2 4 6 8 10 12 14 16 0 20 40 60 80 100 120 cf c f/q roots stems leaves fig. 10. sorption isotherms for the sorption of zn2+ onto roots, stems and leaves of reynoutria japonica, ph 6.0, room temperature 25°c. 4. conclusions this work has demonstrated the possibility of utilization of biomass of algae chlorella vulgaris and spirogyra sp., and of a plant reynoutria japonica for biosorption of zinc ions from aqueous solutions. the binding capacity of zn2+ ions to biosorbent has been shown to depend upon ph, with the highest binding at ph 6.0. the biosorbents have good capacity for zinc adsorption, especially in low metal concentrations. there were no major differences in biosorption of zinc between cultured chlorella vulgaris and natural spirogyra sp. and reynoutria japonica. references ahluwalia, s.s., goyal, d.: microbial and plant derived biomass for removal of heavy metals from wastewater. bioresour. technol., 98, 2007, 2243-2257. 42 melčáková, i . and růžovič, t. bishnoi, n.r., kumar, r., kumar, s., rani, s.: biosorption of cr(iii) from aqueous solution using algal biomass spirogyra spp. j. hazard. mater., 135, 2007, 142–147. bradl, h.: heavy metals in the environment.1sted. london: elsevier, 2005, 282 pp. davis, t.a., volesky, b., mucci, a.: a review of the biochemistry of heavy metal biosorption by brown algae. water res. 37, 2003, 4311–4330. dönmez, g.c., aksu, z., ozturk, a., kutsal, t.: a comparative study on heavy metal biosorption characteristics of some algae. process biochem., 34, 1999, 885–892. cimino, g., passerini a., toscano, g.: removal of toxic cations and cr(vi) form aqueous solution by hazelnut shell. wat. res., 34, 2000, 2955-2962. esposito, a., pagnanelli, f., veglio, f.: ph-related equilibrium models for biosorption in single metal systems. chem. eng. sci., 57, 2002, 307-313. gupta, v.k., rastogi, a.: biosorption of lead from aqueous solution by green algae spirogyra sp.: kinetics and equilibrium studies. j. hazard. mater., 152, 2008, 407-414. gupta, v.k., rastogi, a., saini, v.k., jain, n.: biosorption of copper(ii) from aqueous solutions by spirogyra species. j. colloid interface sci., 296, 2006, 59-63. gupta, v.k., sharma, s.: removal of zinc from aqueous solutions using bagasse fly ash a low cost adsorbent. ind. eng. chem. res., 42, 2003, 6619-6624. haase, e.: pflanzen reiningen schwermetall-böden. umwelt (dusseldorf), 7-8, 1988, 342-344. hashim, m.a., chu, k.h.: biosorption of cadmium by brown, green and red seaweeds, chem. eng. j. 97, 2004, 249–255. chojnacka, k., chojnacki, a., górecka. h.: biosorption of cr3+, cd2+ and cu2+ ions by blue–green algae spirulina sp.: kinetics, equilibrium and the mechanism of the process. chemosphere, 59, 2005, 75-84. chojnacka, k.: using biosorption to enrich the biomass of chlorella vulgaris with microelements to be used as mineral feed supplement. world j. microbiol. biotechnol. 23, 2007, 1139-1147. chovancová,i.: uptake of trivalent chromium by biosorbent of algae of chlorella vulgaris, new trends in mineral processing iv, ostrava 28-30.6. 2001, 493-501. kaduková, j., virčíková, e.: comparison of differences between copper bioaccumulation and biosorption. environ. int., 31, 2005, 227– 232. klimmek, s., stan, h.-j., wilke, a., bunke, g. buchholz. r.: comparative analysis of the biosorption of cadmium, lead, nickel, and zinc by algae. environ. sci. technol., 35, 2001, 4283-4288. michalak, i., zielinska, a., chojnacka, k., matula, j.: biosorption cr (iii) by microalgae and macroalgae: equilibrium of the process. am. j. agri. biol. sci., 2, 2007, 284-290. romera, e., gonzalez, f., ballester, a., blazquez, m.l., munoz, j.a.: biosorption with algae: statistical review. crit. rev. biotechnol., 26, 2006, 223-35. salehizadeh, h., shojaosadati, s.a.: removal of metal ions from aqueous solution by polysaccharide produced from bacillus firmus. water res., 17, 2003, 4231–4235. nova biotechnologica 10-1 (2010) 43 tee, t.w., khan, a.r.m.: removal of lead, cadmium and zinc by waste tea leaves. environ. technol. lett., 9, 1988, 1223–32. váňa j., roth, j.: zabezpečení fytopaliva v oblasti elektrárny tušimice. dílčí zpráva. envicho s.r.o., chomutov, 1994. volesky, b.: detoxification of metal-bearing effluents: biosorption for the next century. hydrometallurgy, 59, 2001, 203-216. wang, j.,chen, c: biosorbents for heavy metals removal and their future. biotechnol. adv., 27, 2009, 195-226. williams, c.j., aderhol, d., edyvean, r.g.j.: comparison between biosorbents for the removal of metal ions from aqueous solutions, water res., 32, 1998, 216-224. nova biotechnol chim (2022) 21(2): e1322 doi: 10.36547/nbc.1322 1 nova biotechnologica et chimica chemical profiles and antibacterial activities of acetone extracts of globba macrocarpa hong thien van1,, tan viet pham1, ngoc an nguyen1, hanh thi dieu nguyen1, quoc hung nguyen2, thanh tho le2, van son le3 1institute of biotechnology and food technology, industrial university of ho chi minh city, no. 12 nguyen van bao street, go vap district, ho chi minh city, vietnam 2center of analytical services and experimentation hcmc, vietnam, no. 2 nguyen van thu, dakao ward, district 1, ho chi minh city, vietnam 3binh chau-phuoc buu nature reserve, bung rieng ward, xuyen moc district, ba ria-vung tau province, vietnam  corresponding author: vanhongthien@iuh.edu.vn article info article history: received: 13th december 2021 accepted: 7th april 2022 keywords: acetone extract antibacterial activities gc/ms globba macrocarpa abstract globba macrocarpa gagnep. is a rare species of globba genus (zingiberaceae family). the present study reported the chemical compositions and antibacterial effects of acetone extracts obtained from the g. macrocarpa rhizomes and aerial parts. by using gas chromatography mass spectrometry (gc/ms) assay, fifty and thirty-two chemical compounds were identified from rhizomes and aerial parts of the species, respectively. of those, germacrene d (15.25 %), 1h-indole, 4-(3-methyl-2butenyl)(14.33 %), (e)-β-farnesene (11.28 %), and 2-biphenylamine, 3-methyl (10.27 %) were the major constituents in the rhizome extract while the aerial part extract was characterized by the predominance of linolenic acid (19.89 %), palmitic acid (13.05 %), phytol (7.52 %), and neophytadiene (4.76 %). in addition, the rhizome extract had antibacterial activities against five 5 out of 6 oral bacteria, including pseudomonas aeruginosa, salmonella enteritidis, salmonella typhimurium bacillus cereus, and staphylococcus aureus. meanwhile, the aerial part extract was active against 4 out of 6 test bacteria, except for escherichia coli and s. typhimurium. introduction globba l. is a third largest genus belonging to zingiberaceae with over 100 species. this genus is distributed widely throughout tropical and subtropical of asia such as india, southern china, new guinea and southeast asia. globba plants are small perennial herbs, reaching to a height of 1 m, except for g. racemosa (about 3 m) (williams et al. 2004). members of globba consist of a large number of useful plants. for instance, the g. bulbifera rhizomes have been used to cure cough, asthma, and snakebite. g. multiflora was used to treat headache and rheumatic inflammation (jain 1995). the anti-inflammatory, antioxidant, and antipyretic activities were recorded as the biological activities of g. malaccensis (ngamrojanavanich et al. 2005). in addition, previous studies showed the phytochemical composition and bioactivities of several globba species (andila and tirt 2019; raj et al. 2020). globba macrocarpa gagnep. is a rare species of globba genus. this species was described for the first time by gagnepain (1901) and mainly mailto:vanhongthien@iuh.edu.vn.sk nova biotechnol chim (2022) 21(2): e1322 2 distributed in cambodia, thailand and vietnam (pham 2000; nguyen 2017). in 2020, we conducted some field trips to the binh chau-phuoc buu nature reserve, bung rieng ward, xuyen moc district, ba ria-vung tau province, and encountered a flowering population of g. macrocarpa. to date, the chemical compositions and bioactivities of g. macrocarpa are still unknown. the present study, thus, firstly reported the chemical constituents and antibacterial effects of acetone extracts from the g. macrocarpa rhizomes and aerial parts. experimental plant materials the samples of g. macrocarpa were collected from binh chau-phuoc buu nature reserve, bung rieng ward, xuyen moc district, ba ria-vung tau province, vietnam, location of about 10o32’19.4”e 107o26’57.4”n, 18 m in elevation (fig. 1). fig.1. globba macrocarpa. a – species in habitat, b – flowers, c – rhizome. bacterial strains in this study, the antibacterial properties of acetone extracts of the g. macrocarpa rhizome and aerial parts were investigated by using six bacterial strains such as salmonella typhimurium-atcc 13311, salmonella enteritidis-atcc 13976, pseudomonas aeruginosa-atcc 27853, escherichia coli-atcc 25922, staphylococcus aureus-atcc 25923, and bacillus cereus-atcc 11774. extraction procedures the rhizome and aerial parts of g. macrocarpa were dried at 50 oc until constant weight. the dried samples were pulverized. 250 ml of acetone 99 % solution was used to macerate 50 g of the dried powders at ambient temperature for three days. the studied samples were then filtered through the whatman paper. the process was repeated twice and filtrates were concentrated under the reduced pressure at 60 oc to obtain the brown extracts. the final extracts were subjected to sublimation drying to completely remove the remaining acetone (bobinaitė et al. 2013). gas chromatography/mass spectrometry (gc/ms) assay the trace 1310 gas chromatograph (thermo fisher scientific, waltham, usa) and isq 7000 single quadrupole mass spectrometer was used to identify the chemical compositions in the acetone nova biotechnol chim (2022) 21(2): e1322 3 extract. gc column db-5ms 30 m, 0.25 mm, 0.25 µm (agilent technologies, santa clara, usa) was used and carrier gas was helium with the column flow rate of 1.2 ml.min-1. the specimen was added into the system with the split ratio of 30 : 1, the splitless mode of 1 min, and the split flow of 36 ml.min-1, the inlet temperature of 250 oc. the initial temperature was set for 5 min at 80 oc. the temperature was then raised to 280 oc at the rate of 20 oc.min-1 and hold for 10 min. the electron ionization mode and the ion source temperature were 70 ev and 250 oc, respectively. the mass scan range was 29 – 650 m/z. the nist 2017 library version 2.3 (nist 2017) was used to identify the chemical constituents of studied samples. antibacterial assay the antibacterial properties of the acetone extract of the g. macrocarpa were conducted by disc diffusion assay following the clsi guideline (clsi 2010). luria-bertani broth was used to activate the bacterial strains until their turbidity was equivalent to 0.5 mcfarland. mueller hinton agar plate was inoculated with 0.1 ml of the bacterial culture by spread – plate technique before sterile paper discs containing 10 µl of the extract solution were placed on its surface. gentamycin antibiotic discs (10 µg.ml-1) (nam khoa biotek, ho chi minh city, vietnam) were used as the positive control. the plates were incubated at 37 oc for 18 – 24 h. the antibacterial effects of the studied samples were identified by recording the size of the zone of inhibition. three biological replicates were used for the experiment, and results were expressed as mean ± standard deviation (sd). differences between means groups were calculated by lsd procedure using the statgraphics centurion xv software (statgraphics technologies, inc., the plains, usa) with p < 0.05. results and discussion constituents of g. macrocarpa extracts the acetone extracts isolated from rhizomes and aerial parts of g. macrocarpa in this study contained a total of 50 and 32 components, respectively (table 1 and 2). accordingly, the rhizome extract was characterized by the predominance of germacrene d (15.25 %), 1h-indole, 4-(3-methyl-2-butenyl)(14.33 %), (e)-β-farnesene (11.28 %) and 2-biphenylamine, 3-methyl(10.27 %) (fig. 2a). meanwhile, the aerial part extract was found to be rich of linolenic acid (19.89 %), palmitic acid (13.05 %), phytol (7.52 %) and neophytadiene (4.76 %). previous studies have been reported the biological properties of some compounds obtained from the acetone extracts of g. macrocarpa rhizomes and aerial parts in this study. for instance, germacrene d, a major component from both rhizome and aerial part extracts, possessed the strong insecticidal activities against acyrthosiphon pisum, sitobion avenae, and myzus persicae (bruce et al. 2005). similarly, germacrene d had also potent larvicidal effects against three mosquitos such as anopheles gambiae, culex quinquefasciatus, and aedes aegypti with ld50 values of 1.8, 2.1 and 2.8 mg.cm-3 (ravi ands sita 2007). recently, schepetkin et al. (2020) demonstrated that germacrene d possessed the immunomodulatory activities. accordingly, germacrene d could inhibit neutrophil ca2+ mobilization, chemotaxis, and reactive oxygen species production with ic50 values of 0.51, 5.4 and 9.9 µg.ml-1 (schepetkin et al. 2020). in addition, (e)-β-farnesene, another component from both rhizome and aerial part acetone extracts of g. macrocarpa, showed the effects on natural enemies to cabbage aphid (brevicoryne brassicae) control in chinese cabbage fields (cui et al. 2012). also, this compound has been reported to possessed other biological activities, including repellent and aphicidal activities against myzus persicae (qin et al. 2016). furthermore, α-pinene and β-pinene, two bioactive compounds found in the rhizome and aerial part extracts, has been suggested as the larvicidal and insecticidal agents against aedes aegypti, lasioderma serricorne, and rhodnius nasutus (aparna et al. 2012; wu et al. 2015; carta et al. 2017). palmitic acid, a compound from both rhizome and aerial part acetone extracts of g. macrocarpa, possessed the anti-inflammatory activities (aparna et al. 2012), physiological role, nova biotechnol chim (2022) 21(2): e1322 2 metabolism and nutritional implications in human (carta et al. 2017). fig. 2. gc/ms chromatograms of studied extracts from g. macrocarpa rhizomes (a) and aerial parts (b) with major components. table 1. constituents of extract of g. macrocarpa rhizome. no. rt components [%] no. rt components [%] 1 2.15 tyranton 0.23 26 10.83 γ-amorphene 0.45 2 3.25 α-pinene 0.14 27 10.87 guaia-10(14),11-diene 0.40 3 3.54 camphene 0.69 28 10.91 α-bulnesene 0.22 4 4.06 sabinen 0.38 29 10.95 epicubebol 0.48 5 5.28 isosylvestrene 0.42 30 11.17 germacrene b 0.53 6 5.38 orthodene 0.28 31 11.21 tricyclo[5.1.0.0(2,4)]oct-5-ene-5propanoic acid, 3,3,8,8tetramethyl 0.34 7 5.63 β-ocimene 0.21 32 11.27 isoaromadendrene epoxide 0.59 8 6.36 3-(pyrrolidin-1-yl)cyclopent-2en-1-one 0.56 33 11.40 1h-indole, 4-(3-methyl-2butenyl) 1.65 9 6.93 triacetoneamin 0.14 34 11.51 1-epi-cubenol 0.24 10 7.10 4(1h)-quinolinone, octahydro-1methyl 0.39 35 11.56 aromadendrene oxide-(1) 0.12 11 7.42 alcanfor 0.51 36 11.60 benzeneacetoneitrile, αcyclopentyl 0.21 12 7.97 methyl salicylate 0.11 37 12.01 1h-indole, 4-(3-methyl-2butenyl) 14.33 13 8.12 dihydroanethole 0.77 38 12.38 3-(2-methylbut-3-enyl)-1h-indole 8.01 14 9.89 β-elemen 1.33 39 12.53 quinoline, 2-ter_butyl2.57 15 10.06 α-gurjunene 1.60 40 12.69 2-biphenylamine, 3-methyl10.27 16 10.17 caryophyllene 0.49 41 13.11 3-methyldiphenylamine 0.73 17 10.20 γ-elemene 0.43 42 13.32 palmitic acid 2.52 18 10.32 (e)-β-farnesene 11.28 43 13.41 benzenamine, 4-methyl-nphenyl 0.61 19 10.38 aristolene 0.13 44 14.18 9(e),11(e)-conuated linoleic acid 2.0 20 10.44 humulene 0.43 45 14.21 linolenic acid 1.44 21 10.55 isogermacrene d 0.40 46 15.95 palmitin, 2-mono0.63 22 10.58 (z)-α-farnesene 1.93 47 17.04 9,12-octadecadienoic acid (,),2,3dihydroxypropyl ester 0.93 23 10.62 germacrene d 15.25 48 17.23 stearin, 2-mono0.44 24 10.72 bicylogermacrene 1.35 49 24.13 stigmasterol 3.08 25 10.75 β-bisabolene 0.36 50 25.42 γ-sitosterol 0.94 4 nova biotechnol chim (2022) 21(2): e1322 3 table 2. constituents of extract of g. macrocarpa aerial part. no. rt components [%] no. rt components [%] 1 4.07 β-pinene 0.70 17 12.69 neophytadiene 4.76 2 4.24 cyclohexane, 1,2,4-trimethyl 0.38 18 12.72 3,7,11,15tetramethylhexadec-2-ene 1.05 3 6.37 3-(pyrrolidin-1-yl)cyclopent-2-en-1one 0.77 19 12.82 phytol 0.57 4 6.93 triacetonamin 0.21 20 12.69 neophytadiene 1.13 5 7.01 isophorone 1.62 21 13.32 palmitic acid 13.05 6 7.10 (5r,8ar)-5propyloctahydroindolizine 0.22 22 13.41 2-biphenylamine, 3-methyl3.17 7 8.07 pyrazine, 3-butyl-2,5-dimethyl 0.24 23 14.08 phytol 7.52 8 9.02 5h-1-pyrindine 0.12 24 14.18 linoleic acid 4.36 9 9.17 2-methoxy-4-vinylphenol 0.20 25 14.21 linolenic acid 19.89 10 10.31 (e)-β-farnesene 0.41 26 14.30 octadecanoic acid 1.48 11 10.57 trans-α-bergamotene 0.24 27 15.94 palmitin, 2-mono1.94 12 10.61 germacrene d 1.06 28 17.08 2-monolinolenin 3.93 13 10.68 α-farnesene 2.17 29 23.58 campesterol 0.55 14 11.26 (-)-spathulenol 0.30 30 24.10 stigmasterol 1.04 15 11.99 1h-indole, 4-(3-methyl-2-butenyl)2.84 31 25.39 β-sitosterol 5.80 16 12.52 3-(2-methylbut-3-enyl)-1h-indole 2.91 32 26.37 cholesteryl formate 0.70 several chemical compounds obtained from g. macrocarpa aerial parts and rhizomes in this study have been reported to possess the antimicrobial properties by previous studies. accordingly, simionatto et al. demonstrated that (e)-β-farnesene had antibacterial effects against bacillus subtilis, staphylococcus aureus, salmonella setubal, and pseudomonas aeruginosa (simionatto et al. 2007). in addition, linolenic acid showed strong bacterial activities against staphylococcus aureus, and streptococcus pyogenes (zheng et al. 2005). also, α-pinene presented the antimicrobial against a large amount of bacterial and fungal strains, including pseudomonas aeruginosa, staphylococcus aureus, escherichia coli, streptococcus faecalis, candida albicans, sclerotinia sclerotiorum, mycobacterium smegmatis, cylindrocarpon mali, aspergillus niger, and stereum purpureum (prudent et al. 1993). in another report, α-pinene has been also reported to possess the antibacterial activities against staphylococcus aureus, s. epidermidis, streptococcus pyogenes, and s. pneumonia. moreover, β-pinene had the antibacterial activity against gram-positive bacteria causing potential infectious endocarditis such as staphylococcus aureus, s. epidermidis, streptococcus pyogenes, and s. pneumonia (medeiros et al. 2007). as mentioned above, g. macrocarpa is a rare species. the phytochemicals and biological properties of this plant are limited. however, there are some publications for chemical compositions and antimicrobial effects of other member of the globba species using gs/ms assay. for instance, the major components of ethanol extracts isolated from g. candida rhizomes grown in indonesia included levoglucosan (19.07 %), allylhydrazone acetaldehyde (5.52 %), trans-2,3-epoxybutane (6.30 %), butan-3-enoic acid methyl ester (4.36 %) while the leaf extract has been reported to contain pinostrobin chalcone (75.63 %), 1-(1-(hydroxyphenyl-methyl)-cyclopropyl)-2-phenyl-ethano (2.4 %), benzenepentanal (2.08 %) as the major compounds (andila and tirta 2019). in addition, the chemical profiles of the essential oil extracted from the rhizomes of g. pendula from vietnam were found to be rich in -selinen (36.45 %) and ishwarane (10.76 %) (ngo et al. 2020). furthermore, the chemical compositions of rhizome essential oils of three globba species collected from india, including g. cernua, g. marantina, and g. ophioglossa have been reported (menon and dan 2009). as a result, caryophyllene was the most 5 nova biotechnol chim (2022) 21(2): e1322 2 components in the oils (19.3 – 24.2 %), followed by α-humulene, (z)-nerolidol, and (z,z)-farnesol (menon and dan 2009). antibacterial activities of g. macrocarpa extracts the extracts of g. macrocarpa rhizomes were found to be effective against five oral bacteria, except for e. coli (fig. 3 and table 3). as a result, the rhizome extract showed potent antibacterial effects against p. aeruginosa and s. aureus with the zone of inhibition of 19.0 ± 1.7 and 14.7 ± 2.5 mm, respectively which higher than that of positive control (table 3). also, the rhizome extract possessed moderate effects against b. cereus (14.2 ± 0.8 mm), s. enteritidis (11.2 ± 1.2 mm), and s. typhimurium (10.8 ± 1.1 mm). the data in table 3 and fig. 3 presented the antimicrobial effects of aerial part extracts of g. macrocarpa. among 6 tested bacteria, the extract was found to be effective against four studied bacteria, including p. aeruginosa, b. cereus, s. enteritidis, and s. aureus. generally, the aerial part extract possessed antibacterial effects weaker than that of rhizome extract. this extract only possessed the moderate effects against s. enteritidis with the zone of inhibition of 13.5 ± 1.3 mm while this sample presented the weak antibacterial activities against b. cereus (9.3 ± 0.3 mm), s. aureus (9.3 ± 0.3 mm), and p. aeruginosa (7.2 ± 0.3 mm). table 3. zone of inhibition of acetone extracts from g. macrocarpa against six oral bacteria. microorganism size of zone of inhibition [mm] rhizome aerial part gentamycin b. cereus 14.2 ± 0.8b 9.3 ± 0.3a 22.3 ± 0.6c e. coli 21.3 ± 1.5 p. aeruginosa 19.0 ± 1.7c 7.2 ± 0.3a 13.5 ± 1.8c s. enteritidis 11.2 ± 1.2a 13.5 ± 1.3a 20.3 ± 1.5b s. typhimurium 10.8 ± 1.1a 14.8 ± 1.1b s. aureus 14.7 ± 2.5b 9.3 ± 0.3a 12.3 ± 2.1ab a,b,cthe notable variation (p < 0.05) was represented by distinct superscript lower-case letters in the same row. fig. 3. antibacterial effects of the rhizome (r) and aerial part (a) extracts of g. macrocarpa. a – b. cereus; b – p. aeruginosa; c – s. aureus; d – s. enteritidis; e – s. typhimurium. (-) – negative control, (+) – positive control. 6 nova biotechnol chim (2022) 21(2): e1322 3 the chemical components of hexane and dichloromethane extracts obtained from different parts of g. schomburgkii collected from thailand have been reported. accordingly, hexane extract of rhizomes was characterized by the predominance of β-patchoulene (9.8 %), 3-acetoxy-5-pregnene (7.8 %), and γ-bicyclohomofarnesal (6.4 %) while phytol was the most abundant components in the hexane extract of stalks (13.8 %) and leaves (34.6 %). the major constituents in the hexane extract of flowers were β-caryophyllene (16.5 %) and γ-bicyclohomofarnesal (14.6 %). meanwhile, the most major constituent the dichloromethane extracts of rhizomes, stalks, leaves, and flowers were α-gurjunene (16.3 %), β-caryophyllene (11 %), phytol (19 %), and caryophyllene oxide (15.8 %), respective (doungchawee et al. 2019). in addition, the antimicrobial activities of the hexane, dichloromethane, and methanol extracts from four plant parts of g. schomburgkii have been investigated. all twelve extracts had an inhibitory effect on streptococcus sobrinus. the hexane and dichloromethane extracts displayed activity against streptococcus mutans, salmonella typhimurium, and staphylococcus aureus whereas aspergillus flavus was inhibited by the dichloromethane extracts (leaves, stalks, and flowers) and the methanol extracts of leaves (doungchawee et al. 2019). similarly, the dichloromethane extract and its fractions and sub-fractions obtained from g. schomburgkii rhizomes were mainly composed of γ-bicyclohomofarnesal (4.1 – 20.8 %), (e)-15,16dinorlabda-8(17),12-dien-14-one (7.6 – 58.2 %). moreover, crude dichloromethane extract and its fractions were found to be effective against four pathogenic bacteria, including s. aureus, m. luteus, e. coli, and p. aeruginosa (suekaew et al. 2020). conclusion this study identified 50 and 32 chemical compositions in the acetone extracts of g. macrocarpa rhizomes and aerial parts, in which some components have been reported to possess many biological properties. the rhizome extract was demonstrated to be active against 5 bacterial strains with the diameter of inhibition zones of p. aeruginosa (19.0±1.7 mm), s. aureus (14.7 ± 2.5 mm), b. cereus (14.2 ± 0.8 mm), s. enteritidis (11.2 ± 1.2 mm) and s. typhimurium (10.8 ± 1.1 mm) while the aerial part extract showed antibacterial effects s. enteritidis (13.5 ± 1.3 mm), s. aureus (9.3 ± 0.3 mm), b. cereus (9.3 ± 0.3 mm) and p. aeruginosa (7.2 ± 0.3 mm). the results from the present study can be used as reference for pharmaceutical products and relative fields from g. macrocarpa which could increase the economic valuation of this species. acknowledgement the authors would like to thank ms. thi ngọc anh nguyen, mr. tan loc tran, mr. tri phong nguyen, ms. hong bao nghi nguyen, ms. thuy tien le and ms. thi bao tran nguyen for their cooperation. conflict of interest the authors declare that they have no conflict of interest. references andila p, tirta i (2019) distribution and phytocomponent in the ethanol extract of globba candida gagnep. 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20: 21939-21945. zheng cj, yoo js, lee tg, cho hy, kim yh, kim wg (2005) fatty acid synthesis is a target for antibacterial activity of unsaturated fatty acids. febs letters 579: 5157-5162. 8 microsoft word mocak 9-1 2009.doc nova biotechnologica 9-1 (2009) 91 evaluation of iupac limit of detection and iso minimum detectable value electrochemical determination of lead ján mocák1, ivan janiga2, estera rábarová1 1department of chemistry, university of ss. cyril and methodius, nám. j. herdu 2, trnava, sk-917 01, slovak republic (jan.mocak@ucm.sk) 2department of theoretical bases of mechanical engineering, faculty of mechanical engineering, slovak university of technology, nám. slobody 17, sk-81231 bratislava, slovak republic abstract: the way of calculating the limit of detection recommended by iupac is compared to the minimum detectable value used by iso as one of the most important performance characteristics of a measurement process. in this work, theoretical analysis of both characteristics is given together with directions for their practical use. calculations are exemplified using electrochemical trace analysis of lead in surface water. key words: limit of detection, critical value, minimum detectable value, limit of quantification, determination of lead, voltammetric water analysis. 1. introduction capability of detection is an important performance characteristic of a measurement process. in chemistry, a representative characteristic of any analytical method is the smallest concentration or the mass of the analyte (the analyzed sample component) that can be detected with a specified degree of certainty. the related quantity is the limit of detection, lod, defined by international union for pure and applied chemistry (iupac, 1978) first of all as yd = μb + kd σb (1) where yd denotes the lod in the signal domain, μb is the expected mean blank value (the analyte-free sample), σb is the standard deviation of the blank and kd is a proportionality factor. the statistical quantities μb and σb are related to a very large set of observations and are unknown therefore they were in chemical practice commonly approximated by the sample quantities the arithmetic mean by of nb blank measurements, and the blank standard deviation sb. together with the lod further limits have also been invented and used in chemistry. among them, the limit of quantification (or determination), loq, refers to the smallest analyte concentration or mass, which can be quantitatively analysed with a reasonable reliability by a given procedure. its oldest, traditional definition (acs 92 mocák, j. et al. committee, 1980) is similar to that given for lod in the signal domain, but the numerical factor kq is used: yq = μb + kq σb (2) in practice however, a more important task is to know the concentration equivalents of the signal lod and loq values. for this purpose the slope q1 of the linear calibration line, y = q0 + q1x, expressing the dependence of the signal y on concentration x, is commonly used: lod = (yd −⎯ by ) / q1 = kd sb / q1 (3) loq = (yq −⎯ by ) / q1 = kq sb / q1 (4) it is noteworthy that the calibration model should be written in statistics using the variables denoted by capital letters, i.e. y = q0 + q1x, but it is frequently ignored in chemical literature for the sake of simplicity. the proportionality factors kd = 3 and kq = 10 have been traditionally accepted in this approach therefore this way of the lod and loq calculation will be designed in this paper as “traditional approach”. it is imperfect with regard to contemporary statistical theory mainly due to the following drawbacks (mocak et al., 1997): (1) the normal distribution is used for typically small sets of observations, supposing equality μb = by and σb = sb, (2) an exact intercept value is considered in calibration, supposing q0 = by , unaffected by random errors. despite these mistakes, mainly due to its simplicity and a long term usage, the traditional approach has been still used even though newer, more correct ways have been described in the literature, especially in the documents recommended by iupac (currie, 1994a, b; 1995; mocak et al., 1997). situation in this field is rather complicated also due to some terminological inconsistency introduced in the past. some authors (demanding equality of the α and β errors) used the proportionality factor 6 for the limit of detection and the factor of 3 assigned to the limit of decision; others suggested to keep the way of the lod calculation as explained above (with kd = 3) and utilized the proportionality factor 6 for the limit of identification, loi (alternatively named also as the limit of guarantee of purity). a more detailed discussion on this topic can be found e.g. in the iupac document (mocak et al., 1997). the aim of this work is to explain in a statistically correct way the calculation of the lod and further limits characterizing the measurement method in chemistry in the region of low concentrations (trace analysis) and, in addition, to compare these limits to analogical characteristics defined by international standards organization (iso, 2002), which is nowadays universally accepted as a leading metrological institution in many branches of science and technology. moreover, it will be recommended in the conclusion part of this work what performance characteristics should be implemented when evaluating measurements in chemical trace analysis and a guideline will be proposed regarding the use of appropriate terminology. nova biotechnologica 9-1 (2009) 93 2. theory 2.1. limit of detection obtained by upper limit approach the upper limit approach, ula, is fundamental newer way of the lod and loq calculations. it is based on the following details (mocak et al., 1997; mocak and bobrowski, 2000): (a) it makes use of the one-sided upper confidence limit for a future individual observation (green, 1978; massart et al., 1988), which defines the one-sided prediction band in calibration for predicting the maximum possible signal value, induced by random errors in measurement. the signal value corresponding to the zero analyte concentration (the blank) is here used at the 100(1−α) % probability level. (b) as the most suitable, the significance level (1−α) = 0.99 was recommended, which guarantees the best agreement of this calculation procedure with the previous traditional approach. (c) the signal variance is assumed constant (homoscedastic) therefore the sample standard deviation is considered constant at zero as well as non-zero concentrations (but not too far from zero). consequently, the residual standard deviation syx, expressing the regression error, is used instead of the blank standard deviation sb. (d) the values of the multiplication factors kd and kq are not fixed but depend on the number of experiments performed, which is reflected by the critical value of tdistribution utilized in calculation. (e) the concentration lod and loq values are estimated from the corresponding signals rigorously by regression using the inverse calibration model, x = f−1(y). it means that the lod and loq calculations are calibration model dependent. the concentration lod and loq values for the general straight line calibration model, y = q0 + q1x, are given as: lod = [t(n−2,1−α) syx / q1 ] [1 + 1/n + 2x / 1 ( = n i ∑ xi − x ) 2 ]1/2 (5) loq = 3 [t(n−2,1−α) syx / q1 ] [1 + 1/n + 2x / 1 ( = n i ∑ xi − x ) 2 ]1/2 (6) where n concerns the number of calibration points involved in the regression procedure, t(n−2,1−α) is the critical tvalue for the number of degrees of freedom (equal to n−2) and the significance level 0.99, xi is the i-th point of the concentration coordinate, x is the mean concentration of all points used in calibration. residual standard deviation syx represents the error in regression and is given by the squared deviation of ˆiy , calculated in regression, from yi, measured in calibration experiment: 2 2 0 1 1 1 1 1ˆ( ) ( ) 2 2 n n yx i i i i i i s y y y q q x n n= = = − = − − − −∑ ∑ (7) using this approach, the multiplication factor kd is defined as: kd(n,α) = t(n−2, 1−α) [1 + 1/n + 2x / 1 n i= ∑( xi − x ) 2 ] 1/2 (8) 94 mocák, j. et al. with regard to equations (5) and (6) there exists a simple relation between two multiplication factors: kq(n,α) = 3 kd(n,α). if the calibration experiment is performed in the equidistant manner, it is possible to utilize the corresponding entries of table 1 for a quick calculation of the lod and loq. moreover, the lod and loq values can be then calculated in a way similar to the traditional approach using simple multiplication formulae: lod = kd(n,α) syx / q1 ; loq = kq(n,α) syx / q1 = 3 lod (9a,b) the c(n) and b(n) terms introduced in table 1 depend exclusively on the concentration values and are independent of the signal values therefore they can be pre-calculated. the only condition to assure the validity of this simplified calculation procedure is to keep strictly the equidistant allocation of all calibration points, including the blank value (x = 0). 2.2. critical value and minimum detectable value a performance characteristic of any measurement process, characterizing the capability of detection, has been defined by (iso, 2000 a,b; 2007) as the minimum detectable value, mdv. another characteristic defined by iso is the critical value, cv. according to iso 11843-2, the concentration of analyte in the laboratory sample is named the state variable, z, since it represents the state of the material being analyzed. an analyte-free material is considered to be in the basic state. the difference between the state variable, z, and its value in the basic state is called the net state variable, denoted by x. the state variable or the net state variable cannot be observed directly, but they are related to an observable response variable, y, via calibration function f, defined by the mathematical relationship y = f(z) or y = f(x), representing the mathematical model of the measurement. in chemical calibration measurements, the response variable y is usually an instrument signal. the investigated analyte concentration is finally calculated by means of the evaluation function f−1, which represents the inverse of the calibration function, x = f−1(y). the iso critical value, xc, and the minimum detectable value, xd, of the net state variable are defined (janiga et al., 2004, 2006) by the equations cv = 2 0 1 1 1 ( 1 ) 1cc xx ˆ ˆy q x x t v, ˆ ˆq q i j s σ α − = = − + + (10) mdv = 2 1 1 ( , , ) 1d xx ˆ x x q̂ i j s σ δ ν α β= + + (11) where t(ν, 1−α) denotes a (1−α) % quantile of the tdistribution with ν = (i j – 2) degrees of freedom, i number of states (calibration standards), j number of parallel measurements, δ − non-centrality parameter of the non-central t-distribution, σ̂ − estimated residual standard deviation of the calibration line (identical to syx in part 2.1 for n = i j). nova biotechnologica 9-1 (2009) 95 table 1. the k d factors and auxiliary quantities used in the lod and loq calculation for α = 0.01 (onesided) and the number of experiments n assuming equidistant calibration* ) n ν (1+1/n)1/2 c(n) b(n) t(ν, 0.99) kd(ν, 0.99) 3 1 1.15470 0.50000 1.35401 31.821 43.086 4 2 1.11803 0.45000 1.30384 6.965 9.081 5 3 1.09545 0.40000 1.26491 4.541 5.744 6 4 1.08012 0.35714 1.23443 3.747 4.625 7 5 1.06905 0.32143 1.21008 3.365 4.072 8 6 1.06066 0.29167 1.19024 3.143 3.741 9 7 1.05409 0.26667 1.17379 2.998 3.519 10 8 1.04881 0.24546 1.15994 2.897 3.360 11 9 1.04447 0.22727 1.14812 2.821 3.239 12 10 1.04083 0.21154 1.13792 2.764 3.145 13 11 1.03775 0.19780 1.12904 2.718 3.069 14 12 1.03510 0.18571 1.12122 2.681 3.006 15 13 1.03280 0.17500 1.11430 2.650 2.953 16 14 1.03078 0.16544 1.10813 2.624 2.908 17 15 1.02899 0.15686 1.10258 2.602 2.869 18 16 1.02740 0.14912 1.09758 2.583 2.836 19 17 1.02598 0.14211 1.09304 2.567 2.806 20 18 1.02470 0.13571 1.08891 2.552 2.779 21 19 1.02353 0.12987 1.08512 2.539 2.756 22 20 1.02247 0.12451 1.08165 2.528 2.734 23 21 1.02151 0.11957 1.07844 2.518 2.715 24 22 1.02062 0.11500 1.07548 2.508 2.698 25 23 1.01980 0.11077 1.07274 2.500 2.682 26 24 1.01905 0.10684 1.07019 2.492 2.667 27 25 1.01835 0.10317 1.06781 2.485 2.654 28 26 1.01770 0.09975 1.06558 2.479 2.641 29 27 1.01709 0.09655 1.06350 2.473 2.630 30 28 1.01653 0.09355 1.06155 2.467 2.619 32 30 1.01550 0.08807 1.05800 2.457 2.600 34 32 1.01460 0.08319 1.05480 2.449 2.583 36 34 1.01379 0.07883 1.05200 2.441 2.568 38 36 1.01307 0.07490 1.04940 2.435 2.555 40 38 1.01242 0.07134 1.04710 2.429 2.543 ∞ ∞ 1.00000 0.00000 1.00000 2.326 2.326 *) t(ν, 0.99) denotes the critical tvalue ; ν = n − 2 ; b(n) = [1 + 1/n + c(n)] 1/2 ; ( ) ( ) ( ) .x/x/xx/xnc n i n i ii∑ ∑ = = −=−= 1 1 222 11 symbol sxx conventionally represents the sum 2 1 ( ) i i i xxs j x x = = −∑ (12) 96 mocák, j. et al. a considerable similarity of eqs. (5) and (10) is evident. moreover, it should be noted that for the sake of simplicity (appreciated by a practical chemist) some symbols in the lod calculation recommended by iupac (mocak et al., 1997) were simplified using e.g. q0, q1 and syx instead of 0q̂ , 1q̂ and σ̂ (or yxσ̂ ); another change valid for this work is using x for concentration instead of c. 3. material and methods all chemicals used were of analytical reagent grade; distilled and de-ionised water was used in all measurements. lead(ii) ions in surface water were determined by differential pulse anodic stripping voltammetry (dpasv) using an autolab/pgstat 20 electrochemical instrument, the netherlands. a standard three-electrode voltammetric cell with the static mercury drop electrode smde-1 (laboratorní přístroje, prague), a reference 3 mol/l silver-silver chloride electrode, and a platinum wire auxiliary electrode were used in all electrochemical measurements. the following parameters were set for the pb(ii) determination: deposition potential −1 v, equilibration time 10 s, modulation time 0.04 s, interval time 0.1 s, initial potential −0.8 v, end potential −0.2 v, step potential −0.002 v, modulation amplitude −0.05 v, and temperature 25 ± 0.5 °c. experimental data sampled by the electrochemical instrument were written to the computer hard disk and finally processed by microsoft excel and origin (microcal software, inc., northampton, ma) software. 4. results and discussion 4.1. comparison of iupac and iso measurement characteristics the calibration experiment was designed in the following way: (a) blank solution and seven standard solutions with a non-zero concentration were used in the concentration range 0–1.40 ppb pb(ii) (i = 8). (b) four replicate measurements (j = 4) of the signal (dpasv current) were performed four each solution (including blank) so that altogether n = i j = 8×4 = 32 measurements were performed. (c) two additional signal measurements were made for the calculations of the lod and loq values by “traditional approach” so that altogether six blank measurements were made and nb = 6 was used in eqs. (3) and (4). (d) the obtained values of signal and concentration were processed by linear regression and the corresponding quantities were calculated using the equations shown above. since the regression calculation in “traditional approach” is usually made without the blank measurements (which create here a distinct data set), the blank signals were not included so that n = i j = 7×4 = 28 in this case. the most important results and values characterizing the measurement performance, mainly lod, loq, cv and mdv, obtained for determination of lead in surface water, are summarised in table 2 together with the needed auxiliary quantities. nova biotechnologica 9-1 (2009) 97 several important inferences are available when exploring the results shown in table 2 (where in its entries more decimal figures are left than necessary only due to a better comparison): (a) exactly equal lod and cv values are not surprising since by a thorough inspection of eqs. (5) and (9) it can be found that these equations are identical. (b) in the given case, the lod calculated by traditional approach is not very different from the correct lod (and cv) value but it may be by chance more different, higher or lower, since it depends on the differences between sb and syx as well as 3 and t(ν, 0.99). (c) the found minimal detectable concentration is a bit smaller than the doubled lod value but the difference is small (0.73 %); it is explained by the fact that the non-centrality parameters δ of the non-central t-distribution are not too different from the doubled critical tvalues assuming equal α = β and the same (not too small) number of degrees of freedom. table 2. determination of lead by dpasv comparison of the lod and loq values with the critical value, cv, and the minimum detectable value, mdv * ) traditional approach ula (iupac recommended) iso nb 6 n 32 n 32 ⎯yb 19.2917 ν 30 ν 30 sb 0.47726 syx 0.58427 σ̂ 0.58427 3sb 1.4318 i 8 10sb 4.7726 j 4 q0 19.5186 q0 19.4067 q0 19.4067 q1 7.2437 q1 7.3557 q1 7.3557 t(ν, 0.99) 2.457 t(ν, 0.99) 2.457 t(ν, 0.95) 1.697 kd 3.741 δ(ν, 0.01,0.01) 4.879 kq 11.223 δ(ν, 0.05,0.05) 3.367 x 0.7000 x 0.7000 sxx 6.7200 sxx 6.7200 lod, ppb 0.1977 lod, ppb 0.2051 cv (xc), ppb 0.2051 loi, ppb 0.3953 2 lod, ppb 0.4102 mdv (xd), ppb 0.4072 loq, ppb 0.6589 loq, ppb 0.6153 *) the measured quantity with the corresponding unit of the blank signal mean by and the blank standard deviation sb is the maximum dpasv peak current in na. the ratio of the signal unit to the concentration unit (ppb) makes the slope unit. the loi and loq in traditional approach are defined as 6sb / q1 and 10sb / q1, resp. the residual standard deviation is defined as: 2 0 1 1 1 1ˆ ˆ ˆ( ) 2 i j ij i i j y q q x i j σ = = = − − ⋅ − ∑ ∑ . the most needed values δ can be found in table 3 otherwise 2 t(ν,1−α) may be approximately used. (d) if α = β = 0.05 were used in the iso approach then the 98 mocák, j. et al. resulting mdv would be smaller by 31 % however, it was justified in the iupac recommendation (mocak et al., 1997) that a better choice for chemical measurements should be α = 0.01 otherwise the lod and further limits used in chemical trace analysis would be too low, i.e. too optimistic. the best design of the calibration experiment is equidistant with at least one standard, except the blank, located in the region around the loq. the equidistant design allows using of very simple eqs. (9a,b) with the kd factor found in the last column of table 1. the usage of the calibration points at the concentration levels much higher than the limits of detection and quantification is sometimes made in practice but is not permissible (massart et al., 1988) because of errors caused by a distant extrapolation. therefore very often a special calibration experiment is necessary for determining the lod and loq, which is different from that used in a routine laboratory work. 4.2. recommendation what limits to use as mentioned in the first two parts of this work, there are nowadays known and defined several performance characteristics of a measurement process in chemical trace analysis due to the existence of iupac as well as iso standards, recommendations and guidelines. therefore it is reasonable to select those of them which are most important with regard to current trends of their utilization. consequently, we would like to propose three main performance characteristics for a general use: (1) the limit of detection, lod, as an equivalent of cv but much more widespread in chemical literature, (2) the minimum detectable value, mdv, the iso quantity widely widespread in science and technology, (3) the limit of quantification, loq, as an unique chemical characteristic relevant to the smallest measure at which quantitative analysis is possible. 5. conclusions newer way of calculation of the limit of detection, lod, and limit of quantification, loq, recommended by iupac (mocak et al., 1997), overcomes the problems caused by statistical incorrectness of by now still used traditional way of calculation and can be applied easily as shown in this paper. correct lod and loq values can be obtained by equations (5) and (6) or, which is the simplest way, using eqs. (8) and (9a,b) under condition that an equidistant calibration design is realized. in such a case the proportionality factor kd can be found from table 1 and the kq factor is computed as its triple. the iso defined critical value, cv, is identical to the lod defined by eq. (5). the minimum detectable value, mdv, is calculated by means of eq. (11) using the relevant non-centrality parameter δ of the non-central t-distribution, accessible in table 3 for common cases. otherwise the non-centrality parameter δ can be approximated by the doubled critical tvalues assuming equality α = β and the same number of degrees of freedom ν. under these conditions 2 lod represents a good mdv approximation. the calculation possibilities are demonstrated in table 2. nova biotechnologica 9-1 (2009) 99 table 3. values of the non-centrality parameter δ (v, α, β) of the non-central t-distribution for v degrees of freedom and significance levels α and β (here α = β ). v δ (v, 0.05, 0.05) δ (v, 0.01, 0.01) v δ (v, 0.05, 0.05) δ (v, 0.01, 0.01) 2 5.516 15.217 39 3.349 4.824 3 4.456 9.338 40 3.347 4.819 4 4.067 7.520 41 3.346 4.815 5 3.870 6.683 42 3.344 4.811 6 3.752 6.213 43 3.343 4.807 7 3.673 5.915 44 3.342 4.803 8 3.617 5.710 45 3.341 4.800 9 3.575 5.562 46 3.339 4.797 10 3.543 5.449 47 3.338 4.793 11 3.517 5.361 48 2.337 4.790 12 3.496 5.290 49 3.336 4.787 13 3.479 5.232 50 3.335 4.785 14 3.464 5.184 51 3.334 4.782 15 3.451 5.143 52 3.334 4.779 16 3.440 5.108 53 3.333 4.777 17 3.431 5.077 54 3.332 4.774 18 3.423 5.051 55 3.331 4.772 19 3.415 5.027 56 3.330 4.770 20 3.408 5.006 57 3.330 4.768 21 3.402 4.987 58 3.329 4.766 22 3.397 4.971 59 3.328 4.764 23 3.392 4.955 60 3.328 4.762 24 3.388 4.942 70 3.322 4.746 25 3.383 4.929 80 3.318 4.734 26 3.380 4.917 90 3.315 4.724 27 3.376 4.907 100 3.312 4.717 28 3.373 4.897 120 3.309 4.706 29 3.370 4.888 150 3.305 4.695 30 3.367 4.879 200 3.301 4.685 31 3.365 4.871 300 3.297 4.674 32 3.362 4.864 400 3.295 4.669 33 3.360 4.857 500 3.294 4.665 34 3.358 4.851 600 3.293 4.663 35 3.356 4.845 700 3.293 4.662 36 3.354 4.839 800 3.293 4.661 37 3.352 4.834 1000 3.292 4.659 38 3.350 4.829 ∞ 3.290 4.653 acknowledgement: financial support of this work by the grants vega 1/1005/09 and vvce-0004-07 is highly acknowledged. references acs committee of environmental improvement: guidelines for data acquisition and data quality evaluation in environmental chemistry. anal. chem., 52, 1980, 2242-2249. 100 mocák, j. et al. currie, l.a., horwitz, w.: iupac recommendations for defining and measuring detection and quantification limits. analysis, 22, 1994, m24-m26. currie, l.a., svehla, g.: nomenclature for the presentation of results of chemical analysis. pure appl. chem., 66, 1994, 595-608. currie l. a.: nomenclature in evaluation of analytical methods including detection and quantification capabilities. iupac recommendations 1995. pure appl. chem., 67, 1995, 1699-1723. green, j.r., margerison, d.: (1978). statistical treatment of experimental data. amsterdam. elsevier. chapter 14.3. iso 11843-2:2000: capability of detection − part 2: methodology in the linear calibration case. international organization for standardization (01-may-2000). 24 pp. corrigendum: iso 11843-2/cor1:2007. iupac, analytical chemistry division: nomenclature, symbol, units and their usage in spectrochemical analysis. ii. data interpretation. spectrochim. acta, 33 b, 1978, 241-246. iupac: comission v5 web site (1999): http://users.unimi.it/ape/v5. janiga, i., garaj, i., cisko, p.: estimation of minimum detectable value by using linear calibration with constant standard deviation. forum metricum slov., 8, 2004, 68-73. janiga, i., mocak, j., cisko, p., garaj, i., szarková, d.: detection of the mercury content in food and medicines by means of linear calibration funktion. forum statisticum slov., 2, 2006, 67-72. massart d.l., vandeginste, b.g.m., deming, s.n., micotte, y., kaufman, l.: chemometrics: a textbook. elsevier, amsterdam, 1988, p. 86-91; p. 113-114. mocak, j., varga, s., polak, p., gergely, s., izak, j.: calibration some newer chemometrical aspects in instrumental analysis. wissenschaftliche zeitsch., 32, 1990, 43-49. mocak, j., bond, a. m., mitchell, s., schollary, g.: a statistical overview of standard (iupac and acs) and new procedures for determining the limits of detection and quantification: application to voltammetric and stripping techniques. pure appl. chem., 69, 1997, 297-328. mocak, j., bobrowski, a. determination of cadmium and lead in water – new recommended way of evaluating the limits of detection and quantification. water sci. technol., 1, 2001, 19-26. stn iso 11843-2: detekčná schopnosť. časť 2: metodika lineárnej kalibrácie (in slovak). stn (slovak technical standard), bratislava, 2002. 46 nova biotechnologica et chimica 12-1 (2013) doi 10.2478/nbec-2013-0005 © university of ss. cyril and methodius in trnava application of isotopic dilution and single-step extractions for labile soil zinc determination vladimír frišták, martin pipíška, tatiana gablovičová, juraj lesný department of ecochemistry and radioecology, university of ss. cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic (vladimir.fristak@ucm.sk) abstract: concentration of available zinc from soils is the primary concern in assessment of its toxicity or essentiality for plants. this study evaluates the changes in chemical extractable zn from three slovak typical soils with simultaneous extractions as tools of zinc bioavailability. we found out that extractability of binding zinc decreased in order na2edta, mehlich 3, mehlich 2, nh4no3 and cacl2 for all soil samples. using flow-through stripping chronopotentiometry (scp) and atomic absorption spectrometry (gfaas) we found out that maximum of soil zinc was removed by organic ligands. lability of zn determined by isotopic dilution method using 65zn and γ-spectrometry showed the significant decrease of isotopic exchangeable zinc fraction (e-value) with decrease of soil reaction. obtained e-values of uppermost soil horizons showed the zinc lability ranged from 20 to 39%. our research confirmed the effect of soil reaction, composition and physico-chemical characteristics to zn lability. for further assessment of zinc bioavailability is needed to find the correlation and effects of structural changes and aging in studied soils. key words: soil, zn, bioavailability, extraction, e-value 1. introduction zinc is an essential trace element for the biological systems and is getting into the soil weathering of minerals and rocks forming the subsoil of the environment. major form is divalent ion zn2+ that is involved into sorption interactions of individual soil components. the increased concentrations of zinc can be potential risk of phytotoxicity. many elements involved as trace elements at higher than optimal concentrations can be toxic (frišták et al., 2013). soil contamination is not directly limited but can be reasonably associated with the negative anthropogenic effects as one of the major environmental problems. generally, the mobility of trace metals in soils is a function of its chemical forms (vijver et al., 2003). bioavailability may be defined as a fraction of metal that is available or can be made available for uptake of organisms (van gestel, 2008). mobility and bioavailability of heavy metals in soil depend on their speciation or fractionation. luoma and rainbow (2005) showed factors of metals bioavailability such as soil characteristics, routes exposure and physiological attributes. bioavailability can be also affected by the application of fertilizers and soil conditioners, which can significantly change the soil reaction (ph), thus uptake of element by plants acceptors. generally, the higher value of ph of the soil can cause more mobile and accessible elements forms for plant uptake (frišták et al., 2012). as a tool for estimation and determination of bioavailable metals fraction and metal fractionation in soils are commonly used simultaneous and sequential extraction bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 14:49 utc nova biotechnologica et chimica 12-1 (2013) 47 protocols as parts of fraction analysis. non selectivity of extracting agents and redistribution of elements among phases during extraction are disadvantages of these methods (tessier et al., 1979). despite a weak selectivity, chemical extraction methods are still often used to provide an understanding of mobility and bioavailability of metals (hullebusch et al., 2005). direct methods have generally insufficient sensitivity for metal speciation analysis and give the quantity of metal ions in solution together with those in the solid phase which are in equilibrium with the dissolved metal ions. therefore, determination of exchangeable metal fraction (evalue) represents quantification of ion pool from which ambient living organisms may take up the metal (sterckeman et al., 2009). the main aim of our paper was to describe distribution, leaching and bioavailability of zinc in soil samples from three typical slovak areas by series of simultaneous extraction protocols. for obtaining of relevant data and comparing the method the isotopic dilution with 65zn was used. 2. materials and method 2.1 experimental available fractions of zinc in samples of soil extract were measured using flowthrough stripping chronopotentiometry. experimental measurements were carried out on electrochemical analyser ecaflow model glp 150 (istran, ltd., bratislava, slovakia) equipped with electrochemical cell of type 104 with auxiliary, ag/agcl reference and e-104l graphite porous working electrodes. used parameters are given in table 1. obtained results were compared with reference values of gfaas measurements by atomic absorption spectrophotometer shimadzu aa-7000 (usa). for correction of background d2 lamp was used, after microwave digestion of the samples by the multiwave system mw 3000 (anton paar gmbh, aus). to calculate bioavailable zinc and obtain parameters of paired t-test, origin 8.0 professional (originlab corporation, northampton, usa) was used. table 1. operation parameters of electrochemical determination of zinc by galvanostatic stripping chronopotentiometry analysis (scp). parameter unit value deposition potential mv -1800 quiescence potential mv -1800 quiescence time 1 s 5 quiescence potential 2 mv -1400 quiescence time 2 s 30 terminal potential mv 100 stripping current µa 200 stand by potential mv 0 2.2 reagents and solutions all the chemicals used were of analytical reagent grade. deionized water (<0,05 μs/cm) prepared by simplicity 185 (millipore, france) was used for the bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 14:49 utc 48 frišták et al. preparation of all solutions. for electrochemical analysis, carrier electrolyte r-008 (0.01 mol/l ch3cooh + 0.01 mol/l ch3coona + 0.2 mol/l nacl) and background electrolyte r-013 (0.1 mol/l hcl) were used. the bulk standard solution and calibration solutions of zinc were prepared in the background electrolyte from certified reference material (999 mg/l znno3, sigma-aldrich, germany). 2.3 sampling and sample preparation three typical slovak soil types were obtained from localities jaslovské bohunice (jb, calcic phaenozem), sihla (s, haplic cambisol) and borský mikuláš (bm, haplic arenosol). the related sampling sites are shown in figure 1. the samples were collected from horizon in depth of 0-20 cm. before the subsequent analytical procedures the soil samples were dried (at 22 °c), homogenised and sieved through a 2 mm sieve. samples were stored at dark and dry place. fig. 1 sampling sites of investigated soils. 2.4 physico-chemical characterisation of soil samples for actual soil ph, 5 g of air-dried soil samples was allowed to equilibrate in 25 ml of deionised water. flask was agitated on reciprocal shaker (150 rpm) for 1 h. to determine potential soil ph, 25 ml of 1 mol/l kcl was added to 5 g of air-dried soil samples and allowed to equilibrate for 1 h. after 1 h consolidation, ph values of supernatants were measured using a ph glass electrode (inolab ph/ion/cond 750, wtw, france). total carbonate content in soil samples was obtained by lime-analyser of own construction (gablovičová et al., 2012). the cation exchange capacity (cec) of samples was determined according to the stn iso 11260 modified by frišták et al. (2013). soil samples were suspended (83.3 g/l) in 0.1 mol/l bacl2 and mixed on a laboratory shaker for 1 h at 22°c and 150 rpm. phases were separated after centrifugation (5 min at 5000 rpm). this procedure was repeated twice. the next bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 14:49 utc nova biotechnologica et chimica 12-1 (2013) 49 step of cec determination consisted of suspending of soil sediments in 3 ml of 0.025 mol/l bacl2 and agitation for 19 h at 22°c. after phases separation, 3 ml of 0.02 mol/l mgso4 was added to sediments. after agitation (19 h at 22°c), centrifugation and phases separation, cec by standardized 0.02 mol/l na2edta was determined. the cec values were determined by chelatometric determination of mg2+ ions in liquid phase and calculated according equation: ( ) 3 00 10− − = εvmvvmcec (1) where cec is cation exchange capacity (meq/100g), m0 is molar concentration of magnesium added to the sample (mol/l), v0 is volume of solution of magnesium added to the sample (l), m is molar concentration of the magnesium in the leachate (mol l1), vv is volume of obtained extract (l) and ε is the conversion factor that has for the bivalent ions and amount 0.25 g of soil value 800 meq (100 g/mol). 2.5 total (aqua regia extractable) zn fraction pseudo total soil content of zinc was estimated by aqua regia digestion (3:1, v/v, hcl:hno3). this digestion procedure is considered adequate for analysing totalrecoverable heavy metals in soils (meers et al., 2007). residual elements that are not released by aqua regia digestion are mostly bound to silicate minerals and are considered unimportant for estimating the mobility and behaviour of metals (niskkavaara et al., 1997). 2.6 simultaneous extraction protocols mobile zn-fractions were obtained after simultaneous extractions with 0.01 mol/l cacl2, 1 mol/l nh4no3, 0.05 mol/l na2edta, mehlich 2 (0.2 mol/l ch3cooh + 0.2 mol/l nh4cl + 0.015 mol/l nh4f + 0.012 mol/l hcl) and mehlich 3 (0.2 mol/l ch3cooh + 0.25 mol/l nh4no3 + 0.013 mol/l hno3 + 0,015 mol/l nh4f + 0.001 mol/l edta). extraction conditions of all cationic exchange and complexation procedures are given in table 2. table 2. extraction conditions of single-step extraction protocols used in experiments extraction solution e:s * ratio equilibration time [h] ph reference 0.01 mol/l cacl2 10:1 2 6 donner et al. (2010) 1 mol/l nh4no3 10:1 2 6 meers et al. (2007) mehlich 3 10:1 2 2.5 mehlich (1984) mehlich 2 10:1 2 3 mehlich (1984) 0.05 mol/l na2edta 10:1 2 3 tica et al. (2011) *e:s is a ratio between extractant phase and solid phase simultaneous extractable fractions were obtained by mixing of soil samples (1 g) with 10 ml of extractant on laboratory shaker (150 rpm) for 2 h at 22 °c. after bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 14:49 utc 50 frišták et al. centrifugation (10 min, 8000 rpm), 5 ml of supernatant was added to bank with 20-30 ml of reagent solution r-013 and 0.5 ml 0.01 mol/l kmno4. the solution was heated to 80-95 °c for 5-10 min. the oxalic acid was added to reduce the excess of permanganate. the volume of samples was adjusted to 50 ml with the r-013 reagent solution. solid particles were removed by filtering, centrifugation or sedimentation. zinc analysis in purified extracts was subsequently performed using stripping chronopotentiometry by electrochemical analyser ecaflow model glp 150 (istran, ltd., bratislava, slovakia). obtained data were compared with data obtained by gfaas analyse. all the analyses were carried out in triplicates. 2.7 isotopic dilution with 65zn (e-values) isotopic dilution with 65zn was used to monitor changes in the labile zn fraction over time. the procedure was based on the method of goldberg and smith (1984) using 0.05 mol/l cacl2 for displacement of soil zinc and top horizons of studied soils. to 2.5 g of soil samples, 25 ml of 0.05 mol/l cacl2 was added. to minimize the microbial activity, 0.1 ml of chcl3 was added. flasks were agitated 5 days at 22 ± 2 °c and 150 rpm. calcium chloride increased the zn concentration in solution, making its determination more precise. process of chemical equilibrium was characterized by determination of exchangeable zinc in 5 ml aliquots by galvanostatic stripping chronopotentiometry (scp). these values were assigned to be the neutral salt extractable zn concentration. the suspensions were subsequently spiked with 0.1 ml of 65zn (as zncl2) solution of 25 kbq/ml (czech institute of metrology, praque, czech republic). spiked suspensions were shaken for 5 days. after centrifugation (5 min, 4000 rpm) radioactivity in 3 ml of solid-free solution was measured by gamma spectrometric assembly using a well-type scintillation detector 54bp54/2-x, nai(tl) (scionix, the netherlands) and the data processing software scintivision 32 (ortec, usa). all measurements were carried out in triplicates. the quantities of the isotopically exchangeable zn in soil samples (zne) were calculated according to equation: s s s e znr r zn ].[⎟⎟ ⎠ ⎞ ⎜⎜ ⎝ ⎛ = (2) where rs is radioactivity introduced in the suspension (bq/ kg d.w.) and rs is the radioactivity measured in reaction solution at the end of experiment (bq/ kg d.w.) and [zn]s is the mean concentration of extractable zn in the soil extract as determined by scp (mg/kg d.w.). 3. results and discussion the soil samples used in experiments varied widely in soil properties and characteristics (table 3). determination of soil ph noted the slightly acidic character of the soil sample s, and low alkaline character of soil sample jb. soil reaction of soil sample bm varied between 5.9 and 6.8, depending on the method of determination. the sub-alkaline ph of jb sample, likely played a crucial role in reducing the zn bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 14:49 utc nova biotechnologica et chimica 12-1 (2013) 51 levels in soil solution. a decrease of zn solubility with increasing ph has been reported by many authors (frišták et al., 2012; pardo and guadalix, 1994; zambella and adamo, 2010). carbonate content was in the range from 0.5 to 0.7 in all soil samples. kiekens (1990) studied the reversibility of the exchange reaction between ca and zn and found that a key fraction of zn was irreversibly bound by the soil components and following adsorption of zn2+ and desorption of ca2+ during zn2+/ca2+ exchange process. associated with the wide range in soil texture, cec value varied from 5.9 to 18.1 mmol/100g. specific adsorption reactions, adsorption sites dependent on ph and reversibility of zinc binding may contribute to selective or major zn adsorption (maes, 1973). the determination of pseudo total zinc concentrations in studied soil samples by gfaas analyses confirmed the increasing trend in order bm < s < jb. the uppermost parts of the rich soil on organic matter and humus contain increased concentration of heavy metals (gablovičová et al., 2012). table 3. physico-chemical properties of studied soil samples. soil sample pseudo total zn [mg/kg] phh2o phkcl cec [mmol/100g ] caco3 [%] jb 75 8.3 7.5 18.1 0.7 bm 12 6.8 5.9 5.9 0.5 s 61 4.6 3.8 6.0 0.5 application of aqua regia extraction confirmed the lowest concentration of zinc (12 mg/kg) in bm soil samples obtained from haplic arenosol area with high content of calcium clays, dust, sand, conglomerate, coal beds and seams of lignite. chemical extraction methods are widely used to assess the release of contaminants from soils, sludges, and sediments. as extracting agents in extraction procedures, strong acid and their mixtures (hno3, h2so4, hcl, aqua regia), neutral solution of salts (cacl2, mgcl2, nacl), pending puffer and complex-forming agents (na2edta) can be used (meers, 2007). however, no single method is recognized universally (tica et al., 2011). available zinc concentrations, expressed as a pore water concentration or concentrations extractable with agent of ion exchange were lower in comparison with other tested extracting agent (figure 2a). the other extraction protocols can be used for the assessment of potentially toxic metals released from soils to the water recipients and their potential availability to all biological systems (mclaughlin et al., 2000). for determination of soil zinc mobile fractions 5 extracting agents were used. we tried to quantify the zinc content in extracts using stripping chronopotentiometry. zinc was deposited on porous electrode from acidic solution with high efficiency dependent on deposition potential. obtained data were compared to values from gfaas as reference method (figure 2b). coefficient of determination (r2) of linear correlation was 0.998 and it showed the comparability of used analytical methods. paired t-test also confirmed nonsignificance of differences between used methods and thus statistical significance of obtained data of extractable zinc (α=0.05). the extractability of zn obtained with the nh4no3 protocols was in general higher than that obtained with the cacl2 protocols for all soil samples. low alkaline sample bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 14:49 utc 52 frišták et al. jb released zn easily in reaction system of nh4no3 in comparison to studied acidic agents. effect of this extraction protocol can be attributed to the possible complexation of zn by nh3 (lebourg et al., 1998) and higher ionic strength of extracting agent. extraction efficiency of acidic agents increased in order mehlich 2, mehlich 3 and na2edta for all soil samples. chelating effect of used extraction agent caused significant increasing of extractable zinc from exchange sites, carbohydrate and organic matter [9]. we confirmed the extraction efficiency of organic ligands on wide range of soil components. jb bm s 0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 [z n] so lu te / [z n] to ta l . 10 0 [% ] soil samles a 0 5 10 15 20 25 30 35 0 5 10 15 20 25 30 35 c r ef er c exp b fig. 2. efficiency of simultaneous extraction protocols of zinc (mg/kg) from the three soil samples (jb, bm, s). extraction conditions: 2 h, 22°c, 150 rpm, 100g/l, extracting agents: cacl2 ( ), nh4no3 ( ), mehlich 2 ( ), mehlich 3 ( ), na2edta ( ). all experiments were carried out in triplicates. error bars represent standard deviation of the mean (±sd) (a). comparison obtained concentrations of extractable zinc determined by electrochemical analyses (cexp) with reference values determined by gfaas analyses (cref) (b). naidu and harter (1998) showed that metal extracted by a mixture of organic acids is well-correlated with the mobile metal fraction in the soil solution. metal fraction extracted by organic acids is more available for biological system compared to other complexing agents. low molecular weight organic acids such as ethylene diamine tetraacetic acid (edta) and their salts (na2edta) were reported to remove metals organically bound, occluded in oxides, and associated with secondary clay minerals (paya-perez et al., 1993). effect of soil reaction was less significant. we found out that simultaneous extraction protocols had maximal efficiency for low acidic soil sample of haplic arenosol (bm). thus we confirmed the effect of soil composition as a parameter of zinc availability from this typical slovak soil. for next investigation of labile or potentially available zn fraction in the studied soil samples, the isotopic dilution (e-value) was used. the studied samples of uppermost horizons contain the highest pseudo total concentration of zinc. the evalues reported in table 4 show how much the zn in soil samples was isotopically exchangeable within experimental equilibrium period. zinc availability in three soil samples ranged from 20 to 39%. these values were comparable with concentrations of na2edta extractable zinc. degryse and smolders (2006) reported e-values of bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 14:49 utc nova biotechnologica et chimica 12-1 (2013) 53 zinc equivalent to 32-49 % lability in upper horizons of acid soils (ph 3.3-4.5). on the other hand, donner et al. (2010) showed the exchangeable fraction of zinc in the range from 12 to 15% for agricultural soils with ph from 5 to 6.6. our study confirmed decreasing concentration of labile soil zinc with increased soil reaction of samples in order haplic cambisol, haplic arenosol and calcic phaenozem. measurements by radioisotope dilution with 65zn demonstrate a significant of soils ph and variation of zn bioavailability depending on soil type and physic-chemical characteristics. further work is needed to assess the importance of soil amendments and long-term ageing in terms of zinc bioavailability. table 4. e-values of soil samples jb , bm and s depending on ph and total zn concentration [mg/kg]. all experiments were carried out in triplicates, mean ± sd. soil sample jb bm s ph 8.3 6.8 4.6 total zn [mg/kg] 75.0 ± 6.0 12.0 ± 0.9 61.0 ± 4.7 zn e-value [mg/kg] 15.1 ± 1.9 2.51 ± 0.2 23.8 ± 1.3 labile zn [%] 20.1 20.9 39.01 4. conclusions as tools of available zinc fraction determination, single-step extraction methods can be used. our paper confirmed the effect of physico-chemical properties (ph) of soil samples and applied extraction protocol to extractable zinc concentration. we found out that extractability of binding zinc decreased in order na2edta, mehlich 3, mehlich 2, nh4no3 and cacl2 for studied soil samples. flow-through stripping chronopotentiometry (scp) and atomic absorption spectrometry (gfaas) confirmed the maximum of removable soil zinc by organic ligands. lability of soil zn can be determined by isotopic dilution method using radioactive isotope 65zn and γspectrometry. determination showed the significant decrease of isotopic exchangeable zinc fraction (e-value) with decrease of soil reaction. e-values of studied soil samples showed the zinc ability in range from 20 to 39%. our study confirmed the effect of soil reaction, composition and physico-chemical characteristics to zn lability. acknowledgment: this work was financially supported by university of ss. cyril and methodius in trnava (project fppv-01-2013). references frišták, v., pipíška, m., horník, m., augustín, j., lesný, j.: sludge of wastewater treatment plants as co2+ ions sorbent. chem. pap., 67, 2013, 265-273. vijver, m.g., vink, j.p.m., miermans, c.j.h., van gestel, c.a.m.: oral sealing using glue: a new method to distinguish between intestinal and dermal uptake of metals in earthworms. soil biol. biochem., 35, 2003, 125-132. van gestel, c.a.m: physico-chemical and biological parameters determine metal bioavailability in soils. sci. total environ., 406, 2008, 385-395. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 14:49 utc 54 frišták et al. luoma, s.n., rainbow, p.s.: why is metal bioaccumulation so variable? biodynamic as a unifying concept. environ. sci. technol., 39, 2005, 1921-1931. frišták, v., valovčiaková, m., pipíška, m., augustín, j.: simultaneous and sequential extraction protocols as tools for determination of zinc bioavailability in 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niskavaara, h., reimann, c., chekushin, v., kashulina, g.: seasonal variability of total and easily leachable element contents in topsoils (0-5 cm) from eight catchments in the european arctic (finland, norway and russia). environ. pollut., 96, 1997, 261-274. donner, e., broos, k., heemsbergen, d., warne, m.s.j., mclaughlin, m.j., hodson, m.e., nortcliff, s.: biological and chemical assessments of zinc ageing in field soils. environ. pollut., 158, 2010, 339-345. mehlich, a.: mehlich-3 soil test extractant: a modification of mehlich-2 extractant, comm. soil sci. plant anal., 15, 1984, 1409-1416. tica, d., udovic, m., lestan, d.: immobilization of potentially toxic metals using different soil amendments. chemosphere, 85, 2011, 577-583. goldberg, s.p., smith, k.a.: soil manganese: e value, distribution of manganese 54 among soil fractions, and effects of drying. soil sci. soc. am. j., 48, 1984, 559-564. pardo, m.t., guadalix, m.e.: chemical factors affecting selenite sorption by allophanic soils. geoderma, 63, 1994, 43-52. zampella, m., adamo, p.: chemical composition and zn bioavailability of the soil solution extracted from zn amended variable charge soils. j. environ. sci., 22, 2010, 1398-1406. kiekens, l.: heavy metals in soils, blackie usa and canada halsted press, new york, 1990. maes, a.: ion exchange of some transition metal ions in montmorillonites and synthetic faujasites, doctoral thesis, louvain, 1973. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 14:49 utc nova biotechnologica et chimica 12-1 (2013) 55 mclaughlin, m.j., hamon, r.e., mclaren, r.g., speir, t.w., rogers, s.l.: review: a bioavailability-based rationale for controlling metal and metalloid contamination of agricultural land in australia and new zealand. aust. j. soil res., 38, 2000, 1037-1086. lebourg, a., sterckeman, t., ciesielski, h., proix, n.: trace metal speciation in three unbuffered salt solutions used to assess their bioavailability in soil. j. environ. qual., 27, 1998, 584-590. naidu, r., harter, r.d.: effects of different organic ligands on cadmium sorption and extractability from soils. soil sci. soc. am. j., 62, 1998, 644-650. paya-perez, a., sala, j., mousty, f.: comparison of icp-aes and icp-ms for the analysis of trace elements in soil extracts. int. j. environ. anal. chem., 51, 1993, 223-230. degryse, f., smolders, e.: mobility of cd and zn in polluted and unpolluted spodosols. eur. j. soil sci., 57, 2006, 122-133. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 14:49 utc microsoft word hornik et al nb 2008.doc nova biotechnologica 8-1 (2008) 55 bioaccumulation of 137cs and 60co in freshwater plants miroslav horník, martin pipíška, jozef augustín department of biotechnology, university of ss. cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic (hornikm@ucm.sk) abstract: contamination of the aquatic environment by the heavy metals and radionuclides has become a serious concern in the world. in our study, gamma-spectrometry of freshwater plants bacopa monnieri and egeria densa growing in cultivation media spiked with 137cscl and 60cocl2 was used for quantitative determination of bioaccumulation kinetic and distribution cs+ and co2+ ions in plant tissues. we found, that bioaccumulation of cs and co by fully immersed b. monnieri in hoagland media (hm) was dependent on ion concentration in medium. approx. 5-times lower cs uptake 2.9 nmol/g (d.w.) was obtained in plants cultivated in 20% hm than from deionized water. the maximal co uptake was 4-times higher than cesium uptake at the same conditions. both cs and co were localized mainly in roots. the highest immobilization from roots to shoots was found in the case of co uptake from deionized water with concentration ratio [co]leaves : [co]stem : [co]root = 1.00 : 5.33 : 56.8. cesium uptake by submerged plant e. densa was also strongly dependent on nutrients concentration in medium. however, in the case of cobalt uptake this dependence was less pronounced. nutrients concentration also had a significant influence on distribution of cs between stems and leaves of e. densa. cesium was localized in leaves, however with increasing of nutrients concentration in cultivation media cs was localized for account of stem. on the other hand, cobalt was immobilized mainly in leaves in whole range of nutrients concentration. obtained data can serve as a models for understanding of phytoaccumulation of radionuclides from open water ponds and water channels in the vicinity of nuclear power plants and monovalent and bivalent metals from industrial sources of contamination. keywords: cesium, cobalt, 137cs, 60co, bioaccumulation, freshwater plants 1. introduction heavy metals are toxic pollutants released into the surface and ground water as a result of different activities such as industries, mining, and agriculture. at present, a number of technologies can be used to remove of heavy metals from contaminated water such as filtration, reverse osmosis, solvent extraction, adsorption, chemical precipitation and ion-exchange (cheremisinoff, 2002). however, these methods are not efficient in removing low heavy metals concentrations, can be relatively expensive and may fail to achieve legal limits. contrary to this, phytoremediation, i.e. removal of pollutants by the use of plants offers a promising technology for heavy metal removal from waste water (sternberg, 2007; fiol et al., 2005). aquatic macrophytes have a great potential to accumulate heavy metals inside their plant body (prasad, 2007; otte and jacob, 2006). most studies on pollutant bioaccumulation in macrophytes are aimed at assessing removal efficiency or toxic effects without taking into account the metal bioaccumulation process by macrophytes, key knowledge not only to understand the behavior of macrophytes but also to optimize effluent depuration by means of artificial wetlands. wetlands have significant merits of low capital 56 horník, m. et al. and operating costs compare with conventional system as activated sludge, aerated lagoon system etc.. this technology has been used mainly in the case of mine waters (see e.g. lesley et al., 2008; lesley and younger, 2007; batty et al., 2005). the nuclear revolution (weapons testing or accidents at power production) has resulted in the large-scale release of cesium into the environment, in particular l34cs (τ = 2.07 y) and the long-lived radionuclide 137cs (τ = 30.2 y). radiocesium 137cs persists in aquatic systems, with environmental half-lives in monomitic lakes, meromitic lakes and flowing rivers 1.2, 6.7 and 1.4 years, respectively (avery, 1996). its almost unlimited solubility in aquatic systems and chemical similarity to potassium means that it can be easily assimilated by terrestrial and aquatic organisms (mould, 2000; kerpen, 1986). large variations in the activity concentrations of 137cs from chernobyl nuclear accident in fish and lake water were still being observed in the 1990s and even in the 2000s (saxén and ilus, 2008; saxén, 2007). cobalt usually occurs in the environment in association with other metals such as copper, nickel, manganese and arsenic. cobalt released by human activities comes mainly from: nickel, copper, silver, lead and iron mines and refineries; metal production facilities; industrial boilers that burn coal and oil; vehicles that burn gasoline; and incinerators that burn refuse and sewage sludge (perez-espinoza et al., 2005). cobalt, as microelement for methanogenic bacteria, not for higher plants, can be also trapped in anaerobic bottom sediments. cobalt 60co (τ = 5.27 y) is also present in low-level radioactive wastes (caron and mankarios, 2004). our previous papers were oriented to bioaccumulation of radionuclides by terrestrial vascular plants from defined water solutions (horník et al., 2007; barátová et al., 2006). the objectives of this study are the investigation of 137cs and 60co uptake and their distribution in roots, stems and leaves of freshwater plants bacopa monnieri and egeria densa, in order to evaluate the role of nutrient concentration in bioaccumulation processes. b. monnieri is an emergent, wetland macrophyte. it grows very fast with its creeping stem in wetlands as a weed. it is well known from ancient times for its medicinal properties having active ingredients like bacosides and bacopasides. e. densa is an introduced invasive species, mainly via the aquarium trade. also, this invasive submerged species is distributed in lakes and rivers of europe. 2. materials and methods 2.1 plant material freshwater plants bacopa monnieri and egeria densa were obtained from common aquarium shops. one week before experimentation, plants were pre-cultivated in 15 dm3 aquaria filled with 50% hoagland medium (hm), (hoagland, 1920) at artificial illumination with 12h/12h light/dark cycle (illumination with 2 tubes brilliant daylight 6000 k, 1 300 lm and tropic sun – 4 700 k, 1 000 lm; sera, d) and at 22±2°c. for experiments, healthy green plants of comparable weight (0.4-0.5 g nova biotechnologica 8-1 (2008) 57 fresh weight; f.w.) were used and three-times washed in deionized water before experiments. the following molar concentrations of salts were presented in full-strength hm (mm): mgso4.7h2o – 1.5; kno3 – 4.0; cacl2 – 4.0; nah2po4.2h2o – 1.87; na2hpo4.12h2o – 0.13; feso4.7h2o – 0.06; nano3 – 4.0; nh4cl – 3.17; nh4no3 – 2.0; h3bo3 – 0.14; na2moo4.2h2o – 0.0025; mnso4.5h2o – 0.21; znso4.7h2o – 0.023; cuso4.5h2o – 0.033; ph 6.5. 2.2 bioaccumulation experiments for bioaccumulation experiments, freshwater plants b. monnieri or e. densa (0.40.5 g; f.w.) were placed on the bottom in 100 cm3 erlenmayer flasks containing 50 cm3 deionized water or hm diluted with deionized water in the ratio 1:1, 1:3, 1:4, 1:7, 1:11 or 1:25, and spiked with both 137cscl and 60cocl2. cultivation was carried out at artificial illumination with 12h/12h light/dark cycle (2 000 lx) and 22±2°c under occasional shaking. in time intervals, aliquots were taken and the remaining radioactivity in the cultivation media was estimated. at the end of the experiments, plants were washed in deionized water, dried at 60°c during 48 h and incorporated radioactivity of 137cs or 60co in leaves, stems or roots was measured by gammaspectrometry. all the experiments were performed in triplicate series. 2.3 radiometric analysis for radiometric determination 137cs and 60co in plants and cultivation media gamma-spectrometric scintillation detector 54bp54/2-x with well type crystal nai(tl) (scionix, nl) with data processing software scintivision32 (ortec, usa) were used. counting time 600 s allowed obtaining data with measurement error <2 %, which do not reflect other source of errors. standardized solutions of 137cscl (5.723 mbq/cm3; 20 mg/dm3 cscl + 3 g/dm3 hcl) and 60cocl2 (5.571 mbq/cm 3; 20 mg/dm3 cocl2 + 3 g/dm 3 hcl) were obtained from czech metrology institute (cz). 2.4 speciation modeling prediction of cs and co speciation in the nutrient solutions as a function of the total salt concentrations, solution ph and temperature was performed using the software visual minteq ver. 2.53. this speciation model allows the calculation of the composition of solution, in regard to formation of metal complexes. 3. results and discussion freshwater plants may take up nutrients from the sediments by roots or may absorb nutrients from the water column by foliar uptake. determining the principal mode of toxic metals and radionuclides uptake by macrophytes is important because it affects the interpretation of the role of macrophytes in aquatic systems. if root 58 horník, m. et al. uptake is the principal mode, then the metals and radionuclides content of the macrophytes represents remobilization from the sediments. if foliar uptake is the principal mode, then the metals and radionuclides content of the macrophytes represents a reduction in the water column concentration with the macrophytes serving as at least a temporary sink for these pollutants (kelly and pinder iii, 1996). however, in these processes the speciation of metals and radionuclides in both water and sediment can play an important role. for example, madruga and carreiro (1992) found in tejo river water, that 60co was almost 100% in cationic forms, however, in the presence of sediment there was a decrease in proportion of cationic forms (to 50%), with some anionic forms appearing. 0 1 2 3 4 5 6 7 8 0 4 8 12 16 20 b io ac cu m ul at io n of c s+ [n m ol /g ]; d. w . time [d] 20% hm deionized water 0 1 2 3 4 5 6 7 8 0 10 20 30 40 50 60 70 80 90 b io ac cu m ul at io n of c o2 + [n m ol /g ]; d. w . time [d] 20% hm deionized water fig. 1. bioaccumulation kinetics of cs+ ions (a) and co2+ (b) by freshwater plant b. monnieri (25 g/dm3; f.w.). fully immersed plants were cultivated in deionized water or 20% hoagland medium (hm), ph 6.5 containing 0.12 µmol/dm3 cscl (17 kbq/dm3 137cscl) and 0.11 µmol/dm3 cocl2 (13 kbq/dm3 60cocl2) at light/dark cycle 12h/12h (2 000 lx) and at 22±2°c. total uptake of cs: deionized water – 8.3%; 20% hm – 0.9%. total uptake of co: deionized water – 35%; 20% hm – 6.3%. data represent average of three independent experiments. bioaccumulation kinetics of cs+ and co2+ ions by emergent freshwater plant bacopa monnieri are presented in fig. 1a, b. under given experimental condition, i.e. the initial concentration c0 = 0.12 µmol/dm 3 cscl and biomass concentration 25 g/dm3 (f.w.) at 22°c the maximum cesium uptake was observed after 24 h and was stable within the next 7 days. as can be seen from fig. 1a, bioaccumulation of cs is dependent on ion concentration in medium. cesium uptake 14.1 nmol/g (dry weight; d.w.) was obtained in deionized water after 8 days cultivation. approximately 5-times lower 2.9 nmol/g (d.w.) was found at plants cultivation in 20% hm, where concentration of competing k+ and nh4 + ions was 0.8 and 1.2 mmol/dm3, respectively. nevertheless, as can be calculated by visual minteq speciation program, cesium in 20% hm at ph 6.5 occurs practically as free cation (> 99% cs+). monovalent k+ and nh4 + ions act competitively on cesium uptake by plants. vascular plants can accumulate cs+ ions through both their leaves and through their roots. substrate affinity i.e. km values for cs + uptake in shoots and roots of winter wheat is 25.5 and 16.7 μmol/dm3 respectively. according to shaw et al. (1992) the measured transfer factor of roots is one order of magnitude greater than that of shoots. smith et al. (2003) in a whole-lake experiment at study to reduce the bioaccumulation of radiocesium 137cs in fish in lakes contaminated a b nova biotechnologica 8-1 (2008) 59 by the chernobyl accident found, that after the addition of 15 t of potassium chloride to lake svyatoe, kostiukovichy resulted in a decrease in activity concentration of 137cs to approximately 40% of pre-countermeasure values in a number of different fish species. however, the addition of 4 kg 133cscl into an 11.4-ha, 157 000 m3 reservoir previously contaminated with 137cs from past reactor operations at the us department of energy’s savannah river site near aiken, south carolina (usa) increased of 6.1 mbq of 137cs (1.9 mg 137cs) in the water column (pinder iii et al., 2006; 2005). these authors supposed, that possible sources for the increased 137cs included release from the sediments (the principal source), release from the approx. 26 000 kg of aquatic macrophytes that occupied 80% of the reservoir, and wash-in from the pond’s watershed. 0 2000 4000 6000 8000 10000 deionized water s pe ci fic r ad io ac tiv ity 1 37 c s [b q/ g] ; d .w . 20% hoagland medium root stem leaves 0 20000 40000 60000 80000 100000 120000 140000 deionized water s pe ci fic r ad io ac tiv ity 6 0 c o [b q/ g] ; d .w . 20% hoagland medium root stem leaves fig. 2. specific radioactivities of 137cs (a) and 60co (b) in root, stem and leaves of b. monnieri after 8 days cultivation of fully immersed plants in deionized water or 20% hm, ph 6.5 containing 0.12 µmol/dm3 cscl (17 kbq/dm3 137cscl) and 0.11 µmol/dm3 cocl2 (13 kbq/dm3 60cocl2) at light/dark cycle 12h/12h (2 000 lx) and at 22±2°c. data represent average of three independent experiments. bioaccumulation kinetic of co2+ ions by b. monnieri was identical with the process of cs bioaccumulation at the same conditions, but only in the case of plants cultivation in 20% hm (fig. 1b). cobalt in 20% hm at ph 6.5 occurs practically as free cation (> 93% co2+). when plants were cultivated in deionized water containing 0.11 µmol/dm3 cocl2, the bioaccumulation of cobalt gradually increased to the maximum 62 nmol/g (d.w.) in 5 day of cultivation, and then slowly decreased to the value 54 nmol/g (d.w.) in 8 day of plants cultivation. the bioaccumulation of co is also dependent on ion concentration in medium. it can be concluded, that cobalt was accumulated in more extent than cesium practically at the same conditions. adam and garnier-laplace (2003) found similar results at accumulation of 137cs and 60co by freshwater alga cyclotella meneghiana. from results of cesium distribution in plant organs of b. monnieri we found (fig. 2a), that cesium is mainly localized in roots than in stems and leaves with concentration ratio [cs]leaves : [cs]stem : [cs]root = 1.00 : 0.69 : 1.76 at plants cultivation in 20% hm and [cs]leaves : [cs]stem : [cs]root = 1.00 : 1.22 : 2.14 at plants cultivation in deionized water. similarly, cobalt was mainly immobilized in roots with concentration ratio [co]leaves : [co]stem : [co]root = 1.00 : 0.39 : 1.49 at plants cultivation in 20% hm (fig. 2b). in the case of plants cultivation in deionized water a b 60 horník, m. et al. cobalt was much more immobilized in roots with concentration ratio [co]leaves : [co]stem : [co]root = 1.00 : 5.33 : 56.8. its generally known, that at emergent species of water plants root uptake is presumed to be the dominant mechanism of nutrients absorption. in this regard, mineral nutrients, mainly macroelements (ca and mg), from 20% hm are probably preferentially accumulated by roots than cobalt. 0 1 2 3 4 5 6 7 8 0 10 20 30 40 b io ac cu m ul at io n of c s+ [n m ol .g -1 ]; d. w . time [d] deionized water 8,3% hm 12,5% hm 25% hm 50% hm 0 1 2 3 4 5 6 7 8 0 20 40 60 80 100 120 b io ac cu m ul at io n of c o2 + [n m ol .g -1 ]; d. w . time [d] deionized water 8,3% hm 12,5% hm 25% hm 50% hm fig. 3. bioaccumulation kinetics of cs+ (a) and co2+ (b) ions by e. densa (20 g/dm3; f.w.). fully immersed plants were cultivated in deionized water or diluted hm (8.3%, 12.5, 25% or 50%), ph 6.5 containing 0.12 µmol/dm3 cscl (17 kbq/dm3 137cscl) and 0.11 µmol/dm3 cocl2 (13 kbq/dm3 60cocl2) at light/dark cycle 12h/12h (2 000 lx) and 22±2°c. total cs uptake (%): deionized water – 46.4; 8.3% hm – 5.7; 12.5% hm – 6.4; 25% hm – 2.1; 50% hm – 3.3. total co uptake (%): deionized water – 70.3; 8.3% hm – 66.8; 12.5% hm – 72.0; 25% hm – 81.8; 50% hm – 70.6. data represent average of three independent experiments. 0 10 20 30 40 50 0 20 40 60 80 100 b io ac cu m ul at io n of c s+ [n m ol /g ]; d. w . hm concentration [%] 0 20 40 60 80 100 b io ac cu m ul at io n of c o2 + [n m ol /g ]; d. w . 0 10 20 30 40 50 0 20 40 60 80 100 0 20 40 60 80 100 ra tio [c o] fo rm /[c o] to ta l hm concentration [%] cs+ co2+ coso 4 cohpo 4 ra tio [c s] fo rm /[c s] to ta l fig. 4. a. dependence of bioaccumulation of cs+ (-■-) and co2+ (-○-) ions by e. densa (20 g/dm3; f.w.) on dilution of hoagland medium at ph 6.5 after 8 d cultivation of fully immersed plants at light/dark cycle 12h/12h (2 000 lx) and 22±2°c. for details see fig. 3. b. the percentage (ratio of concentration metal form to the total concentration of metal) of cesium in the form of cs+ and cobalt in the forms co2+ ions, coso4 or cohpo4 in dependence on dilution of hoagland medium at ph 6.5 and 22°c calculated by the speciation program visual minteq. as can be seen from fig. 3a,b and fig. 4a, cs+ uptake by freshwater submerged plant egeria densa is strongly dependent on ion concentration in medium. however in the case of cobalt uptake this dependence was less pronounced. cesium uptake 46% (32.8 nmol/g; d.w.) in deionized water decreased to 6% (6.0 nmol/g; d.w.) in 8.3% a b a b nova biotechnologica 8-1 (2008) 61 hm, where concentration of competing k+ and nh4 + ions was 0.33 and 0.5 mmol/dm3, respectively. on the contrary, uptake of co2+ ions increased with concentration of monovalent and bivalent cations in hm, however at highest concentration, i.e. 8 mmol/dm3 me+ ions and 3 mmol/dm3 me2+ ions in 50% hm cobalt uptake slightly decreased. the speciation of cesium and cobalt in individual cultivation media at ph 6.5 and 22°c can be seen in fig. 4b. 0 10 20 30 40 50 0 1 2 60co [6 0 c o] st em /[ 60 c o] le av es accum ulation in leaves hm concentration [%] accum ulation in stem 137cs 0 1 2 [1 37 c s] st em /[ 13 7 c s] le av es fig. 5. influence of dilution of hoagland medium on 137cs (-■-) and 60co (-○-) distribution in stems and leaves of e. densa (20 g/dm3; f.w.) after 8 d cultivation of fully immersed plants at light/dark cycle 12h/12h (2 000 lx) and 22±2°c. data expressed as the ratio of concentration in stems to the concentration in leaves (bq/g / bq/g; d.w.). for details see fig. 3 concentration of mineral nutrients had also a significant influence on distribution of 137cs between stems and leaves of submerged plant e. densa (fig. 5). in the case of plants cultivation in deionized water containing 0.12 µmol/dm3 cscl cesium was localized manly in leaves, however with increasing of nutrients concentration in cultivation media cesium was localized for account of stem. on the other hand, cobalt was immobilized mainly in leaves of e. densa in whole range of nutrients concentration. 4. conclusions cesium and cobalt in contaminated water systems undergo concentration equilibrium in contact with water plants, occurring in nearly all water bodies. obtained data from short-time laboratory experiments showed, that presence of monovalent and bivalent ions in defined cultivation media significantly influenced the bioaccumulation and distribution of 137cs+ and 60co2+ ions in freshwater plants bacopa monnieri and egeria densa. these results can serve for understanding of phytoaccumulation of radionuclides from open water ponds and water channels in the vicinity of nuclear power plants and monovalent and bivalent metals from industrial sources of contamination. 62 horník, m. et al. references adam, ch., garnier-laplace, j.: bioaccumulation of silver-110m, cobalt-60, cesium-137, and manganese-54 by the freshwater algae scenedesmus obliquus and cyclotella meneghiana and by suspended matter collected during a summer bloom event. limnol. oceanogr., 48, 2003, 2303-2313. avery, s.: fate of caesium in the environment: distribution between the abiotic and biotic components of aquatic and terrestrial ecosystems. j. environ. radioact., 30, 1996, 139-171. barátová, z., sekáčová, j., horník, m., pipíška, m., augustín, j.: bioaccumulation of 137cs and 60co by mustard sinapis alba l. and celery apium graveolens l.. nova biotechnol., vi-i, 2006, 7-18. batty, l.c., atkin, l., manning, d.a.c.: assessment of the ecological potential of mine-water treatment wetlands using a baseline survey of macroinvertebrate communities. environ. pollut., 138, 2005, 413-420. caron, f., mankarios, g.: pre-assessment of the speciation of 60co, 125sb, 137cs and 241am in a contaminated aquifer. j. environ. radioact., 77, 2004, 29-46. cheremisinoff, n.p.: handbook of water and wastewater treatment technologies. butterworth-heinemann, woburn, ma, usa, 2002, 631 p. fiol, n., serarols, j., poch, j., martínez, m., miralles, n., villaescusa, i.: low cost materials for metal uptake from aqueous solutions. in: lichtfouse, e., schwarzbauer, j., robert, d. 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(ed.) phytoremediation: methods and reviews, humana press, totowa, new jersey, usa, 2007, 185-203. microsoft word vidova 9-1 2009.doc nova biotechnologica 9-1 (2009) 63 multiplex pcr method for detection of variability in genes encoding the alpha proteins of streptococcus agalactiae barbora vidová1, 2, michal chotár2, jozef timko2 andrej godány2, 3 1institute of biochemistry, nutrition and health, slovak university of technology, sk-812 37 bratislava, slovak republic (barbora.vidova@savba.sk) 2institute of molecular biology, slovak academy of sciences sk-845 51, bratislava, slovak republic 3department of biotechnology, university of ss. cyril and methodius, sk-917 01 trnava, slovak republic abstract: the majority of streptococcus agalactiae strains express one or more surface-anchored proteins that vary by strain. these proteins, which are characteristic for s. agalactiae, and are able to induce protective antibodies, include the alpha c, rib proteins, alpha-like protein 2, and alpha-like protein 3. in this study was developed multiplex pcr method for detection of genes encoding these proteins, and its occurrence within a various s. agalactiae isolates of bovine origin. also are reported two new genes from bovine isolates of s. agalactiae amplified by pcr, encoding other putative members of the family, alphalike protein 6, and alpha-like protein 7. they contain an overall genetic organization highly similar to that of the alpha c and rib proteins. key words: streptococcus agalactiae, alpha-like family, variability, multiplex pcr 1. introduction the importance of streptococcus agalactiae as a major perinatal pathogen for invasive disease has been well documented (baker and edwards, 2000; zaleznik et al., 2000; ferrieri, 1997). the s. agalactiae first received attention as a cause of bovine mastitis, a disease defined as ‘inflammation of the mammary gland’, that cause the losses in a diary industry associated with clinical and subclinical mastitis, which arise from the costs of treatment, culling, death and decreased milk production (bradley, 2002). epidemiological studies of s. agalactiae infections are mainly based on capsule serotyping. the capsule is an antigenic determinant and a major virulence factor as it interferes with complement mediated killing (edwards et al., 1982). the s. agalactiae strains are classified into nine different serotypes based on differences in the capsular polysaccharide antigens ia, ib, and ii through viii (paoletti et al., 2000). serotype distribution varies with geographical region and ethnic origin, and the virulence of clinical isolates with similar capsular composition can also vary widely, suggesting that other bacterial virulence factors, except a capsule, are involved in the pathogenesis of s. agalactiae (spelleberg, 2000). in addition, several surface–anchored proteins that vary by strain have been described for s. agalactiae (moyo et al., 2002; kvam et al., 1995). 64 vidová, b. et al. the proteins include the immunoglobulin a-binding beta c protein (cβ) encoded by bac, the alpha c protein (cα) (bevanger and maeland, 1979) encoded by bca (michel et al., 1992), and the proteins r1, r3, and r4 (flores and ferrieri, 1996, 1989; lancefield and perlmann, 1952). the cα and the r proteins belong to a family of so-called “ladder-forming” proteins, a designation based on the banding patterns generated on western blotting (wästfelt et al., 1996). some of the best characterized protein antigens used as candidate vaccines belong to the alpha protein family, reviewed by lindahl et al. (2005). these major antigens are encoded by allelic genes. five different alleles, named alp2, alp3, rib, r28 and epsilon (alpha-like proteins) have been described (lachenauer et al., 2000; lachenauer and madoff, 1996; wästfelt et al., 1996; stålhammarcarlemalm et al., 1993). all these proteins are encoded by stable mosaic genes, generated by a recombination of modules at the same chromosomal locus (lachenauer et al., 2000). the proteins exhibit size variation between strains depending on the number of repeats in the corresponding gene. moreover, it has been demonstrated that, in the course of infection, the number of repeats inside the alpha c proteins can undergo internal deletions as a means for evading the host immune response (madoff et al., 1996). diversity of s. agalactiae strains has been analyzed using a broad range of methods. aside from serotyping and multilocus enzyme electrophoresis (mlee) (musser et al., 1989), a method based on primary structures of proteins, other typing methods used are dna based. these include ribotyping (blumberg et al., 1992), random amplified polymorphism (limansky et al., 1998), pulsed field gel electrophoresis (rolland et al., 1999; gordillo et al., 1993) and more recently, multilocus sequence typing (mlst) (jones et al., 2003). the study of surface proteins and their genes encoding sequences is important from the aspect of epidemiological analysis of the infections caused by streptococcus agalactiae, and simultaneously, surface proteins hold capability to be used in vaccines against this pathogen (maione et al., 2005; larsson et al., 2004; paoletti and madoff, 2002; brodeur et al., 2000). the aim of the present study was to analyse the gene content, which could indicate distribution of surface proteins, in the set of bovine s. agalactiae isolates. this was performed by multiplex pcr method for detection of genes bca, rib, alp2/3, alp4, and alp5 directly according the pcr products sizes. 2. materials and methods 2.1 bacterial strains and media the streptococcal isolates were obtained from different farms in slovakia (147 strains) and from czech republic (5 strains), and could be identified as streptococcus agalactiae belonging to lancefield’s serological group b. the identification was performed by pcr identification (chotár et al., 2006). s. agalactiae cultures were grown overnight on todd-hewitt (biomark) broth at 37°c on rotary shaker. nova biotechnologica 9-1 (2009) 65 2.2 preparation of bacterial cell suspension for pcr one milliliter of overnight culture was transferred in sterile tube and centrifuged at 10.000 rpm for 3 min, pellet was washed twice with sterile distilled water, once with 0.1 m phosphate buffered saline, ph 7.2 (pbs), and then resuspended in 1 ml of deionized sterile water to allow the burst of bacterial cells. samples of 2 μl of these preparations were used directly for pcr. 2.3 pcr conditions reactions were carried out in final volume of 20 µl. the reaction mixture contained 0.5 u dynazyme™ dna polymerase (finnzymes), 0.4 µl 10 mm dntp mix (finnzymes), 4 µl optimized dynazyme™ 10x reaction buffer (finnzymes). primers listed in table 1 were used in concentrations: 0.5 μm of universal forward primer saganf, and reverse primers were added as follows 0.16 μm of saga4, 0.4 μm of sagarib, 0.7 μm of sagaalpc, 0.9 μm of saga2/3, and 1.3 μm of saganr. all dna oligonucleotides were synthesized by sigma. table 1. oligonucleotide primers used in this study. primers sequences 5´-> 3´ size (bp) reverse: sagaalpc tat atg tgg tag tcg atc ttc acc 428 sagarib cac act gaa ctt tta aac caa gtg a 325 saga2/3 cat tca gat tat tat aat ata tag cac 630 saga4 tta atat gca ctg gat taa ctc cac 140 saganr cgc gga tcc atc ctc ttt ttt ctt aga aac 852 forward: saganf gga att cca taa tgt tta gaa ggt cta aaa a two microliters of bacterial suspension was used as a template. the amplification program consisted of denaturation at 96°c for 5 min, 30 cycles of denaturation at 96°c for one minute, annealing at 55°c for one minute and extension at 72°c for two minutes, followed by a final extension at 72°c for 8 minutes. ten microliters of pcramplified product was analyzed by electrophoresis in 0.9 % agarose gel stained with ethidium bromide. this was carried out in 1x bbe (0.65 m boric acid, 29 mm sodium tetra borate, 250 mm edta, ph 7.8). pcr amplicons were analyzed by uv transluminization. 2.4 dna sequence analysis pcr products were sequenced and compared with genebank sequences using blast (basic local alignment search tool) (altschul et al., 1990). the new sequences generated during this study have appeared in genebank with the following accession numbers: dq629924 (alp6) and dq629925 (alp7). previously published gene sequences used in this study and their genebank accession numbers are as follows: m97256 (bca), u58333 (rib), ay345596 (alp1), aj488912 (alp4) and ay461799 (alp5). 66 vidová, b. et al. 3. results and discussion alpha proteins of streptococcus agalactiae have typical repetition region consisted of about 80 amino acids, which are highly homologous (lindhal et al., 2005). while these repeats present extensive homology between alpha-protein-like proteins, the n-terminal portion is distinctive. the analysis of a clustalw amino acid multisequence alignment of the n-terminal portions of the alpc, rib, alp2, alp3, alp4 and alp5 identified distinctive strings for each protein, except for the alp2 and alp3 proteins, which are identical over the first half of their length. primer nucleotide sequences corresponding to the distinctive strings were used in a multiplex assay as the reverse primers, while a nucleotide string, common to all the surface protein genes, was used as the forward primer (table 1). these primers allowed detection of nucleotide sequences specific for single alp proteins, discriminated according to the size of pcr product, which directly indicated the presence of gene encoding specific alp protein. these primers were used to screen 152 isolates s. agalactiae of bovine origine by multiplex pcr. representative results are shown on fig. 1. results derived from the direct analysis of amplicon size were correlated with the gene sequence of the corresponding amplified product for each individual strain. by this multiplex analysis in set of bovine isolates were identified 31 isolates with gene encoding alpc protein, 50 isolates with sequence for gene encoding rib, 39 isolates with alp2/3 coding sequence, 10 isolates with gene alp4, and 6 isolates with gene alp5. also two another amplicons with significantly longer lengths 1.095 bp and 1.347 bp were found. the amplicon with 1.095 bp length was found in case of 9 strains, namely 245, 251, 252, 256, 257, 259, 264, 347 and 348, the amplicon with 1.347 bp length was detected in 2 strains, 1925/3 and 2285/1 (fig. 1.). all these amplicons were sequenced and compared by blast. pcr with dna s. agalactiae from the strain 341 resulted an amplicon with length 852 bp, that was 99.5 % identical to original alp5 from strain 27. comparison showed the differences in nucleotide sequence observed on 23rd, 25th, 29th and 81st nucleotide downstream, that resulted in change of 3 amino acids at nterminal coding region of translated protein. the amplicon sequence of alp6 showed considerable homology with alp4, bca, rib and other members of the surface protein gene family defined by bca-rib. the homologous regions were located at the 5` ends of the genes (for bca, the positions are in region between nucleotides 251 and 559, and for the corresponding amino acid sequence, they are between positions 58 and 160). the ratios of similarity to dna sequences of alp4, bca, rib, alp2 and alp3 are 89 %, 73 %, 66.9 %, 62.4 % and 62.3 %, respectively. the proteins belonging to the alpha-like protein family are of interest as models for other repetitive proteins, which are common in gram-positive bacteria (kong et al., 2002; lachenauer et al., 2000). this typical feature was not recognized in alp6, but its sequence is the most similar to that of bca, which encodes c alpha, the prototype of the surface protein family, here it is proposed, that the gene could be considered as putative alpha-like protein. in the case of two isolates, 1925/3 and 2285/1, was observed the pcr product with 1.347 bp length, and was named alp7. sequencing of this amplicon and its comparison by blast showed similarity to the members of alpha-like family; in particular alp1, alp5 and bca, the ratios of similarity nova biotechnologica 9-1 (2009) 67 were 82.8 %, 88.2 % and 77 %, respectively. the homologous regions were located at the 5` ends of the genes, whereas for alp1 and alp5 the positions are in the region between nucleotides 297 to 710. the nucleotide sequence organization in alpha-like family proteins is similar to that in many surface proteins of gram positive bacteria. an n-terminal signal sequence is followed by a nonrepeated n-terminal region, a repeated region, a wall anchoring region by which the protein is anchored to the cell wall via a structure close to the c-terminus consisting of an lpxtg sequence motif followed by a membrane-spanning hydrophobic region and a charged sequence (deswaux et al., 2006; wästfelt et al., 1996; michel et al., 1992). fig. 1. elecrophoresis of multiplex pcr for detection of presence the genes encoding alp proteins, alp2/3, rib, alphac, alp4, and alp5, discriminable by pcr product size on 0.9% agarose gel. other two new genes were also detected in the set of s. agalactiae bovine isolates, alp6 and alp7. dna ladder represents molecular size marker (finnzymes). a repetitive structure in amino acid sequence is conserved and was remarked also in nucleotide sequence of alp7, where differ in the last one base pair, which had no impact to the amino acid sequence. this tandem repeat consists of 82 amino acid residues, whereas one consists of 246 base pairs repetition. the alp7 tandem repeat motif is similar to that of alp1, alp4, bca and rib, with the ratios of similarity 93.9 %, 91.7 %, 91.6 % and 44 %, respectively (fig. 2.). it has been supposed, that the repeat region may act as a rod needed for exposure of the unique ligand-binding region (luo et al., 2000; hamburger et al., 1999). the lpxtg motif was found in both, alp6 and alp7, amino acid sequences, whereas in for this part of sequence in alp7 was observed similarity related to immunoglobulin a1 protease. because domains with the ig-like fold are often implicated in molecular recognition it could has such function (callebaut et al., 2000). like many other surface proteins of gram-positive bacteria, alpha-like protein family members, also 68 vidová, b. et al. with recently here reported, lack cysteine residues. the importance of alpha-like surface proteins consists in the facts, that these proteins play a role as serotype markers, may be important in the pathogenesis of s. agalactiae disease, and may be considered vaccine candidates (maeland et al., 2004). they play an important role as serotype markers, because were noted relationships between serotypes and surface protein genes occurrence (kong et al., 2002), eg. protein alpc is commonly expressed with serotype ib or ii, protein rib with serotype iii, and alp3 protein with serotype v (persson et al., 2008). s. agalactiae strains are typical in high variability on the gene level, and genes under high selection pressure could undergo to various mutations. fig. 2. multiple sequence alignments of the deduced amino acid sequences of the repeat regions of the selected alpha-like proteins. alignments of the repeat regions illustrated conserved motifs near the beginnings and the ends of the repeats. black boxes indicate identity and gray boxes indicate similarity. alpc, alpha c protein repeat element, rib, repeat element from protein rib, alp1, alpha-like repeat element from alp1, alp4, alpha-like repeat element from alp4, and alp7, alpha-like repeat element from alp7. the results of this study indicate that the genes encoding surface proteins were found to constitute a heterogeneous group, with no particular gene dominating. the genes studied here were found in all of the bovine isolates. in the set of bovine isolates was the most common gene encoding protein rib (34%). the overall distribution of these genes was similar to that reported previously (zeng et al., 2006; kong et al., 2002; lachenauer et al., 2000). in this study are also reported two new putative members of this family. like the alpha c and rib protein genes, these genes each contain conserved nand c-terminal encoding regions, and a tandem repeat region was recognized in amino acid sequence of alp7. it has been previously reported, that with a few exceptions, s. agalactiae strains of a given polysaccharide serotype contain the same alpha-like protein, disregarding tandem repeat number (lachenauer et al., 2000, 1999). this concordance may reflect clonal linkages within a species that is naturally incompetent and consistent with several studies showing a predominance of individual clones among s. agalactiae isolates (blumberg et al., 1996). alternatively, it is conceivable that there is a functional linkage between the alpha-like proteins and polysaccharide serotype that would require this specificity. because of a relatively low occurrence of the alp6 and alp7 within the set of bovine isolates and dependence of their presence on a geographical locality, these genes of the alpha-like nova biotechnologica 9-1 (2009) 69 protein family could not be designated for the detection of s. agalactiae, but they could be proof of the biological variability within this protein family. furthermore, characterisation of variability in expression of surface proteins is very important with the perspective of surface proteins application in vaccine development. in this context, it is extremely important to have a rapid and reliable molecular test, as here reported multiplex pcr method, 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ecochemistry and radioecology, university of ss. cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic (pipiska@ucm.sk) 2consortium for environmental biotechnology and environmental chemistry, hlavná 418, špačince, sk-919 51, slovak republic abstract: removal of cd2+ and zn2+ ions from single and binary solutions by dried activated sludge was studied in batch experiments. it was shown that the metal removal is a rapid process significantly influenced by solution ph. maximum uptake of both cd and zn was reached at ph 6.0 and negligible uptake was observed at ph 2.0. the langmuir isotherm was found to well represent the measured equilibrium sorption data in single metal systems and the maximum sorption capacities qmax of the activated sludge (d.w.), calculated from langmuir model were 540 ± 16 μmol/g for zn2+ and 510 ± 17 μmol/g for cd2+ ions. the response surface methodology (rsm) was used for investigation of interaction and competitive effects in binary metal system. it was found that dried activated sludge in binary system cd-zn has slightly higher affinity for cd2+ comparing with zn2+ ions. competitive effect of cd on zn uptake increased with increasing solution ph and cd initial concentration. maximum sorption capacities of the activated sludge were 321 μmol cd2+/g and 312 μmol zn2+/g. rsm appears to be a better tool for the evaluation of interaction and competitive effects in binary systems than both the simple extrapolation from single-component systems and experimentally difficult study of multi-component systems. key words: cadmium, zinc, biosorption, activated sludge, isotherms, rsm 1. introduction industrial effluents contain both organic and inorganic pollutants. these pollutants upset natural balance in water ecosystems, interfere with organisms, accumulate in biota and enter into the food chain with human on the top. contaminants removal by conventional treatment methods, such as chemical precipitation, membrane separation, evaporation and ion-exchange is often limited due to their low efficiency and economic viability (nayak and lahiri, 2006). therefore, there is a need for an effective and economical treatment alternative. biological processes such as biosorption and bioaccumulation represent possible interactions of toxic pollutants with biological systems in contaminated environment. current research activity in the field attempts to evaluate whether biosorption may eventually provide such an effective and economical treatment process alternative (naja et al., 2010). many researchers studied biosorption from single systems (ghodbane et al., 2008; kang et al., 2007), although the degree of removal of metal ions from wastewaters by biosorption depends mainly on the competitive interactions of co-ions when present in solution (ma and tobin, 2003). results from single component systems can provide useful data about the uptake capacity of used biosorbent, but they 118 remenárová, l. et al. do not exactly reflect the real situation in wastewaters (gönen and aksu, 2009). therefore it is necessary to study sorption process as complex process, which consists of many mechanisms and can be affected by many parameters. effect of various parameters (ph, temperature, sorbent particle size, initial concentration of sorbates) can be studied by the classical approach, when one variable is changed at a time. however this procedure represents a time consuming and less effective method. multivariate optimization is faster and overcome circumstances not explained by the traditional methods such as interactions between the variables that influence the response e.g. sorption capacity (zolgharnein et al., 2010). response surface methodology (rsm) is a collection of mathematical and statistical techniques useful for designing experiments, building models and analyzing the effects of the several independent variables (mune et al., 2008). main advantage of statistical design of experiments is the reduced number of experiments to be performed as well as it considers interactions among the variables and can be used for optimization of the operating parameters in multivariable systems (gönen and aksu, 2009). from the literature it was found that rsm has been widely used for optimization of biosorption processes mainly in single systems. only a few studies utilized rsm methodology for statistical analysis of individual and interaction effects of parameters in binary and ternary sorption systems (fereidouni et al., 2009; pakshirajan and swaminathan, 2009). within this context the objective of present study was firstly to quantify the ability of the biosorbent prepared from dried activated sludge to sorb cd2+ and zn2+ ions. equilibrium isotherm models according to langmuir and freundlich were used for mathematical description of sorption equilibria in single systems. the second objective was to study the competitive and interaction effects of above mentioned ions in binary cd2+-zn2+ system at various solution ph values using response surface methodology (rsm). 2. material and methods 2.1 biosorbent preparation activated sludge was obtained from waste water treatment plant in enviral a.s. (leopoldov, slovak republic) producing fuel ethanol. the sludge was washed twice in deionised water, oven-dried for 72 h at 90°c. after drying activated sludge was ground to various particle sizes, from which particle size <450 μm was used in biosorption experiments. 2.2 batch sorption experiments in single systems the biosorption kinetics was determined by suspending of activated sludge (2.5 g/l, d.w.) in metal solutions (ph 6.0) containing 1000 μmol/l cdcl2 or zncl2 spiked with 109cdcl2 or 65zncl2. the content was agitated on a reciprocal shaker (120 rpm) at 20°c and in time intervals liquid samples were taken and the radioactivity was measured. nova biotechnologica 10-2 (2010) 119 the metal sorption capacity of dried activated sludge was determined by suspending of activated sludge (2.5 g/l, d.w.) in metal solutions (ph 6.0) containing cdcl2 or zncl2 in concentration range 100-4000 μmol/l spiked with 109cdcl2 or 65zncl2 and exposing for 4h at 20°c on a reciprocal shaker (120 rpm). to analyze the influence of ph, activated sludge was shaken in metal solutions containing 1000 μmol/l cdcl2 or zncl2 spiked with 109cdcl2 or 65zncl2 for 4 h on a reciprocal shaker at 120 rpm and 20°c adjusted to different ph values (2.0 – 9.0) by adding 0.5 m hcl or 0.1 m naoh. at the end biomass was filtered out, washed twice in deionised water and radioactivity of both activated sludge and liquid phase was measured. the metal uptake was calculated as mccvq eq /)( 0 −= (1) where q is the uptake (μmol/g, d.w.), c0 and ceq is the initial and the final metal concentrations in solution (μmol/l) and m is the amount of dried biosorbent (given in grams). all experiments were performed in duplicate. 2.3 experimental design of binary cd-zn system the box-behnken design under response surface methodology (rsm) was used to investigate interaction and competitive effects in binary metal system cd2+-zn2+. levels of factors (initial concentrations c0 of cd 2+ and zn2+ ions and initial ph of solution) considered for sorption in binary system are shown in table 1. the design matrix of 16 experiments is given in table 3. based on the matrix, experiments were performed in erlenmeyer flasks, activated sludge (2.5 g/l, d.w.) was added and the content was agitated on a reciprocal shaker (120 rpm) for 4 h at 20°c. table 1. levels of factors considered for sorption of cd2+ and zn2+ ions from binary system using boxbehnken design. coded levels factor unit factor code -1 0 1 c0 cd 2+ µmol/l a 1000 2000 3000 c0 zn 2+ µmol/l b 1000 2000 3000 ph c 3.0 4.5 6.0 the behavior of the binary sorption system is explained by the following empirical second-order polynomial model ∑∑∑ ≤≤== +++= k ji jiij k i iiii k i i xxxxq 11 2 10 ββββ (2) where q is the predicted response (specific sorption qeq of both cd and zn), xi, xj, .....xk are the input variables (c0 cd 2+, c0 zn 2+ and solution ph) which affect the response q, β0 is the intercept term, βi is the linear effect, βii is the quadratic effect and βij is the interaction effect (fereidouni et al., 2009). 120 remenárová, l. et al. 2.4 radiometric analysis the gamma spectrometric assembly using the well type scintillation detector 54bp54/2-x, nai(tl) (scionix, the netherlands) and the data processing software scintivision 32 (ortec, usa) were used for 109cd and 65zn determination in activated sludge and supernatant fluids at the energy of γphotons: 109cd – 88.04 kev and 65zn – 1115.52 kev. standardized 109cdcl2 solution (3.937 mbq/ml; 50 mg cdcl2/l in 3 g/l hcl) and 65zncl2 solution (0.8767 mbq/ml; 50 mg zncl2/l in 3 g/l hcl) were obtained from the czech institute of metrology, prague (czech republic). 2.5 speciation modeling prediction of the speciation of cd and zn in the aqueous systems as a function of total salt concentration and solution ph was performed using the visual minteq (version 2.52) program. visual minteq 2.52 is a chemical equilibrium computer program that has an extensive thermodynamic database for the calculation of metal speciation, solubility and equilibria (gustafson, 2004). 2.6 data analysis to calculate the qmax values and the corresponding parameters of adsorption isotherms non-linear regression analysis was performed by origin 7.0 professional (originlab corporation, northampton, usa) and graphpad prism 5.0 (graphpad software, usa). response surface graphs and regression analysis of the obtained data were performed by statgraphics centurion xv (statpoint inc., usa) and the design expert 7.0 (stat-ease, inc., usa). 3. results and discussion 3.1 cd2+ and zn2+ uptake by activated sludge in order to determine the minimum necessary time to reach the sorption equilibrium, the time-course studies on the biosorption of cadmium and zinc ions from single metal systems by biosorbent prepared from dried activated sludge were performed. fig. 1 shows that biosorption of cd2+ and zn2+ ions is a rapid process where equilibrium is reached within several tens minutes. at initial phase driving force is higher and binding sites on activated sludge with higher affinity are occupied. after that time concentration of cd2+ and zn2+ ions in solution decreases and the residual binding sites with lower affinity toward metal ions are occupied slowly. the final equilibrium was reached within 4 hours. such two-phase sorption has been also reported by yang et al. (2010) in the case of zn sorption by activated sludge. they found that zinc adsorption capacity increased obviously during the first 60 min and the final equilibrium was reached within 180 min. nova biotechnologica 10-2 (2010) 121 from fig. 2 it can be seen that maximum biosorption of both cd2+ and zn2+ occurred at ph 6.0. this curve is characteristic also for cd and zn biosorption by the moss rhytidiadelphus squarrosus (pipíška et al., 2010) and biosorption of other metal ions on activated sludge, algae and other biosorbents (wang et al., 2010; liu et al., 2009; gundogdu et al., 2009). observed slightly lower biosorption at ph 4.0 and negligible at ph 2.0 is closely related to protonation of binding sites, resulting in competition between h+ and cd2+ or zn2+ ions for occupancy of the active sites. in the case of zn2+ at ph 8.0 sharp decrease of biosorption was observed. 0 200 400 600 800 1000 1200 1400 1600 0 50 100 150 200 250 300 350 400 q eq [μ m ol /g ] t [min] cd2+ zn2+ fig. 1. effect of contact time on cd2+ (c0 = 1000 μmol/l, 100 kbq 109cdcl2) and zn2+ (c0 = 1000 μmol/l, 65 kbq 65zncl2) ions biosorption by dried activated sludge (2.5 g/l d.w.) at 20°c and ph 6.0. it must be pointed out, that the ph influenced also the level of ionization and speciation of metals in aqueous solution. as can be calculated by visual minteq speciation program (data not shown) at ph 8.0 besides the divalent cation zn2+, zinc occurs in solution also in insoluble forms such as [zn(oh)]+. therefore the decrease of zn2+ sorption at higher ph values (> ph 8.0) can be caused also by precipitation. according to calculations insoluble cadmium species occurred at ph > 9.0. it is reasonable to suppose that the dependence of metal uptake on ph is related to both the surface functional groups on the biosorbent and the metal speciation in solution. during sorption experiments ph was not regulated. from fig. 2 it is evident that the equilibrium ph increased after biosorption experiments what indicates that functional groups on the surface accumulate besides cd2+ and zn2+ ions simultaneously h+ ions. similar behaviour observed also chen et al. (2002) in cu sorption by activated sludge. several mechanisms of heavy metals uptake by activated sludge have been proposed (wang et al., 2010; laurent et al., 2010). short-term cation uptake is generally regarded as an abiotic process governed by: surface complexation of cations with exposed functional groups (carboxyl-, sulfhydryl-, amineetc.) on the biosorbent; ion exchange; coordination and chelation of metals; adsorption or by precipitation of solid phases on the cell walls. 122 remenárová, l. et al. 2 4 6 8 0 50 100 150 200 250 300 350 q eq cd2+ ph 0 q eq [μ m ol /g ] 2 4 6 8 ph eq 2 4 6 8 0 50 100 150 200 250 300 350 q eq zn2+ ph 0 q eq [μ m ol /g ] 2 4 6 8 ph eq fig. 2. effect of initial ph on cd2+ and zn2+ ions (c0 = 1000 µmol/l) sorption by dried activated sludge (2.5 g/l, d.w.) at 20°c; (-) represents shifts in ph after biosorption. 3.2 sorption equilibrium in single systems two well known adsorption isotherm models langmuir (eq. 3) and freundlich (eq. 4) were applied for the analysis of the experimental data in single sorption systems. eq eq eq bc cbq q + = 1 max (3) )/1( n eqeq kcq = (4) parameters of these models provide an insight into the sorption process, reflect the nature of the sorbent, surface properties as well as the degree of the affinity of the nova biotechnologica 10-2 (2010) 123 sorbents and can be used to compare biosorption performance (volesky, 2003). the langmuir and freundlich isotherms were fitted to the equilibrium data for cd2+ and zn2+ sorption on dried activated sludge. isotherm curves and parameters of the models determined from the experimental data using non-linear regression analysis are reported in fig. 3, 4 and table 2. 0 1000 2000 3000 0 200 400 600 langmuir a ceq [μmol/l] q eq [ μ m ol /g ] 0 1000 2000 3000 0 200 400 600 800 freundlich b ceq [μmol/l] q eq [ μ m ol /g ] fig. 3. isotherms for the sorption of zn2+ ions by dried activated sludge at 20°c and ph 6.0 according to langmuir (a) and freundlich (b). data points represent experimental results, curves represent the calculated values from isotherm models, dotted lines represent the 95 % confidence interval. the langmuir isotherm fits the data of both cd2+ and zn2+ ions sorption by dried activated sludge better than the freundlich isotherm, as is demonstrated by higher values of coefficient of determination (r2), the more homogeneous standard deviation of each observed parameter and by the lower the sum of squares (rss) values obtained as well as standard deviation of the residuals (sy,x ) (table 2). also hammaini et al. (2007) found that the sorption of cd2+ and zn2+ ions by activated sludge was well described using the langmuir isotherm. the maximum sorption capacity qmax obtained from langmuir isotherm for cd 2+ was 510 ± 17 μmol/g at ph 6.0. slightly higher value of qmax was observed in the case of zn2+ sorption, 540 ± 16 μmol/g at ph 6.0. the affinity constant b of the isotherms corresponds to the initial gradient, which indicates the biosorbent affinity at low 124 remenárová, l. et al. 0 1000 2000 3000 0 200 400 600 langmuir a ceq [μmol/l] q eq [ μ m ol /g ] 0 1000 2000 3000 0 200 400 600 800 freundlich b ceq [μmol/l] q eq [ μ m ol /g ] fig. 4. isotherms for the sorption of cd2+ ions by dried activated sludge at 20°c and ph 6.0 according to langmuir (a) and freundlich (b). data points represent experimental results, curves represent the calculated values from isotherm models, dotted lines represent the 95 % confidence interval. table 2. langmuir and freundlich parameters for the sorption of cd2+ and zn2+ ions by dried activated sludge obtained by non-linear regression analysis. model metal ion qmax [μmol/g] b [l/μmol] k [l/g] 1/n r 2 rss sy,x zn2+ 540 ± 16 0.006 ± 0.001 0.995 723 15.5 l an gm ui r cd2+ 510 ± 17 0.005 ± 0.001 0.994 769 16.0 zn2+ 50.3 ± 29.4 0.30 ± 0.08 0.877 18817 79.2 fr eu nd lic h cd2+ 49.9 ± 28.9 0.29 ± 0.08 0.878 16347 73.8 concentrations of metal ions. a greater initial gradient corresponds to a higher affinity constant (sheng et al., 2007). from fig. 3 and 4 it is evident that the cadmium and nova biotechnologica 10-2 (2010) 125 zinc isotherms have similar behavior at lower equilibrium concentrations. in the case of b, cadmium recorded 0.005 ± 0.001 l/μmol compared to 0.006 ± 0.001 l/μmol for zinc indicating slightly higher affinity of activated sludge for zinc ions. it should be realized that despite the fact that langmuir isotherm offers no insights into the mechanism of biosorption (liu and liu, 2008) it remains a convenient tool for comparing equilibrium data on a quantitative basis (determination of maximum sorption capacity qmax and affinity parameters b) and providing information on biosorption potential. 3.3 experimental design of binary cd-zn system box-behnken design under the response surface methodology (rsm) was used for investigation of interaction and competitive effects between variables in binary system cd-zn. according to preliminary experiments and our previous studies (pipíška et al., 2010; pipíška et al., 2008) the sorption capacity of biosorbent in multi-component systems mainly depends on the initial concentration of primary ion and co-ions in sorption system and on the solution ph. therefore, initial concentration of cd and zn and solution ph were used as process variables in experimental design (table 3) and two responses – qeq(cd) and qeq(zn) were studied simultaneously. table 3. box-behnken experimental design matrix and experimental and predicted values of sorption capacity (qeq) of cd2+ and zn2+ ions by dried activated sludge from binary system cd-zn. a – c0 cd (µmol/l), b – c0 zn (µmol/l), c – ph. factor qeq cd qeq zn run order a b c qeq (experimental) (µmol/g) qeq (predicted) (µmol/g) qeq (experimental) (µmol/g) qeq (predicted) (µmol/g) 1 1000 1000 4.5 205.8 206.5 178.0 179.2 2 3000 1000 4.5 321.0 321.7 113.2 122.8 3 1000 3000 4.5 130.7 130.0 312.0 302.4 4 3000 3000 4.5 261.4 260.7 226.2 226.9 5 1000 2000 3 93.77 90.64 138.1 145.5 6 3000 2000 3 211.2 208.0 118.3 115.3 7 1000 2000 6 170.8 173.9 284.9 287.8 8 3000 2000 6 299.3 302.4 193.3 185.9 9 2000 1000 3 180.9 183.4 75.86 69.18 10 2000 3000 3 132.7 136.5 154.0 156.1 11 2000 1000 6 297.8 294.0 151.1 148.9 12 2000 3000 6 206.0 203.5 282.6 289.3 13 2000 2000 4.5 242.5 245.0 213.3 214.6 14 2000 2000 4.5 242.5 245.0 213.3 214.6 15 2000 2000 4.5 254.5 245.0 227.8 214.6 16 2000 2000 4.5 241.1 245.0 198.4 214.6 126 remenárová, l. et al. the behavior of the binary sorption system cd-zn is explained by the following quadratic models determined by multiple regression analysis: ( ) phzncphcznccdcphznc cdcphznccdccdqeq ××−××+××⋅+×− ×⋅−×⋅−×+×⋅−×+−= − −−− 0007.000019.000109.303.170 103.20103.11940101.20097.0382 622 6255 (5) ( ) phzncphcznccdcph znccdcphznccdcznqeq ××+××−××⋅−×− ×⋅−×⋅+×+×+×+−= − −− 0009.00012.000108.42.16 0102.10105.51870075.00008.0394 62 2526 (6) the adequacy of the models was further justified through anova (data not shown). the model f-values of 246 (for cd2+ sorption) and 58.3 (for zn2+ sorption) and values of p<0.0001 indicate that both models are significant. good agreement between experimental and predicted values of sorption capacity qeq (table 3) confirmed high values of coefficient of determination (r2), 0.997 (for cd2+) and 0.987 (for zn2+). equations 5 and 6 represent the quantitative effect of the variables (initial concentration of cd and zn, solution ph) and their interactive effects on the qeq(cd) and qeq(zn) in binary system cd-zn. a positive sign in the equation implies a synergistic effect of the variables, while a negative sign indicates an antagonistic effect. 1000,0 c0 zn (µmol/l) 3000,0 6,0 q eq c d (µ m ol /g ) 160 190 220 250 280 310 c0 cd (µmol/l) 3000,0 1000,0 ph 3,0 fig. 5. main effects plot for cd2+ biosorption by dried activated sludge from binary system cd-zn. fig. 7a, b, c illustrate the three-dimensional response surface plots of the quadratic model (eq. 5) for cd2+ sorption from binary system cd-zn. the combined effect of initial cd2+ concentration and ph on cd2+ sorption by dried activated sludge at various concentrations of zinc as co-ion is shown. it is evident that cd2+ uptake increased with increasing of initial solution ph as well as with initial cd2+ concentration. on the contrary, increasing zn2+ concentration from 1000 to 3000 μmol/l diminished cd2+ sorption as a result of competition between metal ions (fig. 5). increase in solution ph and initial zn2+ sorption caused increase in zn2+ sorption as can be seen from main effects plot (fig. 6). similarly, increase in cd2+ concentration decreased zn2+ sorption from binary system cd-zn. nova biotechnologica 10-2 (2010) 127 1000,0 c0 zn (µmol/l) 3000,0 3,0 6,0 q eq z n (µ m ol /g ) 120 150 180 210 240 270 c0 cd (µmol/l) 3000,0 1000,0 ph fig. 6. main effects plot for zn2+ biosorption by dried activated sludge from binary system cd-zn. 3.00 3.75 4.50 5.25 6.00 1000.00 1500.00 2000.00 2500.00 3000.00 0 87.5 175 262.5 350 q eq c d µm ol /g c: ph c0 cd µmol/l 3.00 3.75 4.50 5.25 6.00 1000.00 1500.00 2000.00 2500.00 3000.00 0 87.5 175 262.5 350 q eq c d µm ol /g c: ph c0 cd µmol/l b a 128 remenárová, l. et al. 3.00 3.75 4.50 5.25 6.00 1000.00 1500.00 2000.00 2500.00 3000.00 0 87.5 175 262.5 350 q eq c d µm ol /g c: ph c0 cd µmol/l fig. 7. response surface plots showing the effect of ph and initial cd2+ concentration on cd2+ biosorption by dried activated sludge (2.5 g/l d.w.) at 20°c and different concentrations of zn2+ as competing ion (a) 1000 µmol/l, (b) 2000 µmol/l, (c) 3000 µmol/l. maximum sorption capacities of the activated sludge were 321 μmol cd2+/g and 312 μmol zn2+/g. it was found that dried activated sludge in binary system cd-zn has higher affinity for cd2+ ions when cd2+ and zn2+ are present in equimolar ratio 1:1 (table 3) comparing with higher affinity to zn2+ in single systems. this is consistent with the hypothesis that variance in affinity in multi-component systems could be attributed to different ionic characteristics of metal ions (pakshirajan and swaminathan, 2009). 4. conclusions biosorption of cd2+ and zn2+ from aqueous solution by dried activated sludge is a rapid and ph dependent process. maximum uptake of metals was found to occur at ph 6. the experimental equilibrium data of the single-component systems for cd2+ and zn2+ ions have been well described by the langmuir isotherm and the maximum sorption capacity qmax were 540 ± 16 μmol/g for zn 2+ and 510 ± 17 μmol/g for cd2+ ions. the use of rsm revealed the existence of interaction and competitive effects between variables in binary system cd-zn. cd2+ uptake increased with increasing of initial solution ph as well as with initial cd2+ concentration. on the contrary, increasing zn2+ concentration from 1000 to 3000 μmol/l diminished cd2+ sorption as a result of competition between metal ions. activated sludge in binary system cd-zn has higher affinity for cd2+ comparing with zn2+ ions when cd2+ and zn2+ are present in equimolar ratio 1:1. rsm appears to be a useful tool for obtaining interaction and competitive effects in binary systems since it requires less reagents and experimentation time. references chen, j.p., lie, d., wang, l., wu, s., zhang, b.: dried waste activated sludge as biosorbents for metal removal: adsorptive characterization and prevention of organic leaching. j. chem. technol. biotechnol., 77, 2002, 657-662. c nova biotechnologica 10-2 (2010) 129 fereidouni, m., daneshi, a., younesi, h.: biosorption equilibria of binary cd(ii) and ni (ii) systems 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shahmoradi, a., mousavi, s.n.: optimization of removal of methylene blue by platanus tree leaves using response surface methodology. anal. sci., 26, 2010, 111-116. nova biotechnol chim (2022) 21(1): e1089 doi: 10.36547/nbc.1089 1 nova biotechnologica et chimica in vitro culture initiation and regeneration of two highly productive clones of poplar yuliia khoma, lidiia khudolieieva, namik rashydov, nataliia kutsokon department of biophysics and radiobiology, institute of cell biology and genetic engineering, national academy of sciences of ukraine, acad. zabolotnogo, 148, 03143, kyiv, ukraine  corresponding author: kutsokon@nas.gov.ua article info article history: received: 6th august 2021 accepted: 9th january 2022 keywords: growth media leaf and petiole explants microclonal propagation of trees plant regeneration populus spp. abstract in vitro shoot regeneration is a fast and reliable method for propagation of valuable tree genotypes and important step in genetic manipulations. this study aimed to establish an optimal in vitro culture initiation and regeneration protocol for highly productive poplar clones ‘novoberlinska-3’ (populus pyramidalis × p. laurifolia) and ‘volosystoplidna’ (p. trichocarpa). in vitro culture was initiated either on ms (im-ms) or wpm (im-wpm) medium both containing bap (0.2 mg.l-1) and iba (0.1 mg.l-1). results demonstrated that the best initiation medium for the clone ‘volosystoplidna’ was im-wpm on which 93.3 % of explants survived, while explants from ‘novoberlinska-3’ better survived on im-ms. after establishing both genotypes into aseptic culture, regeneration experiments were started using two types of explants, leaf and petioles, planted on callus induction medium containing 2ip (1.02 mg.l-1) and naa (1.86 mg.l-1). furthermore, microshoots were placed on shoot induction medium supplemented with 0.04 mg.l-1 thidiazuron, and then transferred on shoot elongation medium with 0.2 mg.l-1 bap. regeneration protocol showed better performance of poplar ‘novoberlinska-3’, but it was also efficient for ‘volosystoplidna’. plant regeneration from leaf explants in the clone ‘novoberlinska-3’ showed the highest regeneration percentage (92.3 %) and the number of shoots per explant (3.1), which significantly exceeded other explants. our results showed a significant difference between the survivability of two clones during culture initiation. the differences in regeneration rates between the clones as well as leaf and petiole explants were also determined. obtained aseptic cultures of highly productive poplar hybrids will be used in our further studies, especially for genetic transformation. introduction poplars (populus spp.) belong to the plants of the salicaceae family, which are ecologically and economically important tree species. these fastgrowing trees are widely used for biofuel production, wood, pulp, and paper industries, environmental protection, and restoration of degraded soils (gordon 2001; pilipović et al. 2019; galović et al. 2021). poplars are also trees of great scientific importance due to ease of vegetative propagation, short rotation cycle, small genome size, and the ability to regenerate in vitro. these important features, combined with the complete sequencing of the genome of populus trichocarpa, made poplar a model plant offering molecular tools for basic research in genetics, physiology, and mailto:kutsokon@nas.gov.ua nova biotechnol chim (2022) 21(1): e1089 2 biochemistry of trees (han et al. 2000; tuskan et al. 2006; kutsokon et al. 2020). in recent decades, short-rotation plantations of fastgrowing trees for biomass production have been increasingly established worldwide (wullschleger et al. 2002; aylott et al. 2008; kutsokon et al. 2017; moravčíková et al. 2017). for the effective management of these plantations, it is important to properly select highly productive and easily propagated intensively growing clones. it is known that some valuable poplar hybrids do not reproduce vegetatively or reproduce poorly. the method of micropropagation can overcome this problem by providing genetically homogeneous planting material identical to the original form. application of in vitro culture methods makes it possible to produce high-quality plants at any time, quickly and in large quantities. in addition, micropropagation preserves the genotype of the original plant, allows to control the growth environment, monitor the physiological and biochemical parameters of the plants, as well as to work regardless of weather conditions and season (giri et al. 2004). micropropagation of trees is much more difficult than the micropropagation of herbaceous plants. it requires the development of specific cultivation techniques for different species. in addition to selection of the nutrient medium composition for macroand micronutrient content, it is also necessary to add various vitamins, phytohormones or growth regulators. it may be also necessary to add absorbents and antioxidants, as woody plant species can release phenolic compounds into the growth environment. these compounds can be rapidly oxidized and may lead to plant death (shahzad et al. 2017; abiri et al. 2020). in vitro shoot regeneration is not only a rapid and reliable method for valuable genotypes propagation but also the indispensable prerequisite for some biotechnological techniques, such as genetic transformation and gene editing. genetic manipulations are able to increase the plant growth and resistance to biotic and abiotic stresses, change the quality of wood (e.g., reduce or change lignin content), and improve phytoremediation characteristics (confalonieri et al. 2003; kutsokon 2011; song et al. 2019). however, not all tree species can be easily in vitro regenerated. their ability to morphogenesis depends on the genotype, tissue types or explants, cultivation environment, media nutritional components, and growth regulators (giri et al. 2004; musienko and panyuta 2005; ferreira et al. 2009). the ratio of auxins to cytokinin plays a crucial role in the success of plant regeneration (hill and schaller 2013; bidabadi and jain 2020). several authors have shown that the effective plant regeneration methods should be optimized for each clone individually (noël et al. 2002; thakur et al. 2012; kutsokon et al. 2013; kwon et al. 2015; pokorná et al. 2017). additionally, although many studies have been reported using the populus explants for tissue culture propagation, those studies are limited to a small number of reports on shoots regeneration from leaf and petiole explants for different species that is an important step in genetic manipulations. in our previous work, poplar clones ‘novoberlinska-3’ (populus pyramidalis × populus laurifolia) and ‘volosystoplidna’ (populus trichocarpa torr. et gray) were found to be between the most productive and energy-valuable clones in the short-rotation trials (kutsokon et al. 2017). these clones can easily be multiplied by woody cuttings; however, for regeneration, gene transformation, and other in vitro manipulations, a homogeneous quality of the plant material is needed, thus the use of micropropagation is strongly recommended (müller et al. 2013). one of the clones studied, p. trichocarpa, as described for genotype ‘nisqually-1’, is known as recalcitrant in in vitro conditions, though few protocols are known for regeneration (kang et al. 2009) and transformation (li et al. 2015) of ‘nisqually-1’ clone. a limited number of papers about in vitro cultivation and genetic transformation of hybrids p. laurifolia x nigra 'italica' (p. x berolinensis) were published, but they described only partial steps of the protocol (pavlichenko et al. 2016; zolotovskaya et al. 2018). nevertheless, the clones ‘novoberlinska-3’ and ‘volosystoplidna’ have not been used in in vitro culture in the studies before. therefore, in this paper we reported the optimal conditions for their in vitro culture initiation and regeneration which are the key steps for further genetic transformation. nova biotechnol chim (2022) 21(1): e1089 3 experimental plant material and surface sterilization buds and young softwood shoots of poplar clones ‘novoberlinska-3’ (p. pyramidalis × p. laurifolia) and ‘volosystoplidna’ (p. trichocarpa torr. et gray) were collected at the beginning of the growing season. the plants in the juvenile stage of development, maintained in a pot stock plant collection, kept at the institute of cell biology and genetic engineering nas of ukraine, were used as softwood shoot sources. explants were surface sterilized using our previously established protocol (khudolieieva et al. 2017), by treating them with the different solutions in three subsequent steps: 1) concentrated soap solution (2 min); 2) commercial bleach solution of sodium hypochlorite diluted with distilled water to 30 % (10 min); 3) 70 % ethanol solution (1 min). after each step, the decontaminated explants were rinsed three times with sterile water. culture initiation, shoot regeneration, media, and growth conditions in order to evaluate the effect of basal salt medium on plant growth during culture initiation, surfacesterilized stem explants of poplar clones ‘novoberlinska-3’ and ‘volosystoplidna’ were placed on two different types of initiation media, either on ms (im-ms) or woody plant (im-wpm) medium. both nutrient media were modified with 0.2 mg.l-1 6-benzylaminopurine (bap) and 0.1 mg.l-1 indole-3-butyric acid (iba). detailed compositions of all nutrient media used in this research are summarized in table 1. table 1. composition of the nutrient media. im-ms 2.18 g.l-1 ms, 2 ml.l-1 wpm vitamins, 0.1 g.l-1 myo-inositol, 30 g.l-1 sucrose, 0.26 g.l-1 mes, 0.2 g.l-1 l-glutamine, 7.5 g.l-1 agar, 0.2 mg. l-1 bap, 0.1 mg. l-1iba, ph 5.8 im-wpm 1.15 g.l-1 wpm, 2 ml.l-1 wpm vitamins, 20 g.l-1 sucrose, 7.5 g.l-1 agar, 0.2 mg. l-1 bap, 0.1 mg. l-1 iba, ph 5.8 cim 2.18 g.l-1 ms, 2 ml.l-1 wpm vitamins, 0.1 g.l-1 myo-inositol, 30 g.l-1 sucrose, 0.26 g.l-1 mes, 0.2 g.l-1 l-glutamine, 7.5 g.l-1 agar, 1.86 mg. l-1 naa, 1.02 mg. l-1 2-ip, ph 5.8 sim 2.18 g.l-1 ms, 2 ml.l-1 wpm vitamins, 0.1 g.l-1 myo-inositol, 30 g.l-1 sucrose, 0.26 g.l-1 mes, 0.2 g.l-1 l-glutamine, 7.5 g.l-1 agar, 0.04 mg. l-1 tdz, ph 5.8 sem 2.18 g.l-1 ms, 2 ml.l-1 wpm vitamins, 0.1 g.l-1 myo-inositol, 30 g.l-1 sucrose, 0.26 g.l-1 mes, 0.2 g.l-1 l-glutamine, 7.5 g.l-1 agar, 0.2 mg. l-1 bap, ph 5.8 pm-ms 2.18 g.l-1 ms, 2 ml.l-1 wpm vitamins, 0.1 g.l-1 myo-inositol, 30 g.l-1 sucrose, 0.26 g.l-1 mes, 0.2 g.l-1 l-glutamine, 7.5 g.l-1 agar, ph 5.8 pm-wpm 1.15 g.l-1 wpm, 2 ml.l-1 wpm vitamins, 20 g.l-1 sucrose, 7.5 g.l-1 agar, ph 5.8 im-ms – initiation media contained ms (murashige and skoog) salts; im-wpm – initiation media contained wpm (mccown woody plant medium) salts; cim – callus induction medium; sim – shoot induction medium; sem – shoot elongation medium; pm-ms – propagation media contained ms (murashige and skoog) salts, pm-wpm – propagation media contained wpm (mccown woody plant medium) salts; bap – 6-benzylaminopurine; iba – indole-3-butyric acid; mes – 2-(nmorpholino) ethanesulfonic acid; naa – α-naphthaleneacetic acid; tdz – thidiazuron. all chemicals were purchased from duchefa (the netherlands) unless otherwise stated. fifteen explants per variant were planted, each in a separated glass tube. the explants were maintained in a tissue culture growth room at 24 °c under a 16-h photoperiod. the percentage of surviving stem explants was determined after 30 days of cultivation on induction media. successfully initiated into in vitro culture poplars ‘novoberlinska-3’ and ‘volosуstoplidna’ were micropropagated on pm-ms and pm-wpm respectively (table 1) and maintained by subculturing at 4-week intervals. well-developed onemonth plants were used for indirect shoot regeneration according to the protocol of meilan and ma (2006). this protocol was successfully performed in our previous studies for the regeneration of several poplar clones (khudolieieva et al. 2014; 2017). therefore, it was tested in the current study. leaf and petiole explants were cultivated on petri dishes with callus-inducing medium (cim) supplemented with growth regulators 1.02 mg.l-1 n6-(2-isopentenyl) adenine (2-ip) and 1.86 mg.l-1 α-naphthaleneacetic acid nova biotechnol chim (2022) 21(1): e1089 2 (naa) (table 1) at 21 °c in the dark for 3 weeks. the explants produced calli were transferred on petri dishes with shoot induction medium (sim) supplemented with 0.04 mg.l-1 thidiazuron (tdz) (table 1). plants were cultured in the tissue culture growth room at 24 °c under a 16-h photoperiod for 2 weeks. then the explants with microshoots (1 – 1.5 cm) were transferred to shoot elongation medium (sem) containing 0.2 mg.l-1 bap (see table 1). at least 15 leaf and 15 petiole explants were collected per clone at the initial stage of regeneration. the efficiency of regeneration was evaluated after six weeks since beginning the experiment by the percentage of explants producing at least one shoot to the total number of explants used as well as by the number of shoots per regenerated explant. statistical analysis statistical processing of the results was performed according to standard methods. data are expressed as % ± sp or as mean ± standard error of the mean. data normality and variance homogeneity were checked using shapiro-wilk and levene’s tests, respectively. because the data were not normally distributed, nonparametric tests were applied. significant differences in the survivability of explants and percentages of explants producing the shoots were tested with the chi-square test. the differences in the number of shoots per regenerated explant were tested using the mann-whitney u test. all tests were declared significant at p ≤ 0.05. all statistical analyses and tests were performed using originpro9.0 software (originlab corporation). results and discussion survivability of stem explants initiated into in vitro culture in this study, two poplar clones ‘novoberlinska-3’ and ‘volosystoplidna’ were established in aseptic cultures (fig. 1), and the optimal composition of the im for the first stage of cultivation was selected. as shown in fig. 2, the best initiation nutrient medium for the poplar clone ‘volosystoplidna’ was the im-wpm on which the survival rate was 93.3 %. for poplar clone ‘novoberlinska-3’, a higher survival rate (73.3 %) was observed on im-ms compared to im-wpm (46.7 %), but in this case, the difference between the rates was not significant. fig. 1. establishment of aseptic cultures of poplars from stem explants: clone ‘novoberlinska-3’ on the im-ms (a) and clone ‘volosystoplidna’ on the im-wpm (b). fig. 2. survivability of stem explants of the poplar clones ‘novoberlinska-3’ and ‘volosystoplidna’ while initiated into in vitro culture. im-wpm and im-ms were both supplemented with 0.2 mg.l-1 bap and 0.1 mg.l-1 iba. different letters above the bars indicate significant differences in survivability between the samples (% ± sp) after the chi-square test (p ≤ 0.05), n = 15 replicates for each genotype. a b 4 nova biotechnol chim (2022) 21(1): e1089 3 the survival rates of both poplar clones on the im demonstrated that initiation into in vitro culture requires an individual approach for each clone separately. in general, the use of growth regulators has different effects on plant regeneration and rooting efficiency in populus species (bannoud and bellini 2021). in particular, the study by pardhi et al. (2019) showed that the addition of 0.5 mg.l-1 bap promoted the initiation of p. nigra explants into in vitro culture on the 21-st day of the experiment. an application of 0.1 μm iba showed high efficiency in rooting of himalayan poplar shoots (p. ciliata wallich ex royle) (aggarwal et al. 2015). shoot indirect regeneration from leaf and petiole explants after establishing both poplar genotypes, and their micropropagation in aseptic cultures, regeneration experiments were started. both types of explants, the leaf and petioles, formed callus within three weeks on cim with the growth regulators 2-ip and naa (fig. 3a). the explants of both poplar clones, transferred on sim with tdz (0.04 mg.l-1), formed the microshoots after two weeks of cultivation, more actively in poplar ‘novoberlinska-3’ compared to poplar ‘volosystoplidna’(fig. 3b and 3c). later, these microshoots were transferred on sem with the addition of bap (0.2 mg.l-1) (fig. 3d) and within two weeks regenerants from leaf and petiole explants in both poplar clones were obtained (fig. 3e and 3f) with different regeneration efficiencies (table 2). fig. 3. regeneration of poplar clones ‘volosystoplidna’ (a, c, e) and ‘novoberlinska-3’ (b, d, f) from leaf and petiole explants. a – callogenesis on cim after 10 days of cultivation; b, c – formation of microshoots after two weeks of cultivation on sim; d – microshoots transferred on sem; e, f – shoots growing on sem during two weeks. table 2. shoot regeneration from leaf and petiole explants of poplar clones ‘novoberlinska-3’ and ‘volosystoplidna’. clone type of explant the number of explants planted the number of explants with shoots the number of shoots per explant ‘novoberlinska-3’ leaves 39 36 112 petioles 30 27 43 ‘volosystoplidna’ leaves 38 19 30 petioles 31 18 33 5 nova biotechnol chim (2022) 21(1): e1089 3 the poplar clone ‘novoberlinska-3’ showed higher regeneration efficiency. in particular, the percentage of regeneration of this clone from leaf (92.3 %) and petiole (90 %) explants was significantly higher than in the poplar clone ‘volosystoplidna’, where the percentage of regeneration was lower, at 50 % from both leaf and petiole explants (fig. 4). as shown in the table 2, the number of shoots obtained from leaf explants in the clone of poplar ‘novoberlinska-3’ was 112, and from petiole explants – 43, while in the clone ‘volosystoplidna’ the number of shoots obtained from leaf and petiole explants was 30 and 33, respectively. therefore, the number of shoots per regenerated explant in the clone of poplar ‘novoberlinska-3’ from leaf explants was 3.1 (fig. 4b) that significantly exceeded all other variants by 1.5 – 2 times. thus, plant regeneration from leaf explants in the clone ‘novoberlinska-3’ showed the highest efficiency, which significantly differed from all other explants. as our experiments have shown, the composition of the nutrient medium plays an important but different role in the regeneration of the shoots of individual poplar clones. many studies (khatab 2011; cai et al. 2015; kwon et al. 2015; pardhi et al. 2019) have demonstrated that the optimal composition of the nutrient medium and concentration of phytohormones should be selected separately for each species and even for each cultivar and the type of explants. in particular, studies (tsvetkov et al. 2007) have shown that the addition of thidiazuron to the main nutrient medium at both high and low concentrations has different effects on shoot regeneration in white poplar (p. alba). the greatest regeneration efficiency was observed when lower concentrations were added (0.11 – 0.56 μm) compared to higher concentrations (14 μm). similarly, thidiazuron applied to stem, leaf, and root explants of p. berolinensis in higher concentrations (0.1 – 0.5 mg.l-1), than we did (0.04 mg.l-1), was inefficient for regeneration. in those experiments only very weak efficiency was determined for petiole explants under the lowest concentration of tdz (0.1 mg.l-1) (pavlichenko et al. 2016). addition of 0.5 μm naa induced callus formation in p. euphratica oliv. (cai et al. 2015). studies by garcia-angulo et al. (2018) showed that the addition of 0.5 μm naa leaded to the highest frequency of shoot regeneration in two hybrid clones of populus (p.×euramericana) and (p.×interamericana), but the shoots formed roots better in medium without naa. all these studies suggest that the appropriate composition of the nutrient medium must be selected at each stage of organogenesis. fig. 4. the efficiency of regeneration from leaf and petiole explants of poplar clones ‘novoberlinska-3’ and ‘volosystoplidna’ in vitro. the percentage of regenerated explants (% ± sp) (a) and the number of shoots per regenerated explant (mean ± standard error of the mean) (b) are presented. different letters above the bars indicate significant differences between the samples in the percentage of regenerated explants and the number of shoots per regenerated explant after the chi-square and the mannwhitney u test, respectively (p ≤ 0.05), n = 15 replicates. our results showed a significant difference between the survival rates of two clones during the culture 6 nova biotechnol chim (2022) 21(1): e1089 2 initiation. the differences in regeneration rates were also determined between the clones as well as leaf and petiole explants at the same composition of medium and growth regulators. thus, we can assume that the regeneration of shoots in poplar clones depends on both the genotype of the plants and on the tissues to be regenerated, and therefore requires the selection of optimal conditions for each clone. conclusion in this study, two clones of poplar ‘novoberlinska3’ and ‘volosystoplidna’ were introduced into in vitro culture. an optimal initiation nutrient medium for poplar ‘volosystoplidna’ was im-wpm supplemented with bap (0.2 mg.l-1) and iba (0.1 mg.l-1), on which the survival rate was 93.3 %. it was significantly higher than the survival rate of explants cultivated on im-ms with the same hormone composition. for poplar clone ‘novoberlinska-3’, although better survival rate (73.3 %) was observed on im-ms than on imwpm (46.7 %) but without a significant difference. the protocol chosen for indirect in vitro regeneration showed better performance of poplar clone ‘novoberlinska-3’, but was also efficient for the clone ‘volosystoplidna’. the percentage of regeneration in the clone ‘novoberlinska-3’ from leaf (92.3 %) and petiole (90 %) explants was significantly higher than in the poplar clone ‘volosystoplidna’, where the percentage of regeneration in each type of explants equalled 50 %. the regeneration rate of leaf explants of clone ‘novoberlinska-3’ (3.1) was also significantly higher than that of petiole explants and exceeded the rates of explants of clone ‘volosystoplidna’. obtained aseptic cultures of two highly productive poplar hybrids will be used in our further studies, and optimal protocols for regeneration will be applied for their genetic transformation. acknowledgements this work was carried out in the frame of the national academy of sciences of ukraine program “biofuel resources and bioenergy” (2019-2021) (the state registration number 0120u000278). it was also partially supported by the national research foundation of ukraine within the research competition “support for research of leading and young scientists”, the project “effects of stress factors on prion-like proteins synthesis in plants” (registration number 2020.02/0316). conflict of interest the authors declare that they have no conflict of interest. references abiri r, atabaki n, abdul-hamid h, sanusi r, ab-shukor na, shaharuddin na, malik s (2020) the prospect of physiological events associated with the micropropagation of eucalyptus sp. forests. 11: 1211. aggarwal g, gaur a, srivastava dk (2015) establishment of high frequency shoot regeneration system in himalayan poplar (populus ciliata wall. ex royle) from petiole explants using thidiazuron cytokinin as plant growth regulator. j. forestry res. 26: 651-656. aylott m, casella e, tubby i, street n, smith p, taylor g (2008) yield and 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participation and schools of young scientists “mechanisms of resistance of plants and microorganisms to unfavourable environmental”, irkutsk, russia, july, 1015. pp. 1244-1247. 8 microsoft word vidova2008b_manuscript_phagedispnbt.doc nova biotechnologica 8-1 (2008) 23 phage display – a tool for detection and prevention against pathogens. a review barbora vidová1,2, andrej godány2, ernest šturdík1 1institute of biochemistry, nutrition and health, slovak university of technology, sk-812 37 bratislava, slovak republic (b.vidova@gmail.com) 2 institute of molecular biology, slovak academy of sciences sk-845 51, bratislava, slovak republic 3department of biotechnology, university of ss. cyril and methodius, sk-917 01 trnava, slovak republic abstract: in this article are reviewed the promising uses of phage display in the areas such as microbial pathogens detection of and vaccination. phage display is a molecular technique by which foreign proteins are expressed at the surface of phage particles. such phages thereby become vehicles for expression that not only carry within them the nucleotide sequence encoding expressed proteins, but have also the capability to replicate. recent data acquired from genome sequencing and advances in phage biology research have aided the development of phage-derived bacterial detection and treatment strategies. key words: phage display, microbial pathogens, detection 1. introduction bacteriophages (phages) are viruses that infect bacteria. phages are either virulent (lytic) or temperate and use the host bacterium as a factory for their own replication. since their independent discovery by twort and d’herelle, research on phage has enabled major fundamental and technological advances that have been essential for the emergence of modern molecular biology (mcauliffe et al., 2007). in fact, it is difficult to over-emphasize the large impact that phage research has had on molecular biology. for example, phage research was cardinal in defining the central dogma of molecular biology, in the identification of dna as the genetic material, the definition and mapping of the gene, and the discovery of mrna as an intermediate for the production of proteins. furthermore, phages were used, simply and elegantly, to demonstrate the random pre-existing nature of genetic mutations before evolutionary selection, providing clear evidence of darwin’s natural selection theory (cairns et al., 2006). our understanding of gene regulation has also profited immensely from studies using lambda phage (λ) (ptashne, 2004). in molecular biology, the impact of phage-derived technology is clearly visible: transducing phage, restriction enzymes, phage promoter-based expression systems, random mutagenesis (e.g. phage mu), phage-based cloning vectors and genomic libraries, and phage display techniques, to name but a few. the sheer abundance of phage on earth (estimated to be 1031 (wommack and colwell, 2000)) and the accumulating data from both phage and bacterial genome sequencing projects have highlighted the global significance of phage in bacterial ecosystems and their key role in the adaptive evolution of bacteria. 24 vidová, b. et al. sequence analysis indicates that up to 20% of each bacterial genome might consist of phage-related dna in the form of prophage or phage remnants (casjens, 2003). the importance of these phage-related sequences in the evolution of bacteria is most striking in the phenomenon of lysogenic conversion. for example, in vibrio cholerae, the genes encoding cholera toxin are provided by a converting phage, resulting in a virulent strain (waldor and friedman, 2005). phage are genetically diverse; approximately half of newly sequenced phage genes have no known homologues (hambly and suttle, 2005), and phage genomes vary in size by at least two orders of magnitude (kutter, 2005). this review aims to provide an insight into how an understanding of phage biology can be exploited to generate novel bacterial detection and vaccination strategies. 2. phage display principles in phage display, a heterologous peptide or protein is displayed on the surface of the phage (fig. 1) through transcriptional fusion with a coat-protein gene (smith, 1985), which is accomplished by the incorporation of the nucleotide sequence encoding the protein to be displayed into a phage or phagemid genome as a fusion to a gene encoding a phage coat protein. this fusion ensures that as phage particles are assembled, the protein to be displayed is presented at the surface of the mature phage, while the sequence encoding it is contained within the same phage particle. this physical link between the phenotype and genotype of the expressed protein and the replicative capacity of phage are the structural elements that underpin all phage display technology (fig. 1) (willats, 2002). this results in a production a novel phage particle that has a variety of potential uses. the most widely used phage display methods are based on the use of m13 and related filamentous phages of escherichia coli but others, including the e. coli phages λ and t7, have also been used (benhar, 2001, willats, 2002). because particulate phages are relatively easy and inexpensive to purify, phage display can also provide a means of purifying a particular protein or antibody. phage-display libraries can be screened in several ways to isolate displayed peptides or proteins with practical applications. for example, it is possible to isolate displayed peptides that bind target proteins with affinities similar to those of antibodies. they can then be used as therapeutics, which act either as agonists or through the inhibition of receptor–ligand interactions. the high-affinity, displayed peptides also have the potential to be used for the detection of pathogens and agents posing a biological threat in the environment (petrenko and vodyanoy, 2003). a more complete discussion of the potential of phage display is given in several recent reviews (benhar, 2001, willats, 2002, wang and yu, 2004). the simplest way of achieving the expression of a foreign protein is to simply create a fusion between the nucleotide sequence to be expressed and a coat protein gene within the viral genome (fig. 2a). using this direct approach all the copies of the chosen coat protein become fusion proteins (winter et al. 1994). this can be advantageous in terms of numbers of nova biotechnologica 8-1 (2008) 25 expressed foreign proteins but if the functionality of the chosen coat protein is compromised by the fusion then phage viability may be affected, especially since no wild type versions of the coat protein are retained. fig. 1. the principle of phage display. (a) simplified hypothetical bacteriophage with coat proteins piii, pvi, pviii, pvii, pix. (b) forein peptide or protein is dispalyed at the phage surface by the fusion of gene encoding forein protein with phage piii coat protein coding gene, or (c) by the fusion of gene encoding forein protein with phage pviii coat protein coding gene. the number of copies of forein protein displayed is related to which phage coat protein is chosen as a fusion partner (melita et al., 2001). this can be avoided if hybrid phages are produced in which some versions of a given coat protein are wild type and some are fused to a foreign protein (fig. 2b and 2c). in some hybrid phage systems, the gene fusion is an additional element of the phage genome so that a wild type copy of the coat protein gene is retained and phage particles express both wild type and fusion proteins (fig. 2b) (sidhu, 2001). alternatively, hybrid phage may be created using a phagemid-based system and this approach has been widely adopted (fig. 2c). sequences encoding fusion proteins are carried by phagemids (plasmids with a phage origin of replication) while the most of the genes required for the formation of phage particles are carried by helper phage that is co-infected together with phagemids into host bacteria (sidhu, 2001) (fig. 2c). 26 vidová, b. et al. fig. 2. strategies for the expression of proteins at the surface of a simplified hypothetical bacteriophage. the simplest format for the expression of a peptide or protein (a) is to fuse the gene (gχ) encoding the foreign protein (pχ) to one of the phage coat protein genes (e.g., g1) hybrid phage (b) may be created by incorporating the gene fusion (g1/gχ) as an additional element in the phage genome. with this arrangement, two versions of the phage coat protein chosen as the fusion partner are encoded one by the native gene (p1) and one by the fusion gene (p1/pχ). as phage particles are assembled both p1 and p1/pχ are incorporated into the phage coat. phagemid based systems (c) are also widely used to construct hybrid phage. however, instead of being present on a single genome, the genes encoding wild type coat protein and fused protein are carried by helper phage and phagemid respectively. host bacteria contain both phagemid and helper phage dna and both genomes contribute to the synthesis of hybrid phage particles (willats, 2002). 3. phages for the detection and typing of bacteria many methods of detecting specific bacteria are available, but the low-cost and ready production of large numbers of phage, added to their specificity for a target nova biotechnologica 8-1 (2008) 27 bacterial species, makes them ideal for bacterial detection. although other biomolecules can confer specificity of molecular recognition, they have their own limitations. for example, antibodies are expensive to produce and sensitive to harsh environmental conditions. another important advantage of phage-based systems is that they usually only detect living bacteria, thereby reducing the number of false positives that arise from the use of approaches such as pcr. furthermore, dead cells present after processes such as pasteurization or disinfection might be no hazardous but still can be detected by antibodies (petty et al., 2007). phages bounded to bacteria can be detected by specific labeled antibodies, thereby increasing the sensitivity of detection (watson and eveland, 1965). for specific typing, different species of phage can be plated out onto a lawn comprising an unidentified bacterial strain, and the presence of clear areas (plaques) where an individual phage particle has grown and lysed the surrounding cells enables identification of the specific bacteria. recombinant phages are often used in phagebased detection systems (benhar, 2001; willats, 2002). the methods that have been used to detect pathogenic bacteria include (i) using phages specifically to deliver reporter genes, e.g. lux (kodikara et al., 1991) or green fluorescent protein (funatsu et al., 2002), which are expressed after infection of target bacteria; (ii) using phages that have a fluorescent dye covalently attached to the phage coat, and detecting the specific adsorption (hennes et al., 1995; goodridge et al., 1999); (iii) the detection of released cellular components, such as adenylate kinase (corbitt et al., 2000), after specific lysis; and (iv) using phages displaying peptides or antibody fragments that will bind specific bacterial pathogens or toxins. other means of improving the sensitivity of detection are phage amplification assays. in brief, phage infection of the pathogenic bacterium results in the release of many phage particles that can be detected by a second (non-pathogenic), sensitive bacterial strain. success with this approach has been seen with the detection of mycobacterium tuberculosis (petrenko and vodyanoy, 2003). a more detailed account of these and other techniques is provided elsewhere (kutter, 2005) and a selection that emphasizes the range and sensitivity of the technologies used and the diversity of detectable bacterial species is summarized in table 1 (petty et al., 2007). 4. phages as vaccine delivery vehicles phages have been used as potential vaccine delivery vehicles in two different ways: by directly vaccinating with phages carrying vaccine antigens on their surface or by using the phage particle to deliver a dna vaccine expression cassette that has been incorporated into the phage genome (clark and march, 2004). in phage-display vaccination, phages can be designed to display a specific antigenic peptide or protein on their surface. alternatively, phages displaying peptide libraries can be screened with a specific antiserum to isolate novel protective antigens or mimetopes – peptides that mimic the secondary structure and antigenic properties of a protective carbohydrate, protein or lipid, despite having a different primary structure (folgori et al., 1994; phalipon et al., 1997). the serum of convalescents can also be used to screen phage-display libraries to identify potential vaccines against 28 vidová, b. et al. a specific disease, without prior knowledge of protective antigens (meola et al., 1995). in a few cases, whole phage particles displaying antigenic proteins have been used as vaccines in animal models (wang and yu, 2004; irving et al., 2001). specific antibody responses (di marzo veronese et al., 1994) and protection against an immune challenge have been shown (bastien et al., 1997). tab. 1. applications of the different phage-based antibacterial strategies target species type of assay matrix assay sensitivity refs time (hours) listeria monocytogenes luxab reporter phage and single-tube culture 2 102–103 cfu/ml loessner et al., 1996 luminometer spiked salad 22–24 1 cfu/g e. coli 0157:h7 fluorescently labeled phage and flow ground beef 6 2.2 cfu/g goodridge et al., 1999 cytometry milk 10 10 1–102 cfu/ml e. coli xl1blue quorum sensing and bioluminescence culture 1.5 10 8 cfu/ml ripp et al., 2006 (luxcdabe) 10.3 1 cfu/ml spiked lettuce 12.1 105 cfu/ml leaves 22.4 102 cfu/ml e. coli bl-21 biotin-tagged phage and quantum dots culture 1 10 cfu/ml edgar et al., 2006 nanocomplexes, fluorescence microscopy and flow cytometry pseudomonas aeruginosa phage amplification culture 4 40 cfu/ml stewart et al., 1998 e. coli phage-mediated release of adenylate culture 1 10 4 cfu/ml blasco et al., 1998 kinase mycobacteriu m tuberculosis phage replication assay sputum 2 days 100 cfu/ml mcnerney et al., 2004 microlunatus phosphovorus fluorescently labelled phage and activated sludge 1 10 2 cfu/ml lee et al., 2006 epifluorescent microscopy e. coli k-12, mg1655 b-d-galactosidase reporter phage and culture 6–8 0.01 cfu/ml neufeld et al., 2003 amperometric detection e. coli k-12 w3110 sensing of phagetriggered ion cascade culture 10 min 1 cfu/ml dobozi-king et al., 2005 (septic) staphylococcu s aureus spreeta surface plasmon resonance culture not stated 10 4 cfu/ml balasubra manian et al., 2006 nova biotechnologica 8-1 (2008) 29 rather than generating a transcriptional fusion to a coat protein, substances could also be artificially conjugated to the surface of phages after growth, which further increases the range of antigens that can be displayed (molenaar et al., 2002). because phage particles are naturally immunostimulatory (clark and march, 2004; kleinschmidt et al., 1970), an antigen presented on the phage coat would come ‘ready conjugated’ with a natural adjuvant activity, without the need for separate protein purification and subsequent conjugation to a carrier molecule before immunization. more recently, it has also been shown that unmodified phages can be used to deliver dna vaccines more efficiently than standard plasmid dna vaccination (clark and march, 2004; march et al., 2004; jepson and march, 2004). when compared with standard dna vaccination, superior antibody responses have been shown in mice (clark and march, 2004) and rabbits (march et al., 2004). 5. conclusion according to here reviewed information about phage display, this technique/tool has a multipurpose utilization in molecular evolution, analysis of protein/ligand interactions and the generation of antibodies. taking into account a prevention against pathogenic microorganisms, phage display could be used as a potential vaccine against streptococcus agalactiae, a well-known bovine mastitis pathogen of particular importance because it is highly infectious (spreading from cow to cow by machine milking, unless care is taken to disinfect the teat cups), and causes mainly subclinical infections. as a result, s. agalactiae can spread widely within a herd, causing immediate loss due to reduced milk yield, and eventual large losses, when it is finally recognized. additionally, this pathogen can be transmitted through dairy product to consumers. therefore, useful vaccine against this bacterium is of great interest. all clinical isolates of s. agalactiae express a polysaccharide capsule, with nine capsular serotypes identified so far. the major invasive disease causing serotypes are ia, ib, ii, and iii (schuchat, 1998). indeed, it was observed that the protection conferred by capsular polysaccharides is type specific (kasper et al., 1996). noncapsular surface antigens are being investigated as potential vaccine candidates or carrier proteins (gravekamp et al., 1999; stålhammar-carlemalm et al., 1993). one of these noncapsular antigens, the sip protein, was highly conserved and produced by every s. agalactiae strain examined to date, which included representative isolates of all serotypes (brodeur et al., 2000; chotár et al., 2006). it was also established that sip-specific antibodies recognized their epitopes at the cell surfaces of different s. agalactiae strains (rioux et al., 2001). more importantly, the immune response to purified recombinant sip protein efficiently protected adult mice against experimental infection with s. agalactiae strains representing serotypes ia/c, ib, ii/r, iii, v, and vi (brodeur et al., 2000). however, the direct use of a peptide presenting by a recombinant phage displaying as a vaccine to examine its protective potential would be simpler and much less expensive than the conventional method of peptide synthesis or recombinant protein preparation and purification for immunization. the recombinant phage displaying a pathogen specific peptide, in s. agalactiae the displaying of mentioned sip protein or its part, representing an immunogenic mimic of 30 vidová, b. et al. natural antigen. this could lead to production of antibodies specific to pathogen. recombinant bacteriophage displaying a disease specific epitope can be use as a vaccine to examine the potential of an epitope of interest to prevent disease. phage display has also the overwhelming advantage that it is has cheap and easy. it uses standard microbiological techniques that are familiar to all molecular biologists, and its key resources phage libraries and clones are replicable and therefore nearly costfree after their initial construction or selection. it is astonishing to contemplate that within a single tube could be fit a few hundred trillion phage particles displaying billions of different peptide structures an abundance and diversity from which hundreds of different users with altogether different purposes in mind can select clones of great value. and when that supply has nearly run out, only simple propagation is needed to replenish what is left to satisfy the needs. where a safe and efficacious vaccine available, screening and administration of antibiotics would be unnecessary, policies for the prevention of s. agalactiae infections would be simplified and importantly, prevention would be more successful, whereby this approach is applicable to many other pathogenic microorganisms. additionally, cost-effectiveness analyses invariably demonstrate that vaccination is the most cost-effective of all potential prevention. acknowledgements: figure 1 has been reprinted from current opinion in 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ecosystems. microbiol. mol. biol. rev., 64, 2000, 69–114. nova biotechnol chim (2022) 21(2): e1228 doi: 10.36547/nbc.1228 1 nova biotechnologica et chimica phenolic contents, antioxidant, and enzyme inhibitory effects of crude extracts of polycarpon polycarpoides fiori subsp. catalaunicum o. bolòs & vigo madiha arioua1, asma cheribet1, lynda gali2, 1department of biochemistry and cellular and molecular biology, faculty of natural and life sciences, frères mentouri constantine 1 university, constantine, algeria 2biotechnology research center (crbt), ali mendjli, nouvelle ville, uv 03, bp e73 constantine, algeria  corresponding author: lyndag652@gmail.com article info article history: received: 14th october 2021 accepted: 11th march 2022 keywords: α-amylase acetylcholinesterase antioxidant activity caryophyllaceae polycarpon polycarpoides urease abstract the present work aimed to study some pharmacological effects of extracts of the aerial parts of polycarpon polycarpoides fiori subsp. catalaunicum o. bolòs & vigo (caryophyllaceae) widely distributed in the mediterranean basin. the crude extracts were prepared using four solvents (petroleum ether, ethyl acetate, methanol, and methanol: water 1 : 1, v/v), and then examined for their phenolic contents using spectrophotometric methods and for their in vitro antioxidant activity and ability to inhibit urease, acetylcholinesterase, and α-amylase. low levels of total phenolic were recorded ranging from 14.39 ± 3.40 to 101.84 μg.gae.mg-1 of extract corresponding to the petroleum ether and ethyl acetate extracts, respectively. as for the flavonoids, very low values varying from 0.37 ± 0.13 to 4.22 ± 0.83 μg.gae.mg1 of extract were obtained. a moderate antioxidant effect was exerted by the extracts most often the methanol and ethyl acetate extracts were the most potent probably due to their polyphenolic content. remarkable inhibitory effect has been exhibited by the extracts against α-amylase and more specifically, the petroleum ether extract displayed the strongest capacity with a percentage inhibition of 48.19 ± 2.99 % at 400 µg.ml-1. however, all extracts were inactive against urease and acetylcholinesterase. these results could constitute a starting point for carrying out more studies on the plant in order to assess the possibility of valuing it as a source of bioactive compounds. introduction recently, the awareness of the harmful effects of the excessive use of synthetic products incorporated in pharmaceutical or food formulations for therapeutic, nutritional, organoleptic purposes has led to increased interest in natural products. in addition, the interest of natural products has also arisen from the fact that these compounds can exert multiple effects by their action on various targets providing more beneficial effects (ayaz et al. 2019). therefore, it is important to research new therapeutic substances, nutraceuticals, or food additives as alternatives to synthetic products (moldes et al. 2017). in this context, plants remain the main source of new therapeutic molecules with high healing potential and less toxic effects (christaki et al. 2012; gali et al. 2020). mailto:lyndag652@gmail.com nova biotechnol chim (2022) 21(2): e1228 2 natural antioxidants have received a lot of attention in recent decades for their incorporation into foods as additives to delay the oxidation reactions responsible for the loss of their nutritional and organoleptic qualities (lourenço et al. 2019). in fact, the use of synthetic antioxidants such as butylhydroxyanisol (bha) and butylhydroxytoluene (bht) in the food industry has raised concerns about their possible involvement in certain carcinogenesis processes and therefore their replacement by natural compounds with less harmful effects constituted a primary need (dolatabadi and kashanian 2010). antioxidants-based supplements have also been the subject of recent years as there is growing evidence for the involvement of free radicals and other reactive species in the development of certain chronic diseases such as cancer, inflammatory, metabolic, cardiovascular and neurological diseases (moure et al. 2001). among phytochemicals, polyphenols are recognized as the most potent natural antioxidants found in both edible and nonedible plants due to their structure with hydroxyl groups giving them potential redox properties (shahidi and ambigaipalan 2015). plants are also considered an important source of therapeutics to treat many diseases due to the presence of various phytochemicals targeting cellular constituents such as enzymes that are central to biochemical reactions. in fact, many therapies used in the management of certain diseases are based on the inhibition of key enzymes as in the case of alzheimer's disease and type 2 diabetes. the need for new molecules and especially of natural origin comes from the toxicity and/or non-specificity of the available treatments and therefore lower effectiveness of these therapies (kekuda and rao 2019). caryophyllaceae also known as the rose family is one of the largest families of around 3,000 species generally distributed in the northern hemisphere, particularly in the mediterranean basin (derici et al. 2021). this family is known for its richness in active metabolites, in particular flavonoids, alkaloids, triterpene saponins, phytoecdysteroids and sterols (jakimiuk et al. 2021). the presence of various active constituents makes the species of this family of medical importance and can be interesting sources of new bioactive constituents of therapeutic or food interests. caryophyllaceae plants have been reported to exert various biological effects such as antioxidant, antiviral, anticancer, anti-inflammatory and antimicrobial effects. (chandra and rawat 2015). polycarpon polycarpoides (biv.) fiori subsp. catalaunicum o. bolòs & vigo is a species of the caryophyllaceae family that grows in northern algeria. however, data on its pharmacological effects are poorly provided. thus, this study is devoted to determining some of the biological effects of this species for its valuation as medicinal or food plant. experimental chemicals folin-ciocalteu, sodium carbonate, vanillin, 2,2-diphenyl-1-picrylhydrazyl (dpph), 2,2′-azinobis(3-ethylbenzothiazoline-6-sulfonic acid) (abts), potassium persulfate (k2s2o8), neocuproine, ache type vi-s from electric eel (<1000 u.mg-1 solid), urease from canavalia ensiformis (jack bean, ≥5 u.mg-solid), α-amylase from aspergillus oryzae (≥150 u/protein) trolox, gallic acid, quercetin, catechin, and other chemicals were purchased from sigma-aldrich (saint-louis, usa) acetylthiocholine-iodide was obtained from applichem gmbh, (darmstadt, germany. all organic solvents and chemicals used in this study were of analytical grade. all the assays were carried out on a 96-well microplate, and the absorbance was recorded using a enspire multimode plate reader (perkinelmer, waltham, usa). plant material the aerial part of polycarpon polycarpoides was collected in annaba (northern algeria) in december 2017. the plant was identified by dr. tarek hamel (department of biology, badji mokhtar university, annaba, algeria). the samples were cleaned and air dried in the dark, and then ground to a fine powder using an electric grinder. nova biotechnol chim (2022) 21(2): e1228 3 preparation of crude extracts the extraction procedure was carried out by soaking 25 g of vegetable powder in 100 ml of the extraction solvent (petroleum ether, ethyl acetate, ethanol and methanol: water (1:1, v/v) for 2 h with continuous stirring (300 rpm) at room temperature, the solution obtained was filtered through a whatman filter (whatman filter paper n°4). the marc is extracted twice more to extract the maximum of soluble compounds. the various solvents were then eliminated under reduced pressure at 40 °c using the rotary evaporator buchi r-215 (büchi ag, uster, switzerland). the residues were stored at 4 °c for further analysis. total phenolic contents total phenolic content in polycarpon polycarpoides extracts was determined by the folin-ciocalteu method on a 96-well microplate as reported by müller et al. (2010). the reaction consisted of mixing 20 µl of samples (1 mg.ml-1), 100 µl of folin-ciocalteu reagent (diluted in distilled water, 1 : 9, v/v), and 75 µl of sodium carbonate (7.5 %) for 2 h in darkness at room temperature. the absorbance was then read at 765 nm in a microplate reader (perkin elmer enspire, singapore). total phenolic contents were expressed as µg gallic acid equivalents per mg of extract (µg.gae.mg-1) using the equation of linear regression obtained from the gallic acid standard curve (y = 0.0034 gallic acid + 0.1044, r2 = 0.9972). total flavonoids content total flavonoids were quantified by the aluminum chloride (alcl3) method according to terkmane et al. (2018) with some modifications. a volume of 100 µl of plant extract (1 mg.ml-1) and an equal volume (100 µl) of a methanolic solution of aluminum chloride hexahydrate (alcl3·6h2o, 2 % prepared in methanol) were mixed. the reaction was left for 15 min and the absorbance was then recorded at 415 nm against a blank containing the sample and methanol instead of alcl3. the results were reported in µg of quercetin equivalent per mg of extract (µg.qe.mg-1) calculated from the standard curve of quercetin (y = 0.027 quercetin, r² = 0.9989). condensed tannins content condensed tannins contents were investigated following the method reported by bakhouche et al. (2021). in a 96-well microplate, each extract was reacted with hydrochloric acid (30 %) and a methanolic solution of vanillin (4 % in methanol). the absorbance of the red complex flavonolsvanillin was measured at 500 nm. the results were expressed as µg of catechin equivalents (µg ce) per mg of extract calculated from the standard curve of catechin (y = 0.0026 catechin + 0.0301). dpph scavenging activity the capacity of the polycarpon polycarpoides extracts to trap the dpph radical was determined according to the method reported by el aanachi et al. (2020). briefly, 40 µl of extracts or standards (trolox and ascorbic acid) at different concentrations (6.25 – 800 µg.ml-1) were reacted with a 160 µl of a freshly prepared solution of dpph (1 mm in methanol). the residual purple color of the dpph radical was followed at 517 nm after 15 min of incubation. the results were expressed as percentages of inhibition calculated according to the formula below (eq. 1): inhibition (%) = ((ac – as)/ ac) × 100 (1) where ac and as are the absorbances of the control (methanol and dpph solution) and of the sample, respectively. the concentration of the extract inhibiting 50 % of the radical (ic50) was determined from the curve drawn by the percentages of inhibition at different concentrations. scavenging activity of abts•+ the ability of extracts to trap radicals abts has been evaluated using the method described by dudonné et al. (2009) with some modifications. the abts•+ cation solution has been previously prepared by reacting a volume of 7 mm of abts with a same volume of 2.5 mm potassium persulfate for 16 hours at room temperature and in nova biotechnol chim (2022) 21(2): e1228 2 the dark. the resulting solution is diluted with distilled water to obtain a solution having an absorbance of 0.7 at 734 nm. then, samples (40 μl) at different concentrations were pipetted in a microplate and then 160 μl of a diluted solution of abts•+ were added and the mixture was allowed to react for 10 min. the absorbance was recorded at 734 nm. the inhibition rates of the radical were determined using the previous formula (1). ic50 values were calculated from the equation of the regression curves. phenanthroline assay the method reported by szydłowska-czerniak et al. (2008) was used to measure the ability of extracts to reduce ferric iron in the phenanthroline-fe (iii) complex. in a 96-well microplate, 10 µl of extract, 50 µl fecl3 (0.2 %), 30 µl phenanthroline (0.5 % in methanol), and 110 µl methanol were mixed. the reaction was left for 20 min at room temperature and the absorbance was then measured at 510 nm. the results are reported in the form of absorbances. trolox and ascorbic acid were used as standards. cupric reducing antioxidant capacity (cuprac) the cuprac test was performed by the method described by apak et al. (2004). in a 96-well microplate, 40 μl of extract, 60 μl of ammonium acetate (1 m), and 50 μl of neocuproine (7.5 mm), and 50 μl of copper (ii) chloride (10 mm) are mixed. the mixture is incubated for 1 h, and the absorbance was read at 450 nm. results were reported as absorbances at different concentrations and were compared to the standards trolox and ascorbic acid. α-amylase inhibition the determination of the inhibitory activity of α-amylase is carried out according to the method of yang et al. (2012) with modifications. in a 96 wellmicroplate, 25 μl of each extract at different concentrations was mixed with 50 μl of the αamylase solution (1 u.ml-1 in the phosphate buffer saline, 100 mm, ph, 6.9, 6 mm nacl) for 10 min at 37 °c. the enzymatic reaction was initiated by adding 50 μl of starch (0.1 %). a second incubation for 10 min at 37 °c is carried out and the reaction was stopped by the addition of 25 μl hcl (1 m), and the residual starch is revealed by 100 μl of iodine-potassium iodide solution (iki). the reading is carried out at 630 nm against a negative control containing all reagents without the extracts. in parallel, controls containing only the starch solution and iki, or the sample solutions and iki were performed. results are reported as percentages of inhibition at different concentrations using the formula below (eq. 2): inhibition (%) = [1-((as-ab)/(ae-ac))]*100 (2) where: ac is the absorbance of the reaction containing only starch, iki, and hcl without enzyme and inhibitor solutions, ae is the absorbance of the control containing all the reagents without inhibitor, as is the absorbance of the reaction containing all the reagents in presence of the test sample, ab is the absorbance of the blank containing only the test sample and iki. urease inhibition the inhibitory effect of the extracts on urease was examined using the protocol described by nabati et al. (2012). the extracts (10 μl) were mixed with 25 μl of the urease solution (1 mg.ml-1 in 100 mm of phosphate buffer, ph 8.2) and 50 μl of urea (30 mm). the amount of ammonia in the medium was quantified by adding 45 µl of phenol reagent (0.4 g of phenol and 2 mg of sodium nitroprusside in 40 ml of deionized water) and 70 µl of the basic reagent (0.3 g of naoh and 0.5 ml of hypochlorite in 60 ml of deionized water). the absorbance of the blue color of the complex ammonia-phenol-hypochlorite was recorded at 630 nm. results are reported in terms of percent inhibition calculated using the following formula (eq. 3): % inhibition = (e-s/e)× 100 (3) where e represents the absorbance of the control containing the enzyme solution without the tested samples, whereas s is the absorbance of the 4 nova biotechnol chim (2022) 21(2): e1228 3 reaction medium in the presence of the tested sample. acetylcholinesterase inhibition the inhibition of acetylcholinesterase was examined by the method previously reported by (cetin cakmak and gülçin 2019). briefly, a volume sample (10 µl) were put in contact with 20 µl of acetylcholinesterase (5.32.10-3 u in 0.1 m phosphate buffer, ph 8) at 25 °c for 15 min. the reaction was started by adding acetylthiocholine iodide (0.71 mm) and the resulting thiocholine was quantified by dtnb (10 µl, 0.5 mm). the absorbance as monitored at 415 nm. the rate of inhibition was determined using the preceding eq. 3. statistical analysis data were presented as mean ± standard deviation of three measurements. one-way anova analysis followed by the tukey's multiple comparison test was adapted to analyse the difference between samples using graphpad software version 5 (graphpad software inc, california, usa). the p-value was set at 0.05. results phenolic compounds contents the results of the quantification of the main classes of polyphenols are shown in table 1. as shown, the total phenolic and flavonoids contents are influenced by the extraction solvent. ethyl acetate and methanol extracts gave the highest total phenolic contents with values of 108.12 ± 8.15 and 101.84 ± 2.21 µg.gae.mg-1 of extract, respectively (the values are not significantly different, p>0.05). in another hand, the contents of flavonoids recorded were very weak ranging from 0.37 ± 0.13 (petroleum ether) to 4.22 ± 0.83 µg.gae.mg-1 of extract observed in the ethyl acetate extract. table 1. extraction yield, total phenolic, total flavonoids, and condensed tannins contents of polycarpon polycarpoides extracts. total phenolic [µg.gae.mg-1] total flavonoids [µg.gae.mg-1] condensed tannins [µg.ce.mg-1] petroleum ether 14.39 ± 3.40c 0.37 ± 0.13c nd ethyl acetate 108.12 ± 8.15a 4.22 ± 0.83a nd methanol 101.84 ± 2.21a 1.43 ± 0.27b nd methanol: water 43.12 ± 1.02b 1.04 ± 0.26b nd gae – gallic acid equivalents, qe – quercetin equivalents, ce – catechin equivalents. values bearing different letters in the column are statistically different (p < 0.05). antioxidant activity the antioxidant activity of the extracts was assessed using five different methods and the results were reported as percentage of inhibition or absorbances at different concentrations (fig. 1). the values of ic50 obtained in the dpph and abts assays were also reported in table 2. anti-free radical scavenging activity has been studied using free radicals dpph and abts, which are widely used to determine in vitro the ability of extracts or compounds to scavenge free radicals. the extracts showed dose-dependent scavenging activity against both dpph and abts free radicals, as shown in fig. 1a, b. comparing the extracts on the basis of their ic50 values, the methanol extract showed the most potent scavenging activity against dpph and abts radicals with ic50 values of 249.46 ± 11.22 and 73.86 ± 1.89 µg.ml-1, respectively, followed by ethyl acetate extract, methanol: water and petroleum ether showing the weakest effect against these radicals (ic50>800 µg.ml -1). in addition, the antioxidant activity of polycarpon polycarpoides extracts was measured by methods based on the reduction of a metal ion associated with a chromophore, which undergoes a color change upon receipt of an electron. the ability of the extracts to reduce iron ions was assessed using the phenanthroline test (fig. 1c). the extracts can 5 nova biotechnol chim (2022) 21(2): e1228 2 be classified according to their ability to reduce fe (iii) to fe (ii) reported in terms of absorbances at 200 µg.ml-1in descending order as follows: methanol: water > ethyl acetate > methanol > ether from petroleum giving the corresponding absorbances 0.65 ± 0.02, 0.58 ± 0.03, 0.50 ± 0.00, 0.35 ± 0.04, respectively. these results were considered low compared to trolox and ascorbic acid standards giving absorbances of 0.56 ± 0.02 and 0.80 ± 0.0, respectively using a very low concentration (6.25 µg.ml-1). in the reduction of copper ions evaluated by the cuprac assay (fig. 1d), ethyl acetate extract was the most potent providing the highest absorbance at the concentration of 800 µg.ml-1 (1.85 ± 0.09). methanol extract also showed a remarkable ability to reduce copper ions with the absorbance of 1.85 ± 0.09 at the highest concentration used (800 µg.ml-1), followed by ether petroleum extract (1.11 ± 0.02), and finally, aqueous methanol has the lowest reducing capacity with an absorbance of 0.8 ± 0.03. trolox and ascorbic acid exerted a very potent ability to reduce copper ions with absorbances of 1.34 ± 0.13 and 1.38 ± 0.11, respectively at very low concentrations (25 µg.ml-1). 0 200 400 600 800 0 20 40 60 80 100 petroleum ether ethyl acetate methanol methanol: water concentration µg/ml % i n h ib it io n o f d p p h 0 200 400 600 800 0 20 40 60 80 100 petroleum ether ethyl acetate methanol methanol: water concentration µg/ml % i n h ib it io n o f a b t s 0 50 100 150 200 0.0 0.2 0.4 0.6 0.8 petroleum ether ethyl acetate methanol methanol: water concentration µg/ml a b s o rb a n c e a t 5 1 0 n m 0 200 400 600 800 0.0 0.5 1.0 1.5 2.0 2.5 petroleum ether ethyl acetate methanol methanol: water concentration µg/ml a b s o rb a n c e a t 4 5 0 n m a b c d fig. 1. dose-dependent effect of the extracts showed in the antioxidant activity determined by different assays. scavenging effect of the radical dpph (a), abts (b), reduction of fe (iii)-phenanthroline (c), and reduction of copper (d). each point presents the mean ± sd (n = 3). table 2. ic50 values of polycarpon polycarpoides obtained with dpph and abts. dpph ic50 [µg.ml-1] abts ic50 [µg.ml-1] petroleum ether >800 >800 ethyl acetate 333.76 ± 1.08b 90.51 ± 2.82a methanol 249.46 ± 11.22a 73.86 ± 1.89b methanol: water 500,06 ± 3.19c 92.15 ± 1.99a trolox 5.12 ± 0.21 3.21 ± 0.06 ascorbic acid 4.39 ± 0.01 3.04 ± 0.05 values are reported as means ± sd of three measurements. values bearing different letters in the same column are significantly different (p < 0.05). 6 nova biotechnol chim (2022) 21(2): e1228 3 enzyme inhibitory effect p. polycarpoides extracts have been tested for their ability to inhibit certain enzymes, including αamylase, urease and acetylcholinesterase and the results were shown in fig. 2. the results indicated that all the plant extracts exhibited remarkable inhibition of alpha-amylase at a dose-dependent manner (results not shown) and was significantly (p < 0.05) influenced by the extraction solvent (fig. 2a). in this context, the petroleum ether extract was the most potent with a percentage inhibition at 400 µg.ml-1 of 48.19 ± 2.99 %.the other extracts also exerted an interesting inhibitory effect and can be classified in ascending order as follows: ethyl acetate > methanol > methanol : water showing percentages of inhibition at the highest concentration (400 µg.ml-1) of 38.89 ± 0.82, 31.74 ± 2.27, and 15.31 ± 2.75 %, respectively. all the extracts were more potent than acarbose, which moderately inhibited the enzyme using high concentrations (62.5 – 4,000 µg.ml-1). at the highest concentration (4,000 µg.ml-1), acarbose inhibited the enzyme with a rate of 53.05 ± 1.59 %. all the extracts were inactive against urease and acetylcholinesterase (fig. 2b, c, respectively). p et ro le um e th er e th yl a ce ta te m et ha no l m et ha no l:w at er a ca rb os e 0 10 20 30 40 50 60 400 µg/ml (4 00 0 µg /m l) in h ib it io n o f a lp h a -a m y la se ( % ) p et ro le um e th er e th yl a ce ta te m et ha no l m et ha no l:w at er t hi ou re a 0 20 40 60 80 100 200 µg/ml in h ib it io n o f u r e a se ( % ) p et ro le um e th er e th yl a ce ta te m et ha no l m et ha no l:w at er g al an ta m in e 0 20 40 60 80 100 200 µg/ml in h ib it io n o f a c h e ( % ) a b c a b c d fig. 2. enzyme inhibitory effect of polycarpon polycarpoides extracts. inhibition pecentages of the extracts on α-amylase at 400 µg.ml-1 in comparison with acarbose at 4,000 µg.ml-1 (a). activity of the extracts and thiourea on urease at 200 µg.ml-1 (b). effect of the extracts and galantamine on acetylcholinesterase at 200 µg.ml-1 (c). each column presents the mean ± sd of three measurements. columns bearing different letters are significantly different (p < 0.05). 7 nova biotechnol chim (2022) 21(2): e1228 3 discussion natural bioactive compounds in plants have gained a lot of attention in recent decades as alternatives to synthetics widely used in the pharmaceutical and food industries. local plants can constitute potential reserves of new bioactive molecules and the study of their bioactivity, and their phytochemical composition represents the starting point of their valuation. polyphenols are an important class of molecules of plant origin exhibiting a wide range of pharmacological effects and exerting beneficial effects on human health (quiñones et al. 2013). the phenolic structure of these compounds makes them the most potent antioxidants among other natural phytoconstituents and therefore it is essential to quantify them in plant extracts (shahidi and ambigaipalan 2015). the quantity as well as the nature of the compounds extracted strongly depend on the extraction solvent. the highest yield is observed in methanol: water (1 : 1) and this observation could be explained by the fact that caryophyllaceae plants are particularly rich in glycosylated saponins with high solubility in water. however, phenolic compounds are more concentrated in ethyl acetate and methanol extracts, which is in agreement with the reported literature supporting that these compounds are more soluble in the polar organic solvent than water alone or weakly polar solvents (babbar et al. 2014; gali and bedjou 2019; yakoubi et al. 2021) the antioxidant properties of plant extracts or natural ingredients have prompted manufacturers to incorporate them as natural alternative additives in foodstuffs to preserve their nutritional and organoleptic quality or for their use for therapeutic purposes in the form of supplements in order to prevent the deleterious actions of reactive species on biological molecules (moure et al. 2001). polycarpon polycarpoides extracts have shown moderate antioxidant activity as studied by free radical scavenging methods (dpph and abts) and by the reduction of iron and copper ions indicating that the various constituents of the extracts can act as free radical scavengers or reducing agents. although various phytoconstituents have an antioxidant effect, phenolic compounds are to date the most powerful natural antioxidant due to their structure bearing hydroxyl groups allowing them to transfer electrons and/or hydrogen (shahidi and ambigaipalan 2015). this fact can explain the high antioxidant effect exhibited by the ethyl acetate, methanol, and methanol: water extracts with the highest phenolic levels in comparison with petroleum ether extract having the lowest contents. indeed, several studies have reported a tight relationship between the phenolic content of different materials (fruits, vegetables, and medicinal plants, and algae) and their antioxidant capacity (abdullah et al. 2013; odabasoglu et al. 2004; ye et al. 2015) besides the antioxidant action, p. polycarpoides showed an interesting effect of inhibiting α-amylase, a key enzyme involved in the degradation of polysaccharides and therefore preventing their absorption. this approach is widely adopted to control postprandial hyperglycemia and prevent the complications characteristic of type 2 diabetes (bourebaba et al. 2016). indeed, herbal extracts have been reported to exert a better effect than the most widely used drugs like acarbose and miglitol and therefore can be used as alternatives. especially, the species belonging to the caryophyllaceae family are known to exert antidiabetic effects through their ability to inhibit carbohydrates hydrolysing enzymes including α-glucosidase and α-amylase (patra et al. 2020; derici et al. 2021).in contrast to the antioxidant effect of p. polycarpoides, the petroleum ether extract with low content of phenolic compounds exhibited the highest inhibitory effect on α-amylase compared to other extracts which suggests that lipophilic molecules can exert a more effective action than hydrophilic molecules. the effect of extraction solvent on decreasing α-amylase activity was also observed in extracts of swertia chirata where the inhibitory effect diminished with increasing solvent polarity to be totally inactive using water (dutta et al. 2012). on another hand, p. polycarpoides was inactive against urease and acetylcholinesterase. urease is involved in the survival mechanisms of helicobacter pylori in the acid environment of the stomach by producing ammonia. the action of plants or drugs on urease may be of therapeutic interest in combating the development of h. pylori 8 nova biotechnol chim (2022) 21(2): e1228 2 since it is believed that most gastric and duodenal ulcers are due to this bacterium (amtul et al. 2012). while acetylcholinesterase is the principal target for alzheimer's disease treatments that aim to increase the concentrations of acetylcholine in the synapsis clefts to replace the lack of the secretion of this neurotransmitter due to the degeneration of neurons and therefore restore the cholinergic transmission directly associated with the cognitive capabilities (gali and bedjou 2019). by referring to literature, only a small number of species belonging to the caryophyllaceae family have been reported for their inhibitory effect on urease. saponaria officinalis l. has been reported to inhibit jack bean urease with an ic50 value of 607.80 µg/ml, which is very low activity compared to standard hydroxyurea (ic50 = 37 µg.ml -1) (mahernia et al. 2015). similarly, the anticholinesterase effect of caryophyllaceae species has been rarely studied. recently, mamadalieva et al. (2019) reported slight activity against acetylcholinesterase and butyrylcholinesterase from a methanolic extract as well as some ecdysteroids isolated from silene viridiflora. since ethyl acetate extract gave significant antioxidant activity and inhibitory effect on α-amylase, one would conclude that ethyl acetate is the best solvent to extract bioactives of therapeutic interest from p. polycarpoides. this solvent exhibited some degree of hydrophobicity to extract low polar molecules with inhibitory effects on α-amylase and was able to extract aglycone phenolic compounds with antioxidant properties. conclusion throughout the paper, some biological effects (antioxidant activity and the inhibition of α-amylase, urease, and acetylcholinesterase) of the endemic plant polycarpon polycarpoides were examined to investigate its possible therapeutic potential or its use as a source of bioactive compounds. following the various results showing the low contents of polyphenols explaining the moderate antioxidant activity of the plant, and no activity against urease and acetylcholinesterase but remarkably active against alpha-amylase, the plant can be valued in the management of type 2 diabetes. however, as this work represents the first study on the biological actions of p. polycarpoides, other biological effects must be studied to take into account the possible presence of compounds that may exert other effects to conclude on the usefulness of the plant as a remedy or as a source of bioactive ingredients. acknowledgements we gratefully thank wissam mazouz (larbi ben mhidi university, oum el bouaghi, algeria) for providing us with the plant material. we also thank the biotechnology research center of constantine (algeria) and the dgrsdt for their contribution to the realization of this work. conflict of interest the authors declare that they have no conflict of interest. references abdullah ar, bakhari na, osman h (2013) study on the relationship of the phenolic, flavonoid 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(2021) phenolic contents and in vitro antioxidant, antityrosinase, and anti-inflammatory effects of leaves and roots extracts of the halophyte limonium delicatulum. s. afr. j. bot. 139: 42-49. bourebaba l, saci s, touguit d, gali l, terkmane s, oukil n, bedjou f (2016) evaluation of antidiabetic effect of total calystegines extracted from hyoscyamus albus. biomed. pharmacother. 82, 337-344. cetin cakmak k, gülçin i̇ (2019) anticholinergic and antioxidant activities of usnic acid-an activity-structure insight. toxicol. rep. 6: 1273-1280. chandra s, rawat ds (2015) medicinal plants of the family caryophyllaceae: a review of ethno-medicinal uses and pharmacological properties. integr. med. res. 4: 123-131. 9 nova biotechnol chim (2022) 21(2): e1228 3 derici ge, özdaş s, canatar i̇, koç m (2021) antidiabetic activities of bolanthus spergulifolius (caryophyllaceae) extracts on insulin-resistant 3t3-l1 adipocytes. plos one 16: e0252707. dolatabadia jen, kashanian s (2010) a review on dna 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phytotherapie 16 (s1): s225-s236. yakoubi r, megateli s, hadj sadok t, gali l (2021) photoprotective, antioxidant, anticholinesterase activities and phenolic contents of different algerian mentha pulegium extracts. biocatal. agric. biotechnol. 34: 102038. yang xw, huang mz, jin ys, sun ln, song y, chen hs (2012) phenolics from bidens bipinnata and their amylase inhibitory properties. fitoterapia 83: 1169–1175 ye f, liang q, li h, zhao g (2015) solvent effects on phenolic content, composition, and antioxidant activity of extracts from florets of sunflower (helianthus annuus l.). ind. crops prod. 76: 574-581. 10 microsoft word brodnjak2 nb 9-2.doc nova biotechnologica 9-2 (2009) 211 chemometrics in analytical chemistry darinka brodnjak vončina faculty of chemistry and chemical engineering, university of maribor, smetanova 17, 2000 maribor, slovenia (darinka.brodnjak@uni-mb.si) abstract: chemometrics is a scientific discipline closely connected with statistics and mathematics. it has an important role in analytical chemistry. modern analytical methods provide opportunity to collect large amounts of data for various samples. for handling analytical results different chemometric methods are employed, such as basic statistical methods for the determination of mean and median values, standard deviations, minimal and maximal values of measured parameters and their mutual correlation coefficients, the principal component analysis (pca), cluster analysis (ca), and linear discriminant analysis (lda). the objectives of chemometrics in analytical chemistry are focused on characterization and chemometrical classification of different samples. the quality of environmental samples such as water, sediment, soil, air samples etc. can be determined according to measured physical and chemical parameters, which represent the individual samples. chemometric methods give information regarding measured parameters about similarity between sampling locations, sources of pollution, seasonal behavior and time trends. monitoring of general pollution of environmental samples and following measuring parameters which are above permitted level given by legislation can be used for searching of pollution source and for planning prevention measures from pollution. food samples can also be characterized by chemometrical methods. chemometrics can be used for fast and efficient determination of food sample categories, such as edible oils, wines, fruits and fruit juices etc. classification can also be performed according to the origin, source or season. from all these facts it is evident that the aim of chemometrics in analytical chemistry is high and extensive. key words: analytical chemistry, chemometrics, principal component analysis, classification, characterization 1. introduction chemometrics is a scientific discipline between measurement oriented chemistry and applied statistics. analytical chemistry is the most significant discipline where chemometrics plays an important role (adams 1990; wilkins 1990). chemometrics uses mathematical and statistical methods to choose optimal procedures and experiments and to provide chemical information by analysing chemical data (willet 1987; nilsson 1965). in many fields of chemistry there is a need for solving practical oriented problems. chemists usually can not measure directly the parameters they want to determine, but they are measuring signals on the instruments which then should be calculated into individual parameters, like concentration of components in samples, or different physical parameters. modern analytical methods provide large amounts of data. in environmental chemistry monitoring of pollutants in waters, soil and air, provides different multidimensional data, which comprise measurements of parameters for the individual sample, named also an object. each sample is revealed by many measurements, named also variables. using multivariate analysis can give us hidden information about quality of environmental samples or about similarity or dissimilarity between different environmental samples (šnuderl et al., 2007; vončina et al., 2007). one use of 212 brodnjak vončina, d. multivariate data in chemistry is discrimination, another is classification. each object is characterised by a set of measurements. it can be presented as a vector in a multidimensional space. multivariate methods can help in visualising different objects. chemometrics includes exploratory data analysis (massart et al., 1997; brereton 1990), experimental design (varmuza 1980; van der waterbeemd 1995; demming et al., 1987) and modelling. chemometrics methods are used to find hidden information present in multivariate data, coming from analytical instruments. it can also be used for instrument control, or for multivariate calibration (adams 1990). there is also possibility to use chemometrics for determining different properties of individual samples in biology, food chemistry, forensic chemistry, geochemistry, archaeology etc. (lankmayr et al., 2004; šnuderl et al., 2005; brodnjakvončina et al., 2005). it has to be stressed that measurements should be of good quality, accurate and reliable, as this is necessary for obtaining high quality information from multivariate data. chemometrics methods are divided mainly into two groups. first group are so called “unsupervised learning methods“ where problems are solved by finding similarities in the data. the second group are “supervised learning methods”, where also quantitative information about known classes of different samples is available. unsupervised learning methods group analytical data using clustering methods, or by projecting high dimensional data onto lower dimensional space, usually onto one plane (fig. 1). supervised learning is a technique for providing a mathematical function from training data. training consists from pairs of input, objects (vectors) and desired outputs (class label). the most used techniques for exploratory data analysis are principal component analysis, cluster analysis (massart et al., 1997; brereton 1990), and kohonen maps (kohonen 1998). training set with known class memberships is used to calculate a classifier. a prediction set, containing objects not used in the training and also with known class memberships, serves to test the performance of the classifier. the most used techniques for classification are linear discriminant analysis, k nearest neighbour classification and artificial neural networks, (hecht-nielsen 1987; kohonen 1998; dayhof 1990; zupan 1989; zupan et al., 1993). the application of supervised learning methods in chemistry is: recognition of compound classes, determination of origin of samples, detection of low/high quality products, etc. multivariate calibration is the multivariate technique, used in chemical laboratories (adams 1990). traditional techniques are multiple linear regression and non linear neural networks. the goal in chemometrics methods is to find a mathematical function of the multivariate data for defining new latent variables, possessing maximum problem relevant information. methods can be grouped in linear and nonlinear methods. 2. cluster analysis (ca) clustering techniques have been applied to a wide variety of research problems, usually for classification or characterisation. cluster analysis belongs to exploratory nova biotechnologica 9-2 (2009) 213 data analysis. it allows grouping of samples on the basis of their similarities or differences. cluster analysis uses all the variance or information contained in original data set. the starting point is a distant matrix containing the distances between all possible pairs of objects. the pairs with the smallest distance are merged and thus number of object is reduced. result is a hierarchical tree, named “dendrogram”. 3. principal component analysis (pca) principal component analysis pca is by far the most important method in multivariate data analysis. it has two main applications: visualisation of the multivariate data and data reduction and transformation. mathematical pre-processing of the variables, features may have a great influence on the result of data interpretation. usually data transformation should be performed for variables, i.e. columns in data matrices. best known are two methods, column centering and column standardisation. column centering data means that the mean value of each column is subtracted from individual elements of all objects. column standardisation or autoscaling is performed in such way, that the mean of the column elements is subtracted from individual elements and divided by the column standard deviation. consequently, each column has zero mean and unit variance. the column standardisation method is used when units of individual variables are incomparable. principal component analysis pca is also the most frequently used concept for defining a latent variable. it tries to represent the multidimensional data structure optimally. direction which best describes the relative distance between the objects is the direction with maximum variance. this direction is called first principal component pc1. the second principal component (pc2) is orthogonal to pc1 and has the second maximum possible variance. pca can transform data from multidimensional space into two dimensions without losing considerable amount of information. pca estimates the correlation structure of the variables and hence the possible structure of latent variables, (principal component influencing data structure). detection of outliers is also possible since they do not belong to a certain class of objects. the projection of the data on the plain of the new latent variables (principal components) is called score of the objects. the scores of the principal component are weighed sum of original variables and weights are called loadings. the scores contain information about objects, and loadings about variables. similar object are placed closely together in the pc1/pc2 plane. in fig. 1 the classification of different vegetable oils according to the content of fatty acids is presented. it is evident that the clusters are formed, corresponding to seven different oil classes. the samples of mixed or unknown oil type labeled with “0” are distributed into seven classes according to their composition of oils.. 4. linear discriminant analysis (lda) linear discriminant analysis belongs to supervised pattern recognition methods (jurs et al., 1975, varmuza 1980, massart et al., 1997, brereton 1990) 214 brodnjak vončina, d. and has the aim to assign object to several predetermined classes. lda uses latent variables (discriminant variables), that maximally separate different classes of objects between each other. using data from training set linear functions named discriminant functions are calculated that can be used to predict a class for samples with unknown class label. fig. 1. 132 oil samples: pumpkin (1), sunflower (2), peanut (3), olive (4), soybean (5), rapeseed (6), corn (7), mixed or unknown type (0) in the pc1-pc2 co-ordinate system. 5. conclusions it is evident that importance of chemometrics methods in analytical chemistry is exceptional. it helps in solving problems and in obtaining hidden information from complex data and in evaluating different analytical results. it can be applied to develop and implement automated methods for classification of different samples in routine control laboratories. it is used for classification and characterisation of different nova biotechnologica 9-2 (2009) 215 samples from environmental chemistry, food chemistry, biology, forensic chemistry, geochemistry, archaeology and many other scientific disciplines. references adams, m.j.: chemometrics in analytical spectroscopy. the royal society of chemistry, cambridge 1990. brereton, r.g.: chemometrics. application of mathematics and statistics to laboratory systems, ellis horword, new york, 1990. brereton, r.g.: multivariate pattern recognition in chemometrics. elsevier, amsterdam 1990. brodnjak-vončina, d., cencič-kodba, z., novič, m.: multivariate data analysis in classification of vegetable oils characterized by the content of fatty acids. chemometr. intell. lab. syst., 75, 2005, 31-43. brodnjak-vončina, d., dobčnik, d., novič, m., zupan, j.: determination of concentrations at hydrolytic potentiometric titrations with models made by artificial neural networks. chemometr. intell. lab. syst., 47, 1999, 79-88. dayhof, j.: neural network architectures, an introduction. van nostrand reinhold, new york, 1990, p.192. demming, s. n., morgan, s.l.: experimental design: a chemometric approach. elsevier, amsterdam, 1987. hecht-nielsen, r.: counterpropagation networks. appl. optics, 26, 1987, 49794984. kohonen, t.: self-organization and associative memory. springer-verlag, berlin, 1988. jurs, p.c., isenhour, t.l.: chemical application to pattern recognition. wiley, new york, 1975. lankmayr, e., mocak, j., šnuderl, k., balla, b., wenzl, t., bandoinene, d., gfrerer, m., wagner, s.: chemometrical classification of pumpkin seed oils using uv-vis, nir and ftir spectra. j. biochem. biophys. methods, 61, 2004, 95-106. massart, d.l., vandeginste, b.g.m., buydens, l.m.c., de jong, s. lewi, p.j., verbeke, j.s.: handbook of chemometrics and qualimetrics: part a. elsevier, amsterdam, 1997. nilsson, n.j.: linear learning machines. mc.graw-hill, newyork, 1965 sharaf, m.a., illman, d. l., kowalski, b.r.: chemometrics. wiley, new york, 1986. šnuderl, k., netriová, j., mocak, j., lehotay, j., brodnjakvončina, d.: chemometric analysis of biochemical laboratory data of oncology patients after morphine treatment. sci. pap. univ. pardubice. ser. a, fac. chem. technol., 11, 2005, 315-330. šnuderl, k., simonič, m., mocak, j., brodnjak-vončina, d.: multivariate data analysis of natural mineral waters. acta chim. slov., 54, 2007, 33-39. teach/me, sdl software development lohninger. teach/me datalab 2.002 © 1999 springer, berlin, developed by h. lohninger and the teach/me people. 216 brodnjak vončina, d. van der waterbeemd, h.: chemometric methods in molecular design. methods and principles in medical chemistry. vch, weinheim, 1995. varmuza, k.: pattern recognition in chemistry. springer, berlin, 1980. vončina, e., brodnjak-vončina, d., sovič, n., novič, m.: chemometric characterisation of the quality of ground waters from different wells in slovenia. acta chim. slov., 54, 2007, 119-125. wilkins c.l, computerenhanced analytical spectroscopy. the royal society of chemistry, cambridge, 1990. zupan, j.: algoritms for chemists. wiley , chichestert, 1989. zupan, j.: gasteiger, j.: neural networks for chemists. vch, weinheim, 1993. willet, p.: similarity and clustering in chemical information. wiley, new york, 1987. microsoft word el baz et al. nb 2010-2-corr.doc 79 ) 2010(2 -10nova biotechnologica callus formation, phenolics content and related antioxidant activities in tissue culture of a medicinal plant colocynth (citrullus colocynthis) farouk k. el-baz, amal a. mohamed, sami i. ali plant biochemistry department, national research centre, dokki, cairo, egypt (amin_amal@yahoo.com) abstract: callus cultures from stems, leaves and roots of colocynth were initiated on ms media supplemented with various combinations of 2,4 dichlorophenoxyacetic acid (2,4-d) with kinetin (kin) and benzyladenine (ba) with α-naphthaleneacetic acid (naa). the highest percentage of callus formation frequency (98.9%) was obtained from stem explants grown on ms media supplemented with (1.0 mg/l) 2,4-d + (1.0 mg/l) kin. the total phenolics and flavonoid content of the colocynth callus cultures were measured. the results showed that the ms medium supplemented with 6.0 mg/l 2,4-d + 2.0 mg/l kin (md3) gave the highest content of total phenolics (19.2 mg/100g d.w.) in leaf-derived calli. the highest content of flavonoids (47.3 mg/100g d.w.) was obtained in stem derived calli grown on the same medium (md3). antioxidant activities of extracts were determined using different assays, including dpph radical scavenging activity, hydrogen peroxide (h2o2) scavenging activity and ferric reducing power. leaf-derived calli cultured on ms medium + 2.0 mg/l 2,4-d + 1.0 mg/l kin (md1) showed the highest dpph radical scavenging activity (85.3%). the highest percentage of h2o2 scavenging activity (61.4%) was detected in leaf explant-derived calli growing on md1. the leaf-derived calli growing on (md3) gave the highest ferric reducing power (22.3 µg/g d.w.), compared to the activities of stems, leaves and roots of in vitro grown seedlings (3.28, 12.9 and 2.85 µg/g d.w.), which were used as controls. on the basis of the current findings, we conclude that ms media supplemented with different combinations of 2,4-d and kin yields higher phenolics, flavonoids contents and antioxidant activities than ms media supplemented with ba and naa. key words: callus culture, phenolics, flavonoids, h2o2 scavenging activity, plant growth regulators 1. introduction plant cell cultures are an attractive alternative source to whole plant for the production of high value secondary metabolites (alfermann and petersen, 1995; dornenburg and knorr, 1997). however, a considerable progress has been made to stimulate production and accumulation of secondary metabolites using plant cell cultures (kalidass et al., 2010; abouzid et al., 2010). several strategies have been adopted for the enhancement of bioactive metabolite production in in vitro cultures; one of them is using growth regulators which are often a crucial factor in secondary product accumulation (duangporn and siripong, 2009). the type and concentration of auxin or cytokinin or the auxin/cytokinin ratio may alter dramatically both the growth and the product formation in cultured plant cells (mantell and smith, 1984). auxin appears to be the primary factor controlling growth and morphology of roots, while the effects of cytokinin vary depending on secondary metabolites and species concerned (roa and ravishankar, 2002). for example kinetin stimulated the production of anthocyanins in haplopappus gracilus but inhibited the formation of anthocyanins in populus cell cultures (seitz and hinderer, 1988). .et al. k.f, baz el80 in recent years, with enhanced awareness of the importance of antioxidant compounds in health and disease, considerable attention has been devoted to medicinal plants with high antioxidant properties (kong et al., 2010; mohamed et al., 2010). colocynth or bitter melon (citrullus colocynthis) is a medicinal plant species of cucurbitaceae family. it grows fast in sandy soils and is widespread in different parts of south eastern desert of egypt (hassanane et al., 2001). a number of secondary metabolites have previously been reported in this plant including cucurbitacins, flavonoids, caffeic acid derivatives and terpenoids in addition to flavonoid glycosides and cucurbitacin glucosides (seger et al., 2005; delazar et al., 2006). moreover, higher content of total cucurbitacins and cucurbitacin-e have been attained in colocynth callus culture as a result of the impact of different combinations of growth regulators (hegazy et al., 2010). colocynth fruit extracts demonstrated activity against some bacteria and fungi prevalent in dermatology, so it can be considered as an effective antimicrobial agent to treat numerous diseases (ziyyat et al., 1997). no information is available about the stimulation effects of plant growth regulators on antioxidant activity of colocynth callus cultures. the aim of this study was to develop conditions for callus cultures of c. colocynthis manipulating the concentrations and combinations of plant growth regulators, and determination of the effect of media composition on total phenolics and flavonoids content together with the related antioxidant activity of induced calli. 2. materials and methods 2.1 plant material mature seeds of c. colocynthis (l.) schrad. were collected from naturally growing plant populations in wadi soule, sinai, egypt. the collected seed material was botanically authenticated by the herbarium of the botany dept., faculty of science, cairo university. dehusked sterilized seeds were in vitro germinated on hormone-free ms medium (murashige and skoog, 1962). 2.2 in vitro culture and growth regulators treatments two weeks old in vitro germinated seedlings of c. colocynthis were used as a source of explants for initiation of callus cultures. stems, leaves and roots were cut into small pieces and cultured on ms medium supplemented with different combinations of 2,4-dichlorophenoxyacetic acid (2,4-d) and kinetin (kin) as well as ba and naa in different concentrations as presented in table 1. the cultures were incubated for callus induction in the growth chamber at 24 ± 2ºc under a fluorescent light (80 µe m-2 s-1) at a 16-h photoperiod for three weeks. after that callus samples were collected for determination of callusing frequency as well as determination of total phenolics, total flavonoid and antioxidant activity by different methods. 2.3 callusing frequency the frequency of callus induction was calculated according to the following formula: callus induction frequency (%) = [no. of seeds produced calli / no. of seeds cultured] x 100. 81 ) 2010(2 -10nova biotechnologica table 1. list of ms media supplemented with different growth regulators used for colocynth callus cultures. no. media codes growth regulators concentration (mg/l) 1 md1 ms + 2.0 2,4-d + 1.0 kin 2 md2 ms + 1.0 2,4-d + 1.0 kin 3 md3 ms + 6.0 2,4-d + 2.0 kin 4 md4 ms + 2.0 2,4-d + 4.0 kin 5 mb1 ms + 0.0 ba + 5.0 naa 6 mb2 ms + 0.01 ba + 1.0 naa 7 mb3 ms + 0.1 ba + 5.0 naa 8 mb4 ms + 1.0 ba + 0.1 naa 2.4 preparation of plant extracts callus cultures derived from stems, leaves and roots as well as in vitro raised seedling materials (used as control) were air dried at room temperature and ground in a mortar. the extracts were prepared using the modified method of matkowski and piotrowska (2006). briefly, 0.5 g of the dried powder from each sample was refluxed with methanol in a water bath at 45°c for 3 h. the extracts were filtered through whatman filter paper no. 4. the collected filtrates were dried under vacuum at 40°c. the extraction was repeated twice. the resulting residue was re-dissolved in methanol and used for the determination of phenolics, flavonoid contents and antioxidant activities. 2.5 determination of total phenolics content the total phenolics content of the extracts was determined using the folinciocalteu reagent (kaur and kapoor, 2002). each extract solution (200 µl) was completed to 3 ml with distilled water then mixed thoroughly with 0.5 ml of folinciocalteu reagent. after mixing for 3 min, 2 ml of 20% (w/v) sodium carbonate was added and allowed to stand for a further 60 min in the dark. the absorbance of the reaction mixtures were measured at 650 nm. the total phenolics content was expressed as mg pyrogallol equivalents / 100 g dry weight (d.w.) of the extract. 2.6 determination of total flavonoid content the total flavonoid content was determined according to the method of kim et al. (2003). in brief, 0.5 ml of sample solution was completed to 1 ml with methanol then mixed with 4 ml of distilled water and subsequently with 0.3 ml of 5% nano2 solution. after 6 min of incubation, 0.3 ml of 10% alcl3 solution was added and then allowed to stand for 5 min, followed by adding 2 ml of 1 m naoh solution to the mixture. immediately after water was added to the sample to bring the final volume to 10 ml and the mixture was thoroughly mixed. the absorbance was determined at 510 nm. the total flavonoid content was expressed as mg rutin equivalents / 100 g d.w. of the extract. .et al. k.f, baz el82 2.7 determination of antioxidant activity 2.7.1 dpph free radical scavenging activity quantitative measurement of radical scavenging properties of colocynth was carried out according to the method of blois (1958). briefly, 0.1 mm solution of 1,1diphenyl-2-picryl-hydrazyl (dpph·) in methanol was prepared and 1 ml of this solution was added to 3 ml of each methanolic extract at one concentration (500 μg/ml). butylated hydroxytoluene (bht) was used as a positive control. discoloration was measured at 517 nm after incubation for 30 min. measurements were taken at least in triplicate. the capacity to scavenge the dpph· radical was calculated using the following equation: dpph· scavenging effect (%) = [adpph − as / adpph] x100 where, adpph is the absorbance of the dpph· solution and as is the absorbance of the solution when the sample extract is added. the extract concentration providing 50% inhibition of radical-scavenging activity (ic50) was calculated and expressed as mg/ml, d.w. 2.7.2 ferric reducing power determination ferric reducing power was determined following the method reported by zhao et al. (2008). extracts at concentration of 500 µg/ml were mixed with phosphate buffer (2.5 ml, 200 mm, ph 6.6) and 1% potassium ferricyanide (2.5 ml). then the mixtures were incubated at 50 °c for 20 min. the quantity 2.5 ml of 10% trichloroacetic acid was added and the mixture was centrifuged at 10000 rpm for 10 min. the upper layer of the solution (5 ml) was mixed with distilled water (5 ml) and 0.1% ferric chloride (1 ml). the absorbance of the reaction mixtures were measured at 700 nm. the final results were expressed as µg ascorbic acid equivalents / g based on dry weight of the extract. 2.7.3 hydrogen peroxide scavenging activity the hydrogen peroxide scavenging ability of methanolic extracts was determined according to the method of shon et al. (2007). a solution of h2o2 (43 mm) was prepared in phosphate buffer (0.1 m, ph 7.4). extracts at concentration 50 μg/ml dissolved in 3.4 ml phosphate buffer were added to a h2o2 solution (600µl). the absorbance of the reaction mixture was recorded at 230 nm. the percentage of h2o2 scavenging of each extract and bht at concentration 50µg/ml used as positive control was calculated as: h2o2 scavenging effect (%) = [acontrol – asample / acontrol] x 100 where acontrol is the absorbance of the control (blank, without extract), and asample is the absorbance in the presence of the sample extract. 83 ) 2010(2 -10nova biotechnologica the extract concentration providing 50% of h2o2 scavenging activity (ic50) was calculated and expressed as µg/ml based on sample dry weight. 2.8 statistical analysis the experiment was conducted using completely randomized design (crd). all tests were conducted in triplicate. data are reported as means ± standard deviation (sd). analysis of variance and significant differences among means were tested by one-way anova using the costat computer package (cohort software, 1989). the least significant difference (lsd) at p ≤ 0.05 level was calculated. correlation coefficients (r2) from regression analysis between total phenolic or total flavonoid contents and antioxidant activities were also calculated. 3. results and discussion calli of colocynth began to appear on stems, leaves and roots grown on ms media supplemented with different concentrations and combinations of growth regulators (2,4-d/kin and ba/naa) within one weak. the results presented in table 2 shows that the stem explants grown on md2 gave the highest frequency of callus formation (98.9 %). generally, among all 2,4-d and kin combination treatments, the medium md2 showed significant superiority in frequencies of callus formation for the three studied explants. these results are in accord with hegazy et al. (2010) who reported that high concentration of kin more than 2,4-d in the ms-media had a positive effects on the callus induction (fresh and dry weight) in both stem and root explants of colocynth. on the other hand, dabauza et al. (1997) found that the highest frequency (81.8 %) of citrullus colocynthis cotyledon explants derived calli was obtained on a medium containing 25 µm 6-benzylaminopurine (6-ba). table 2. callusing frequency of different explants derived from seedlings of colocynth cultured on ms media supplemented with different combinations of growth regulators. callus formation frequency (%, mean ± sd) origin of callus (explants) growth regulators treatments media codes stems leaves roots md1 94.9 ± 1.80e 68.6 ± 1.81b 26.8 ± 1.41a md2 98.9 ± 1.10g 86.4 ± 1.38f 61.1 ± 0.95d md3 83.2 ± 2.17b 70.5 ± 1.78c 44.2 ± 0.96b 2, 4d + k in md4 98.8 ± 1.20g 47.8 ± 0.82a 45.2 ± 1.29c mb1 85.1 ± 1.73c 85.0 ± 1.30e 68.6 ± 1.58e mb2 81.8 ± 1.42a 74.3 ± 1.48d 77.8 ± 1.62f mb3 97.9 ± 1.38f 98.2 ± 1.17h 91.7 ± 1.80g b a + n a a mb4 90.9 ± 1.90d 92.6 ± 1.53g 92.9 ± 1.50h lsd ≤ 0.05 0.699 0.324 0.281 data represents mean of 10 replicates per treatment in three repeated experiments. data with different superscript letters in the same column were significantly different (p ≤ 0.05). .et al. k.f, baz el84 fig. 1 and 2 show the total phenolics content in different colocynth callus cultures. one-way anova analysis showed significant differences (p ≤ 0.05) in total phenolics content among the eight studied media formulations. a wide range of total phenolics content was found in 2,4-d and kin treatments as shown in fig. 1. the high concentration of 2,4-d over kin in md3 media yielded the highest phenolics content (19.2 mg/100g d.w.) in the leaf derived calli. this content was higher than the content of phenolic compounds in stems, leaves and roots organs of seedlings (3.32, 17.1 and 4.49 mg/100g d.w.) which were used as controls. fig. 1. total phenolics content of colocynth callus cultures grown on ms media supplemented with different combinations and concentrations of 2,4-d and kin. data with different superscript letters in the same column were significantly different (p ≤ 0.05). bars on the columns represent the standard deviation. fig. 2 shows the total phenolics content in calli derived on ba and naa containing media. overall, the higher concentration of naa over ba (mb2) gave the maximum amount of total phenolics (7.54 and 6.52 mg/100g d.w.) in the stem and root derived calli respectively. unlike, the lowest value of phenolics content (2.71 mg/100g d.w.) was detected in the leaf-derived calli cultured on medium mb3. the effect of plant growth regulators on biosynthesis of phenolic compounds were studied in hairy roots of panax ginseng by jeong et al. (2007). they found that addition of benzylaminopurine and kinetin to the culture media led to increasing the phenolic compound biosynthesis. in addition, nikolaeva et al. (2009) reported that growing transgenic tea callus tissue (strain ifr chs-2) on nutrient medium containing naa at concentration of 2 × 10–5 m stimulated total soluble phenolics more than total phenolics which presented in intact plants. the total flavonoid content showed significant (p≤ 0.05) differences among the explant types and the different combinations of growth regulators as shown in fig. 3. dealing with 2,4-d and kin media treatments, md3 gave the maximum values of total flavonoid content (47.3 mg/100g d.w.) in the stem derived calli. this content is higher than those contents (11.8, 46.4 and 15.6 mg/100g d.w.) of in vitro raised 85 ) 2010(2 -10nova biotechnologica seedlings stems, leaves and roots respectively, which were used as a control. it is clear that 2,4-d was the favorable enhancer of flavonoids accumulation in colocynth callus cultures. these results are in agreement with matkowski (2004), who reported that medium containing 2,4-d was found to be optimum for isoflavone accumulation in callus cultures of pueraria lobata and psoralea sp. similarly, shinde et al. (2009) confirmed that the content of isoflavones in root and leaf-derived callus cultures of psoralea corylifolia was higher on medium containing 2,4-d and iaa than in intact plant roots and leaves. fig. 2. total phenolics content of colocynth callus cultures grown on ms media supplemented with different combinations of ba and naa. data with different superscript letters in the same column were significantly different (p ≤ 0.05). bars on the columns represent the standard deviation. fig. 3. total flavonoid content of colocynth callus cultures grown on ms media supplemented with different combinations of 2,4-d and kin. data with different superscript letters in the same column were significantly different (p ≤ 0.05). bars on the columns represent the standard deviation. .et al. k.f, baz el86 the effect of ba and naa treatments on stimulation of total flavonoid content is presented in fig. 4. the high concentration of ba over naa (mb4 media) gave the highest flavonoid content (34.0 mg/100g d.w.) in the stem derived calli. however, this content is lower than the flavonoid content (46.4 mg/100g d.w.) detected in the leaves of the in vitro raised seedlings. the present results are in agreement with findings of agarwal and kamal (2007). the authors confirmed that the maximum flavonoid content was observed in 2 weeks old callus culture of momordica charantia cultured on ms medium supplemented with naa (2 mg/l) and bap (0.5 mg/l). fig. 4. total flavonoid content of colocynth callus cultures grown on ms media supplemented with different combinations of ba and naa. data with different superscript letters in the same column were significantly different (p ≤0.05). bars on the columns represent the standard deviation. it is well known that, the concentrations of phenolics content usually higher than the concentrations of flavonoid in most cases, but in this study we found an inverse trend. it can be explained by the fact that differences in the polarity of the extracting solvents could result in a wide variation in polyphenolic contents of the extract. so, the low content of phenolics in our extracts may be possibly due to the fact that extraction with methanol does not release bound phenolics from the callus cells. on the other side, the folin-ciocalteu method is a rapid and widely-used assay, to detect the total phenolic content but it is known that different phenolic compounds have different responses in the folin-ciocalteu method (kähkonen et al., 1999). moreover, different authors found a higher concentrations of flavonoid more than phenolics such as sultana et al. (2009) found a higher concentration of total flavonoids (1.68 g/100g, d.w.) in absolute methanolic extract of moringa oleifera root more than the total phenolics (0.22 g/100g, d.w.). also, the aqueous extract of momordica charantia yielded higher content of total flavonoid (62 mg/g, d.w.) than total phenolics (51.6 mg/g, d.w.) as reported by (wu and ng, 2008). the variation in the total flavonoid production may be attributed to the activation of key enzyme phenylalanine ammonialyase (pal) which is involved in the flavonoid biosynthesis pathway (guo et al., 87 ) 2010(2 -10nova biotechnologica 2007). the knowledge of biosynthetic pathway and mechanisms for stimulation of flavonoids production in callus culture remains unclear. whether phytohormones induce different biosynthetic enzymes responsible for the biosynthesis of flavonoids is yet to be clarified. the antioxidant activities of methanolic extracts of colocynth callus cultures and of the standard antioxidant bht were determined using the dpph method. this method is based on the reduction of alcoholic dpph solution in the presence of a hydrogendonating antioxidant due to the formation of the non-radical form dpph-h by the reaction (gülçin, 2006). the dpph radical scavenging activity of methanolic extracts of colocynth callus cultures at concentration 500 µg/ml is presented in table 3. the leaf-derived calli cultured on md1 showed relatively higher radical scavenging activity (85.3 %) with ic50 value (0.209 mg/ml) as presented in table 4. this activity was higher than the activity of stem, leaf and root organs of seedling which were used as control (51.6, 80.9 and 27.9 %) with ic50 values (0.485, 0.241 and 0.915 mg/ml) respectively. the scavenging activity of bht which was used as positive control showed higher activity (87.5 %) with ic50 value (0.086 mg/ml) than our methanolic extracts of colocynth callus cultures. these results are consistent with those of tadhani et al. (2007) who found a relatively higher dpph radical scavenging activity (56.8%) with ic50 value (0.528 mg/ml) of extract of stevia rebaudiana leafderived callus cultured on ms media supplemented with 2.0 mg/l naa and 0.3 mg/l ba than the activity (33.2 %) with ic50 value (0.904 mg/ml) of intact plant leaves. table 3. dpph radical scavenging activity of colocynth callus cultures grown on ms media supplemented with different combinations of growth regulators. dpph scavenging activity (%, mean ± sd ) origin of callus (explants) growth regulators treatments media codes stems leaves roots md1 15.23 ± 0.046g 85.31 ± 0.685i 38.73 ± 0.158h md2 11.62 ± 0.016c 56.32 ± 0.213f 27.55 ± 0.110d md3 8.45 ± 0.028a 70.89 ± 0.223g 22.80 ± 0.073c 2, 4d + k in md4 10.02 ± 0.016b 23.01 ± 0.084a 28.17 ± 0.081f mb1 14.70 ± 0.770f 44.63 ± 0.276c 32.13 ± 0.097g mb2 13.83 ± 0.012e 46.78 ± 0.014d 19.56 ± 0.035b mb3 12.59 ± 0.013d 41.47 ± 0.066b 25.44 ± 0.047a b a + n a a mb4 16.60 ± 0.073h 49.32 ± 0.110e 59.42 ± 0.204i control 51.60 ± 0.445i 80.90 ± 0.748h 27.91 ± 0.081e lsd≤ 0.05 0.442 0.705 0.299 bht (150µg/ml) 87.50± 0.099 note: media formulations are presented in table 1. each value is expressed as mean ± standard deviation (n =3). data with different superscript letters in the same column were significantly different (p ≤ 0.05). in addition, grzegorczyk et al. (2007) reported that the methanolic extracts (50 µg/ml) of salvia officinalis shoot cultures grown on ms media supplemented with .et al. k.f, baz el88 0.1 mg/l iaa and 0.45 mg/l bap possessed a high dpph radical scavenging activity (81.4 %) comparable to that (72.3 %) of shoots from field collected plants. with respect to these results, it is possible to consider the callus cultures as a potential source of natural antioxidants. although, which constituents of colocynth callus methanolic extracts, show the free radical scavenging action is still unclear. it is possible that the antioxidative properties of colocynth extracts are caused, at least in part, by the presence of polyphenols and flavonoids and other yet to be discovered antioxidant compounds. table 4. ic50 for inhibition of dpph radical formation of colocynth callus cultures grown on ms media supplemented with different combinations of growth regulators ic50 values (mg/ml, d.w.) of dpph scavenging activity origin of callus (explants) growth regulators treatments media codes stems leaves roots md1 1.670 0.209 0.654 md2 2.190 0.449 0.919 md3 2.970 0.354 1.118 2, 4d + k in md4 2.500 1.090 0.898 mb1 1.730 0.569 0.794 mb2 1.860 0.540 1.325 mb3 2.030 0.613 1.000 b a + n a a mb4 1.520 0.511 0.428 control 0.485 0.241 0.915 bht (150µg/ml) 0.086 the presence of reductants such as antioxidant substances in samples causes the reduction of the fe3+ ferricyanide complex to the ferrous form. the transformation of iron (iii) to iron (ii)-reducing activity in the colocynth callus methanolic extracts was expressed as µg ascorbic acid equivalent/g sample based on dry weight. the results showed statistically significant (p≤0.05) differences among the explant types and growth regulator treatments. fig. 5 shows that the highest reducing power activity (22.3 µg/g d.w.) was found in leaf-derived calli cultured on md3 comparing to the activities (3.28, 12.9 and 2.85 µg/g d.w.) of stems, leaves and roots of the in vitro seedlings which were used as controls, respectively. among the ba and naa treatments, fig. 6 indicated that high concentration of naa in the medium (mb1) has notable effect on total reductive activity. it gave the highest activity (7.52 and 6.61 µg/g d.w.) in the callus cultures of stem and leaf explants respectively. however, these activities are lower than those of leaves of in vitro seedlings (12.9 µg/g d.w.). in this concern, parsaeimehr et al. (2010) reported that ephedra strobilacea stem callus cultures grown on ms media supplemented with 1.5 mg/l naa and 1 mg/l kin gave ferric reducing antioxidant power (0.28 mmol quercetin/g). this value was lower than in intact plants (1.61 mmol quercetin /g). 89 ) 2010(2 -10nova biotechnologica fig. 5. ferric reducing power of colocynth callus cultures grown on ms media supplemented with different combinations of 2,4-d and kin. data with different superscript letters in the same column were significantly different (p ≤ 0.05). bars on the columns represent the standard deviation. fig 6. ferric reducing power of colocynth callus cultures grown on ms media supplemented with different combinations of ba and naa. data with different superscript letters in the same column were significantly different (p ≤ 0.05). bars on the columns represent the standard deviation. hydrogen peroxide can cross membranes and may slowly oxidize a number of compounds. thus, removing of hydrogen peroxide as well as superoxide anion is very important for protection of food systems (gülçin et al., 2007). table 5 points out that h2o2 scavenging activity of colocynth callus methanolic extracts at concentration 150 µg/ml differed significantly (p≤0.05) among the different concentrations of .et al. k.f, baz el90 growth regulators. generally, high ratio of 2,4-d over kin in md1 exhibited remarkable scavenging activity on hydrogen peroxide, it gave the highest h2o2 scavenging activity (61.4 %) in leaf-derived calli with ic50 value 40.74 µg/ml as presented in table 6. this activity value was higher than the activity of the in vitro grown seedlings stems, leaves and roots organs (used as controls) which showed h2o2 scavenging activities of 26.2, 27.3 and 26.4 % with ic50 values 95.4, 91.7 and 94.7 µg/ml, respectively. the bht which was used as a positive control gave h2o2 scavenging activity of 90.5 % with ic50 value 27.64 µg/ml, this value was higher than in colocynth callus cultures. moreover, high concentration of ba in mb4 media gave the highest hydrogen peroxide scavenging activity in the root derived calli (51.8 %). table 5. hydrogen peroxide (h2o2) scavenging activity of colocynth callus cultures grown on ms media supplemented with different combinations of growth regulators h2o2 scavenging activity (%, mean ±sd) origin of callus (explants) growth regulators treatments media codes stems leaves roots md1 23.59 ± 0.117b 61.37 ± 0.089g 35.97 ± 0.056h md2 24.26 ± 0.139bc 33.44 ± 0.062d 15.19 ± 0.023a md3 21.36 ± 0.110a 39.22 ± 0.407e 17.47 ± 0.027d 2, 4d + k in md4 39.37 ± 0.121e 24.42 ± 0.048a 18.83 ± 0.051e mb1 25.83 ± 0.094cd 40.38 ± 0.455f 33.03 ± 0.053g mb2 22.32 ± 0.049ab 30.00 ± 0.070c 16.72 ± 0.026b mb3 27.66 ± 0.091d 33.48 ± 0.039d 16.75 ± 0.053c b a + n a a mb4 21.48 ± 0.058ab 38.44 ± 0.062e 51.77 ± 0.079i control 26.21 ± 0.235d 27.27 ± 0.623b 26.39 ± 0.051f lsd≤0.05 1.572 1.088 0.022 bht (50µg/ml) 90.46±0.011 each value is expressed as mean ± standard deviation (n =3). data with different superscript letters in the same column were significantly different (p ≤ 0.05). in this concern, rakotoarison et al. (1997) found that both callus and cell suspension cultures of crataegus monogyna showed high scavenging activities against h2o2. the decomposition of hydrogen peroxide into water may occur according to the presence and character of antioxidant compounds. since antioxidant compounds present in the extract are good electron donors, they may accelerate the conversion of h2o2 into h2o. phenolic and flavonoid compounds have been reported to be responsible for the antioxidant activities of medicinal plants and other botanical materials (mohamed et al., 2010). table 7 shows that the total phenolic compounds gave a positive correlation (r2 = 0.511 and r2 = 0.667) with dpph radical scavenging activity and ferric reducing power respectively. these data could indicate that phenolic compounds in colocynth calli were the major contributors to dpph radical scavenging activity and ferric reducing power. polyphenolic compounds in extracts of colocynth 91 ) 2010(2 -10nova biotechnologica callus cultures might play a role as electron and hydrogen donors. the antiradical activity of flavonoids and phenolics is principally based on the redox properties of their hydroxy groups and the structural relationships between different parts of their chemical structure (burda and oleszek, 2001). in this concern, shinde et al. (2009) indicated that the content of phenolics is partially correlated with dpph radical scavenging (r2 = 0.466) in callus cultures of psoralea corylifolia. table 6. ic50 values of hydrogen peroxide (h2o2) scavenging activity of colocynth callus cultures grown on ms media supplemented with different combinations of growth regulators. ic50 values (µg/ml, d.w.) of h2o2 scavenging activity origin of callus (explants) growth regulators treatments media codes stems leaves roots md1 105.98 40.74 69.5 md2 103.05 74.76 164.58 md3 117.04 63.43 143.1 2, 4d + k in md4 63.50 102.38 132.77 mb1 96.79 61.91 75.69 mb2 112.01 83.33 149.52 mb3 90.38 74.67 149.7 b a + n a a mb4 116.39 65.04 48.29 control 95.38 91.68 94.73 bht (50µg/ml) 27.64 table 7. correlation analysis (r2)* between antioxidant activities and antioxidant content (total phenolics and total flavonoids). antioxidant contents antioxidant activities total phenolics total flavonoids dpph radical scavenging activity 0.511 0.048 h2o2 scavenging activity 0.017 0.026 ferric reducing power 0.667 0.358 * correlation coefficient (r2) however, the poor correlations of h2o2 scavenging activity (r 2 = 0.017) with the total phenolic compounds as well as the poor correlations of dpph radical scavenging activity, h2o2 scavenging activity and ferric reducing power (r 2 = 0.048, r2 = 0.026 and r2 = 0.358) with total flavonoids respectively in this study suggested that flavonoid compounds in colocynth calli might be a weak scavenger of dpph radical and h2o2 and they do not contribute to ferric reducing power. in conclusion, the development of in vitro cell lines with high antioxidant capacities provides a possibility of generating uniform material cultured under conditions independent of environmental factors. the results of the present study concluded that ms media supplemented with 2,4-d and kinetin produced higher contents of total phenolics, total flavonoids and antioxidant activities more than ms .et al. k.f, baz el92 media supplemented with ba and naa in colocynth callus cultures. stimulation of antioxidant activities in c. colocynthis will help to select callus culture type as a source of natural antioxidants and nutraceuticals to enhance health benefits. moreover, more scientific work needs to be done regarding the characterization of effective antioxidant compounds contained in this plant species in order to further verify their antioxidant effects in in vitro conditions. acknowledgments: we are grateful to dr. mahmoud m. saker, professor of plant biotechnology, national research centre, where the practical part of tissue culture was carried out in his lab. we are also grateful to dr. ahmed k. hegazy, professor of plant ecology, faculty of science, cairo university, for his critical reading of the manuscript. references abouzid, s.f., el-bassuony, a.a., nasib, a., khan, s., qureshi, j., choudhary, m.i.: withaferin a production by root cultures of withania coagulans. int. j. appl. res. nat. prod., 3, 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(2017), administering probiotics increases the activity of natural killer (nk) cells in humans. furthermore, probiotics heighten the activity of phagocytes from macrophages and levels of immunoglobulin a (iga) in mice model diarrhea (rocha-ramírez et al. 2017). jatmiko et al. (2017) stated that lactic acid bacteria (lab) from the genus lactobacillus and bifidobacterium also act as probiotics. studies on lab probiotics from fermented products, digestive system, feces, milk, and human breast milk have been widely published. some labs found in human breast milk include b. longum, l. gasseri, l. rhamnosus, l. acidophilus, l. pentosus, l. plantarum, l. reuteri, l. fermentum, l. brevis, l. casei, l. gastricus, and l. salivarius (sinkiewicz and ljunggren 2008; jamyuang et al. 2019; łubiech and twarużek 2020). the isolation of lab from different humans can affect the differences in species obtained and their abilities. in algeria and china, lab isolates, including l. casei, l. paracasei, l. rhamnosus, l. fermentum, and l. plantarum, and, namely, l. plantarum were found in human breast milk. according to jiang et al. (2016), lab isolated from human breast milk is probiotic and contains various health benefits. the lab of human breast milk as a probiotic potential was assessed by following specific criteria and tested to determine low ph and bile salts resistance. furthermore, it was analyzed to determine the antimicrobial properties, hydrophobicity, and aggregation, correlating with the ability to attach to the digestive tract (li et al. 2020). during initial selection, an in vitro assessment of hydrophobicity and auto-aggregation properties was performed to assess lab's capacity to bind the digestive tract. one of the important functions for inhibiting pathogenic bacteria colonization is its ability to co-aggregate with lab. a partial sequence of the 16s rrna gene was used to identify the lab with the best ability as an indigenous probiotic substance. the standard identification method and phylogenetic relationships in a bacteria is 16s rrna gene sequence analysis, consisting of highly converted and hypervariable regions (tilahun et al. 2018). therefore, it can be used to determine phylogenetic relationships and the levels of kinship between microbes. moreover, the 16s rrna gene is constant and does not change for long, though there is a minute mutation rate (johnson et al. 2019). furthermore, its amplification and sequencing processes identify a bacterial isolate to the species level. this study used universal primers to partially amplify lab isolates from human breast milk to a base sequence of 1,500 bp in the v1-v9 regions of the 16s rrna gene. according to bukin et al. (2019) and michel et al. (2016), the v1-v9 regions can differentiate between species. regional sequences v1 and v3 were used to identify lab up to strain level (bin masalam et al. 2018). variations in subjects used to collect human breast milk samples affected the lab skill obtained and the results of species recognition. this study aimed to obtain lab species that can serve as an indigenous probiotic from human breast milk for health benefits. experimental sampling breast milk samples were collected from 20 mothers (aged 27 – 30) breastfeeding babies of 0 – 6 months. participants were recruited from malang regional unit hospital, east java, indonesia, between september-october 2020. the sampling process involved using a sterilized breast pump. however, the initial 10 – 50 ml was discarded, while the subsequent 50 – 100 ml was put into a sterile bottle for utilization. the sample was kept frozen at 4 oc. the lab isolation process was conducted (kaškonienė et al. 2017). this study was approved for ethical clearance from lppt ugm no 00154/08/lppt/ii/2020. the isolation and purification of lab the isolation and purification of lab from human breast milk were effected using the kaškonienė et al. (2017) method. a sample of 10 ml was put into nova biotechnol chim (2022) 21(2): e1053 3 a test tube and diluted to 10-5 by inserting 1 ml spacemen into 99 ml of equates. the inoculum was streaked using de man rogosa and sharpe agar (mrsa) medium alongside1 % calcium carbonate. thereafter, samples were incubated for 48 h at 37 oc with a clear zone around a single bacterial colony, indicating a positive result. the cultures were further purified using the streak plate method and incubated at 37 oc for 48 h on mrsa. notably, the pure cultures were stored on mrsa slants at 4 – 10 oc. analysis of lab resistance to acid ph and bile salts plab resistance test from human breast milk to acidic ph 2.0 and bile salts was carried out by shehata et al. (2016) with the same method used on the de man rogosa and sharpe broth (mrsb), which rejuvenated lab culture for 24 h. a culture of 0.1 ml was inoculated into 10 ml of mrsb media (control) with ph 2.0 by adding 37 % hcl into the medium and incubated at 37 °c for 5 h. a total culture of 0.1 ml was inoculated into 10 ml mrsb (control) and added 0.3% bile salt, then incubated at 37 °c for 5 h. afterward, calculations on the number of colonies on mrsa media using the plate count method were conducted. the resistance of lab isolates to acidic ph bile salts was calculated based on the difference in log units of the number of colonies that grew in control. the smaller the difference grew, the more resistant the lab culture was to acid ph and bile salts. hydrophobicity analysis of lab from human breast milk activities from hydrophobicity analysis of bacteria were determined using the microbial adhesion to solvent (mats) (krausova et al. 2019). the analysis was conducted using solvents with different polarities, namely: xylene, ethyl acetate, and chloroform (all from merck kgaa, darmstadt, germany). adhesion of bacteria cells to xylene solvents describes hydrophobicity, while chloroform and ethyl acetate analyze cell surface properties. bacteria were grown in mrsb at 37 °c for 16 – 18 h. the cells were harvested using the centrifugation method (hermle z 383 k, hermle ag, gosheim, germany) at a speed of 3,500 rpm for 20 min. the precipitates were washed using urea magnesium phosphate buffer (pum) and suspended in the pum buffer until the bacterial cell was collected at 108 cfu.ml-1. afterward, the original value was calculated at 600 nm wavelength (x0) with a total cell suspension of 5 ml in the pum buffer transferred to a new tube. furthermore, 1 ml of solvents like xylene, ethyl acetate, and chloroform were applied and combined with the vortex in a test tube rapidly for a minute and left still for an hour at 37 °c for disillusion. the aqueous was carefully transferred using a sterile pipette alongside a spectrophotometer (uv1800 uv-vis, shimadzu corp., kyoto, japan) to measure its absorbance at 600 nm (x1). absorbance decrease value in the aqueous phase is expressed as adhesion value to the solvent (%) using eq. 1. (1) x0 = initial absorbance value at 600 nm x1 = final absorbance value at 600 nm autoaggregation analysis of lab from human breast milk the autoaggregation analysis of lab was determined using the krausova et al. (2019) method, with the isolates grown on mrsb for 18 h at 37 °c. the cells were then harvested using centrifugation at 3,500 rpm for 20 min. the residue was washed twice with phosphate buffer saline (pbs) and later suspended in pbs up to 108 cfu.ml-1. furthermore, autoaggregation was determined by measuring the initial (0 hours) alongside the final absorbance (5 h) after incubation at room temperature. this process was implemented by putting 0.1 ml of the upper suspension into 3.9 ml of pbs with a spectrophotometer at 600 nm, measuring the absorbance. the autoaggregation percentage is expressed in eq. 2. (2) at = absorbance at time t = 5 a0 = absorbance at time t = 0 nova biotechnol chim (2022) 21(2): e1053 2 coaggregation analysis of lab from human breast milk the coaggregation analysis conducted by krausova et al. (2019) proposed this method. lab isolates were grown on the mrsb and pathogenic bacteria on tsb for 18 h at 37 °c. furthermore, the lab and pathogenic cells were later harvested by centrifugation at 3,500 rpm for 20 min. notably, the residue obtained was washed twice and suspended in pbs up to 108 cfu ml-1. the volume of 2 ml of each suspension was then mixed in a control tube containing 4 ml per bacteria. the coaggregation was determined by measuring the initial (0 h) and the final absorbance (5 h) after room temperature incubation. this measurement was determined by putting 0.1 ml of the upper suspension into 3.9 ml of pbs and measuring the absorbance using a spectrophotometer at 600 nm. the percentage of co-aggregation is expressed in eq. 3. (3) mx = absorbance of lab isolate suspension my = absorbance of pathogenic isolate suspension mx+y = absorbance of the mixture of lab and pathogenic isolate suspensions antimicrobial activity of lab from human breast milk antimicrobial activity was qualitatively analyzed using the proper diffusion method proposed by le et al. (2019). the test microbes used were e. coli atcc 25922, s. aureus atcc 25923, and c. albicans atcc 11778. also, 1 ml of test microbes were piped into a petri dish and poured in a sterilized medium before cooling to about 40 oc. the tryptone soy agar (tsa) is left to solidify for 1 h after cooling, with a diameter of 0.5 cm at room temperature. the 1 ml test isolate was inoculated in the well and incubated at 37 oc for 2 d. after that, the inhibition zone diameter was measured from three different sides. molecular identification direct pcr is the initial stage for 16s rrna gene analysis. 16s rrna gene is a common feature for best acid ph and bile salts, antimicrobial, and autoaggregation. the process of amplifying 16s rrna gene partial sequence from lactic acid bacteria was conducted using direct pcr amplification as proposed by woodman et al. (2008). one lab colony with the potential of an indigenous probiotic was withdrawn from a petri dish to a tube. thereafter, the pcr mix (50 μl) contained 2 μl dna templates (100 ng/μl), 5 μl 10x buffer (mg2+), 4 μl dntp (10 mmol/l), 1.5 μl primer fa-27f (10 pmol/μl), 1.5 μl primer ra-1495r (10 pmol/μl), 0.5 μl taq dna polymerase (5 u/μl) and 35.5 μl tri-distilled water were added. the primers used to amplify lactic acid bacteria were 27f (5’agagtttgatcctggctcag-3’) and 1495r (5’-ctacggctaccttgttacga-3’). afterward, pcr amplification was carried out by denaturation of 94 oc for 5 minutes, to 30 denaturation cycles at 94 oc for 1 min, annealing at 58 oc for 1 min, to 72 oc for 2 min, and the final extension of 72 oc for 10 min and 4 °c for heat preservation (wang et al. 2016). the pcr products were separated on 1 % gel agarose by electrophoresis process in 100 volts for 30 min and visualized using gel documentation (gel doc xr+ system, bio-rad laboratories, inc., hercules, usa). the dna marker benchtop 1kb (promega corp., madison, usa) was used as the molecular weight standard. moreover, dna sequencing was achieved using an automated dna sequencer. the results were analyzed by comparing the dna sequences database from ncbi (http://www.blast.ncbi.nlm.nih.gov) with blast (basic local alignment search tool). mega 5.0 used for phylogenetic tree analysis was achieved using the neighbor-joining (nj) algorithm method with 1,000 bootstrap repetitions based on pdistance. data analysis the quantitative data group was analyzed by spss 16.0 and tested for normality and homogeneity using the shapiro-wilk and levene test. when the 4 http://www.blast.ncbi.nlm.nih.gov/ nova biotechnol chim (2022) 21(2): e1053 3 results are normal and homogenous, the analysis of variance process is carried out by further dmrt test to determine the effect of differences between isolates. results the ability of lab at acidic ph and bile salts a total of eight lab isolates were collected with different macro and microscopic characters and later purified with human breast milk. all isolates were analyzed and proved to function as probiotics, including low ph resistors. the lab analysis with low ph and bile salts indicated that the l19a isolate had better resistance. however, l19e and l19h isolates performed better than l19b, l19c, l19d, l19f, and l19g, as shown in fig. 1. the tolerance for bile acids and salts was characterized by survival in media containing a ph of 2.0 and a bile salt of 0.5 % with a difference below 2 logs. fig. 1. analysis of the resistance of lab isolates to low ph and bile salts; asterisks indicate mean comparisons that differ significantly (p < 0.05). hydrophobicity analysis of lab from human breast milk the hydrophobicity nature affects its autoaggregate and adhesiveness to various surfaces. some isolates indicated a higher affiliation to chloroform than for ethyl acetate, as shown in table 1. l19a had the strongest hydrophobicity properties based on xylene solvent affinity and was significantly unique. the high xylene affinity is indicated by l19e and l19h, and those above 50 % are declared strong hydrophobic. table 1. adhesion (%) of lab isolates from human breast milk with various solvents. bal isolate adhesion [%] xylene eethyl acetate chloroform l19a 71.01 ± 3.17e 77.21 ± 3.54f 52.01 ± 2.20d l19b 28.21 ± 2.50a 10.68 ± 5.47a 16.23 ± 1.33a l19c 37.05 ± 0.67b 17.47 ± 2.13b 13.89 ± 2.22a l19d 38.18 ± 4.80b 22.32 ± 3.81b 18.05 ± 2.82a l19e 66.02 ± 1.85de 65.33 ± 6.06e 45.56 ± 2.50c l19f 38.45 ± 3.70b 32.44 ± 4.40c 19.44 ± 3.80ab l19g 48.13 ± 3.63c 44.52 ± 4.66d 20.69 ± 2.95b l19h 55.09 ± 0.71de 69.41 ± 1.45e 47.26 ± 1.44c note: asterisks indicate mean comparisons that differ significantly (p < 0.05). 5 nova biotechnol chim (2022) 21(2): e1053 2 autoaggregation analysis of lab from human breast milk lab isolates from human breast milk showed autoaggregation of over 10 %. however, six exceeded 40 %, as shown in fig. 2. l19a, l19e, and l19h isolates had better auto-aggregation than others, while l19a performed best. each lab isolate has a unique probiotic auto-aggregation ability determining its colonization and survival in the digestive tract. based on the analyses, l19a, l19e, and l19h isolates have the best values, despite the statistical analysis indicating varying analysis tests. therefore, the three isolates ought to analyze the 16s rrna gene to determine the species' name to be used as a candidate for probiotics. fig. 2. the ability of lactic acid bacteria to adhere to the small intestinal mucosa; different superscripts showed a different mean comparison significantly (p < 0.05). coaggregation analysis of lab from human breast milk this study conducted co-aggregation testing between lab isolates and two pathogenic bacteria with gram-positive and negative characteristics, as shown in table 2. the co-aggregation activity against s. aureus exceeded e. coli because the cell wall arrangement of gram-positive bacteria contains more peptidoglycan and polysaccharides, with less lipid. the co-aggregation results indicated that isolate l19a had the highest ability with the five pathogenic bacteria. in the following table, the auto-aggregation test correlates with antimicrobial activity, where l19a has the strongest antimicrobial properties. notably, the differences in species and strains strongly influence the coaggregation ability. out of eight isolates tests, only three exceeded 30 % co-aggregation values. meanwhile, the results of this study showed that l19a, l19e, and l19h had a co-aggregation value of 31.05 – 38.08 %, while the rest were below 30 %. table 2. coaggregation ability (%) of lab isolates from human breast milk on gram-positive and negative pathogenic bacteria. bal isolate coaggregation [%] e. coli atcc 25922 s. aureus atcc 25923 l19a 19.00 ± 1.02e 38.08 ± 1.17e l19b 2.86 ± 1.29a 11.46 ± 2.11a l19c 7.76 ± 4.26ab 11.70 ± 1.11a l19d 6.06 ± 1.06ab 16.36 ± 0.29b l19e 15.69 ± 2.72c 31.05 ± 0.20d l19f 12.85 ± 1.04c 17.83 ± 0.48b l19g 1.62 ± 1.80a 19.16 ± 1.27c l19h 17.31 ± 2.74cd 31.82 ± 0.61d note: asterisks indicate mean comparisons that differ significantly (p < 0.05). 6 nova biotechnol chim (2022) 21(2): e1053 3 antimicrobial activity of lab from human breast milk the ability of lab to inhibit pathogenic microorganisms was analyzed based on the presence of hindrance of the zone marked. a clear part appeared around the isolated colonies after 48 hours combination, both in the cultures of s. aureus atcc 25923, e. coli atcc 25922, and c. albicans atcc 11778s. this indicated that lab isolated from human breast milk inhibited pathogenic microorganisms. however, the diameter of the inhibition zone formed by lab isolates against s. aureus, e. coli, and c. albicans varied, as shown in fig. 3. quantitative analysis of the inhibition zone of the antimicrobial test of lab isolates against pathogenic microbes showed that l19a, l19e, and l19h had higher values than l19b, l19c, l19d, l19f, and l19g. however, the l19h isolate had the best ability. fig. 3. inhibition zone of lab isolates antimicrobial test against pathogenic microbes; asterisks indicate mean comparisons that differ significantly (p < 0.05). direct pcr product analyzing based on resistance at low ph and bile salts, hydrophobicity, autoaggregation, co-aggregation, and inhibiting pathogenic microorganism’s properties, l19a, l19e, and l19h were the best indigenous probiotic candidates. however, the 16s rrna gene sequence amplified in direct pcr lab products obtained amplicons with a size of ±1,585 bp, as shown in fig. 4. molecular analysis of lab isolates from human breast milk was carried out using partial sequences of the 16s rrna. the partial sequences were suitable for analysis of bacteria down to the species level. fig. 4. the amplicon of partial sequences of 16s rrna bal gene from human breast milk; m – marker. 7 nova biotechnol chim (2022) 21(2): e1053 2 data from sequences of l19a, l19e, and l19h isolates alongside those in the ncbi were analyzed using the blast program, as shown in table 3. therefore, this analysis indicates that the l19a isolate is similar to l. casei nwafu1544, while l19e and l19h are equivalent to l. rhamnosus jcm 8649 and l. paracasei 2281. table 3. blast results from isolates l19a, l19e, and l19h from human breast milk. isolate blast species similarity [%] seq. id. l19a l. casei nwafu1544 99 mg551218.1 l19e l. rhamnosus jcm 8649 99 ab690234.1 l19h l. paracasei 2281 99 mt604755.1 phylogenetic analysis phylogenetic tree reconstruction based on 16s rrna gene sequences indicated that l19a, l19e, and l19h isolates formes two clades that can be separated from the out-group bacillus subtilis (fig. 5). l19a isolate has similarities with l. casei nwafu1544 up to 99 % with a genetic distance of 0.021. also, the l19e isolate has a similarity value with l. rhamnosus jcm 8649 with a genetic distance of 0.00, meaning both are identical. similarly, the l19h isolate has 99 % resemblance with l. paracasei 2281 with a genetic distance of 0.011. the bootstrap value for branching between isolates is 99 %, indicating stability. fig. 5. phylogenetic tree reconstruction of l19a, l19e, and l19h isolates with reference species based on the neighborjoining method, bootstrap 1,000x. discussion the study aimed to investigate whether human breast milk can be the best indigenous probiotics. several supporting methods were considered, including the ability of lab at acidic ph and bile salts resistance, hydrophobic analysis, autoaggregation, coaggregation analysis, antimicrobial, and gene analyses based on 16s rrna. the initial analysis was conducted to determine whether the lab isolates obtained could survive and grow in acid and bile salt conditions. the eight isolates showed positive results following li et al. (2020) and shehata et al. (2016). some of the main requirements for microbes that function as probiotics include the resistance to low ph, ability 8 nova biotechnol chim (2022) 21(2): e1053 3 to grow on bile salts, the capability to colonize and possess antimicrobial activity. tolerance of acidic ph and bile salts is an important characteristic of probiotic bacteria since its a requirement to pass through the digestive tract to reach the colon. lab isolates adapt to low ph due to their ability to balance the internal cell ph, carried out by removing a proton (h+) from the cell through the hydrolysis process of atp (h+-atpase). also, the lab has histidine decarboxylase and arginine deaminase, an important condition for acidic survival (chen et al. 2019). some lactic acid bacteria comprise of enzyme bile salt hydrolase (bsh) to hydrolyze, which changes physicochemical properties to non-toxic. hydrophobicity is a significant supporting characteristic for probiotics. the nature of hydrophobicity determines the ability to adhere and auto-aggregate to various surfaces. according to krausova et al. (2019), the hydrophobic nature of the lab cell surface is demonstrated by its adhesion or affinity to xylene. specifically, the hydrophobic tests help comprehend the surface properties of the bacterial cells critical for adhesion. in an acidic solvent, an affinity for chloroform indicates that the cell surface is an electron donor. aggressiveness and hydrophobicity are among the components responsible for adhesion because the attachment mechanism is complex (li et al. 2020). based on the outcomes, a few isolates have a high affinity for xylene exceeding 50 %. however, it is considered moderate between 20 – 30 %, while below 20 % is indicated as negative (guan et al. 2020). moreover, a few isolates had a poor affinity for xylene, indicating a more hydrophilic surface with cell wall components such as phospholipids and polysaccharides (krausova et al. 2019). the bacterial cell wall component is attached to the host, forming hydrophobic interactions. according to li et al. (2020), hydrophobic properties result from protein on the cell surface and lipoteichoic acid, while polysaccharides produce hydrophilic properties. bacteria are hydrophobic because their cell surface is negatively charged and associated with bacterial adhesion properties, which vary depending on the strain. also, it is influenced by the plant medium, the age of the bacteria, and the bacterial cell's surface structure. the hydrophobicity of probiotics depends on autoaggregation. all lab isolates samples from human breast milk indicated autoaggregation ability, shown by the results exceeding 10 %. according to li et al. (2020), bacteria with autoaggregation ability below 10% are non-autoaggregation, important for probiotics in intestinal epithelial cells attachment. subsequently, the autoaggregation nature of probiotic strains is important for attaching the intestinal epithelial cells (krausova et al. 2019). li et al. (2020) stated that cellular aggregation depends on species and the environment because aggregates stick to the mucosal surface, supporting probiotic bacteria survival in the intestine. aggregates also hinder pathogenic bacteria from sticking to the intestine's surface, hence it is easy to extract from the digestive tract. the cellular aggregation mechanism is a complex interaction between cell surface components and secreted factors, such as protein, glycoprotein, teichoic acid, and lipoteichoic acid on the bacterial cell's surface, affecting the adhesion autoaggregation hydrophobicity (krausova et al. 2019). however, the mechanism of these compounds in influencing adherence, autoaggregation, and hydrophobicity has not been clearly described. according to krausova et al. (2019), the autoaggregation nature of a bacterium is influenced by the cell surface hydrophobicity. the co-aggregation analysis of a probiotic bacterium correlates with its ability to form a barrier capable of preventing the colonization of pathogenic bacteria in the digestive tract (li et al. 2020). therefore, lab that aggregates with the pathogenic bacteria is a beneficial trait as a probiotic (campana et al. 2017). the coaggregation activity against s. aureus was higher than e. coli because the cell wall arrangement of gram-positive bacteria contains peptidoglycan, less lipid, and more polysaccharides. teichoic acid is a water-soluble polymer that serves as positive ion transport, which demonstrating-positive bacterium that makes it easier to penetrate polar peptidoglycan than non-polar ones (septiani et al. 2017). co-aggregation testing is a suitable method to evaluate the interaction between lab and pathogenic bacteria. lab aggregates with pathogens expose antimicrobial compounds directly to pathogenic bacteria (li et al. 2020). therefore, lab controls the surrounding pathogens 9 nova biotechnol chim (2022) 21(2): e1053 2 (gao et al. 2019). to produce antimicrobial compounds, a mechanism for inhibiting the colonialization of pathogens in the digestive tract involves co-aggregation (campana et al. 2017). antimicrobial tests supported the co-aggregation properties of inhibiting pathogenic microbial colonies based on the clear zone diameter formed. according to li et al. (2015), differences in lab antimicrobial activity against several tested microbes are based on differences in the structure of the cell walls of assessed microbes and the ability of concentrations variation of antimicrobial compounds to produce different inhibition zones. this inhibitory activity occurs due to the accumulation of primary metabolites in lactic acid, ethanol, and carbon dioxide. according to kumar et al. (2016), this also occurred due to the presence of secondary metabolites in the form of hydrogen peroxide and bacteriocins. amarantini et al. (2019) added that clear zones around lab isolates are formed due to the activity of bactericidal antimicrobial compounds in the form of organic acids., which affect the cytoplasm of pathogenic microbial cells to become acidic and inhibit the transmembrane potential along with their substrate transport. according to le et al. (2019), the antibacterial activity was determined based on the diameter of the bacterial inhibition zone against pathogenic microorganisms. inhibition zone diameters ranging from 0 mm to 3 mm have weak antibacterial activity. the ones from 3 mm to 6 mm and over 6 mm contain good and strong antibacterial activities. these results are in line with ren et al. (2018), which stated that lab isolates inhibit escherichia coli bacteria with an inhibition zone diameter of 7 – 14.3 mm. species analysis was performed for the top 3 isolates based on previous tests. furthermore, molecular analysis of lab isolates from human breast milk was carried out using partial sequences of the 16s rrna. the partial sequences were suitable for analysis of bacteria down to the species level. this is in line with bukin et al. (2019), which stated that the 16s rrna gene's partial sequences could be used as a universal barcode of lab. isolates with the same 16s rrna gene sequence above 97 % represent similar species (edgar 2018). wullur et al. (2020) stated that isolates are considered the same species when they have a maximum identity of 99 %. the bootstrap value for branching between isolates is 99 %, indicating stability. according to (tilahun et al. 2018), a branching value of 70 – 100 indicates that phylogenetic trees remain unchanged. comparative sequencing analysis of the 16s rrna gene is currently a common pathway for identifying and classifying bacteria. since 1994, there have been strains with more than 97 % similarity of the 16s rrna gene sequence, considered the same species. in 2018, the percentage level boundary for species was evaluated to be 98.65 % (beye et al. 2018). however, in some cases, there were several adjacents in species, including the lactobacillus buchneri group (l. buchneri, l. kefiri, l. parabuchneri, and l. parakefiri), l. casei group (l. casei, l. paracasei, and l. rhamnosus), lactobacillus plantarum group (l. fabifermentans, l. plantarum, l. paraplantarum, and l. pentosus) and lactobacillus sakei group (l. curvatus, l. graminis, and l. sakei). all these groups were indistinguishable using 16s rrna gene sequencing due to a high degree of similarity up to 99 % between species (fontana et al. 2018). lactobacillus casei, paracasei, and rhamnosus have close phylogenetic and phenotypic relationships considered to be in the l. casei group. according to hill et al. (2018), members of this group are facultative heterofermentative, have a g+c dna content of 45 – 47 %, with identical peptidoglycan types (l-lys-dasp). the widely recognized probiotic strains belonging to this group, such as l. casei strain shirota and l. rhamnosus gg are used worldwide in fermented milk products or dietary supplements to improve the host's health (orlando et al. 2016). although this group comprises many strains of commercial value, their taxonomic status is still debatable. also, strains of commercial value as probiotics, the taxonomic status, and nomenclature of the l. casei are still debatable due to the difficulty in identifying these three species using the most frequently used genotypic methodology of 16s rrna gene sequencing (huang et al. 2018). strain l. casei and l. paracasei are widely used as probiotics or symbiotic supplementation to improve clinical outcomes. the results of several clinical trials indicate that l. casei and l. paracasei improve patients' condition from various digestive diseases, chronic infections, obesity, and depressive disorders. oral administration of probiotics 10 nova biotechnol chim (2022) 21(2): e1053 3 shortens the duration of acute diarrheal disease in children by about 1 day. the prevention of acute diarrhea in adults and children, using l. rhamnosus gg and l. casei, has proven effective in several specific doses (lai et al. 2019; li et al. 2019). according to andriani et al. (2020), l. casei and l. rhamnosus probiotics are effective as a substitute for antibiotic growth promoter (agp) against total cholesterol, low-density lipoprotein (ldl), and high-density lipoprotein (hdl). the l. casei group remains in demand as a probiotic and is widely used. in recent years, many studies have focused on its application to health promotion or prevention of several digestiverelated ailments and disorders. lcg could be used prophylactically or therapeutically in diseases associated with the gut microbiota. this group has been researched extensively on the stress response, essential to their survival, therefore applied as a probiotic. lcg from human breast milk is an indigenous probiotic candidate that needs further investigation to determine other abilities, physiology, and metabolite products. conclusion lactic acid bacteria from human breast milk have the ability of an indigenous probiotic. subsequently, isolates l19a, l19e, and l19h had the best ability to withstand acidic ph and bile salts, hydrophobicity, autoaggregation, coaggregation, and inhibit pathogenic microorganisms. the 16s rrna gene analysis showed that the three isolates belonged to the l. casei (lcg) group. l19a isolate was similar to l. casei, l19e was similar to l. rhamnosus, and l19h was similar to l. paracasei. these isolates can be used as indigenous probiotics. conflict of interest the authors declare that they have no conflict of interest. references amarantini c, satwika d, budiarso ty, yunita er, laheba ea (2019) screening of antimicrobial-producing lactic acid bacteria isolated from traditional fish fermentation against pathogenic bacteria. j. phys. conf. ser. 1397: 012045. andriani ad, lokapirnasari wp, karimah b, hidanah s, alarif ma, soeharsono s, harijani n (2020) efektifitas probiotik lactobacillus casei dan lactobacillus rhamnosus sebagai pengganti antibiotic growth promoter terhadap total kolesterol, low density lipoprotein dan high density lipoprotein ayam broiler. 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biodivers. 21: 2735-2740. yeoh yk, zuo t, lui gcy, zhang f, liu q, li ayl, chung ack, cheung cp, tso eyk, fung ksc, chan v, ling l, joynt g, hui dsc, chow km, ng sss, li tcm, ng rwy, yip tcf, ng sc (2021) gut microbiota composition reflects disease severity and dysfunctional immune responses in patients with covid-19. gut 70: 698-706. 12 microsoft word puterova nb 9-2.doc nova biotechnologica 9-2 (2009) 167 applications substituted 2-aminothiophenes in drug design zita puterová1, alžbeta krutošíková2, daniel végh3 1department of chemical theory of drugs, faculty of pharmacy, comenius university, kalinčiakova 8, bratislava, sk-832 3, slovak republic (puterova@fpharm.uniba.sk) 2department of chemistry, university of ss. cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic (alzbeta.krutosikova@ucm.sk) 3institute of organic chemistry, catalysis and petrochemistry, faculty of chemical and food technology, slovak university of technology, radlinského 9,bratislava, sk-812 37, slovak republic (daniel.vegh@stuba.sk) abstract. highly substituted thiophene derivatives are important heterocycles found in numerous biologically active compounds. title compounds are attractive derivatives because their applications in pharmaceuticals, agriculture and pesticides. they exhibit antimicrobial activity against various gram(+) and gram(-) bacteria and fungi. many of these molecules act as allosteric enhancers of a1-adenosine receptor, glucagon antagonists as well as antioxidant and anti-inflammatory agents. key words: substituted 2-aminothiophenes, gewald reaction, thieno[2,3-d][1,3]oxazin-4-ones, allosteric enhancers, 3-deazathiadiamine, drug design 1. introduction the chemistry of 2-aminothiophenes has received much attention upon their convenient availability through the most versatile synthetic method developed by gewald and his co-workers (gewald et al., 1988,). there are four basic variations originally described by gewald and co-workers and about up to fifteen modifications to accomplish the synthesis of highly functionalized 2-aminothiophenes (sabnis et al., 1999; gronowitz and hörnfeldt, 2004). the improvements of the gewald synthesis are based in diminution of the reaction time using microwave technology (huang et al., 2005, hesse et al., 2007). the recent information of synthesis of title compounds is reviewed in our recent chapter (puterová and krutošíková, 2009). this article details about the use of substituted 2aminothiophenes in the synthesis of thienotype heterocycles as a group of precursors applied in pharmaceuticals and in drug design. 2. synthesis of pharmaceuticals and drugs the ultimate positions of substituted 2-aminothiophenes in the field of drug design and synthesis of pharmaceuticals comes from their advantageous properties – the thiophene ring as is bioisosteric replacement for phenyl group broadly present in an active drugs, the thiophene core exists in many natural and synthetic pharmaceuticals. 168 puterová, z. et al. moreover, they act as active precursors in broad range of synthetic pathways towards compounds used in therapy and biodiagnostic (jarvest et al., 1999; doré et al., 2004). 2.1 5-substituted 2-aminothiophenes as a1 adenosine receptor allosteric enhancers adenosine is an important endogenous tissue-protective compound released during ischemia, hypoxia or inflammation. four receptor subtypes (a1, a2a, a2b, a3) have been defined based on pharmacological properties (linden, 1997). considerable effort has been directed towards developing therapeutic agents targeting these receptors (bruns and fergus, 1990). substituted 2-aminothiophenes of structure 1 – 4, with alkyl, aryl and cycloalkyl substituents in c-4 and c-5 position and aroyl substituent in c-3 position (fig. 1), maintained the best allosteric enhancer activity (nikolakopoulos et al., 2006; fergusson et al., 2008). fig. 1. structure of some aminothiophene-based allosteric enhancers. the significant effort in the area of synthetic aminothiophene-based allosteric enhancer is directed to development and synthesis of adenosine receptor agonists with limited side-effects. since the active compounds with potential and utility are substituted 2-aminothiophenes their synthesis in principal based on the gewald reaction. 2.2 synthesis thieno[2,3-d][1,3]oxazin-4-ones as inhibitors of human leukocyte elastase a series of thieno[2,3-d][1,3]oxazin-4-ones 8a – h was synthesized and evaluated in vitro for inhibitory activity toward human leukocyte elastaze (hle). the strategy presented by authors (gütschow and neuman, 1998; gütschow et al., 1999) is base on the replacement of the benzene ring in benzoxazinones by thiophene. the study demonstrates the versatility of 2-aminothiophenes prepared by gewald reaction as a synthetic entry to serine protease-inhibiting, fused 1,3-oxazin-4-ones. the synthetic route to novel thieno[2,3-d][1,3]oxazin-4-ones 8a – h using alkyl 2aminothiophenecarboxylates 5a,b as substrates exhibits a facile three step synthesis, as is presented on scheme 21. aminothiophenes 5a,b were converted to isothiocyanatonova biotechnologica 9-2 (2009) 169 thiophenes 6a,b by the action of thiophosgene. deprotection of tert-butoxycarbonyl group resulted directly to ring closure of the intermediates isothiocyanatothiophenecarboxylic acids 7a,b. these key intermediates were alkylated with appropriate alkyl halides to furnish the final derivatives 8a – h (scheme 1). scheme 1. synthesis of substituted thieno[2,3-d][1,3]oxazin-4-ones 8a–h extracellurar hle is a serine protease contained in the azurophilic granules of human neutrophils and has been shown to contribute to the pathogenesis of destructive lung diseases, such as pulmonary emphysema, cystic fibrosis, adult respiratory distress syndrome and inflammatory disorders such as rheumatoid arthritis. for that reason, much attention is focused on the inhibition of hle by low-molecular-weight inhibitors that might serve as therapeutic agents. 2.3 synthesis of 3-deazathiamine authors (hawskey et al., 2001) outlined the synthesis of 3-deazathiamine (13) in ten chemical steps, through key intermediate substituted 2-aminothiophene 9. on the scheme 2 we have outlined the synthesis of target compound 13 starting from appropriate aminothiophene 9. deamination of aminothiophene 9 via the bromide and following cleavage with zn in acid media to afford derivative 10 was very efficient, displaying none of side reactions. conversion of formed ester 10 to final 3deazathiamine (12) was accomplished in four subsequent steps isolating the crucial intermediates – aldehyde 11 and nitrile 12. the readily available and inexpensive starting materials and reagents, and the lack of protection and de-protection steps make this synthesis very fashionable (scheme 2). deazathiamine diphosphate (deaza-tdp) is an analogue of thiamine diphosphate (tdp), the biologically active for of thiamin (vitamin b1), with a neutral thiophene replacing positively charged thiazolium ring. tdp is co-enzyme present in a number of enzymes, including pyruvate decarboxylase, transketolase, pyruvate oxidase. 170 puterová, z. et al. scheme 2. reaction sequence towards 3-deazathiamine 13. 2.4 other important pharmaceuticals developed from2-aminothiophenes the synthesis and antitumor a potent thieno[2,3-b]azepin-4-one antineoplastic agents was reported (koebel et al., 1975). the meaningful structure-activity relationships have been established in monocarbonyl and dicarbonyl series of thieno[2, 3-b]azepin-4-one 14, 15 (fig. 2) prepared by dieckmann ring closure reaction in multi step reaction from substituted 2-aminothiophenes. cinnamyl derivatives of thieno[2, 3-d]oxazinones 16 (fig. 3) inhibits herpes protease processing in hsv-2 infected cells. the synthesis and pharmacology of this series of derivatives was presented by authors (jarvest et al., 1997 and 1999) from ethyl 2amino-4-methylthiophene-3-carboxylate. fig. 2. structure of potential antineoplastics thieno (2,3-b) azepin-4-ones 14,15 fig. 3. the family of herpes proteases hsv-2 thieno (2,3-d) oxazinones 16 nova biotechnologica 9-2 (2009) 171 transglutaminases (tgases) are a family of ca2+ dependent enzymes which are normally expressed at low levels in many different tissues and serve vital roles, such as blood clothing and epithelia formation. some tgase isoenzymes are involved in diverse pathological conditions like celiac disease, atherosclerosis and neurodegenerative disorders. thieno[2,3-d]pyrimidin-4-hydrazide derivatives related to structure 17 (fig. 4) were discovered as a moderately potent inhibitors of tgase-2 (tissue transglutaminase) (duval et al., 2000). the rna polymerase holoenzyme is a proven target for antibacterial agents. a high-throughput screening program based on this enzyme from staphylococcus aureus had identified a 2-ureido-thiophene-3-carboxylate 18 (fig. 5) as a low micromolar inhibitor. it displayed good antibacterial activity against s. aureus and s. epidermidis. based on these observations the authors (ahrin et al., 2006) reported a facile synthesis of the number of analogs of 18 via the gewald reaction and evaluated for cytotoxic activity against rifampicin-resistant s. aureus. fig. 4. thieno (2,3-d) pyrimidin-4-hydrazide 17 lead structure in inhibition of tgase-2. fig. 5. 2-ureido-thiophene-3-carboxylate 18 antibacterial agent against s. aureus. a novel class of thiophene-derived antagonists of the human hepatic glucagon receptor (hgcrg) has been discovered (duffy et al., 2005). the synthesis of derivatives based on the lead structure 19 (fig. 6) was accomplished using the gewald reaction. the further investigations of such structures are challenging in development of therapeutics of the diabetes mellitus. diabetes mellitus is a condition characterized by chronically elevated levels of blood glucose caused by incorrect function of the hormone responsible for the hgcrg activation. fig. 6. thiophene-based antagonist of hgcrg 19 172 puterová, z. et al. because the structure-based drug design program through substituted 2aminothiophenes has been investigated broadly, up to this date there are many other research works dealing with the synthesis, pharmacology and application of thiophenebased structures in medicinal chemistry (kourounakis et al., 2000). it is no doubt, that this area of gewald-like thiophene derivatives exhibits the highest progress in a scope and utilization. 3. conclusions in this short review the importance of substituted 2-aminothiophenes in the medicinal chemistry was extended in terms of drug design and synthesis of pharmaceuticals. the scope of this work does not include all of the publications in this field, but the most interesting studies in the subject areas are considered. the further detailed information in the latter aspects can be found within the list of the references. acknowledgements: the support of this work by grants vega 1/1005/09, vega 1/4453/07, vega 1/4300/07, vvce 0004-07 and uk/102/2009 is gratefully acknowledged references arhin, f., bélanger, o., ciblat, s., dehbi, m., delorme, d., dietrich, e., dixit, d., lafontaine, y., lehoux, d., liu, j., mckay, g. a., moeck, g., reddy, r., rose, y., srikumar, r., tanaka, k.s.e., williams, d.m., gros, p., pelletier, j., parr, t.r., rafai far, a.: triaminotriazine dna helicase inhibitors with antibacterial activity. bioor. med. chem. lett., 16, 2006, 1286-1290. bruns, r.f., fergus, j.h.: allosteric enhancement of adenosine a1 receptor binding and function by 2-amino-3-benzoylthiophenes. mol. pharmacol., 38, 1990, 939-949. doré, k., dubus, s., ho, h.-a., lévesque, i., brunette, m., corbeil, g., boissinot, m., boivin, g., bergeron, m., boudreau, d., leclerc, m.: fluorescent polymeric transducers for the rapid, simple and specific detection of nucleic acids at the zeptomole level. j. am. chem. soc., 126, 2004, 263-287. duffy, j.l., kirk, b.a., konteatis, z., campbell, e.l., liang, r., brady, e. j., candelore, m.r., ding, v.d.h., jiang, g., liu, f., qureshi, s.a., saperstein, r., szalkowski, d., tong, s., tota, l.m. xie, d., yang, x., zafian, p., zheng, s., chapman, k.t., zhang, b.b., tata, j.r.: discovery and investigation of a novel class of thiophene-derived antagonists of the human glucagon receptor. bioor. med. chem. lett., 15, 2005, 1401-1405. duval, e., case, a., stein, r., cuny, g.d.: structure-activity relationship study of novel tissue transglutaminaze inhibitors. bioor. med. chem. lett., 15, 2005, 1885-1889. fergusson, g.n., valant, c., horne, j., figler, m., flynn, b.l., linden, j., chalmers, d.k., sexton, p.m., christopoulos, a., nova biotechnologica 9-2 (2009) 173 scammells, p.: 2-aminothienopyridazines as novel adenosine a1 receptor allosteric modulators and antagonists. j. med. chem., 51, 2008, 6165-6172. hawskey, d., griffin, d.a., leeper, f.j.: synthesis of 3-deazathiamine. j. chem. soc. perkin trans., 1, 2001, 144-148. hesse, s., perspicace, e., kirsch, g.: microwave 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(eds.), elsevier academic press, kidlington, oxford, uk, 2004, 1-986. gütschow, m., kuerschner, l., neumann, u., pietsch, m., löser, r., koglin, n., eger, k.: 2-(diethylamino)thieno[1,3]oxazin-4-ones as stable inhibitors of human leukocyte elastaze. j. med. chem., 42, 1999, 5437-5447. gütschow, m., neumann, u.: novel thieno[2,3-d][1,3]oxazin-4-ones as inhibitors of human leukocyte elastaze. j. med. chem., 41, 1998, 1729-1740. jarvest, r.l., connor, s.c., gorniak, j.g., jennings, l.j., serafinovska, h.t., west, a.: potent selective thienoxazinone inhibitors of herpes proteases. bioor. med. chem. lett., 7, 1997, 1733-1738. jarvest, r.l., pinto, i.l., ashman, s.m., dabrowski, c.e., fernandez, a.v., jennings, l.j., lavery, p., taw, d.g.: inhibition of herpes proteases and antiviral activity of 2-substituted thieno[2,3-d]oxazinones. bioor. med. chem. lett., 9, 1999, 443448. koebel, r.f., needham, l.l., de witt blanton, c.: synthesis of thieno[2,3b]azepines-4-ones. j. med. chem.,18, 1975, 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doi: 10.36547/nbc.1258 1 nova biotechnologica et chimica municipal sewage sludge as a source of microelements in sustainable plant production: a laboratory lysimeter study vanda adamcová 1 , martin valica 1 , jozef gubiš 2 , marcela gubišová 2 , katarína ondreičková 2 , miroslav horník 1, , silvia dulanská 3,4 1 department of ecochemistry and radioecology, faculty of natural sciences, university of ss. cyril and methodius in trnava nám. j. herdu 2, trnava 91701, slovak republic 2 plant production research institute, national agricultural and food centre, bratislavská cesta 122, piešťany 92168, slovak republic 3 institute of medical physics, biophysics, informatics and telemedicine, faculty of medicine, comenius university, sasinkova 2, bratislava 81372, slovak republic 4 faculty of public health, slovak medical university, limbová 12, bratislava 83303, slovak republic  corresponding author: miroslav.hornik@ucm.sk article info article history: received: 5 th november 2021 accepted: 18 th december 2021 keywords: agriculturally used soils heavy metals lysimeters nicotiana tabacum plant growth sewage sludge application abstract the aim of the work was to characterize the samples of sewage sludge (ssl) originated from the wastewater treatment plant piešťany (tavos, a.s., trnava, slovakia) in terms of their potential application into the soils. within the physicochemical characterization of ssl, the samples were analysed in terms of the values of ph, cation exchange capacity (cec), total organic carbon (toc), water holding capacity (whc), as well as the presence of heavy metals. it was found that ssl contained significant amounts of microelements zn (1,269 mg.kg -1 , d.w.) and cu (224 mg.kg -1 , d.w.). laboratory lysimeter experiments involving the application of ssl into the top layer of agriculturally used soil (0 – 10 cm) forming a soil column, in which seedlings of tobacco (nicotiana tabacum l.) were cultivated, showed that in the case of ssl application in the highest permitted amounts (15 t.ha -1 ) only 0.11 % zn and 0.07 % cu were released into the soil eluate during a 28 day of exposure, while in tobacco plants 0.13 % zn and 0.05 % cu were accumulated from the total amount of zn and cu originated from the application of ssl (zn – 133 mg and cu – 23.5 mg). when applying ssl in amount 30 t.ha -1 i.e., in the dose exceeding the permitted limits, only 0.02 % zn and 0.04 % cu were released into the soil eluate and 0.16 % zn and 0.09 % cu were accumulated in tobacco plants from the applied amount of ssl (zn – 267 mg and cu – 47.0 mg).  university of ss. cyril and methodius in trnava introduction sewage sludge (ssl) represent large-volume wastes annually produced in the whole world. the current global ssl rate is about 45 million dry tons of sludge per year. approx. 6 million tonnes of dry ssl were produced in china in 2013, while approx. 14 million tons of dry ssl per year were released during wastewater treatment in the united states (seiple et al. 2017; teoh and li 2020). currently, it is estimated that at least 10 million tons of dry ssl will be produced within the european union annually (wang et al. 2019). the composition of ssl is dependent on its origin in mailto:miroslav.hornik@ucm.sk nova biotechnol chim (2021) 20(2): e1258 2 terms of the type of wastewater treatment, and therefore is variable and unpredictable as well. in this way the public concern and definition of regulations or directives are primarily associated with toxic metals, organic xenobiotics or pathogens occurrence in this type of wastes (zhang et al. 2017). all these factors play an important role in decision with regard to the ultimate ssl disposal, which can involve: composting, landfilling, agricultural application, as well as sea or surface waters disposal and incineration (donatello and cheeseman 2013). in the slovak republic, ssl production represents more than 50,000 tons/year and ssl is predominantly used for compost production (62.7 %), reclamation (16.4 %), landfilling (13.5 %), incineration (5.5 %) and direct application into the soil (1.9 %) (according to data of mžp sr, 2012). ssl have increasingly been used in the last decades on farmland, mostly for their potentially appropriate fertilizing properties, due to its high content of organic matter as well as of macroand micronutrients of plant nutrition (usman et al. 2012). the application of ssl into the agriculturally used soils partially solves the problem of ssl disposal but on the other hand, may pose risks related to the contamination of soil and groundwater by inorganic contaminants (especially metals), organic xenobiotics (especially pharmaceuticals or chlorinated compounds) or microbial pathogens (coliform and faecal coliform bacteria) (santoro et al. 2017). in particular, toxic metals (cd, as, pb, hg) entering into agriculturally used soils through the application of ssl may contaminate the food chain through plants and the surface or ground water. however, high amounts of heavy metals belonging to microelements (zn, cu, mn) in ssl may also represent risks associated with the contamination of soils and ground water. in the eu, the application of ssl in agriculture is regulated by the eu council directive 86/278/eec. also, this directive determines the limit values for the content of heavy metals in ssl in this way. in slovak republic, the handling of ssl as a large-volume waste produced is regulated by the act no. 79/2015. in terms of the application of ssl into the soils, these activities are regulated by the act no. 188/2003. this act also determines the characteristics of the soil which must be evaluated, especially in terms of soil ph. the mentioned act no. 188/2003 indicates the value of the amount of ssl that can be applied into the soil, whereby the permitted amount of ssl applied shall not exceed 15 tons of dry matter per 1 ha over a period of five years. in many studies, the application of ssl in agriculture is studied and evaluated mainly from the point of view of ssl utilization as a source of important macroand microelements for plant nutrition, plant production, risks of pathogens transfer present in the ssl, and translocation of toxic elements or xenobiotics to the soils and plants (bettiol and ghini 2011; marguí et al. 2016; mossa et al. 2017; borba et al. 2018). the availability and mobility of macroand microelements or toxic metals in the systems ssl/soil have been examined in short-term laboratory studies using both leaching columns and incubation (toribio and romanyà 2006), lysimeters (borba et al. 2018), and under conditions of experimental fields (wolejko et al. 2013). lysimeter devices currently represent important tools for studying and predicting the behaviour of a wide range of substances in terms of their movement and overall balance within the soil biosystems defined by soil – soil solution – plant, as well as in the solution of various issues in agriculture, forestry, pedology or hydrology. lysimeter systems also offer the possibility to assess and analyse the impacts of climate change, the hydrodynamic changes associated with the construction of water structures or other large structures, the transport of a wide range of pesticides, xenobiotics, toxic metals, and radionuclides into the food chain or subsurface water, as well as in the analysis of microbial activity, whether from the point of view of agricultural production or microbial degradation of organic substances present in the soil. lysimeters also allow to analyse the impacts of the use of fertilizers and various chemicals on soil, groundwater and plant physiological status. in this way, it is possible to optimize the doses not only of the substances mentioned in such a way that they bring maximum benefit to the soil, but also the irrigation can be optimized for the given location. the latest lysimeter systems allow evaluate movement of water in large monolithic soil nova biotechnol chim (2021) 20(2): e1258 3 columns with a diameter of 1 m and a height of 1.5 m with high accuracy at a level of ± 20 g (meissner et al. 2014). in previous papers, samples of municipal ssl were characterized as a potential soil additive (šuňovská et al. 2013) or metals sorbent (frišták et al. 2013) and evaluated from the point of view of responses of rhizosphere bacterial (ondreičková et al. 2019a) or fungal (ondreičková et al. 2019b; 2021) communities to the sewage sludge application into soil as well. the aim of this work was to characterize samples of ssl originated from the wastewater treatment plant of company tavos, a.s. (municipal wastewater treatment plant, piešťany, slovak republic) in terms of their potential application into the soils using a laboratory lysimeter system. in the first part of the work, a physico-chemical characterization of obtained ssl samples as well as samples of reference soil – an agriculturally used soil (aus) was carried out. subsequent laboratory lysimeter experiments were focused on the total balance of the movement of metals – microelements zn and cu occurring in significant amounts in the obtained samples of ssl within the soil biosystem defined by ssl/aus – soil solution – root system and aboveground parts of tobacco (nicotiana tabacum l.) plants as a model of fast-growing crops. experimental sewage sludge and soil samples the sewage sludge (ssl) was sampled from the wastewater treatment plant of company tavos, a.s. (municipal wastewater treatment plant piešťany, slovakia). obtained samples of ssl represented activated sludge treated into the form of solid particles using a mechanical drainage system. in the experiments, ssl dried under laboratory conditions, mechanically homogenized and sieved to achieve a particle size < 0.150 mm was used. a reference soil – an agriculturally used soil (aus) was obtained from experimental fields of plant production research institute (location borovce, slovakia, 4834n, 1744e, altitude 160 m). the individual soil samples were taken gradually in layers with the aim to keep the natural soil stratification: 1. layer 0 – 10 cm; 2. layer 10 – 20 cm; 3. layer 20 – 30 cm, and 4. layer 30 – 40 cm. plant seedlings as a model for fast-growing plants, tobacco (nicotiana tabacum l.) seedlings were chosen. tobacco plants were obtained by germination of seeds and cultivation under hydroponic conditions in the inorganic carrier perlite watered by a nutrient solution according to hoagland (1920) diluted with deionized water in the volume ratio of 1 : 3 (25 % concentration strength). plant cultivation was carried out in a plant growth chamber kbwf 720 (binder, germany) under the following conditions: photoperiod 16 h light/8 h dark (max. photosynthetic photon flux density ppfd = 200 μmol.m 2 .s -1 with gradual reaching of maximum and minimum in the steps of 0 %, 40 %, 60 %, and 100 % light intensity), temperature 28/18 ºc and relative humidity 60 – 80 %. for experimental purposes, uniform plants with slight variations in the growth phase, height (10 – 12 cm), mass (wet material, 2 – 4 g), number of leaves (5 – 6 leaves) after four weeks of cultivation were obtained. characterization of studied matrices the determination of ph or cation-exchange capacity (cec) of ssl and aus were realized according to iso standard method no. 10390 or no. 11260, respectively. the value of ph was measured in the suspension of solutions 0.01 mol.dm -3 cacl2, 1 mol.dm -3 kcl, or deionized water in the volume ratio 1 : 5 (sample : solution) after 1 h of sedimentation. cec determination was carried out using bacl2 solutions. water holding capacity (whc) of individual samples of ssl and aus or mixture ssl : aus in different weight ratio: 1 : 76, 1 : 38, 1 : 19, and 1 : 9 were evaluated using glass columns with an inner diameter of 2.5 cm and length of 30 cm. the elemental analysis of mechanically homogenized ssl (particle size of < 0.063 mm) was performed by xray fluorescence spectrometry using the highperformance x-ray fluorescence spectrometer xlab 2000 (spectro, germany). total organic carbon (toc) was determined using toc analyzer (toc-vcpn, shimadzu, japan). nova biotechnol chim (2021) 20(2): e1258 2 the determination of bioavailable amount of zn and cu in studied samples of ssl and individual layers of aus was realized by one-step extractions using solutions according to mehlich (1984) – mehlich ii (in mol.dm -3 : nh4cl – 0.2; ch3cooh – 0.2; nh4f – 0.015; hcl – 0.12) and mehlich iii (in mol.dm -3 : edta – 0.001; hno3 – 0.001; nh4f – 0.015; nh4no3 – 0.25; ch3cooh – 0.2). the suspension of ssl or aus in mehlich ii or mehlich iii solution (10 g in 100 cm 3 of solution) was incubated for 10 min under agitation (250 rpm) at 25 °c. after exposure, the mixture was filtered through a filter paper and then through a syringe filter (13 mm diameter; 0.45 µm permeability; chs filterpure ptfe hydrophobic) and the content of zn and cu obtained in the filtrate was determined by atomic absorption spectrometry. laboratory lysimeter experiments the laboratory lysimeter system (ecotech, germany) was self-designed and used to perform the lysimeter experiments. this system consisted of two parts (fig. 1a), a vessel to create a soil column (diameter 30 cm and height 40 cm) and a cultivation part for growing plants in a soil column supplemented by a watering head. in this system, it is possible to install the soil monolith or create a soil column with a dry weight of 30 to 40 kg. the lysimeter contains on each side of the lysimetric vessel 3 inputs for sensors recording soil moisture tension, humidity, or temperature. bottom probe input is located at the interface of the lowest fourth and third layer of the soil, the middle probe input at the interface of the third and second layer of the soil, and the upper probe input at the interface of the second and top layer of the soil. data from individual tensiometers and temperature sensors are analysed and collected by a datalogger (fig. 1b), from which they can be wirelessly transferred to a computer. before, during and at the end of the experiment, the whole lysimetric system can be weighed using a weighing device with the aim to evaluate the total water balance (fig. 1c). the lysimeter system also includes apparatus for watering the soil column via a peristaltic pump and watering head, as well as apparatus for suction of soil eluate by a vacuum pump and through the drainage system at the bottom of the lysimeter vessel (fig. 1d). within the preparation of the lysimeter experiment, 8 kg of the soil was transferred from each obtained layer of aus (1. layer 0 – 10 cm; 2. layer 10 – 20 cm; 3. layer 20 – 30 cm, and 4. layer 30 – 40 cm) into the lysimeter vessel (dry weight, particle size < 2 mm, humidity < 5 %). the individual soil layers were inserted into the lysimeter sequentially in the order in which they occurred naturally at the sampling site, thus respecting their natural vertical distribution. in the first lysimeter experiment a, a homogeneous mixture of ssl : aus in the weight ratio 1 : 76 (105 g of the studied ssl) was added to the top (first) layer of the prepared soil column. in the second experiment b, a mixture of ssl : aus with double amount of ssl (210 g of ssl; ssl : aus = 1 : 38) was applied. the first addition of ssl represents the amount of 15 tons of ssl per hectare, which corresponds with the limits permitted by act no. 188/2003. in the case of the second lysimeter experiment, this amount was increased to 30 t.ha -1 thus exceeding the permitted limit value of 15 t.ha -1 . fig. 1. the design of the laboratory lysimeter system used in experiments. due to the fact that dry soil samples were placed into the lysimeter vessel, prior to planting fast4 nova biotechnol chim (2021) 20(2): e1258 3 growing tobacco (n. tabacum l.) plants, it was necessary to water the soil column using 3.5 dm 3 of artificial rainwater prepared according to the authors do lago et al. (2013). after equilibration (24 h) in terms of soil moisture tension distribution analysed by installed tensiometers, the soil eluate was drained from the drainage bottom of the lysimeter vessel before planting the plants of tobacco. subsequently, 3 seedlings of tobacco plants were planted into the topsoil layer of the soil column and the whole lysimeter system was placed in the growth chamber, where plants were cultivated under the following conditions: photoperiod 16 h light/8 h dark (max. photosynthetic photon flux density ppfd = 200 μmol.m -2 .s with gradual reaching of maximum and minimum in the steps of 0 %, 40 %, 60 %, and 100 % light intensity), temperature 28/18 ºc and relative humidity 60 – 80 %. during the experiments, the soil column was subjected to watering by a watering head with the application of 1.5 – 2.0 dm 3 of artificial rainwater at precisely defined intervals. after each watering and equilibrium reaching (after 24 h), the soil eluate was drained from the drainage bottom of the lysimeter vessel by a vacuum pump. the total water balance in the lysimeter system was also evaluated during the experiment by weighing the whole system. a continuous analysis (every 5 min) of soil moisture tension and temperature, as well as air humidity and temperature was carried out using installed probes. data was collected and stored by a datalogger. atomic absorption spectrometry the presence of zn and cu as microelements in the samples of soil layers, soil eluates, or individual parts of tobacco plants at the end of the lysimeter experiments and the bioavailability of zn and cu in aus and/or ssl samples were determined by atomic absorption spectrometry (aas) using atomic absorption spectrometer ice 3000 (thermo scientific, usa). in the case of soil and plant biomass, before the analysis the samples were mineralized in concentrated hno3 at 210 °c and 20 bars using a microwave mineralization system multiwave 3000 (anton paar, austria). based on the estimated amount of studied metals in the given samples, the determination was carried out either by flame atomization (acetylene/air; ppm amounts) or by electrothermal atomization (argon as an inert gas; ppb amounts). in the measurement of absorbance of samples, hollow cathode lamps (heraeus, germany) as radiation sources were used. deuterium background compensation was applied for correction of background effect. results and discussion characterization of studied matrices from the comparison of the values of physicochemical parameters ph, cation-exchange capacity (cec) and total organic carbon (toc) (table 1) it is clear that the samples of sewage sludge (ssl) and samples of agriculturally used soil (aus) differed significantly in these evaluated parameters. in the case of samples of individual soil layers, such significant differences in the mentioned values were not found. soil samples showed ph values within the range from 7.29 to 7.87, while for ssl ph values from 6.04 to 6.11 were determined. the slightly acidic character of the studied ssl samples after their application to soils similar to the soil studied in terms of their ph reaction may have a positive effect on reducing the ph values of typical alkaline soils to values ph of neutral soils. a similar observation was confirmed by žaltauskaitė et al. (2022). however, the reduction in ph is variable depending on the type of soil, sludge dosage, and characteristics, incubation time etc. (dhanker et al. 2021). it is generally known that soil ph value plays an important role in the mobility and bioavailability of some elements, e.g. significant microelements in the soil (see e.g. hechmi et al. 2021). at alkaline and neutral ph, metals tend to form insoluble minerals, whereas at acidic ph, metals are in more soluble and bioavailable forms (alloway 2012). for typical microelements (zn, mn, cu), their mobility and bioavailability for plant uptake in the soil increased with decreasing of ph value (below ph 7.0) of the soil. from the point of view of agricultural production, it can have a positive effect. on the other hand, from an ecotoxicological point of view, it can be evaluated rather negatively due to: (i) risk of heavy metals entering the groundwaters and 5 nova biotechnol chim (2021) 20(2): e1258 2 food chain, and (ii) risk of increased heavy (toxic) metals uptake by plants and their transport into the food chain. in the case of cec values, the studied ssl showed a 1.5-fold higher cec value and in the case of toc values up to 40-fold higher value in comparison with aus samples (cec = 15.1 – 16.8 meq/100 g and toc = 0.21 – 0.76 %) (table 1). for individual samples of vertical soil layers, the cec and toc values decreased slightly from the topsoil layer (0 – 10 cm) to the lowest soil layer (30 – 40 cm). from the literature it is evident that soils showing cec values in the range of 11 – 50 meq/100 g can be characterized as soils with low sand content, high clay content, medium or high organic matter content, and high whc. soils showing low cec values in the range of 0 – 10 meq/100 g are negative in this respect (daniels and haering 2006). based on this, it can be assumed that the addition of the studied ssl to soils can have a positive effect in terms of increasing the cec and toc values of soils, as well as improving the characteristics of the soils important, especially from the point of view of agricultural production. table 1. the values of ph (phh2o, phcacl2, and phkcl), cation exchange capacity (cec) and total organic carbon (toc) determined for ssl and individual layers of aus. sample phh2o phcacl2 phkcl cec [meq/100 g] toc [%] ssl 6.11 6.04 6.04 24.6 27.7 aus1 0 – 10 cm 7.87 7.29 7.42 16.6 0.76 aus2 10 – 20 cm 7.84 7.34 7.53 16.8 0.53 aus3 20 – 30 cm 7.80 7.41 7.47 15.7 0.32 aus4 30 – 40 cm 7.87 7.40 7.51 15.1 0.21 according to performed analyses determining the values of water holding capacity (whc), it was found that ssl samples had more than 4-times higher whc compared to aus samples (whc in the range of 44 to 48 g h2o/100 g, d.w.) (fig. 2). fig. 2. water holding capacity (whc) obtained for studied matrices – sewage sludge (ssl) and individual layers of agriculturally used soil (aus) (aus1: topsoil layer 0 – 10 cm; aus2: 10 – 20 cm; aus3: 20 – 30 cm; aus4: 30 – 40 cm) or for mixtures ssl : aus prepared in different weight ratio. individual experiments also showed that the addition of ssl to soil had a positive effect in terms of gradual increase in whc values, when with increasing ssl : aus weight ratio whc values increased from 73 g h2o/100 g (d.w.) found for ssl : aus = 1 : 76 to the value of 97 g h2o/100 g (d.w.) found for ssl : aus = 1: 9. boudjabi and chenchouni (2021) found that the application of ssl at the soil surface significantly increased soil moisture (25.95 %) compared to ssl mixed treatment, which was 24.46 % and the controls. elemental analysis of ssl samples carried out by x-ray fluorescence spectrometry confirmed that these samples did not exceed the limits for heavy metals concentrations permitted by act no. 188/2003 in terms of their direct application to soil (table 2). however, an interesting finding was that the samples of ssl contained significant amounts of heavy metals – microelements zn (1,269 mg.kg -1 , d.w.) and cu (224 mg.kg -1 , d.w.). table 2. metal concentrations in the studied sewage sludge. total concentration of metal [mg.kg -1 ; d.w.]; (loq) as cd cr cu fe mn ni pb se zn 3 (1) < 5 (1) 36 (5) 224 (5) 2.69 (0.05) 0.21* (0.05) 22 (4) 46 (5) 6 (1) 1,269 (5) * determined in %. 6 nova biotechnol chim (2021) 20(2): e1258 3 it is generally known that higher total amounts of important elements in a given substrate (soil) may not automatically mean a more favourable environment for plant growth. in addition to the total amounts of elements, their chemical form in which they occur in the given environment (free ionic forms, inorganic or organic complexes, and others) and the portion of their bioavailable amounts also play an important role. this results in the fact that the plant is not able to absorb the total amount of the element present in the given environment, but only its bioavailable part. the literature shows that the bioavailability of many heavy metals is strongly dependent on several factors, such as ph, organic matter content, clay content and other components (kabata-pendias 2011). following the above mentioned results regarding the total zn and cu content in the studied matrices, analyses with the aim to evaluate the bioavailability of these metals were carried out. for this purpose, one-step extraction procedures using mehlich ii and mehlich iii solutions were used. the choice of both extraction procedures was made in order to compare the obtained results, despite the fact that the mehlich ii solution is recommended for determination of the extractability of macroelements, e.g. mg, k, ca, and p. one-step extractions using mehlich iii solution showed that the percentage of the extractable zn to the total amount of zn occurring before extraction in the ssl sample was slightly higher compared to the aus samples and reached the value 8.7 % (fig. 3). fig. 3. extractability of zn (a) and cu (b) from the samples of ssl and individual layers of aus determined using mehlich ii and mehlich iii extractions. extractability of metals expressed as the amount of metal released form 1 kg of the given matri x (in mg/kg), the percentages represent the ratio of the extractable amount of metal to the total amount of the metal present before extraction in the matrix (see table 3). error bars represent the standard deviations of the mean (± sd; n = 3). table 3. total concentration of zn and cu in the studied matrices. total concentration of metal [mg.kg -1 ; d.w.] sample ssl aus1 aus2 aus3 aus4 zn 1,269 71 70 70 73 cu 224 24 22 21 23 markowicz et al. (2021) found that the bioavailable fraction of zn in the control soil was only 0.14 % of its total content and was 2.8 ± 0.7 mg.kg -1 . for ssl, the bioavailable fraction of zn was only 7.7 ± 0.5 mg.kg -1 . in contrast, the percentage of extractable cu in ssl (only 1.8 %), was approx. 6times lower compared to aus samples. thus, it can be stated that despite the significant presence of zn and cu in the studied sample of ssl, their bioavailability is relatively low. this result can be evaluated positively because high values of the bioavailability of zn and cu would mean the immediate availability of these metals for plants, and it could be the case that the root system would not be able to absorb this amount effectively at a given moment. it follows that the studied ssl can represent an interesting source of zn and cu as important microelements for plants, but relatively tightly bound, which can be released from this matrix in smaller proportions controlled by the gradual concentration equilibria [m]solution : [m]ssl a b 7 nova biotechnol chim (2021) 20(2): e1258 2 reaching or decomposition of this matrix in the soil environment. laboratory lysimeter experiments in this part of the work, the laboratory lysimetric experiments involving the application of ssl (15 t.ha -1 – experiment a or 30 t.ha -1 – experiment b) into the topsoil layer of aus (0 – 10 cm) forming part of a 40 cm soil column in which seedlings of tobacco (n. tabacum l.) plants were cultivated, allowed us to evaluate the overall balance of zn and cu in terms of their amount applied into the soil in the form of ssl. these experiments were focused on the overall balance of metal movement – zn and cu microelements occurring in significant amounts in the obtained samples of ssl within the designed soil biosystem: ssl/aus – soil solution – root system and aboveground parts of tobacco as a model fast-growing plant. the first addition of ssl represents the amount of 15 tons of ssl per hectare, which corresponds with the limits permitted by act no. 188/2003. in the case of the second lysimeter experiment, this amount was increased to 30 t.ha -1 , thus exceeding the permitted limit value of 15 t.ha -1 . it follows that the first experiment involving the application of ssl within the permitted limits focuses primarily on the evaluation of the positive effects of ssl as potential effective carriers of important microelements for plant growth. on the other hand, the second experiment with a double dose of ssl application (30 t.ha -1 ) makes it possible to assess their negative effects, especially in terms of the risks of heavy metals release from ssl into groundwater or the food chain through the plant uptake. fig. 4 graphically shows the changes in the values of water pressure potential (soil moisture tension) measured by tensiometers placed in individual layers of the prepared soil column caused by watering, suction of the soil eluate or evapotranspiration of water under given conditions. the value of pressure potential near 0 hpa represents saturated soil with water and values up to -600 to -700 hpa represent soil with minimal water content. during a 28 day experiment a, the analysis of zn fig. 4. soil moisture tension changes analysed by tensiometers placed in individual layers of the prepared soil column caused by watering, suction of the soil eluate or evapotranspiration of water under conditions given by the growth chamber during 28 days of the lysimeter experiment a and b. and cu amount in the samples of soil eluates drained from bottom of the lysimeter vessel confirmed a gradual increase in the concentration of zn and cu (0.21 mg.dm -3 for zn and 0.03 mg.dm -3 for cu to 0.96 mg.dm -3 and 0.19 mg.dm -3 , respectively) in the soil eluates collected. a similar phenomenon was also observed in the case of the experiment b. the gradual increase of concentrations of zn and cu in the soil eluates is probably related to the gradual release of these metals from the ssl applied into the topsoil layer (0 – 10 cm). at the end of the experiments, the grown tobacco plants and the individual soil layers were removed from the lysimeter vessel and subjected to quantitative analysis of the content of zn and cu. in the first step, the extractability of these microelements was evaluated by a one-step extraction procedure using a mehlich iii solution in order to determine the bioavailability of zn and cu within the individual layers of the soil column. the highest extractability of zn and cu was determined in the topsoil layer (0 – 10 cm) involving the application of the studied ssl (fig. 5a), when 13.8 % of zn of the total amount of zn in the analysed topsoil occurred in the extractable – bioavailable form. in the case of cu and the topsoil layer, the bioavailable form of this metal represented only 8.4 % of the total amount of cu under the same 8 nova biotechnol chim (2021) 20(2): e1258 3 conditions. from a quantitative point of view, it can also be said that the bioavailability of zn and cu in the topsoil layer was up to 3-times and about 30 % higher than in the case of lower soil layers without the direct application of ssl, respectively. also in the second experiment b (fig. 5b), it was found that the highest extractability of zn and cu was in the topsoil layer involving the application of the studied ssl, when up to 14.6 % of zn and 9.2 % of cu of the total amount of zn and cu in the analysed topsoil were occurred in the bioavailable forms. similarly, the bioavailability of zn and cu in the topsoil layer was up to 2-times and about 40 % higher than in the lower soil layers without the direct application of ssl, respectively. fig. 5. extractability of zn and cu from individual aus layers (aus1: topsoil layer 0 – 10 cm; aus2: 10 – 20 cm; aus3: 20 – 30 cm; aus4: 30 – 40 cm) at the end of laboratory lysimeter experiments a and b expressed as the amount of metal released form 1 kg of the given soil layer. error bars represent the standard deviations of the mean (± sd; n = 3) from the analysis of the samples of tobacco plants, it was observed that during experiment a, the plants increased their quantitative parameters, such as height of plants, length of above-ground parts or weight of plants, at least 3-times. from the point of view of the presence of zn and cu in the tissues of tobacco plants, it can be said that zn was accumulated in the concentration of 84.4 mg.kg -1 (d.w.) and cu in the amount 21.9 mg.kg -1 (d.w.). the ratio between accumulated amounts of zn and cu corresponds to the initial concentration ratio of these metals in the topsoil layer involving the application of ssl (86.8 mg.kg -1 for zn and 26.6 mg.kg -1 for cu). within this analysis, it was also evaluated the transfer factor (tf) defined as [m]plant : [m]soil and the portion of these metals in the tissues of individual parts of plants – root, stem and leaves in order to determine the concentration factor (cf) defined as [m]aboveground parts : [m]root. the calculated tf values were 0.97 for zn and 0.82 for cu and cf reached the same value of 0.74 for both metals. from the results of experiment b, it can also be concluded that during the experiment the plants increased their quantitative parameters at least 3times. due to the double dose of ssl (30 t.ha -1 ), in terms of the amounts permitted by act no. 188/2003 (limit 15 t.ha -1 ), the toxic effects of this increased addition of ssl on the growth of tobacco plants were not observed. based on the portion of zn and cu in the tissues of tobacco plants, it was found that in this case zn was present in a concentration of 96.2 mg.kg -1 (d.w.) and cu in the amount 15.7 mg.kg -1 (d.w.). thus, these amounts represent similar concentrations as in the case of an experiment involving the application of half amount of ssl. when calculating the values of concentration factors (cf) and transfer factors (tf), we found slightly different data than in previous experiment a. in both parameters, higher values were obtained for zn (cf = 0.74; tf = 0.94) in the comparison with the data for cu (cf = 0.36; tf = 0.54). a b 9 nova biotechnol chim (2021) 20(2): e1258 2 fig. 6. percentage distribution of the total amount of zn and cu occurring in the applied ssl (experiment a: zn – 133 mg and cu – 23.5 mg; experiment b: zn – 267 mg and cu – 47.0 mg) within the soil biosystem ssl/aus – soil solution – 3 tobacco plants (n. tabacum l.) at the end of laboratory lysimeter experiments. details are described in fig. 4. the use of a laboratory lysimeter system allowed to assess the total balance of zn and cu, based on the dose of ssl applied into the soil at the beginning of the experiment (experiment a: zn – 133 mg and cu – 23.5 mg; experiment b: zn – 267 mg and cu – 47.0 mg), the amount of zn and cu occurring in the collected soil eluates during the experiment and based on the amount of these metals accumulated in tobacco plants. in the case of the application of ssl in the highest dose permitted (15 t.ha -1 ), the total balance of zn and cu originating from the applied amount of ssl into the soil at the beginning of the experiment showed that only 0.11 % zn and 0.07 % cu were released in the form of soil eluate during a 28 day of exposure, while in tobacco plants 0.13 % zn and 0.05 % cu were accumulated (fig. 6). when applying ssl in the amount of 30 t/ha, i.e. in the amount exceeding the permitted limits, it was found that from the applied amount of ssl into the soil at the beginning of the experiment only 0.02 % zn and 0.04 % cu were released in the form of soil eluate during a 28 day exposure, while in tobacco plants 0.16 % zn and 0.09 % cu were accumulated. the remaining percentages of cu and zn stayed bound in the prepared soil column. similar minimal amounts of zn and cu released in the soil eluate or accumulated in giant reed (arundo donax l.) plants were also observed in the work of šuňovská et al. (2015), despite the increased bioavailability of these metals in the topsoil layer. from the above mentioned results, it is clear that double dose of ssl applied into the topsoil layer had the effect of increasing the accumulated amounts of zn and co in plant tissues rather than releasing them into the lower soil layers or soil eluate at the bottom of the lysimeter vessel. conclusion from the point of view of evaluating the possibility of application of the studied sewage sludge (ssl) to agricultural soils, it can be stated that the applied ssl represents an interesting source of zn and cu as important microelements in plant nutrition. these metals occur in the studied ssl experiment a 0.16 % zn 0.09 % cu 99.82 % zn 99.87 % cu 0.02 % zn 0.04 % cu experiment b plants: soil column: soil eluate: 0.13 % zn 0.05 % cu 99.76 % zn 99.88 % cu 0.11 % zn 0.07 % cu 10 nova biotechnol chim (2021) 20(2): e1258 2 in a bioavailable form, while their bioavailable portion is higher than in the case of agriculturally used soil (aus), but not enough to represent the risk of significant transport of these heavy metals into the lower soil layers or groundwater. in this regard, it was also shown that even exceeding the permitted limits in terms of application of ssl into the soil (30 t.ha -1 ) did not have negative effects in terms of significant vertical transport of zn and cu to lower layers of the soil column or in terms of the growth of tobacco (n. tabacum l.) as a model of a fast-growing plant. however, it must be taken into account that long-term and especially repeated application of higher amounts of ssl into the soils can lead to a negative accumulation of heavy metals originating from this application and to soil contamination. in this sense, relevant legislation of the slovak republic is also drafted (act no. 188/2003). an interesting scientific challenge, as well as a challenge for practice, is the application of ssl as a large-volume waste in terms of their application to 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metals in soil and in mixtures of lawn grasses. environ. prot. eng. 39: 67-76. zhang q, hu j, lee d-j, chang y, lee y-j (2017) sludge treatment: current research trends. bioresour. technol. 243: 1159-1172. žaltauskaitė j, kniuipytė i, praspaliauskas m (2022) earthworm eisenia fetida potential for sewage sludge amended soil valorization by heavy metal remediation and soil quality improvement. j. hazard. mater. 424: 127316. 12 microsoft word urik nb 9-2.doc nova biotechnologica 9-2 (2009) 141 basic interactions of aspergillus niger with se(iv) martin urík1, jaroslav ševc1, pavol littera1, marek kolenčík1, slavomír čerňanský2 1geological institute, faculty of natural sciences, comenius university in bratislava, mlynská dolina, bratislava, sk-842 15, slovak republic (urik@fns.uniba.sk) 2department of ecosozology and physiotactics, faculty of natural sciences, comenius university in bratislava, mlynská dolina, bratislava, sk-842 15, slovak republic abstract: filamentous fungus aspergillus niger is commonly found on decaying vegetation or in indoor environment and has a number of uses, including application in bioremediation. hence, the basic interactions of this common mould with selenite were studied, including biovolatilization, bioaccumulation and toxicity effects of selenite on fungal growth. the fungal strain, originally isolated from noncontaminated soil, was cultivated under aerobic conditions on liquid cultivation media with concentration of se(iv) 19 or 27 mg.l-1 during 25 days. the fungal growth in the presence of selenite was not inhibited when compared to control, only the sporulation was reduced. the concentration of se(iv) in liquid medium decreased rapidly within first ten days to 1 mg.l-1. however, according to results from the 25th day of cultivation, the concentration of total selenium in medium did not change significantly and only negligible amount of selenium (less then 1%) was bioaccumulated. that indicates some biotransformation of selenite into other selenium species. during the cultivation, up to 21% of total amount of selenium was transformed into volatile derivatives (biovolatilization) by filamentous fungus a. niger. key words: selenite, filamentous fungi, biovolatilization, bioaccumulation 1. introduction selenium is an essential micronutrient in animals. however, its elevated concentrations may result in toxic effects (eisler, 2000). hence, environmental pollution with selenium mobilized from geological sources as a result of industrial or agricultural activities may be serious threat for ecosystems (davis et al., 1988). bioremediation, including biosorption, bioaccumulation and biovolatilization is an alternative promising technology for removal of toxic metals from soils and waters (hiller et al., 2008; pipíška et al., 2008). biovolatilization of selenium by microorganisms, including fungi, has received much attention because of its application in bioremediation of selenium contaminated soils or waters (thompsoneagle and frankenberger, 1992). this process is realized via methylation pathway, where the selenium oxyanions are reduced, and the elemental selenium can be produced, a process which also results in detoxification (gadd, 1993). despite fungal capability to biovolatilize selenium, it is need to be known how does the fungi react on elevated concentrations of bioavailable selenium species, especially selenite, which is scavenged from waters to a greater extent then selenate (hamilton, 2004). 142 urík, m. et al. the objective of this study was to evaluate selenite uptake and transformation into volatile derivatives by aspergillus niger and the fungal growth responses to elevated selenite concentrations during cultivation. 2. materials and methods the strain of aspergillus niger used in this study was originally isolated from non-contaminated soil and was maintained on agar medium under laboratory conditions. fungal inocula were prepared from 14-day old cultures of this strain. the stock solutions of selenite were prepared in deionized water from na2seo3.5h2o (merck, germany). the cultivation system for experimental purposes included 15 ml of sabouraud cultivation media (himedia, mumbai, india), 5 ml of prepared fungal inocula and 5 ml of stock solutions to reach concentration 19 or 27 mg.l-1of se(iv) in cultivation system. selenite free control was also set up and monitored for 25 day. the ph of cultivation media, weight of dried biomass and concentration of se(iv) in medium were determined on 5th, 10th, 15th, 20th and 25th day of cultivation. on 25th day the concentration of total selenium in biomass and cultivation media was determined. all experiments were preformed in triplicate. 3. results and discussion growth of aspergillus niger in absence of selenite is illustrated in fig. 1. there is a linear growth phase in first 5 day of cultivation, followed by decline phase. on the 5th day the dry weight of biomass reached its maximum (0.36 g). surprisingly, the declination phase in presence of selenium (fig. 1) is not so evident comparing to the control. fig. 1. changes in weight of dry biomass during cultivation of aspergillus niger in absence (control) or presence of selenite with different initial concentration (19 or 27 mg.l-1). the first phase is followed by relative stationary phase until the 25th day of cultivation. the maximum dry weight of biomass is almost the same for the control nova biotechnologica 9-2 (2009) 143 and growth of a. niger in presence of selenite. however, the presence of selenite significantly reduced sporulation of the fungus. these observations suggest the relative resistance of a. niger to high selenium concentrations. generally, filamentous fungi are resistant to high levels of metals and metalloids, which indicates the potential of fungi as bioremeditation agents (iram et al., 2009). fig. 2. changes in ph of cultivation media during cultivation of aspergillus niger in absence (control) or presence of selenite with different initial concentration (19 or 27 mg.l-1). the initial ph of the cultivation media in absence of selenite was around 5.8 and decreased to 4.03 in first days of cultivation (fig. 2), followed by rapid increase to 7.92 determined on the 10th day of cultivation. the ph of the liquid medium did not significantly change until the end of experiment. the changes in ph value of cultivation media in presence of selenite (fig. 2) were significantly different compared to control. after initial decrease (3.6 and 3.4 for cultivation systems with initial se(iv) concentration of 19 and 27 mg.l-1 , respectively), the ph value only slightly increased with time up to approximately 4.6 for both initial concentrations of selenite. the decrease in ph of liquid medium during cultivation of white-rot fungus phanerochaete chrysosporium in presence of heavy metals was published by falih (1997), who claims, the decrease in ph is unfavorable condition for the fungus, probable because of increasing solubility of metals in the medium. in recent experiment, the ph and metabolic activity of fungus should significantly affect selenium toxicity, its ionic forms and mobility. during the initial growth rate decreased the concentration of se(iv) rapidly by more than 50% and later to 1.07 and 1.26 mg.l-1 at the end of the 10th day of cultivation for systems with initial concentration of se(iv) 19 and 27 mg.l-1, respectively (fig. 3). the concentration of selenite in cultivation media steadily decreased with time. however, the concentration of total selenium should not be changed during the cultivation. the table 1 shows the results of total selenium in media and fungal biomass at the end of cultivation, on the 25th day. the concentration of total selenium in cultivation medium decreased only slightly suggesting possible transformation of se(iv) into different chemical species. biomass-associated transformation of selenite (e.g. reduction to amorphous elemental selenium) has been 144 urík, m. et al. published previously (tomei et al., 1992). according to differences in amount of added se(iv) and the sum of se(iv) in biomass and medium, it is evident that the total selenium mass balance has change during the cultivation period. fig. 3. changes in se(iv) concentration in cultivation media during cultivation of aspergillus niger in presence of selenite with different initial concentration (19 or 27 mg.l-1). table 1. the amount of total selenium in biomass and cultivation media on the 25th day of cultivation with calculated amount of biovolatilized selenium during cultivation. initial concentrations of se(iv) (mg.l-1) concentration of total selenium in medium (mg.l-1) concnetration of total selenium in biomass (mg.kg-1) amount of biovolatilized selenium (%) 19 17.790 1.351 8.89 27 21.355 1.309 21.58 the loss of selenium in cultivation system represents approximately 8.9% and 21.6% for system with initial concentration of se(iv) 19 and 27 mg.l-1, respectively. the amount of accumulated selenium in biomass was negligible, less than 1% of total selenium present in cultivation system. previously, it was demonstrated that penicillium sp. is capable of selenite transformation in aqueous medium by biomass associated process as well as the formation of volatile organic derivatives (brady et al., 1996). 4. conclusions 1. the weight of dry biomass was not significantly different during the cultivation in presence and absence of se(iv) (19 or 27 mg.l-1) in cultivation media. 2. when comparing to control, the ph value of cultivation media in presence of selenite maintained in acidic region of ph (around 4), while the ph value of media in absence of selenite rapidly increased up to ph 8. 3. the concentration of se(iv) decreased rapidly within 10 days of cultivation. however, the concentration of total selenium decreased only slightly suggesting nova biotechnologica 9-2 (2009) 145 possible transformation of se(iv) into different chemical species. 4. while the accumulation of selenium after 25-day cultivation was negligible, the almost all of uptaken selenium was transformed into volatile derivatives (up to 21%) or chemical species other than selenite (according to previous statement). acknowledgements: this research was supported by vega 1/4361/07. references brady, j.m., tobin, j.m., gadd, g.m.: volatilization of selnite in aqueous medium by a penicillium species. mycol. res., 100, 1996, 955-961. davis, e.a., maier, k.j., knight, a.v.: the biological consequences of selenium in aquatic ecosystems. calif. agr., 42, 1988, 29. eisler, r. selenium. in: handbook of chemical risk assasment: health hazards to humans, plant and animals. lewis publishers, crc press, boca raton, 2000, 1649-1705. falih, a.m.: influence of heavy-metals toxicity on the growth of phanerochaete chrysosporium. bioresour. technol., 60, 1997, 87-90. gadd, g.m.: interactions of fungi with toxic metals. new phytol., 124, 1993, 25-60. hamilton, s.j.: review of selenium toxicity in aquatic food chain. sci. total. environ., 326, 2004, 1-31. hiller, e., jurkovič, ľ, bartál, m.: effect of temperature on the distribution of the polycyclic aromatic hydrocarbons in soil and sediments. soil wat. res., 3, 2008, 231-240. iram, s., ahmad, i., stuben, d.: analysis of mines and contaminated agricultural soil samples for fungal diversity and tolerance to heavy metals. pak. j. bot., 41, 2009, 885-889. pipíška, m., horník, m., vrtoch, l., augustín, j., lesný, j.: biosorption of zn and co ions by evernia prunastri. chem. ecol., 24, 2008, 181-190. thompson-eagle, e.t., frankenberger, w.t.: bioremediation of soils contaminated with selenium. adv. soil sci., 17, 1992, 262-310. tomei, f.a., barton, l.l., lemanski, c.l., zocco, t.g.: reduction of selenate and selenite to elemental selenium by wolinella succinogenes. can. j. microbiol., 38, 1992, 1328-1333. microsoft word brodnjak nb 9-2.doc nova biotechnologica 9-2 (2009) 113 high-performance liquid chromatographic determination of selected phenolic acids in wine darinka brodnjak vončina, maša islamčević razboršek, marjana simonič university of maribor, faculty of chemistry and chemical engineering, smetanova 17, maribor, slovenia (darinka.brodnjak@uni-mb.si) abstract: the aim of this study was to develop a method for identification and quantification of phenolic acids in different wine samples. the simple reversed-phase hplc-uv method for simultaneous determination of p-coumaric and ferulic acid was developed. the method was validated and working range, linearity, repeatability, accuracy, limit of quantitation loq and limit of detection lod were determined. the linearity of the method was tested in concentration ranges 0.1-1 mg l-1 and 1-10 mg l-1. the correlation coefficients (r2) were greater than 0.996 and quality coefficients (qc) ≤ 5%. detection limit for both compounds was 0.01 mg l-1. the method is precise (rsd<10%) and accurate. two different wine sorts were used for analysis, slovene red wine refošk and slovene white wine laški rizling. the wine samples were ultrasonically extracted with ethyl acetate, centrifuged, evaporated, re-dissolved in mobile phase and filtered. the solution was analyzed directly by hplc-uv. phenolic compounds were separated with a c18 reversed-phase column by isocratic elution using 2 % acetic acid in water-methanol (85:12, v/v) as the mobile phase at a flow rate of 0.7 ml min-1. acids were detected and quantitation was performed at wavelength of 320 nm. extraction procedure was optimized and yields were calculated from internal standard recovery. o-coumaric acid was used as internal standard. from the results it is evident that the red wine refošk contains higher concentrations of investigated compounds then the white wine laški rizling. stability tests were performed with standard compounds of p-coumaric and ferulic acid. it was established that both standards occur as trans-isomers, but when they were dissolved in methanol and stored exposed to daylight and room-temperature they were gradually transformed to cis-isomers. all closely related geometrical cisand trans-isomers were successfully separated under the same conditions as described before. the described method is simple and rapid as it involves liquid extraction with no other pretreatments of samples. it is suitable for simultaneous determination of cis and trans isomers of p-coumaric and ferulic acid in different liquid samples. key words: p-coumaric acid, ferulic acid, o-coumaric acid, hplc, wine. 1. introduction in recent years lots of studies were focused on phenolic acids due to their antioxidant antiviral, antibacterial and anti-inflammatory properties (zgórka and kawka, 2001). a variety of phenolic acids were separated using high-performance liquid chromatography (hplc) as reported in literature (kallithraka et al., 2006; robbins and bean, 2004; tarnawski et al., 2006; urakova et al., 2008; zgórka and kawka, 2001). in most studies reversed-phase hplc method was applied using non-polar c18 column. isocratic elution was applied (tarnawski et al., 2006; urakova et al., 2008; zgórka and kawka, 2001; yi et al., 2009) as well as a gradient method (kallithraka et al., 2006; robbins and bean, 2004; sladkovský et al., 2004). different mobile phases were prepared, using methanol–aqueous or acetonitrile–aqueous acidified mixtures. it 114 brodnjak vončina, d. et al. was determined that ph value is very important due to protonation of the acids. therefore the best ph was determined to be from 1-3. garciá et al. (2007) paid a lot of attention to sample pre-treatment. they used liquid-liquid separation with diethyl ether, followed by centrifugation, and vacuum evaporation. a variety of different wines was analysed by kallithraka et al. (2006). samples were only filtered and no other pre-treatment methods were used. hplc-dad method was applied for determination of phenolic acids at different wavelengths (265, 280, 320, and 365 nm, respectively, at 1 ml min-1 flow). the concentration of phenolic acids varied a lot depending on weather conditions, geographic sites, the way of wine storage and aging. these discoveries agree also with other studies (özkan et al., 2006). the aim of our work was to develop the analytical method to separate and determine two target components in wine samples, namely p-coumaric and ferulic acid. attention was paid to the most appropriate sample pre-treatment technique. 2. materials and methods all reagents and solvents used were of analytical grade. milli-q water was used. methanol (meoh) was purchased from sigma-aldrich (germany), acetic acid (ch3cooh), ethyl-acetate (c4h8o2), 98% trans ferulic acid (fa), 98 % trans pcoumaric acid (p-ca) and 97% ocoumaric acid (o-ca) were supplied from merck (germany). 2.1 preparation of calibration solutions and calibration curves standard stock solution of trans fa, trans p-ca and o-ca was prepared by dissolving each of them with meoh in 10 ml volumetric glass flasks to obtain concentration of 1 g l-1. o-ca was used as an internal standard (istd). this solution was degassed for 20 minutes by sonication. five working calibration solutions were prepared from standard stock solutions by further dilution with mobile phase consisting of 2% acetic acid in water-methanol mixture (82:18, v/v). concentration ranges of the final standard solutions used for calibration curves were 0.1-1 mg l-1 and 1-10 mg l-1. calibration solutions were injected into the hplc-uv system in five replicates. in addition, three replicate analyses of the calibration solutions were performed. curves were constructed by linear regression of the peak-area ratio (y) of individual acids to the istd, versus the concentration (x). all standard solutions were kept at -18 ° c for a maximum one week. prior to injection the solutions were filtered through 0.45 μm filter. 2.2 sample preparation wine samples were refošk (red wine) and laški risling (white wine) from slovenia. wine samples undergo a liquid-liquid extraction prior to their analysis by hplc. 5 ml of wine sample was transferred into a 50-ml round-bottomed glassstoppered centrifuge tube, spiked with 50 µl of istd (0.5 mg l-1) and extracted with 5 ml of ethyl acetate by sonication (ultrasonic bath model sonis 4, iskra, slovenia) for nova biotechnologica 9-2 (2009) 115 20 minutes. the extract was centrifuged (centrifuge model lc 321, tehnica železniki, slovenia) at 1000 rpm for 10 min and the supernatant was accurately transferred into 200-ml conical glass flask using a glass pasteur pipette. this extraction procedure was repeated three times. supernatants were combined and concentrated to dryness by rotary evaporation (büchi rotavapor r-205, switzerland). the residue was redissolved in 5 ml of mobile phase consisting of 2% acetic acid in water-methanol mixture (82:18, v/v). finally, the pre-treated sample was filtered through 0.45 µm filter and analysed. the compounds in wine extracts were quantified from the corresponding calibration curves. 2.3 stability tests trans p-ca and trans fa standard compounds were dissolved in meoh separately, to obtain concentrations of 1 mg l-1. the contents of trans p-ca and trans fa were determined from the corresponding calibration curves and they were used for the control. then each solution was divided into more equal parts and transferred into graduated glass-stoppered test tubes. four parts were placed under the daylight and room temperature for varied lengths of time (5 h, 24 h, 48 h and 1 week); another four parts of each solution were stored in the refrigerator in the darkness at -18 °c for varied lengths of time (5 h, 24 h, 48 h and 1 week). after exposure to the mentioned conditions, the content of trans p-ca and trans fa were determined from the corresponding calibration curves and compared to the control. equipment and chromatographic analyses a simple and rapid chromatographic separation was carried out using reversephase hplc. chromatographic analyses were performed on varian, prostar (usa) hplc system, which consisted of varian prostar 210 hplc pump, varian prostar injection valve, and uv-vis detector. chromatographic system was connected to the pc. separation was carried out on 250 mm x 3mm i.d., 5 µm non-polar chromspher 5, c18 column. elution was performed isocratically with the mobile phase consisting of 2% acetic acid in water-methanol mixture (82:18, v/v). the flow rate was 0.7 ml min-1, the pressure 180×105 pa and the injection volume was 100 µl. peaks were detected at 320 nm. 3. results and discussion based on linear regression analysis, the responses for investigated compounds were linear over concentration ranges tested. the equations of calibration curves and their correlation coefficients are presented in table 1. the reproducibility of chromatographic analyses was evaluated by the relative standard deviation (rsd) of five replicate analyses of five calibration solutions. rsd was between 2.91 and 3.81 %. the extraction procedure was optimized regarding extraction solvent and recovery. ethyl-acetate was used for extraction of the compounds from wine. the best recoveries (over 89%) were obtained by using three equal volumes of mentioned solvent, while using only two equal volumes gave lower recoveries. the recovery was evaluated using o–ca which was added into the wine sample before the extraction. 116 brodnjak vončina, d. et al. this compound is structurally related to the investigated compounds and behaves similar on the column as analytes. it does not occur in wine. therefore it is suitable for quantitative analysis of investigated compounds. table 1. regression equations and correlation coefficients for investigated compounds investigated compound correlation coefficient (r2) regression equation trans p–ca 0.9969 y = 0.4088 x + 0.1021 trans fa 0.9968 y = 0.3403 x + 0.0705 chromatographic separation was optimized with respect to the mobile phase, eluent composition, and flow rate. several experiments were carried out to resolve the acid mixture using a different mobile phases. to increase the retention behaviour acetic acid was used. optimal peak resolution was achieved using 2% acetic acid in water-methanol mixture (82:18, v/v). in fig. 1 chromatograms of investigated compounds, present red wine extract is presented. the separation with good resolution has been achieved for phenolic acids within 32 min. their average contents in different wine extracts (mg l-1) are presented in table 2. concentrations of trans p-ca and trans fa are higher in red wine. very high concentration of trans fa was determined in refošk, which was even 100-times higher compared with white wine. contents of phenolic acids are comparable to those reported in literature (robbins and bean, 2004; kallithraka et al., 2006; garciá et al., 2007; sladkovský et al., 2004; ozkan et al., 2006; castellari et al., 2002). trans p-ca in different brands of red wine were reported in concentrations between 0.9 to 7 mg l-1 and trans fa from 0.14 to 6 mg l-1l, respectively. concerning white wine brands lower concentrations of both acids were fig. 1. chromatogram of investigated compounds present in extract of red wine-refošk. nova biotechnologica 9-2 (2009) 117 found in literature: trans p-ca varied from 0.2 to 1.4 mg l-1and trans fa from 0.1 to 0.7 mg l-1, respectively. table 2. contents of trans p–ca and trans fa in extracts of red wine-refošk and white wine-laški rizling (mg l-1). each content value is the mean of five replications. compound red wine refošk (n=5) white wine laški rizling (n=5) trans p–ca 2.95 1.82 trans fa 7.75 0.07 the results of stability tests showed that trans p–ca and trans fa gradually converted to their cis forms when they were dissolved in meoh and stored in daylight at room temperature. the trans-cis isomerization started already after a few hours. the content of trans p–ca and trans fa has lowered during the time of storing, while the content of cis p–ca and cis fa has increased. after being stored for 1 week in the refrigerator in darkness at -18 °c, trans p–ca and trans fa dissolved in meoh were found to be stable, and no isomer conversion occurred. although cis and trans forms of phenolic acids are geometric isomers with very similar structures, they can be well distinguished by order of elution during hplc (cis isomers are retained longer than trans isomers) (fig. 2) fig. 2. chromatogram of compounds present in mixture of trans p–ca and trans fa in meoh after being stored in daylight and room temperature for 24 hours. 4. conclusion the developed isocratic hplc method is a rapid and simple one compared with other hplc methods. the selection of proper mobile phase is crucial for good separation of phenolic compounds. proper storing conditions are important to ensure 118 brodnjak vončina, d. et al. stability of the compounds. the described method can be routinely used for separation and determination of closely related cisand trans-isomers of phenolic acids in different wine extracts and other liquid samples with complex natural matrices, even if they are present in the minor contents. references buiarelli, f., cartoni, g., coccioli, f., levetsovitou, z.: determination of phenolic acids in wine by hplc with a microbore column. j. chromatogr., a, 695, 1995, 229-235. castellari, m., sartini, e., fabiani, a., arfelli, g., amati, a.: analysis of wine phenolics by high-performance liquid chromatography using a monolithic type column. j. chromatogr., 973, 2002, 221-227. chamkha, m., cathala, b., cheynier, v., douillard, r.: phenolic composition of champagnes from chardonnay and pinot noir vintages. j. agric. food chem., 51, 2003, 3179-3184. garcía, falcón, m.s., pérez, lamela, c., martínez, carballo, e., simal, gándara, j.: determination of phenolic compounds in wines: influence of bottle storage of young red wines on their evolution. food chem., 105, 2007, 248-259. kallithraka, s., tsoutsouras, e., tzourou, e., lanaridis, p.: principal phenolic compounds in greek red wines. food chem., 99, 2006, 784793. özkan, g., göktürk, baydar, n.: a direct rp-hplc determination of phenolic compounds in turkish red wines. j. fac. agriculture akdeníz university, 19, 2006, 229-234. robbins, r. j., bean, s. r.: development of a quantitative high-performance liquid chromatography-photodiode array detection measurement system for phenolic acids. j. chromatogr., a, 1038, 2004, 97-105. sladkovský, r., solich, p., urbánek, m.: high-performance liquid chromatography determination of phenolic components in wine using off-line isotachophoretic pre-treatment. j. chromatogr., 1040, 2004, 179-184. tarnawski, m., depta, k., grejciun, d., szelepin, b.: hplc determination of phenolic acids and antioxidant activity in concentrated peat extract-a natural immunomodulator. j. pharm. biomed. anal., 41, 2006, 182-188. urakova i. n., pozharitskaya, o. n., shikov, a. n., kosman, v. m.: development and validation of an lc method for simultaneous determination of ascorbic acid and tree phenolic acids in sustained release tablets at single wavelength. j. chromatogr., 67, 2008, 709-713. yi, c., shi, j., kramer, j., xue, s., jiang, y., zhang, m., ma, y., pohorly, j.: fatty acid composition and phenolic antioxidants of winemaking pomace powder. food chem., 114, 2009, 570-576. zgórka, g., kawka, s.: application of conventional uv, photodiode array (pda) and fluorescence (fl) detection to analysis of phenolic acids in plant material and pharmaceutical preparation. j. pharm. biomed. anal., 24, 2001, 10651072. microsoft word miklovic nbc 12-2.doc nova biotechnologica et chimica 12-2 (2013) 75 doi 10.2478/nbec-2013-0009 © university of ss. cyril and methodius in trnava synthesis, crystal structure and spectral properties of copper(ii) and cobalt(ii) 3-methylthiophene-2carboxylato complexes with furopyridines jozef miklovič1, miroslava bašnárová1, peter segľa2, marián koman2 1department of chemistry, faculty of natural sciences, university of ss. cyril and methodius in trnava, j. herdu 2, trnava, sk-917 01, slovak republic (jozef.miklovic@ucm.sk) 2institute of inorganic chemistry, faculty of chemical and food technology, slovak university of technology in bratislava, radlinskeho 9, bratislava, sk-812 37, slovak republic abstract: the synthesis and characterization of eleven new cu(ii) and co(ii) complexes is reported. the complexes were characterized by elemental analyses, infrared and electronic spectra. copper(ii) with 3-methylthiophene-2-carboxylic acid (hmtk) forms a dinuclear complex of the acetate type [cu2(mtk)4(h2o)2]. by reaction of this complex with 2-metylfuro[3,2-c]pyridine (mefp), not only acetate type complexes [cu2(mtk)4l2] (l= fp, mefp) were obtained, but also monomeric complex [cu(mtk)2(fp)2]. in the cases of [1]benzofuro[3,2-c]pyridine (bfp) and 2-(3-trifluoromethylphenyl)furo[3,2-c]pyridine (cf3fp) only monomeric complexes [cu(mtk)2l2] (l = bfp, cf3fp) were obtained. it is possible to observe, that with increasing amount of the ligand, the yield of monomeric complexes increases too. in monomeric complexes, the carboxylic group of anionic mtk binds to atom cu(ii) by asymmetrically chelating o,o-coordination. the crystal structure of the complex [cu(mtk)2(mefp)2] was determined by x-ray single crystal structure analysis. the copper(ii) atom lies in the crystallographic centre of symmetry in an distorted tetragonal-bipyramidal arrangement. the structure of this complex confirms an asymmetric chelate coordination of the carboxylic group. hmtk and cobalt(ii) form coordination compound [co(h2o)6](mtk)2 with assumed ionic mode of coordination of anionic mtk. with furopyridines monomeric complexes [co(mtk)2l2] (l= fp, mefp, bfp, cf3fp) with distorted octahedral coordination polyhedron around co(ii), were formed. key words: complex, copper(ii), cobalt(ii), furopyridine, carboxylate 1. introduction derivatives of thiophene-2-carboxylic acid alone and their coordination compounds are interesting from biological as well as structural point of view (panagoulis, et al., 2007). the thiophene-2-carboxylic acid is an hypocalcemic agent and is effective in lowering the level of serum-glucose and fatty acids (ribeiro and santos, 2008). in this paper, we describe synthesis, spectral properties and crystal structure of 3-methylthiophnenecarboxylatecopper(ii) and cobalt(ii) complexes and their adducts with n-heterocyclic ligands: [cu2(mtk)4l2] (l=h2o, fp, mefp); [cu(mtk)2l2] (l=fp, mefp, bfp, cf3fp); [co(h2o)6](mtk)2, [co(mtk2)l2] (l=fp, mefp, bfp, bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:02 utc 76 miklovič, j. et al. cf3fp). the crystal and molecular structure of one of the complexes under study [cu(mtk)2(mefp)2] has also been studied by x-ray structure analyses. topological structures and abbreviations of heterocyclic ligands under study are given in fig. 1. s ch 3 co 2 o n o n h3c o n o n f 3c 3-m ethyltiophene-2-carboxylate mtk furo[3,2-c]pyridine fp 2-m etylfuro[3,2-c]pyridine mefp 2-(3-trifluorom ethylphenyl)furo[3,2-c]pyrid in e cf3fp [1]benzofuro[3,2-c]pyridine bfp fig. 1. structures and abbreviations of heterocyclic ligands. 2. material and methods 2.1 chemical reagents, analysis and physical measurements all used chemicals were of reagent grade and used without further purifications. derivatives of furopyridine (fp, mefp, bfp and cf3fp) have been prepared using eloy-derickere procedure (eloy and deryckere, 1971). cobalt and copper were determined by chelatometry after mineralization of the complexes. carbon, hydrogen, nitrogen and sulfur were determined by microanalytical methods (thermo electron flash ea 1112). analytical data for the complexes are given in table 1. electronic spectra of the powdered samples were recorded on a specord 200. ir spectra were recorded on a nicolet 5700 ft-ir spectrometer (thermo scientific). 2.2 crystallography data collection for [cu(mtk)2(mefp)2] (complex 4) was obtained using siemens p4 diffractometer (siemens, xemp. version 4.2, 1990) with graphite monochromated mokα , radiation at 293 k. the diffraction intensities were corrected for lorenz and polarization factors. the structures were solved by the heavy atom method with shelxs-86 (g. m. sheldrick, 1985), subsequent fourier synthesis using shelxl-97 (g. m. sheldrick, 1997) and refined by the fullmatrix least-square method on all f2 data using the program shelxl-97 (g. m. sheldrick, 1997). geometrical analysis was performed using shelxl-97 [10]. crystal data and conditions of data collection and refinement are reported in table 2. 2.3 preparation of the complexes [cu2(mtk)4(h2o)2] (1): naoh (0.6 g; 9 mmol) was dissolved in water (10 cm 3) and hmtk was added (1.28 g; 9 mmol). ph was adjusted to 7. solution of cuso4 (1.12 g; bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:02 utc nova biotechnologica et chimica 12-2 (2013) 77 4.5 mmol) in water (5 cm3) was then added. the mixture was stirred for 1 h and precipitate was filtered off. the precipitate was washed with water and dried at room temperature. yield: 0.9 g. table 1. cu(ii) a co(ii) analytical data for the complexes. compounds empirical formula formula weight calcd / found (%) (g mol-1) m c h n s [cu2(mtk)4(h2o)2] 1 c12h12cuo5s2 363.9 17.46 17.98 39.61 39.65 3.32 3.23 17.62 17.78 [cu2(mtk)4(fp)2] 2 c19h15cuno5s2 465.00 13.66 14.15 49.08 48.60 3.25 3.12 3.01 2.67 13.79 13.44 [cu2(mtk)4(mefp)2] 3 c20h17cuno5s2 479.03 13.26 13.74 50.15 49.87 3.57 3.48 2.92 2.70 13.39 13.24 [cu(mtk)2(mefp)2] 4 c28h24cun2o6s2 612.18 10.38 10.84 54.93 54.44 3.95 3.91 4.57 4.34 10.47 10.05 [cu(mtk)2(bfp)2] 5 c34h24cun2o6s2 684.24 9.28 9.66 59.68 59.65 3.53 3.51 4.09 4.08 9.37 8.87 [cu(mtk)2(cf3fp)2] 6 c40h26cuf6n2o6s2 872.32 7.28 7.65 55.07 54.72 3.00 2.86 3.21 3.11 7.35 6.92 [co(h2o)6](mtk)2 7 c12h22coo10s2 449.36 13.11 12.63 32.07 31.99 4.93 4.43 14.27 14.53 [co(mtk)2(fp)2] 8 c26h20con2o6s2 579.51 10.17 9.88 53.89 54.38 3.48 3.80 4.83 4.67 11.06 10.59 [co(mtk)2(mefp)2] 9 c28h24con2o6s2 607.57 9.70 9.36 55.35 54.87 3.98 4.08 4.61 4.51 10.55 10.56 [co(mtk)2(bfp)2] 10 c34h24con2o6s2 679.63 8.67 8.50 60.09 60.58 3.56 3.70 4.12 4.46 9.43 8.84 [co(mtk)2(cf3fp)2] 11 c40h26cof6n2o6s2 867.71 6.79 7.12 55.37 54.93 3.02 3.12 3.23 3.35 7.39 6.98 [cu2(mtk)4(fp)2] (2); [cu2(mtk)4(mefp)2] (3); [cu(mtk)2(mefp)2] (4): complex 1 (0.382 mg; 0.525mmol) was dissolved in methanol (9 cm3) and ligand (fp, mefp; 5 mmol) in methanol (3 cm3) was added. solution was then heated to 50°c and stirred for 1 h. the precipitate formed during the reaction was filtered off, washed with methanol and dried at r. t. blue filtrate evaporated at r. t. and crystals were formed and separated. yield: complex 2 0.5 g; complex 3 0.4 g; complex 4 0.2 g. [cu(mtk)2(bfp)2] (5); [cu(mtk)2(cf3fp)2] (6): complex 1 (0.382 mg; 0.525mmol) was dissolved in methanol (9 cm3) and ligand (bfp, cf3fp, 5 mmol) in methanol (9 cm3) was added. solution was then heated to 50°c and stirred for 1 h. the precipitate formed during the reaction was filtered off, washed with methanol and dried at r. t. yield: complex 5 1.5 g; complex 6 0,7 g. [co(h2o)6](mtk)2 (7): naoh (0.14 g; 3.5 mmol) was dissolved in water (10 cm 3) and hmtk was added (0.5 g; 3.5 mmol). ph was adjust to 7. solution of coso4 (0.49 g; 1.75 mmol) in water (5 cm3) was then added. mixture then evaporated at r. t. and subsequent crystals were separated. yield: 1.1 g. [co(mtk)2(fp)2] (8); [co(mtk)2(bfp)2] (10); [co(mtk)2(cf3fp)2] (11); the complex 7 (0.449 g; 1 mmol) was dissolved in methanol (5 cm3) and ligand (fp, bfp, cf3fp; 5 mmol) in methanol (3 cm 3) was added. solution was then heated to 50°c and bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:02 utc 78 miklovič, j. et al. stirred for 1 h. mixture then evaporated at r. t. and subsequent crystals were separated. yield: complex 7 2.1 g; complex 10 2.1 g; complex 11 0.9 g. [co(mtk)2(mefp)2] (9): the complex 7 (0.449 g; 1 mmol) was dissolved in dmf (15 cm3) and ligand (mefp; 5 mmol) in dmf (5 cm3) was added and stirred for 1 h. mixture then evaporated at r. t. yielded crystals were separated and dried at r. t. yield: 0.4 g. table 2. crystal data and structure refinement for [cu(mtk)2(mefp)2] (complex 4). identification code mk75 empirical formula c28h24cun2o6s2 formula weight 612.19 temperature 293(2) k wavelength 0.71073 å crystal system, space group triclinic, p-1 unit cell dimensions a = 6.352(1) å α = 82.53(1)o b = 10.489(1) å β = 80.95(1)o c = 10.501(1) å γ = 87.09(1)o volume 684.74(14) å3 z, calculated density 1, 1.485 mg/m3 absorption coefficient 0.995 mm-1 f(000) 315 crystal size 0.12 x 0.4 x 0.5 mm θ range for data collection 4.17 to 26.35o. limiting indices -1<=h<=1, -13<=k<=13, -13<=l<=13 reflections collected / unique 1384 / 692 [r(int) = 0.0754] completeness to θ = 26.35 24.8 % absorption correction none refinement method full-matrix least-squares on f2 data / restraints / parameters 692 / 0 / 179 goodness-of-fit on f2 0.901 final r indices [i > 2σ(i)] r1 = 0.0383, wr2 = 0.0886 r indices (all data) r1 = 0.0491, wr2 = 0.0957 extinction coefficient 0.000(5) largest diff. peak and hole 0.165 and -0.128 e. å -3 3. results and discussion 3.1 description of crystal structure of [cu(mtk)2(mefp)2] the structure of [cu(mtk)2(mefp)2] (complex 4) is shown in fig. 2. the copper(ii) atom is bonded in trans square-planar arrangement to two nitrogen atoms of two methylfuropyridine molecules [cu – n1 = 2.050 å] and one carboxylate oxygen atom from each of two 3-methyl-2-thiophene carboxylate anions [cu – o1 = 1.980 å]. the remaining two carboxylate oxygen atoms of [cu(mtk)2(mefp)2] which are bonded to the copper [cu – o2 = 2.560 å] bonds, lie at 57.43o from the plane of cuo2n2 and create tetragonal-bipyramidal coordination. the copper(ii) atom lies in the crystallographic center of symmetry. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:02 utc nova biotechnologica et chimica 12-2 (2013) 79 fig. 2. the molecular structure of [cu(mtk)2(mefp)2] (complex 4). 3.2 ir an electronic data all the typical features of ir spectra are clearly compatible with the structural characteristics of the complexes under study. some characteristic ir bands of the sodium salt namtk.h2o as well as of cu(ii) complexes are given in table 3. the ir spectrum of complex 1 shows absorption bands in the region from 3200 to 3500 cm-1. these bands correspond to the antisymmetric and symmetric oh stretch and confirm the presence of water. the difference between the antisymmetric stretch and symmetric stretch (δ) gives information on carboxylic bonding mode for the complexes after comparison with δ values of compounds with ionic carboxylic groups (nakamoto, 1997). the δ values for the complexes 1 (152 – 211 cm-1), 2 (175 – 234 cm-1) and 3 (181 – 237 cm−1) are comparable with δ value for sodium salt (156 – 211 cm-1) and suggested bridging mode of coordination carboxyl group. the considerable splitting of bands assigned to νs(coo −) for complexes 1, 2 and 3, confirms that the mtk anion as a ligand is most probably coordinated via a bridging carboxyl group (nakamoto, 1997). in these compounds, dimeric structure of acetate type known in other cu(ii) heterocyclic carboxylate (jašková, et al., 2007) is predicted. the δ values for the monomeric complexes 4 (188 – 261 cm-1), 5 (174 – 247 cm-1) and 6 (178 cm-1 – 261 cm-1) are greater than for namtk·h2o (156 – 211 cm -1). that is rather typical for asymmetrically chelating carboxylate groups. however, in these cases, δ values are comparable to those of unidentate complexes (nakamoto, 1997). the suggested asymmetrically chelating o,o’-coordination of carboxylate groups for complexes under study is in agreement with the structure determined by xray analysis for complex 4. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:02 utc 80 miklovič, j. et al. table 3. spectroscopic dataa (in cm-1) of cu(ii) complexes. a vs – very strong; s – strong; m – medium; br – broad; sh – shoulder, bδ = νas(coo-) νs(coo-). the solid state electronic spectra of complexes 1 – 3 show a broad absorption band (band i) in the visible region with a maximum from 13 450 cm−1 to 14 400 cm−1 (table 3), which is assigned to a dxy,yz → dx 2 −y 2 transition (kato, 1988). moreover, the spectrum of complexes 1 – 3 displays a shoulder at about 28 500 cm−1 (band ii). band ii has been assigned to a charge transfer absorption and is believed to be indicative of a dimeric complex, finally, complexes 1 – 3 displays bands i and ii in the usual range for cu(ii) compounds in a square-pyramidal cuo4o’ (complex 1) or cuo4n environment. the solid state electronic spectra of all other copper(ii) complexes under study exhibit a asymmetrical broad ligand field band with a maximum at about 17 500 cm−1. this type of d–d spectra for complexes 4 – 6 is typical for tetragonally distorted octahedral copper(ii) complexes (lever, 1984). some characteristic ir bands of the complexes co(ii) are given in table 4. the ir spectrum for complex 7 shows absorption bands in the region from 3200 to 3500 cm-1 and confirms the presence of water. these bands are not present in other co(ii) complexes and confirm the absence of water. the δ values for the complex 7 (151– 214 cm-1) are comparable with δ values of namtk·h2o (156 – 211 cm -1) which suggests ionic mode of coordination of carboxylate group with hexaaquacobalt(ii) cation and non-coordinated mtk anion. this manner of coordination is known (zhang and ng, 2005). on the other hand, the δ values from 169 to 241 cm-1 for complexes 8 – 11, greater than for namtk·h2o (156 – 211 cm -1) are typical for an asymmetric chelating coordination of the carboxyl group of mtk anion. infrared data carboxyl group electronic data compound νas(coo-) νs(coo-) δb band i band ii namtk.h2o 1573vs,br 1417vs 1364vs,br 156 209 [cu2(mtk)4(h2o)2] 1 1574vs 1422vs 1373vs 1363vs 152 211 14 400 28 600sh [cu2(mtk)4(fp)2] 2 1597vs 1422vs 1375vs 1363vs 175 234 13 700 28 000sh [cu2(mtk)4(mefp)2] 3 1600vs,br 1419vs 1375vs 1363vs 181 237 13 450 29 000sh [cu(mtk)2(mefp)2] 4 1603s 1415vs,br 1342vs,br 188 261 17 500 13 500sh [cu(mtk)2(bfp)2] 5 1592vs 1418vs 1379vs 1345vs 174 247 17 400 13 900sh [cu(mtk)2(cf3fp)2] 6 1601vs 1423vs 1380vs 1340vs 178 261 17500 13 800sh bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:02 utc nova biotechnologica et chimica 12-2 (2013) 81 table 4. spectroscopic dataa (in cm-1) of co(ii) complexes. infrared data carboxyl group electronic data compound νas(coo-) νs(coo-) δb 4t1g(f)→4t1g(p) 4t1g(f)→4t2g namtk·h2o 1573vs,br 1417vs 1364vs,br 156 209 [co(h2o)6](mtk)2 7 1566vs 1415vs 1352s,br 151 214 20 000 21 300 sh 8 600 [co(mtk)2(fp)2] 8 1589s 1420vs 1359vs 169 230 20 900sh 20 100 19 800sh 9400 [co(mtk)2(mefp)2] 9 1605vs 1420vs 1362vs 185 243 20 900sh 20 100 9300 [co(mtk)2(bfp)2] 10 1593vs 1421vs 1358vs 172 235 20 950 20 100sh 9 500 [co(mtk)2(cf3fp)2] 11 1591 1422vs 1350 169 241 21 100 9 300 a vs – very strong; s – strong; m – medium; br – broad; sh – shoulder, bδ = νas(coo-) νs(coo-). the electronic spectra (table 4) of all the cobalt complexes are clearly consistent with tetragonally distorted octahedral structure. the electronic spectra consist of a band ν1 assigned to the lowest energy transition 4t1g(f)→4t2g in the near infrared and the band ν3 in the visible near 20,000 cm -1, which is assigned to the 4t1g(f)→4t1g(p) transition. acknowledgements: this work was financially supported by the grants apvv-0014-11, vega 1/0233/12, vega 1/0472/13 of the slovak grant agency for science. this article was created with the support of the ministry of education, science, research and sport of the slovak republic within the research and development operational programme for the project "university science park of stu bratislava", itms 26240220084, co-funded by the european regional development fund. references eloy, f., deryckere, a.: sur la synthése des furo[3,2-c]pyridines. j. heterocycl. chem. 8, 1971, 57-60. g. m. sheldrick: shelxs-86, oxford university press, oxford, 1985, 175. g. m. sheldrick: shelxl-97, university of göttingen, germany, 1997. jašková, j., mikloš, d., korabik, m., jorík, v., segľa, p., kaliňáková, b., hudecová, d., švorec, j., fischer, a., mrozinsky, j., lis, t., melník, m.: synthesis, spectral and magnetic properties and crystal structures of copper(ii) pyridinecarboxylates as potential antimicrobial agents. inorg. chim. acta 360, 2007, 2711-2720. kato, m., muto, y.: factors affecting the magnetic properties of dimeric copper(ii) complexes. coord. chem. rev. 92 1988 45-83. lever, a,b.p.: inorganic electronic spectroscopy, 2nd ed., elsevier, amsterdam, 1984, p. 480. nakamoto, k.: infrared and raman spectra of inorg. and coord. compounds, part b, 5th edition, new york, 1997, 384-387. panagoulis, d., pontiki, e., skeva, e., raptopoulou, c., girousi, s., hadjipavlou-litina, d., dendrinou-samara, c.: synthesis and bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:02 utc 82 miklovič, j. et al. pharmacochemical study of new cu(ii) complexes with thiophen-2-yl and α,βunsaturated substituted carboxylic acids. j. inorg. biochem. 101, 2007, 623-634. ribeiro da silva, m. a. v., santos, a. f. l. o. m.: thermochemical properties of three 2-thiophene carboxylic acid derivatives. j. chem. therm. 40, 2008, 14511457. siemens, xemp. version 4.2 analytical x-ray instruments inc., madison, wisconsin, usa (1990). zhang, x.l., ng, s. w.: hexaaquacobalt(ii) bis(6-hydroxypyridine-3-carboxylate). acta cryst. e61, 2005, m1140-m1141. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:02 utc microsoft word kodba nb 9-3.doc nova biotechnologica 9-3 (2009) 249 validation of an improved european standard method for the determination of pcbs in oil samples zdenka cencič kodba1, darinka brodnjak vončina2 1institute of public health maribor, environmental protection institute, prvomajska 1, 2000 maribor, slovenia (zdenka.kodba@zzv-mb.si) 2faculty of chemistry and chemical engineering, university of maribor, smetanova 17, 2000 maribor, slovenia (darinka.brodnjak@uni-mb.si) abstract: two european standard methods (en 12766 and en 61619) are currently used for the determination of pcbs in specific oil matrix. however, apolar matrix compounds (e.g. hydrocarbons) elute from the adsorbent together with the pcbs and are injected into the analytical system where their presence contaminates the inlet, detectors and columns; and decreases system performances. insufficient cleanup causes delay of elution of pcbs from gc columns. by using new sulfoxide-bonded silica, pcbs are better separated from aliphatic hydrocarbons because the specificity of the stationary phase for these compounds is much higher that that used in both standard methods. a gas chromatograph at6890 with two capillary columns of different polarities (hp-5ms and db-1701) coupled to two μecds is used. oven temperature program is as followed: 90°c (1 min), 70°c/min to 180°c, 5°c/min to 230°c (0.1 min), 1.5°c/min to 280°c. run time is 46 min. the procedure was validated through regular analysis of blanks, fortified samples (transformer oil, motor used and unused oil) and certified materials (bcr-449 and bcr-420, waste mineral oils, high and low pcb levels). two internal standards were used (pcb 30 and pcb 209). an average recovery ± rsd of 82.8 ± 5.4 % was achieved for all six pcbs in different matrices. the loq per single pcb congener is 0.2 mg kg-1. the average recovery ± rsd for the bcr-420 is 92.0 ± 4.6 % and for the bcr-449 is 105 ± 2.5 % for all certified pcbs in waste oils. key words: pcbs, sulfoxide-bonded silica, validation, oil samples 1. introduction the election of standards to quantify pcbs is based on a number of factors among which the type of sample, the availability of reference compounds and the aim of the determination are included. two european standard methods (en 12766 and en 61619) are currently used for the determination of pcbs in specific oil matrix. the first one is applicable to unused, used and treated petroleum products including synthetic lubricating oils and the second one is applicable to unused, reclaimed or used insulating liquids where it is specifically emphasized that the presence of mineral oil may reduce the sensitivity of the ecd. in addition to the official methods (where a combination of acidified silica/anion exchange (sioh-h2so4/sa) and silica adsorbent is proposed) numerous sample preparation techniques are available for pcb analysis in oil samples ranging from extraction with aprotic solvents (e.g. dimethylsulfoxide, dimethylformamide) (larsen et.al., 1991; lawn and toffel, 1987), enzyme immunoassay (lambert et.al., 1997), hs spme (criado et.al., 2004), sulphuric 250 kodba, z.c. and brodnjak vončina, d. acid and alkali treatment (shin and kim, 2006; shu et.al., 1995), gel permeation chromatography (sheridan et.al., 1995), normal-phase (florisil, alumina) (lulek, 1998; nerin and domeno, 1999; storr-hansen et.al., 1992), reversed-phase chromatography and many surface modified silica for spe may be in use (nh2, nh2cl, nh2-so, scx-2, scx-2-nh4, sax, sax-so4, cn, diol and psa) for the separation of pcbs from mineral oils (takada et.al. 2001; na et.al., 2008; numata et.al., 2006; numata et.al., 2007; numata numata et.al., 2008). pcbs are not easily separated from oil matrices because their physical and chemical characteristics are very similar. the remaining oil during the analytical procedure was not an immediate analytical problem, because when the sample fraction was analyzed by selective detectors like ecd, the co-extracted compounds are not directly detected. also, lower limits of quantification are required. that is why a new modification of silica was used for sample preparation. supelclean sulfoxide spe (psa-so) consists of a patent pending sulfoxide-bonded silica where pcbs are preferentially retained on the spe phase whereas sample interferences (e.g. long chain hydrocarbons) are eluted in the early fraction. the procedure was validated through regular analysis of blanks, fortified samples (transformer oil, motor used and unused oil) and certified materials (bcr-449 and bcr-420, waste mineral oils, high and low pcb levels). two internal standards were used (pcb 30 and pcb 209). the working range, limit of quantification, repeatability, reproducibility and accuracy were determined. 2. materials and methods a surrogate standard solution was prepared by dissolving six pcb congeners (pcb 28, pcb 52, pcb 101, pcb 138, pcb 153 and pcb 180) from dr. ehrenstorfer and two pcb congeners (pcb 30 and pcb 209) in hexane. reference materials bcr crm-420 and bcr crm-449 with a certified concentration of several pcbs were purchased from the institute for reference materials and measurements (geel, belgium). j.t.baker supplied acetone and hexane. individual solutions of internal standards were prepared in acetone followed by dilution with hexane. three different matrices of oil samples were taken for analysis. waste oils were classified according to their origin into transformer oil, motor used and unused oil. 2.1 sample preparation the following spe method is based on a modified supelco procedure. spiked and non-spiked oil samples (0.25 g) were dried with anhydrous sodium sulphate and diluted to 10 ml with hexane. samples were homogenized and placed into the spe station. supelclean sulfoxide pp spe (3g/6ml) from supelco and sioh pp spe (500mg/3ml) from chromabond were used for the sample cleanup. the schematic spe process is shown in table 1. a gas chromatograph at6890 with two capillary columns of different polarities (hp-5ms and db-1701) coupled to two μecds was used. nova biotechnologica 9-3 (2009) 251 oven temperature program was 90°c (1 min), 70°c/min to 180°c, 5°c/min to 230°c (0.1 min), 1.5°c/min to 280°c. four calibration standards were prepared to cover the optimum range with the lowest calibration level of 0.2 mg kg-1 per single pcb congener. table 1. sample cleanup preparation by spe. i. supelclean sulfoxide spe (3g/6ml) 1. condition and equilibration the spe with 10 ml of acetone and 20 ml of hexane 2. add 0.5 ml of pre-treated sample in hexane 3. wash and remove the oil fraction with 0.5 ml and 4.5 ml hexane 4. elute the analytes with 13 ml hexane collect and concentrate an eluent to approximately 0.5 ml ii. sioh spe (500mg/3ml) 1. condition and equilibration the spe with one volume of acetone and one volume of hexane 2. add 0.5 ml of pcb fraction 3. wash and elute the pcb fraction with 2 x 1 ml and one volume of hexane collect and concentrate to 0.2 ml 3. results and discussion as shown in the chromatogram (fig. 1) good peak shape and sufficient separation of the critical pairs was obtained (resolution was 0.5 or greater). the working range of individual pcb congener was from 0.2 mg kg-1 to 100 mg kg-1. the accuracy was also very good. repeatability was less than 10% for all spiked samples, for all congeners over the whole calibration range with some exceptions for the transformer oil. fig. 1. gc-ecd-ecd chromatograms of the bcr standard, waste mineral oil. an average recovery ± rsd of 82.8 ± 5.4 % was achieved for all six pcbs in different matrices (fig. 2). the average recovery ± rsd for the bcr-420 was 92.0 ± 4.6 % and for the bcr449 105 ± 2.5 % for all certified pcbs in waste oils (fig. 3 and fig. 4). 252 kodba, z.c. and brodnjak vončina, d. fig. 2. results of the repeatability and recovery studies on fortified different matrices. fig. 3. results of the repeatability and recovery studies on the bcr-420. fig. 4. results of the repeatability and recovery studies on the bcr-449. 4. conclusions by using new sulfoxide-bonded silica, pcbs are better separated from aliphatic hydrocarbons because the specificity of the stationary phase for these compounds is much higher than that used in both standard methods. this previously developed sulfoxide-bonded silica and ammonium-salt bonded silica stationary phase (psa-so) together with the additional silica one, offer a simple, fast and efficient sample preparation for the extraction of pcbs from waste, transformer and mineral oil samples (especially paraffin-based), which can replace that mentioned in both european standards without any possible damage to the gc system. nova biotechnologica 9-3 (2009) 253 references criado, m.r., pereiro, i.r., torrijos, r.c.: selective determination of polychlorinated biphenyls in waste oils using liquid-liquid partition followed by headspace solid-phase microextraction and gas chromatography with atomic emission detection. j. chromatogr. a, 1056, 2004, 263-266. canals, a., forteza, r., cerda, v.: the routine determination of pcbs in waste automotive engine oils. chromatographia, 34, 1992, 35-40. lambert, n., fan, t.s., pilette, j.: analysis of pcbs in waste oil by enzyme immunoassay. sci. total environ., 196, 1997, 57-61. lulek, j.: levels of polychlorinated biphenyls in some waste motor and transformer oils from poland. chemosphere, 37, 1998, 2021-2030. larsen, b., tilio, r., kapila, s.: a dmso-based cleanup procedure for determination of pcbs in waste oil. chemosphere, 23, 1991, 8-10. lawn, r.e., toffel, s.a.: determination of polychlorinated biphenyls in waste oil by gas-liquid chromatography. analyst, 112, 1987, 53-56. nerin, c., domeno, c.: determination of polyaromatic hydrocarbons and some related compounds in industrial waste oils by gpc-hplc-uv. analyst, 124, 1999, 67-70. numata, m., aoyagi, y., tsuda, y., yarita, t., takatsu, a.: separation of polychlorinated biphenyls from mineral oil using alkylammonium ion-bonded silica stationary phases. anal. sci., 22, 2006, 785-788. numata, m., aoyagi, y., tsuda, y., yarita, t., takatsu, a.: preparation of sulfoxide residue bonded silica stationary phase for separation of polychlorinated biphenyls from mineral oils. anal. chem., 79, 2007, 9211-9217. numata, m., kaneko, t., mi, q., ye, m., kawamata, s., matsuo, m., yarita, t.: preparation of a sulfoxide group and ammonium-salt bonded silica stationary phase for separation of polychlorinated biphenyls from mineral oils. j. chromatogr. a, 1210, 2008, 68-75. na, y., kim, k., hong, j., seo, j.: determination of polychlorinated biphenyls in transformer oil using various adsorbent for solid phase extraction. chemosphere, 73, 2008, s7-s12. shin, s.k., kim, t.s.: levels of polychlorinated biphenyls (pcbs) in transformer oils from korea. j. hazard. mat., 137, 2006, 1514-1522. shu, y.y., dowdall, j.e., chiu, c., lao, r.c.: interference of transformer oil matrices to the internal standards on pcb quantification. intern. j. anal. chem., 60, 1995, 185-194. storr-hansen, e., cleemann, m., cederberg, t., jansson, b.: selective retention of non-ortho substituted coplanar chlorinated biphenyl congener on adsorbents for column chromatography. chemosphere, 24, 1992, 323-333. sheridan, b.r., poole, g., dawdall, e., chiu, c.: the effect of temperature on gpc for the separation of pcbs from transformer oil and subsequent analysis by gc-msd. int. j. environ. anal. chem., 60, 1995, 195-202. takada, m.i., toda, h., uchida, r.: a new rapid method for quantification of pcbs in transformer oil. chemosphere, 43, 2001, 455-459. microsoft word illková nb 9-3.doc nova biotechnologica 9-3 (2009) 225 characterization of preparation for fat separators kateřina illková, jiřina omelková, živan gojković, jana pavlačková faculty of chemistry, brno university of technology, purkyňova 118, 612 00 brno, czech republic, (xcillkova@fch.vutbr.cz;omelkova@fch.vutbr.cz; xcgojkovic@fch.vutbr.cz; xcpavlackova@fch.vutbr.cz) abstract: fats, oils and greases in waste water frequently cause serious environmental problems. a commercial preparation was tested for its ability to degrade oil and grease in wastewater. as substrates, two fats (lard and beef fat) and four oils (rape seed oil, sunflower oil, palm oil and olive oil) were chosen. the degradation ability of commercial preparation for different substrates was investigated by the determination of lipid degradation at ph 7, temperature 25 °c, aerobic condition and agitation at 160 rev/min for 14 days in erlenmeyer flasks. simultaneously, the lipolytic activity was spectrophotometrically determined at 420 nm. all tested substrates were degraded by the different rate to basic units (fatty acids). rape seed oil and lard were decomposed by bacterial lipase from commercial preparation. key words: fats, oils, waste water, lipid degradation, preparation, lipolytic activity 1. introduction a wide variety of industries (e.g. the dairy industry and food processing) produce the effluents rich in fats, oils and greases (fogs). high concentrations of fats, oils and greases in wastewater often initiate problems in wastewater treatment processes (becker et al., 1999; stoll and gupta, 1997). fogs often cause foul odours, the blockage of pipes and sewer lines. these problems are solved by the preliminary refining equipment, so-called grease traps. grease traps may sometimes fail to retain dissolved and emulsified fogs, allowing them to enter the water treatment system. an interesting strategy in present time is the use of lipase producing microorganisms in wastewater treatment system. lipases are hydrolytic enzymes that catalyze the cleavage of ester bonds in triglycerides, resulting in production of glycerol and free fatty acids. microbial lipases are produced by yeasts, fungi and bacteria, as extracellular and intracellular enzymes. the extracellular lipases from bacteria are interesting for their abilities to degrade fogs. in the present study, the degradation ability of commercial microbial product to degrade fogs under laboratory conditions was investigated. as substrates, four oils and two fats were used. 2. materials and methods the degradation ability of the commercial microbial products for grease separators was investigated. as substrates, four plant oils (palm oil, sunflower oil, olive oil and rape seed oil) and two animal fats (lard and beef fat) were used. 226 illková, k. et al. 2.1 commercial microbial product this commercial product is the mixture of bacteria, enzymes and detergents (illková et al., 2008). on the basis of previous study, it was found out that the product in the grease traps contain mixture of spore gram-positive bacteria, obviously bacillus sp. (gojković, 2009). 2.2 medium and growth conditions surface cultivation proceeded on spirit blue agar plates, to which tributyrin and tween 20 were added as a lipase substrate in ratio 1:1. incubation time was three days by 27 °c. this agar was used for the verification of the presence of spores of the lipolytic bacteria. medium for submerged cultivation contain per litre of distilled water 1.12 g k2hpo4; 0.48 g kh2po4; 5 g nacl; 0.1 g mgso4. 7h2o; 2 g (nh4)2so4 and 0.002 g edta. medium was autoclaved at 121 °c for 20 min. then the medium was supplemented with 1 ml plant oil and 1 g animal fats, as the natural substrate. medium was inoculated by commercial microbial product and was incubated under aerobic conditions at 25 °c, agitated at 160 rev/min for 14 days in erlenmeyer flasks in a shaker (el-bestawy et al., 2005). 2.3 verification of the presence of spores of lipolytic bacteria this verification was carried out on spirit blue agar plates. commercial product was diluted to the concentration 10-3, and then was filtered through bacteriological filter. filter was placed on the agar plates (gojković, 2009). a presence of spores of the lipolytic bacteria shows itself as a transparent halo around the colonies. 2.4 growth of the biomass growth of the biomass on various fats and oils substrates was examined spectrophotometrically at 650 nm. samples were taken away in definite time interval for four days and absorbencies were measured against blank (gojković, 2009). 2.5 enzyme assay the lipolytic activity was determined by using 0.5 ml culture in 0.65 ml 0.05 m phosphate buffer (ph 7.2) a 0.1 ml 0.0025 m p-nitrophenyllaurate in ethanol. the hydrolytic reaction was carried out at 37 °c for 30 min, after which 0.25 ml 0.1 m na2co3 was added. the mixture was centrifuged and the activity determined at 420 nm. one unit of lipase activity is defined as the amount of enzyme which liberates 1 µg p-nitrophenol from p-nitrophenyllaurate, as a substrate in 30 min under assay condition (nawani et al., 1998; sigurgísladóttir et. al., 1993). lipolytic activity was calculated on 1 mg of protein and expressed in the form of the specific activity. nova biotechnologica 9-3 (2009) 227 2.6 lipid degradation from each erlenmeyer flasks 20 ml culture medium was aseptically drawn and transferred to a separating funnel, where it was mixed with 20 ml of hexane. the mixture was agitated for 2 min and the upper layer was put into the clean and weighted beaker. the lower layer was re-extracted by a fresh 20 ml of hexane and the upper layer after the extraction was collected to the beaker again. the extract in the beaker was evaporated by heating at 100 °c. then the dry extracted lipids were weighted and dissolved in 50 ml of alcohol in the presence of phenolphthalein indicator. the solution was titrated with 0, 1 m koh until the developing of pink colour. the same procedure was repeated within 2, 6, 8, 10 and 14 days. the free fatty acids (%) in the sample, which indicates the lipid degradation and fatty acids utilization, was calculated according to this equation: m mcv acidsfattyfree kohkoh .1000 100... % =  here, vkoh is the volume of 0.1 m koh at the end point, ckoh actual concentration of the 0.1 m koh, m is the molecular weight of the oleic acid and m is the weight of the dry extract (illková et al., 2008; el-bestawy et al., 1998). 3. results and discussion the ability of commercial product to degrade various lipid substrates, occurring in wastewater, was tested. lipolytic activities, growth of the biomass, presence of spore and lipid degradation were investigated. 3.1 presence of spore for this test spirit blue agar was used. after three days of incubation it was found out that all bacteriological filters caught spore from commercial product. this effect was detected as a transparent halo around the colonies, fig. 1. fig. 1. appearance of colonies at the bacteriological filter. 3.2 growth of the biomass growth of the biomass was investigated by four plant oils (olive, palm and sunflower oil and rape seed oil) and two fats (lard and beef) during four days (fig. 2,3). 228 illková, k. et al. growth of the biomass for oil substrates 0 0,1 0,2 0,3 0,4 0,5 0,6 0,7 0,8 0,9 0 10 20 30 40 50 60 70 80 90 time (hours) to ta l s ol id (m g/ m l) sunflower oil olive oil palm oil rape seed oil fig. 2. growth of the biomass for various plant oil substrates. growth of the biomass for fat substrates 0 0,2 0,4 0,6 0,8 1 1,2 1,4 0 10 20 30 40 50 60 70 80 90 time (hours) to al s ol id (m g/ m l) lard beef fat fig. 3. growth of the biomass for various animal fat substrates. 3.3 lipolytic activity as substrate for lipase 0, 0025 m p-nitrophenyllaurate in ethanol was used, activity was measured spectrophotometrically at 420 nm. activity of lipases was determined as a dependence of absorbance on the time in the definite time interval at 37 °c. results for plant oils were expressed at mg of protein at table 1 and fig. 4 and for animal fats at table 2 and fig. 5. fig. 4. specific activity of lipases (mmol/min/mg protein). nova biotechnologica 9-3 (2009) 229 fig. 5. specific activity of lipases (mmol/min/mg protein). table 1. specific activity for plant oils (mmol/min/mg protein). table 2. specific activity for fats (mmol/min/mg protein). fats/hours 24 48 168 192 lard 0.084 0.032 0.387 0.005 beef fat 0.023 0.021 0.064 0.056 3.4 lipid degradation from the determination of lipid degradation and fatty acid utilization follows that commercial product has the ability to degrade the lipids and then utilize the fatty acids the highest increase of the free fatty acids (ffa) percentage for olive (47.6 %), palm (58.5 %) and rape seed oil (49.8 %) was observed after 72 hours. for sunflower oil (52.2 %) after 120 hours and for lard (88.6 %) and beef fat (86.5 %) after 96 hours, table 3. table 3. percent of free fatty acids during lipid degradation. quantity of the free fatty acids (%) during lipid degradation oils or fats/hours 48 72 96 120 192 216 olive 14.8 47.6 16.8 18.8 13.9 9.9 palm 14.2 58.5 49.8 26.1 12.4 10.9 rape seed 21.3 49.8 20.3 29.3 12.8 6.9 sunflower 18.2 36.6 12.5 52.5 10.3 7.9 lard 40.5 63.7 88.6 12.7 66.5 33.9 beef fat 74.6 83.4 86.5 70.9 33.5 27.3 oil /time (h) 24 48 72 168 192 216 olive 0.222 0.043 0.055 0.042 0.015 0.012 palm 0.111 0.114 0.042 0.008 0.012 rape seed 0.039 0.032 0.023 0.012 0.023 sunflower 0.043 0.042 0.053 0.027 0.030 230 illková, k. et al. 4. conclusions from the experimental results follows that the studied commercial microbial product for grease traps has the ability to degrade various plant oils and animal fats with different efficiency. best lipolytic activity was observed at palm oil, olive oil and lard, but best degrading substrates are rape seed oil and lard. growth of biomass was found out by all used substrates. total concentration of the biomass during cultivation differs, according to the sort of the substrate. it depends on the emulsifier properties of oils or fats. verification of the presence will be investigated in the other study. acknowledgement: this work has been supported by ministry of education, youth and sports under project msm 021630501 references becker, p., koster, d., popov, m.n., markossian, s., antranikian, g., markl, h.: the biodegradation of olive oil and treatment of lipid – rich wool wastewater under aerobic thermophilic condition. water res., 33, 1999, 653-660. el-bestawy, e., el-masry, m.h., el-adl, n.e.: the potentially of free gram – negative bacteria for removing oil and grease from contamined industrial effluents. world j. microbiol. biotechnol., 21, 2005, 815-822. gojković, ž.: studium přípravků do odlučovačů tuků. diplomová práce, vysoké učení technické v brně, fakulta chemická, 2009, 59 p. illková, k., omelková, j., vlčková, b.: lipid degradation and its application in lipid – containing wastewater. chem. listy, 99, 2008, 1234-2345. nawani, n., dosanjh, n. s., kaur, j.: a novel thermostable lipase from a thermophilic bacillus sp.: characterization and esterification studies. biotechnol. lett., 20, 1998, 997-1000. sigurgísladóttir, s., konráösdóttir, m., jónson, á., kristjánsson, j.k., matthiasson, e.: lipase activity of thermophilic bacteria from icelandic hot springs. biotechnol. lett., 15, 1993, 361-366. stoll, u., gupta, h.: management strategies for oil and grease residues. waste manage. res., 15, 1997, 23-32. instructions to authors submitting papers for the nova biotechnologica 9-3 (2009) 271 effect of chelating agents on phytoxicity and bioaccumulation of heavy metals in vascular plants miroslav horník1,2, jana guldanová1, martin pipíška1,2, jana marešová1, jozef augustín1,2 1department of biotechnology, university of ss. cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic (hornikm@ucm.sk) 2 consortium for environmental biotechnology and environmental chemistry, 418 špačince, 919 51, slovak republic abstract: in this work the effect of chelating agents ethylenediaminetetraacetate (edta) and nitrilotriacetate (nta) on phytotoxicity and bioaccumulation of cd and co in tobacco plants (nicotiana tabacum l.) hydroponically grown in diluted hoagland media (hm) spiked with 109cd and 60co was studied. speciation analysis using a program visual minteq showed, that the portion of bioavailable ionic me2+ forms significantly decreased in the presence of edta or nta in 25% hm for account of [me-edta]2or [me-nta]complexes. we found that the equimolar addition of edta or nta to 50 μmol/dm3 cdcl2 or cocl2 in hm positively diminished phytotoxicity of cd or co on tobacco plants. bioaccumulation of cd by tobacco roots during 8 d cultivation was minimally affected in the presence of equimolar concentrations of edta or nta to 10 μmol/dm3 cdcl2 in media. on the contrary, equimolar concentration of edta or nta added into hm caused considerable decrease of co uptake by tobacco roots. cadmium showed higher mobility in conductive tissues of tobacco plants than cobalt and the transport ratio in the presence of edta or nta increased 2-times or 3-times in comparison with control experiments (without addition of chelates), respectively. in the case of cobalt this effect was observed in a less extent. obtained data suggest the possibilities and constraints in the use of chelating agents in phytoextraction technologies in term of phytotoxicity, uptake and translocation of metals in plant tissues. key words: cadmium, cobalt, bioaccumulation, phytotoxicity, nicotiana tabacum, speciation 1. introduction heavy metals soil pollution is a serious worldwide problem and can be potentially harmful to human health via the food chain. in most cases, metals soil contamination results from anthropogenic activities such as mining, smelting, fertilizer application, and in the case of radionuclides from typical operations of nuclear fuel cycle, nuclear weapon testing and occasional nuclear disasters. the stricter implementation of environmental laws urges the development of costeffective soil remediation methods. traditional techniques of remediation are expensive and may cause secondary pollution. phytoremediation, the use of green plants to remove pollutants from soil, is one cost-effective method to remediate metal and radionuclide contaminated soils. the technical aspects of phytoremediation are described in numbers of review papers (see latest works in this area e.g. pilonsmits and leduc, 2009; vangronsveld et al., 2009) and monographs (see e.g. mackova et al., 2006; willey, 2007). phytoextraction as one of the most perspective phytoremediation method depends mainly on the bioavailability of toxic metals and radionuclides in the soil and the plant 272 horník, m. et al. capacity to accumulate these contaminants. therefore, some researchers have found that complexing ligands (e.g. edta, nta, edds and others) can solubilize the heavy metals with the purpose of making them available for uptake (salt et al., 1998), but they are not necessarily available for plant uptake (tandy et al., 2006). they redistribute surface contamination down the soil profile, causing a reduction in the concentration near the soil surface (robinson et al., 2003) and distribute the heavy metals within the entire root zone for uptake. in addition, some authors reported that complexes of me-chelate were less phytotoxic than free me2+ forms or protonated chelates (hernández-allica et al., 2007). our previous works studied the bioaccumulation of zn, co, cd or cs from nutrient solutions by roots of hydroponically cultivated sunflower (helianthus annuus l.), tobacco (nicotiana tabacum l.) and celery (apium graveolens l.) plants (horník et al., 2005; horník et al., 2007; horník et al., 2008) and radiocesium accumulation from contaminated soil by autochthonous vegetation of plants (pipíška et al., 2005). the aim of the current work was to investigate the influence of chelating agents ethylenediaminetetraacetic acid (edta) and nitrilotriacetic acid (nta) on cd and co phytotoxicity and bioaccumulation in tissues of hydroponically cultivated tobacco plants (nicotiana tabacum l.). bioaccumulation of cd and co ions in plants was analyzed by gamma-spectrometry using 109cd and 60co as radiotracers. 2. material and methods 2.1 plant material seeds of tobacco (n. tabacum l.) were germinated and grown in pots filled with granulated perlite as an inert carrier and watered with 25% strength hoagland nutrient medium (hoagland, 1920) at light/dark photoperiod 12/12 h (2 000 lx) and 22°c. the composition of the full strength (100%) nutrient solution was (in mg/dm3) mgso4.7h2o – 370; kno3 – 404; cacl2 – 444; nah2po4.2h2o – 292; na2hpo4.12h2o – 46.5; feso4.7h2o – 17.9; nano3 – 340; nh4cl – 214; nh4no3 – 160; h3bo3 – 8.5; na2moo4.2h2o – 0.06; mnso4.5h2o – 5.0; znso4.7h2o – 0.66; cuso4.5h2o – 0.8 (ph 6). after 8 weeks pre-cultivation seedlings were gently removed from perlite and roots were washed free of any adhering perlite granules by deionized water and used in bioaccumulation experiments. 2.2 bioaccumulation experiments and cultivation conditions plants from pre-cultivation phase were transferred into vessels with a cover to protect plant roots against lights and cultivated for 8 days in 25% strength hoagland medium containing cdcl2 or cocl2 spiked with 109cd or 60co. there were two treatments without or with chelating agents edta or nta. the ph of nutrient solutions was adjusted to 6.0 using 1 m naoh. bioaccumulation experiments were carried out in triplicate series at photoperiod 12/12 h (2000 lx) and 22°c. in time intervals samples of nutrient solution were taken and 109cd or 60co radioactivity was measured by gamma-spectrometry. at the end of the experiments plants were nova biotechnologica 9-3 (2009) 273 harvested, roots were carefully rinsed in deionized water and incorporated radioactivity in roots, stems and leaves was measured. plant parts were then oven dried (at 60°c for 24 hours) and dry weights were determined. growth value (gv) was calculated during the experiments as a ratio between m(i) – m(t) and m(i), where m(i) or m(t) are fresh weight of plants at the start or end of experiments, respectively. 2.3 speciation modelling for in silico estimations of cd and co speciation in nutrient solutions as a function of total salt concentration, the presence or absence of chelating agents (edta or nta), solution ph and temperature were carried out with visual minteq (version 2.53). this speciation modelling program allows the calculation of complexes [me-edta] or [me-nta] portion in cultivation media for specified conditions. 2.4 radiometric analysis gamma spectrometric scintillation detectors 54bp54/2-x and 76bp76/3 with well type crystal nai(tl) (scionix, netherlands) and data processing software scintivision32 (ortec, usa) were used for 109cd and 60co determination in plant parts and cultivation media. a library of radionuclides was built by selecting characteristic γ-ray peaks (88.04 kev for 109cd and 1173.24 kev or 1332.50 kev for 60co) for energy and efficiency calibration. standardized 109cdcl2 and 60cocl2 solutions were obtained from czech metrological institute (czech republic). 3. results and discussion 3.1 effect of chelating agents on cd and co phytotoxicity in our work for calculation of cd and co ionic forms in nutrient media the program visual minteq ver. 2.53 we used. however, this evaluation has to be considered with caution, because the modelling program does not include the participation of the plant. moreover, the high concentrations of edta and nta used here likely also mask the effects of the exudates from the roots. plant exudates can contribute to changing the ph, the eh, and the predominant chemical species of the toxins of concern (niu et al., 2007). even so, we used the simulation results as a first approximation to the chemical mechanisms in the near-root zone. we found that in used hoagland media (hm) at ph 6.0 and 22°c more than 95% of co was found as bioavailable me2+ ions. only 78% of cd was found in the form of cd2+ ions, whereby also significant proportion represented ionic cdcl+ form (12.7%) and cdhpo4 form (6.4%). complexing ligands significantly decreased the concentration of cationic co2+ or cd2+ forms and the concentration of [me-edta]2or [me-nta]complex forms increased. for evaluation of cd and co phytotoxic effect on tobacco plants the calculation of growth value (the ratio of fresh weight of plants at the start or end of experiments 274 horník, m. et al. difference to fresh weight of plants at the start of experiments) and macro and microscopy observation of phytotoxic symptoms on leaves were used. 0,0 0,2 0,4 0,6 0,8 1,0 w ith 5 0 μ m n t a 50 μm50 μm50 μm20 μm10 μm w ith 5 0 μ m e d t a g v concentration of cdcl2 in medium 0 μm without chelating agents 0,0 0,2 0,4 0,6 0,8 1,0 w ith 5 0 μ m n t a 50 μμ50 μμ50 μμ20 μμ10 μμ g v concentration of cocl2 in medium 0 μμ w ith 5 0 μ m e d t a without chelating agents fig. 1. the evaluation of phytotoxicity effect of cd (a) and co (b) on the basis of growth value (gv) of tobacco plants (n. tabacum l.) after 8 d cultivation in 25% hm without or with addition of edta or nta at illumination 12/12 day/night period (2 000 lx), ph 6.0 and 22°c. fig. 2. phytotoxicity effect of cadmium (die-back of leaves) in tobacco plants (n. tabacum l.) after 8 d cultivation at illumination 12/12 day/night period (2 000 lx) in 25% hm, ph 6 containing: a. 0 μmol/dm3 cdcl2; b. 10 μmol/dm3 cdcl2; c. 20 μmol/dm3 cdcl2; d. 50 μmol/dm3 cdcl2; e. 50 μmol/dm3 cdcl2 + 50 μmol/dm3 edta; f. 50 μmol/dm3 cdcl2 + 50 μmol/dm3 nta. gv (growth value): a. 0.70; b. 0.69; c. 0.47; d. 0.39; e. 0.59; f. 0.56. fig. 1 shows, that the equimolar addition of edta or nta to 50 μmol/dm3 cdcl2 or cocl2 in hoagland media positively diminished phytotoxicity effect of cd or co on tobacco plants growth evaluated on the basis of growth values (gv) calculation. a b c a b d e f nova biotechnologica 9-3 (2009) 275 fig. 2 and 3 depict the die-back of plant leaves in the presence of cd or chlorosis of leaves in the presence of co in media as well as the effect of chelating agents on these processes. phytotoxicity symptoms (die-back of leaves) and lower growth value were observed at 20 or 50 μmol/dm3 cdcl2 concentrations in media (fig. 1a, 2c, 2d). after 50 μmol/dm3 co-treatment, plants yellowed with typical chlorotic ringspot symptoms and lower growth value than the control were found (fig. 1b, 3d). moreover, we found that this co-treatment used in our experiment had impact on trichomes size and density (fig. 4a). lefèvre et al. (2009) found that more than 30% of accumulated cd was found at the leaf surface and accumulated in trichomes. on the other side bakkaus et al. (2005) reported that cobalt was mainly located around the leaf veins. at the end of the 50 μmol/dm3 cd-treatment or co-treatment with addition of edta or nta in media, no sign of phytotoxicity was observed (fig. 2e, 2f, 3e, 3f and 4b). a b c d e f fig. 3. phytotoxicity effect of cobalt (chlorosis of leaves) in tobacco (n. tabacum l.) plants after 8 d cultivation at illumination 12/12 day/night period (2 000 lx) in 25% hm, ph 6 containing: a. 0 μmol/dm3 cocl2; b. 10 μmol/dm3 cocl2; c. 20 μmol/dm3 cocl2; d. 50 μmol/dm3 cocl2; e. 50 μmol/dm3 cocl2 + 50 μmol/dm3 edta; f. 50 μmol/dm3 cocl2 + 50 μmol/dm3 nta. gv (growth value): a. 0.70; b. 0.72; c. 0.59; d. 0.41; e. 0.57; f. 0.63. we suggest that the decrease of metal concentration in me2+ form caused by chelating agents in nutrient media and the formation of [me-ligand] complexes in media could diminish phytotoxic effect. similar effect was also found by others authors (see e.g. hernández-allica et al., 2007). this fact could be helpful in phytoremediation of contaminated soils with high concentration of toxic metals, where most plants can not grow under normal conditions. 276 horník, m. et al. a1 a2 a3 fig. 4. chlorosis of tobacco leaves (n. tabacum l.) after 8 d cultivation at illumination 12/12 day/night period (2 000 lx) in 25% hm, ph 6 containing: a. 50 μmol/dm3 cocl2; b. 50 μmol/dm3 cocl2 + 50 μmol/dm3 edta. macroand microscopic photos: 1. second the youngest tobacco leaf; 2. surface of adaxial leaf section (magnification 50x); 3. adaxial and abaxial leaf trichomes (magnification 100x). b1 b2 b3 3.2 effect of chelating agents on cd and co bioaccumulation bioaccumulation of cd by tobacco roots during 8 d cultivation was minimally affected in the presence of edta or nta equimolar concentrations to 10 μmol/dm3 cdcl2 in media. on the contrary, equimolar concentration of edta or nta added into hoagland media caused considerable decrease of co uptake by tobacco roots (fig. 5a). calculated speciation of cd and co in used hoagland medium (hm) is depicted in fig. 5b. for evaluation of metals mobility in conductive tissues of plants in the term of metal translocation efficiency we established non-dimensional transport ratio (tr), which represent the ratio of metal concentration in aboveground part of plants [me]shoot to metal concentration in root system of plants [me]root. cadmium showed higher mobility in conductive tissues of tobacco plants than cobalt and the transport ratio in the presence of edta or nta increased 2-times or 3-times in comparison with control experiments (without addition of chelates), respectively (fig. 6). in the case of cobalt this effect was observed in a less extent. some authors reported that metal uptake is related to the availability of metals in soils and the addition of natural and/or synthetic chelators into soil could increase uptake and translocation of metals (see e.g. quartacci et al. (2007). however, the amendment with non-biodegradable chelants of high metal-binding capacity, the high persistence of chelates and their nova biotechnologica 9-3 (2009) 277 potential leaching to groundwater pose severe environmental concerns connected with the use of synthetic chelating agents such as edta and its derivatives. quartacci et al. (2007) found that nta and mainly edds were high effective in enhancing the concentrations of cd, cu, pb and zn in brassica carinata shoots. 0 20 40 60 80 100 co b io ac cu m ul at io n [% ] control edta nta cd 0 20 40 60 80 100 [co-chelate]co2+[cd-chelate] p or tio n in m ed ia [% ] speciation form control edta nta cd2+ a b fig. 5. a. effect of edta and nta on cd and co uptake by tobacco roots (n. tabacum l.). data after 8 d cultivation at 22°c and illumination 12/12 day/night period (2 000 lx) in 25% hm ph 6.0 containing 10 μmol/dm3 cocl2 or 10 μmol/dm3 cdcl2 and equimolar edta or nta. b. portion of me2+ (cd2+ or co2+) and [me-chelate] ([me-edta]2or [me-nta]-) forms in cultivation media at 22°c and ph 6.0. speciation of cd and co was calculated by program visual minteq ver. 2.53. 0,0 0,1 0,2 0,3 0,4 0,5 co [m e] sh oo t/[ m e] ro ot control edta nta cd fig. 6. effect of edta and nta on translocation of cd and co from roots to shoots (tr) of tobacco (n. tabacum l.) after 8 d plant cultivation in 25% hm containing 10 μmol/dm3 mecl2 (me = cd or co) without or with equimolar addition of edta or nta, ph 6.0 at illumination 12/12 day/night period (2 000 lx) and 22°c. 4. conclusions the results from hydroponic cultivation of tobacco plants (n. tabacum) indicate that chelating agents (edta and nta) are able to decrease of cd and co phytotoxicity, and on the other side these agents can increase of metal translocation from roots to shoots of tobacco plants. this fact can positively affect all processes involved in phytoremediation of contaminated environment with toxic metals or radionuclides. 278 horník, m. et al. references bakkaus, e., gouget, b., gallien, j.-p., khodja, h., carrot, f., morel, j.l., collins, r.: concentration and distribution of cobalt in higher plants: the use of micro-pixe spectroscopy. nucl. instrum. methods phys. res. b, 231, 2005, 350-356. hernández-allica, j., garbisu, c., barrutia, o., becerril, j.m.: edta-induced heavy metal accumulation and phytotoxicity in cardoon plants. environ. exp. bot., 60, 2007, s. 26-32. hoagland, d.r.: optimum nutrient solution for plants. science, 52, 1920, 562564. horník, m., pipíška, m., sekáčová, j., augustín, j.: determination of long distance transport of cs+, co2+ and zn2+ ions in vascular plants by autoradiography and gamma-spectrometry. nova biotechnol., vii-1, 2007, 33-40. horník, m., pipíška, m., vrtoch, ľ., sekáčová, j., augustín, j., lesný, j.: influence of complexing ligands on zn uptake and translocation in tobacco and celery plants. acta agronomica ovariensis, 2008, 50, 65-71. horník, m., pipíška, m., vrtoch, ľ., augustín, j., lesný, j.: bioaccumulation of 137cs and 60co by helianthus annuus. nukleonika, 50, 2005, s49-s52. lefèvre, i., marchal, g., meerts, p., corréal, e., lutts, s.: chloride salinity reduces cadmium accumulation by the mediterranean halophyte species atriplex halimus l. environ. exp. bot., 65, 2009, 142-152. mackova, m., dowling, d., macek, t.: phytoremediation rhizoremediation. springer, dordrecht, the netherlands, 2006, 300 pp. niu, z.x., sun, l.n., sun, t.h., li, y.s., wang, h.: evaluation of phytoextracting cadmium and lead by sunflower, ricinus, alfalfa and mustard in hydroponic culture. j. environ. sci., 19, 2007, 961-967. pilon-smits, e.a.h., leduc, d.l.: phytoremediation of selenium using transgenic plants. curr. opin. biotechnol., 20, 2009, 207-212. pipíška, m., horník, m, lesný, j., augustín, j.: transfer rádiocézia 137cs z kontaminovanej neobrábanej pôdy do voľne rastúcej vegetácie. agriculture (poľnohospodárstvo), 51, 2005, 470-478. quartacci, m.f., irtelli, b., baker, a.j.m., navari-izzo, f.: the use of nta and edds for enhanced phytoextraction of metals from a multiply contaminated soil by brassica carinata. chemosphere, 68, 2007, 1920-1928. salt, d.e., smith, r.d., raskin, i.: phytoremediation. annu. rev. plant physiol. plant mol. biol., 49, 1998, 643-668. vangronsveld, j., herzig, r., weyens, n., boulet, j., adriaensen, k., ruttens, a., thewys, t., vassilev, a., meers, e., nehnevajova, e., van der lelie, d., mench, m.: phytoremediation of contaminated soils and groundwater: lessons from the field. environ. sci. poll. res., (in press). willey, n.: phytoremediation. methods and reviews. humana press, new jersey, usa, 2007, 478 pp. microsoft word gasparova nb 9-3.doc nova biotechnologica 9-3 (2009) 349 reactions of 4-hydroxycoumarin with heterocyclic aldehydes renata gašparová1, katarína kotlebová1, margita lácová2 1department of chemistry, university of ss. cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic (gasparor@ucm.sk) 2department of organic chemistry, comenius university, mlynská dolina ch-2, bratislava, sk-842 15, slovak republic (lacova@fns.uniba.sk) abstract: reactions of 4-hydroxycoumarin 1 with heterocyclic aldehydes 2-4 led to bis-4-hydroxycoumarin derivatives 5-7 under microwave irradiation as well as under the classical heating. the subsequent reactions of products 5-7 are described. 4,4’-epoxydicoumarins 8, 9 were prepared by the reaction of 5-7 in acetic acid / p-toluenesulfonic acid medium. compound 10 was prepared by the reaction of 5 in acetic anhydride in the presence sodium acetate. dioxocine-1,15-dione 11 was prepared by the reaction of 6 with dichloromethane in sodium hydroxide-toluene. key words: coumarin, 4-oxo-4h-chromene, furan, furo[3,2-b]pyrrole, microwave 1. introduction coumarins are biologicaly active compounds with antifungal, antineoplastic, antibacterial, spasmolytic or cytotoxic activity (stanchev et al., 2007; jung et al., 2004). 4-hydroxycoumarin 1 and its derivatives, e.g. warfarin and dicoumarol are known as anticoagulants. 4-hydroxycoumarin 1 reacts with aromatic or aliphatic aldehydes to give bis-4hydroxycoumarin derivatives (giovani et al., 1991; manolov et al., 2006; mao et al., 2002), which are interesting for their biological activity and they can serve as intermediates for synthesis of various heterocycles (hamdi et al., 2008; yamashita et al., 1987). 2. experimental melting points of products were determined on a kofler hot plate apparatus and are uncorrected. all solvents were predistilled and dried appropriately prior to use. 1h nmr spectra were obtained on a 300 mhz spectrometer varian gemini 2000 in cdcl3 or dmso-d6 or cf3cood with tetramethylsilane as an internal standard. all microwave experiments were performed in a panasonic nn-e205 type microwave oven. the apparatus was adapted for laboratory applications; n-hexane was used as coolant for the condenser. 2.1 general procedure for 5 and 6 a) classical heating. a mixture of 4-hydroxycoumarin 1 (0.002 mol) and 6-r-4-oxo4h-chromen-3-carbaldehyde 2 (or 5-arylfuran-2-carbaldehyde 3) (0.001 mol) in acetic 350 gašparová, r. et al. anhydride (15 cm3), in the presence of a catalytic amount of k2co3 (or acok) was heated at 80 ºc for 3.5 h. after cooling the solid product was filtered off and crystallized from ethanol. o o oh r-cho r oo o o oh hoac2o, acok (k2co3) r 5 6-r1-4-oxo-4h-chromen-3-yl 6 5-arylfuran-2-yl 7 5-methoxycarbonylfuro[3,2-b]pyrrol-2-yl 1 2-4 r oo o o o o o o o oac oac o o oac br r 8 6-r1-4-oxo-4h-chromen-3-yl 9 5-arylfuran-2-yl 10 ac2o acoh p-tsoh scheme 1 acona r oo o o o r 11 5-(4-iodophenyl)lfuran-2-yl o naoh toluene b) microwave method. a mixture of 4-hydroxycoumarin 1 (0.002 mol) and 6-r-4oxo-4h-chromen-3-carbaldehyde 2 (or 5-arylfuran-2-carbaldehyde 3) (0.001 mol) in acetic anhydride (4 cm3), in the presence of a catalytic amount of k2co3 (or acok) was irradiated in microwave oven for 4 min. the work-up was the same as described above. 2.1.1 3,3'-[(4-oxo-4h-chromen-3-yl)methylene]bis(4-hydroxy-2-oxo-2h-chromen-2one) 5a for c28h16o8 (480.4): mp: 275-280 °c; react. time 3.5h (a), 4min (b); yield: 81% (a), 82% (b); 1h nmr (cdcl3): 6.01 (d, 1h, ch j = 1.5 hz); 7.34-7.36 (m, 1h, h-6); 7.39 (dd, 4h, h-8´, h-8´´, h-6´, h-6´´, 3j = 7.97 hz); 7.46 (d, 1h, h-8, j = 8.25 hz); 7.59-7.61 (m, 2h, h-7´, h-7´´); 7.67 (m, 1h, h-7); 7.92 (d, 1h, h-2, j = 1.7 hz); 8.04 (dd, 2h, h-5´, h-5´´, j = 7.9 hz); 8.11 (dd, 1h, h-5, j = 7.9 hz); 11.50 (bs, 2h, oh) 2.1.2 3,3'-[(6-methyl-4-oxo-4h-chromen-3-yl)methylene]bis(4-hydroxy-2-oxo-2hchromen-2-one) 5b for c29h19o8 (495.5): mp: 276-278 °c; react. time 3.5h (a); yield: 79% (a); 1h nmr (dmso-d6): 2.38 (s, 3h, ch3); 6.07 (d, 1h, ch, j = 1.5 hz); 7.19 (dd, 2h, h8´, h-8´´, j = 7.5, 1.1 hz); 7.24 (dd, 2h, h-6´, h-6´´, j = 7.5, 0.9 hz); 7.46 (ddd, 2h, nova biotechnologica 9-3 (2009) 351 h-7´, h-7´´, j = 8.2 , 1.5 hz); 7.47-7.50 (m, 1h, h-7); 7.55 (dd, 1h, h-8, j = 8.6, 1.6 hz); 7.69 (d, 1h, h-5, j = 1.5 hz); 7.78 (dd, 2h, h-5´, h-5´´, j = 7.9, 1.5 hz); 7.83 (d, 1h, h-2, j = 1.5 hz); 17,2 (bs, 2h, oh) 2.1.3 3,3´-[(5-(4-chlorophenyl)furan-2-yl)methylene]bis(4-hydroxy-2h-chromen-2one) 6a for c29h17clo7 (512.9): mp: 265-269 °c; react. time 93h (a), 1.5h (b); yield: 68% (a), 70% (b); 1h nmr (dmso-d6): 5.15 (s, 1h, ch); 6.52 (d, 1h, h – 4, j = 3.3 hz); 6.91 (d, 1h, h – 3, j = 3.3 hz); 7.41 (d, 2h, ar h, j = 8.5 hz); 7.54 – 7.57 (m, 6h, ar – h); 7.77 (ddd, 2h, h – 7´, j = 8.7, 1.2 hz); 8.43 (dd, 2h, h – 5´, j = 8.5, 1.3 hz). 2.1.4 3,3´-[(5-(4-nitrophenyl)furan-2-yl)methylene]bis(4-hydroxy-2h-chromen-2one) 6b for c29h17no9 (457.5): mp: 317-319 °c; react. time 51h (a), 1.5h (b); yield: 60% (a), 62% (b); 1h nmr (dmso-d6): 5.19 (s, 1h, ch); 6.65 (d, 1h, h – 4, j = 3.3 hz); 7.23 (d, 1h, h – 3, j = 3.3 hz); 7.54 – 7.57 (m, 8h, ar h); 7.82 – 7.84 (m, 5h, ar h); 8.24 (d, 2h, h –8´´, j = 8.3 hz). 2.1.5 3,3´-({5-[4-(3-trifluoromethyl)phenyl]furan-2-yl}methylene)bis(4-hydroxy-2hchromen-2-one) 6c for c30h17f3o7 (546.5): mp: 257-260 °c; react. time 70h (a), 1.5h (b); yield: 50% (a), 51% (b); 1h nmr (dmso-d6): 5.17 (s, 1h, ch); 6.65 (d, 1h, h – 4, j = 3.3 hz); 7.11 (d, 1h, h – 3, j = 3.3 hz); 7.58 – 7.61 (m, 5h, ar h); 7.77 – 7.83 (m, 5h, ar h); 8.44 (d, 2h, h –8´´, j = 8.4 hz). 2.1.6 3,3´-[(5-(4-iodophenyl)furan-2-yl)methylene]bis(4-hydroxy-2h-chromen-2-one) 6d for c29h17io7 (604.4): mp: 248-252 °c; react. time 70h (a), 1.5h (b); yield: 51% (a), 53% (b); 1h nmr (dmso-d6): 5.14 (s, 1h, ch); 6.52 (d, 1h, h – 4, j = 3.3 hz); 6.92 (d, 1h, h – 3, j = 3.3 hz); 7.35 (d, 2h, ar h, j = 8,7 hz); 7.51 – 7.59 (m, 4h, h-6´,h-8´); 7.73 (d, 2h, ar-h j = 8.7 hz); 7.83 (ddd, 2h, h – 7´, j = 8.7, 1.5 hz); 8.42 (dd, 2h, h – 5´, j = 8.4, 1.2 hz). 2.2 synthesis of methyl 2-[bis(4-hydroxy-2h-chromen-3-yl)methyl]-4hfuro[3,2-b]pyrrole-5-carboxylate 7 a) classical heating. a mixture of 4-hydroxycoumarin 1 (0.002 mol) and methyl 2formyl-4h-furo[3,2-b]pyrrole-5-carboxylate 4 (0.001 mol) in pyridine (15 cm3) was heated at 105 ºc for 3 h. after cooling the solid product was filtered off and crystallized from ethanol. b) microwave method. a mixture of 4-hydroxycoumarin 1 (0.002 mol) and 2-formyl4h-furo[3,2-b]pyrrole-5-carboxylate 4 (0.001 mol) in pyridine (4 cm3) was irradiated in microwave oven for 3 min. the work-up was the same as described above. 352 gašparová, r. et al. for c27h15o9n (497.4): mp: 275-280 °c; react. time 3h (a), 3 min (b); yield: 52% (a), 56% (b); 1h nmr (dmso-d6): 3.89 (s, 3h, ch3); 6.90 (s, 1h, ch); 7.33-7.40 (m, 4h, ar-h); 7.71-7.79 (m, 2h, ar-h); 7.97 (m, 2h, ar-h); 8.28 (s, 1h, h-3); 8.66 (s, 1h, h-6); 9.05 (s, 1h, nh); 12.46 (d, 2h, 2 oh). 2.3 general procedure for 8 and 9 compound 5 (or 6) (0.2 mmol) in acetic acid (5 cm3) and catalytic amount of ptoluenesulfonic acid was heated at 80°c. after cooling the solid was filtered off and crystallized in ethanol. 2.3.1 3,3´-[(4-oxo-4h-chromen-3-yl)methylene]-4,4´-epoxydicoumarin 8 for c28h14o7 (462.4): mp: 330-335 °c; react. time 2.5h; yield: 92%; 1h nmr (dmso-d6): 4.77 (s, 1h, ch; 7.41-7.42 (m, 1h, h-6); 7.51-7.78 (m, 4h, h-8´, h-8´´, h-6´, h-6´´); 7.66 (d, 1h, h-8, j = 8,4 hz); 7.76-7.78 (m, 3h, h-7´, h-7´´); 7.88 (d, 1h, h-5, j = 7,8 hz); 8.45 (d, 2h, h-5´, h-5´´, j = 7.8 hz); 8.71 (s, 1h, h-2). 2.3.2 3,3´-[(5-(4-nitrophenyl)furan-2-yl)methylene]-4,4´-epoxydicoumarin 9 for c28h14o7 (439.4): mp: 322-325 °c; react. time 6h; yield: 62%; 1h nmr (dmso-d6): 5.41 (s, 1h, ch); 6.58 (d, 1h, h – 4, j = 3.4 hz); 7.10 (d, 1h, h – 3, j = 3.4 hz); 7.35 – 7.50 (m, 6h, ar h); 7.62 – 7.74 (m, 4h, ar h); 8.10 – 8.13 (m, 2h, h – 3´, 5´). 2.4 synthesis of 2,4´,4´´-triacethyl-3-[bis(4-hydroxy-2-oxo-2hchromen-3-yl)methyl]-chromen-4-one 10 a mixture of 4-hydroxycoumarin 1 (0.002 mol) and 6-bromo-4-oxo-4h-chromen3-carbaldehyde 2 in acetic anhydride (5 cm3) and catalytic amount of sodium acetate was heated at 80 ºc for 4.5 h. after cooling the solid product was filtered off and crystallized from ethanol. for c34h21bro12 (701.4): mp: 158-163 °c; yield: 66%; 1h nmr (cdcl3): 2.09 (s, 3h, ch3); 2 x 2.18 (s, 3h, ch3); 7.12 (d, 1h, h-8, j = 8.5 hz); 7.35-7.41 (m, 4h, h6´, h-6´´, h-8´, h-8´´); 7.63-7.67 (m, 2h, h-7´, h-7´´); 7.66 (d, 1h, h-5, j = 2.4 hz); 7.78 (s, 1h, h-2); 7.96-8.07 (m, 3h, h-5´, h-5´´, h-7). 2.5 synthesis of 16-[5-(4-iodophenyl)furan-2-yl]-1h,15h,16hdibenzopyrano[3,4-g:4'3'-d]dioxocine-1,15-dione 11 a mixture of compound 6d (0.4 mmol), dichloromethane (0.8 mmol) and sodium hydroxide (0.8 mmol) in toluene (3 cm3) was heated at 60°c for 117 h. after cooling the solid was filtered off and crystallized in ethanol. for c30h17io7 (616.4): mp: ›350 °c; yield: 47%; 1h nmr (cf3cood): 4.36 (s, 2h, ch2); 5.32 (s, 1h, ch); 6.57 (d, 1h, h – 3, j = 3.3 hz); 7.26 –7.51 (m, 9h, h – 4, ar h); 7.64 – 7.70 (m, 2h, h -3´,5´); 8.10 – 8.13 (m, 2h, h 2´´, 12´´). nova biotechnologica 9-3 (2009) 353 3. results and discussion reaction of 1 with 6-substituted 4-oxo-4h-chromene-3-carbaldehydes 2 led to bis(4-hydroxy-2-oxo-2h-chromen-2-ones 5 in 79-81% yields after 3.5h of heating. microwave-assisted method gave the comparable yield of 5a (82%), but the reaction time was remarkably shortened (4min). the use of 5-arylfuran-2-carbaldehydes 3 in reaction with 1 led to derivatives 6 in 50-68 % yields.. the effect of microwave irradiation was manifested in the remarkable shortening of reaction time from 51-93 h under classical heating to 1.5h in microwave oven. when 4-hydroxycoumarin 1 was treated with methyl 2-formyl-4h-furo[3,2b]pyrrole-5-carboxylate 4 in pyridine either by classical heating for 3h or in microwave oven for 4 min, product 7 was obtained in comparable yields (52% and 56%, respectively). epoxycoumarins 8 and 9 were obtained in 92% and 62 % yields, respectively by the dehydratation of 5 or 6 in acetic acid / p-toluenesulfonic acid medium. the heating of 4-hydroxycoumarin 1 and 6-bromo-4-oxo-4h-chromen-3carbaldehyde in acetic anhydride led to 3-acetyloxy derivative 10 in 66% yield. dioxocine-1,15-dione 11 was prepared in 47% yield by reaction of 6d with dichloromethane and sodium hydroxide in toluene. the reaction required long reaction time (117 h). the pursuit to shorter the reaction time by the influence of microwave irradiation was not successful and only decomposition polymeric product was isolated. all structures were confirmed by 1h nmr spectra. 4. conclusions 4-hydroxycoumarin 1 reacted with heterocyclic aldehydes 2-4 to give bisderivatives 5-7, which served as intermediates for synthesis of epoxycoumarins 8, 9, 2,4´,4´´-triacethylderivative 10 and dioxocine-1,15-dione 11, respectively. microwave irradiation has proved to be a suitable method for enhancement of reactions of 1 with aldehydes. acknowledgements: this work was supported by the slovak research agency under the contracts no. vega 1/1005/09 and apvv-0006-07 references giovani, a., cravotto, g., tagliapietra, s., ferraro, s., nano, g. m., palisano, g.: synthesis of 3-alkyl-4-hydroxycoumarins by reductive fragmentation of 3,3´-alkylidene-4,4´-dihydroxybis[coumarins]. helv. chim. acta, 74, 1991, 1451-1458. hamdi, n., puerta, m. c., valerga, p.: synthesis, structure, antimicrobial and antioxidant investigations of dikumarol and related compounds. eur. j. med. chem., 43, 2008, 2541-2548. jung, j. ch., lee, j. h., oh, s., leed, j. g., parkb, o. s.: synthesis and antitumor activity of 4-hydroxycoumarin derivatives. bioorg. med. chem. lett., 14, 2004, 5527–5531. 354 gašparová, r. et al. manolov, i., maichle-moessmer, c., danchev, n.: synthesis, structure, toxicological and pharmacological investigations of 4-hydroxycoumarin derivatives. eur. j. med. chem., 41, 2006, 882-890. mao, p.ch.m, mouscadet, j. f., leh, h., auclair, ch., hsu, l.y.: chemical modification of coumarin dimer and hiv-1 integrase inhibitory activity. chem. pharm. bull., 50, 2002, 1634-1637. stanchev, s., momekov, g., jensen, f., manolov, i.: synthesis, computational study and cytotoxic activity of new 4-hydroxycoumarin derivatives. eur. j. med. chem., 20, 2007, 1-13. yamashita, j., takeda, s., matsumoto, h., unemi, n., yasumoto, m.: studies on antitumor agents. vii. antitumor activities of o-alkoxyalkyl derivatives of 2´-deoxy-5-trifluoromethyluridine. chem. pharm. bull., 35, 1987, 2373-2381. microsoft word urgeova nb 9-3.doc nova biotechnologica 9-3 (2009) 327 secondary metabolites with antibacterial effects from leaves of different hop cultivars during vegetal periods eva ürgeová, ľudovít polívka department of biotechnology, university of ss. cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic (eva.urgeova@ucm.sk) abstract: according to the latest eu regulations it is necessary to cut down the consumption of chemically based pesticides. several research programmes are focussed on the study of secondary metabolites of plants, which have antimicrobial or antifungal activity against microbial phytopathogens. other reasons for using of natural biocides are the growth of resistance of phytopathogens against several pesticides; broaden microbial attacks to significant agricultural product for food industry due to the climate changes. the presentation is focussed on the determination of the contents of secondary metabolitesleaves of several cultivars of hop – polyphenols and flavonoids. methanol crude leaves extracts were tested on biocide effects against selected microbial phytopathogens. key words: hop, extracts, polyphenols, flavonoids, antibacterial effect 1. introduction according to the latest eu regulations it is necessary to cut down the consumption of chemically based pesticides. several research programmes are focussed on the study of secondary metabolites of plants which have antibacterial or antifungal activity against microbial phytopathogens. the plants synthesise and accumulate various secondary metabolites which are characterised by the diversity of their chemical structures, restricted distribution and protective function for an organism. in this perspective, increasing attention is being paid to the plant called common hop (humulus lupulus l) (moir, 2000). hop compounds are effective inhibitors of gram-positive bacteria (battacharya et al., 2003), mycobacteria (stavri et al., 2004) and protozoa (srinivasan et al., 2005). in addition, xanthohumol has been reported to be a broad spectrum anti-infective agent working against many bacteria, viruses, fungi, and protozoa (gerhäuser, 2005). in the study of antimicrobial activity of essential oils from the hop plant, lagezaal et al. (1992) identified their inhibitive influence on gram-positive bacteria bacillus subtilis and staphylococcus aureus, as well as on the fungus trichophyton mentagrophyles. one of the big groups of substances contained in the hop plant is the group of polyphenol compounds, chalkones, flavanols, flavonols, and antocyanides (hofta et. al., 2004). content of polyphenols in the leaves can be of potential benefit when speaking of using these as raw material for extraction of these substances (čeh et al., 2007). the most interesting of them are flavonoids, belonging to the most widespread compounds in nature. 328 ürgeová, e. and polívka, ľ. the aim of these experiments was to test the influence of the vegetation period on the content of some secondary metabolites of hop, polyphenol compounds, and flavonoids, which display a wide range of biological and pharmacological properties. biocide activity of extracts from hop leaves was tested, too. 2. material and methods 2.1 plant material the samples of hop taken from the gene bank of the slovak republic in the institute of plant production, piešťany (cvrv – vúrv) were tested. we used the following cultivars of hop: osvald’s clones 31 (k-31) and 72 (k-72), bor, sládek, zlatan, and premiant. we collected the samples at the beginning of vegetal period (april 08), before (june 08) and during the flowering time (july 08) and at the end of the vegetal period (september 08). 2.2 the tested phytopathogene bacteria for the purpose of this study we used phytopathogenic microorganisms erwinia mallotivora ccm 2890, obtained from the czech collection of microorganisms of the masaryk university, faculty of science, brno, clavibacter michiganensis subsp. sepedonicus cppb a098, erwinia amylovora cppb a203, pectobacterium carotovorum pv. carotovorum cppb ao86, pseudomonas syringae pv. syringae cppb a171, and xanthomonas vesicatoria cppb a085, obtained from the collection of phytopathogenic bacteria and referential antidotes (cppb) at the crop research institute in prague-ruzyně, czech republic. bacteria were kept as a stock culture in the refrigerator at the temperature of 8° c. 2.3 extraction the extracts were prepared by methanol extraction in the ratio of 1:20. after extraction it was evaporated on the vacuum rotary evaporator. we dissolved this matter in ethyl acetate and water in ratio 1:1. the organic phase was evaporated. dry matter was dissolved in methanol (4:3 w/v) and stored in a cold store. 2.4 method for testing biocide effect of extracts the antibacterial activity of extracts was determined in vitro against a variety of phytopathogene bacteria. antimicrobial activities were tested by the standard plate diffusion method (piddock, 1989) and zones of inhibition were measured in mm. the biocide effect was compared with the effect of 1.2 % w/v solution of tmtd (tetramethylthiuram disulfide), active substance of commercial pesticides. plant extracts (15 μl) were placed in metal cylinders on the surface of a media plate seeded with the organism being examined. the microorganism grows during incubation at 30° c; clear zones develop around cylinders, indicating the inhibition of growth. the size nova biotechnologica 9-3 (2009) 329 of the zone of inhibition caused by diffusion of agent into agar is directly related to the degree of susceptibility of an organism. 2.5 determination of phenol compounds the content of phenol substances was determined by singelton’s method (singelton et al., 1965). the amount of 0.2 ml of methanol extract was mixed with l ml of folin-ciocalteu's reagent and 0.8 ml of 7.5 % (w/v) na2c03. absorbance was measured at 750 nm after 30 minutes of incubation in dark. the content of polyphenols was compared with the absorbance of galic acid. 2.6 determination of flavonoids flavonoids were determined by rakotoarison’s method (rakotoarison et al., 1997). one ml of methanol extract was added to 1 ml of methanol solution of alcl3.6h20, 2 % (w/v), and absorbance was measured after 10 minutes at 394 nm. quercetin was taken as the standard. 3. results and discussion the first samples were tested before the flowering and the second samples were tested at the end of vegetal period. all cultivars showed different secondary metabolites during the vegetation period, their content in leaves decreased from the end of june to september (table 1). table 1. polyphenols content in hop leaves during the vegetation period. polyphenols [mg g-1 dm] cultivars 6/2008 9/2008 k-31 6.99 ± 0.14 4.53 ± 0.12 k-72 12.48 ± 0.36 3.03 ± 0.09 bor 14.34 ± 0.15 3.77 ± 0.20 sládek 12.32 ± 0.22 3.30 ± 0.12 zlatan 13.38 ± 0.14 3.57 ± 0.11 premiant 9.50 ± 0.33 4.68 ± 0.06 the maximum of content of polyphenols was found in cultivar bor, the cultivar with a high content of bitter acids, at the beginning of the vegetal period; it was more than twice of the content of cultivar k-31. the content of polyphenols at the end of the vegetation period was similar in all the tested hop cultivars. the experiment took place in 2008. some relevant data from 2007 were included for comparison (fig. 1). phenol substances were found in the interval between 5.00 – 8.83 mg g-1 of dry matter in 2007 compared to 9.50 to 14.34 mg g-1 of dry matter in 2008 in leaves before flowering, and from 0.90 to 2.25 mg g-1 of dry matter in 2007 compared to 3.03 – 4.68 mg g-1 of dry matter in 2008 in leaves at the end of the vegetal period. in the year 330 ürgeová, e. and polívka, ľ. 2008, there was less sunshine than in 2007 and there were more showers at the beginning and also during the time of flowering than in 2007. the quantity of phenol substances was higher in 2008 than in 2007. the highest content of polyphenols was detected in cultivar bor at the beginning of the vegetation period in 2008. 0 2 4 6 8 10 12 14 16 k-31 k-72 bor sládek zlatan premiant cultivars of hop po ly ph en ol s [m g g1 d m ] june 07 june 08 september 07 september 08 fig. 1. polyphenol content in hop leaves in 2007 and 2008. flavonoid content in leaves was similar, but different. we noted a decline during the vegetal period in both cases, as well as in phenol substances (table 2). table 2. content of flavonoids in hop leaves in 2007 and 2008. flavonoids [mg g-1 dm] cultivars 6/07 6/08 9/07 9/08 k-31 6.37 ± 0.51 0.24 ± 0.02 0.65 ± 0.02 0.10 ± 0.01 k-72 6.31 ± 0.49 1.43 ± 0.05 0.48 ± 0.02 0.20 ± 0.01 bor 3.45 ± 0.12 0.15 ± 0.01 0.71 ± 0.01 0.16 ± 0.02 sládek 3.24 ± 0.21 0.25 ± 0.01 0.76 ± 0.01 0.15 ± 0.01 zlatan 5.03 ± 0.22 0.14 ± 0.01 0.61 ± 0.01 0.13 ± 0.01 premiant 2.13 ± 0.09 0.19 ± 0.01 0.72 ± 0.01 0.18 ± 0.01 the quantity of flavonoids was higher in 2007. the content of flavonoids was within the range of 2.13 – 6.37 mg g-1 of dry matter in the leaves before flowering in 2007, and 0.14 to 1.43 mg g-1 of dry matter in 2008. the ranges decreased to 0.48 – 0.76 mg g-1 of dry matter of flavonoids at the end of vegetation in 2007. similarly, the interval of flavonoid content at the end of the vegetal period was 0.10 to 0.20 mg g-1 of dry matter in 2008. antibacterial activity was tested during the vegetation of hop plants. the marked inhibition effect of the extract of cultivar bor on erwinia mallotivora, 89% of inhibition effect of the standard tmtd, was noticed. the extracts from cultivars k31a had a similar effect on these bacteria, 67% of inhibition effect of the standard tmtd (fig. 2.). nova biotechnologica 9-3 (2009) 331 0 10 20 30 40 50 60 70 80 90 100 bor k-31 zlatan sládek premiant k-72 h op c ul ti va rs % of biocide effect of tmtd standard sept 08 july 08 june 08 april 08 fig. 2. biocide effect of hop extracts on the growth of erwinia malotivora. the average size of inhibition zones of extracts from leaves at the beginning of vegetation (april 08) was lower than the average size of extracts before the flowering time (june 08) (table 3). tab. 3. antibacterial effect of hop extracts during the vegetal period described as zones without the growth of bacteria on the agar plate in mm. hop cultivars bacteria vegetal period k-31 k-72 bor sládek zlatan premiant april 08 3 2 <1 2 2 2 june 08 4 3 2 4 2 2 e. amylovora sept 08 <1 1 2 <1 <1 1 april 08 3 3 3 2 2 <1 june 08 4 3 4 2 3 3 x. vesicatoria sept 08 4 2 <1 <1 <1 4 april 08 4 <1 2 <1 <1 2 june 08 4 5 3 1 6 4 p. carotovorum subsp. carotovorum sept 08 2 2 <1 4 <1 4 april 08 2 <1 <1 <1 2 4 june 08 4 3 3 2 3 4 p. syringae pv. syringae sept 08 <1 2 1 2 <1 2 april 08 <1 <1 <1 2 2 <1 june 08 2 3 1 3 2 3 c. michiganensis subsp. sepedonicus sept 08 1 1 <1 1 2 2 the inhibition effect of the extracts from hop leaves at the end of the vegetation period was minor. 332 ürgeová, e. and polívka, ľ. 4. conclusions the comparison of the results obtained during two years proved that the concentration of secondary metabolites, phenol substances and flavonoids depended mainly on the vegetal period. the influence of climatic conditions on the contents of these secondary metabolites of hop leaves was verified. the contents of these constituents were different in identical cultivars, compared to the years 2007 and 2008. the results of antibacterial activity suggested that this effect related mainly with sensibility of the bacterial strain and cultivar of hop. we observed the influence of the vegetation period, too. acknowledgement: this work was financially supported within the grants vega 1/0436/08 and av 4/2024/08. references bhattcharya, s., virani, s., zavro, m., haas, g., j.: inhibition of streptococcus mutans and other oral streptococci by hop (humulus lupulus l.) constituents. econ. bot., 57, 2003, 118-125. čeh, b., kač, m., iztok, j., košir, l., abram, v.: relationships between xanthohumol and polyphenol content in hop leaves and hop cones with regard to water supply and cultivar. int. j. mol. sci., 8, 2007, 989-1000. gerhauser, c.: broad spectrum anti-infective potential of xanthohumol from hop (humulus lupulus l.) in comparison with activities of other hop constituents and xanthohumol metabolites. mol. nutr. food res., 49, 2005, 827-31. hofta, p., dostálek p., basařová, g.: xantohumol − chmelová pryskyřice nebo polyfenol? chem. listy, 2004, 98, 825-830. langezaal, c.r.; chandra, a.; scheffer, j.c.: antimicrobial screening of essential oils and extracts of some humulus lupulus l. cultivars. pharm. weekbl., 1992, 14, 353-356. moir, m.: hops a millenium review. j. am. soc. brew. chem., 58, 2000, 131-146. piddock, j. v. l.: techniques used for the determination of antimicrobial resistance and sensitivity in bacteria. j. appl. bacteriol., 68, 1989, 307-318. rakotoarison, d., a., gressier, b., trotin, f., brunet, c., dine, t., luyckx, m., vasseur, j., cazin, m., cazin, j., c., pinkas, m.: antioxidant activites of polyphenolic extracts from flowers, in vitro callus and cell suspension cultures of crataegus monogyna. pharmazia, 52, 1997, 60-63. singleton, v., l., rossi, j., a.: colorimetry of total phenolics with phosphomolybdic-phosphotungstic acid reagents. am. j. enol. vitic, 16, 1965, 144-158. srinivasan, v., goldberg, d., haas, g.j.: contributions to the antimicrobial spectrum of hop constituents. econ. bot., 58, 2004, s230-s238. stavri, m., schneider, r., o‘donnell, g., lechner, d., bucar, f., gibbons, s.: the antimycobacterial components of hops (humulus lupulus l.) and their dereplication. phytother. res., 18, 2004, 774-776. microsoft word závodská et al nb 9-3.doc nova biotechnologica 9-3 (2009) 303 physical-chemical characterization of uranium containing sediments lucia závodská1, eva kosorínová2, juraj lesný2, dušan bodiš3 1department of nuclear chemistry, comenius university in bratislava, mlynská dolina, bratislava, sk842 15, bratislava 4, slovak republic (zavodskalucia@centrum.sk) 2department of biotechnology, university of ss cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic (lesnyj@ucm.sk) 3state geological institute of dionýz štúr, mlynská dolina 1, bratislava 11, sk-817 04, slovak republic (dusan.bodis@geology.sk) abstract: the presented paper is intended to study the chemical behaviour of combined geogenicanthropogenic uranium content in specific stream sediments. the sampling points have been chosen with respect to the natural conditions in the locality of groundwater outflow from a former uranium mine adit in považský inovec mountain range, near kálnica village. besides the total uranium determination and physical-chemical characterization of the relevant waterand sediment samples we carried out modified tessier type sequential fractionation extractions of naturaland artificially contaminated sediment samples after time dependent agitation in air and in the atmosphere of argon. the obtained results have been compared with those fulfilled with montmorillonite k-10. the total uranium concentrations of the relevant groundwater samples as well as of stream sediments have been determined by icp-ms using hp 4500. the determinations of uranium in extracts have been accomplished according stn757614, utilizing arsenazo iii as a selective complex forming reagent for spectrophotometric determination of uranyl-ions at 650 nm. the total uranium concentration of the groundwater outflow and in the sediment taken in its immediate vicinity has been 31.75±0.35 μg dm-3 and 38.0±2.7 μg g-1 respectively. unlike montmorillonit k-10, in which the carbonate-bound fraction of uranium after 1 week aeration and agitation in argon atmosphere represents 22.8% and 18.6% respectively, uranium in investigated sediments has been present predominantly in carbonate-bound fraction-reaching under similar conditions 38.6% and 26.6%, respectively. key words: uranium, sediments, groundwater, sequential fractionation 1. introduction uranium is an element of highly specific chemical, physical and biological properties. mostly because of its essentiality for nuclear energy production and its toxicity, the interest in its environmental mobility attracts constantly increasing attention. among basic features of uranium the following ones are crucial: it is a typical lithophilic natural radioactive component of the environment and contrary to its notoriety its radiotoxicity is negligible in comparison with chemical toxicity. the substantial chemical properties of uranium decisively influencing its transport in the environment as well as its determination possibilities are outlined in our earlier papers (závodská et al., 2008; szabó-nagy et al., 2009). uranium in natural waters may be present in four different oxidation states (u(iii), u(iv), u(v) and u(vi). in general, the tetravalent and hexavalent uranium species are stable in aqueous media, but the u(iv) –ion is only stable under reducing condition. a few solid and semi-metalis compounds such as uo and us exist in the formal oxidation 304 závodská, l. et al. state u(ii), although no simple ions are known to exist in solution for that state. the most prevalent form of uranium in aqueous solution is the light yellow, fluorescent uranyl ion ( uo +22 ). the u 4+ cation (green in solution) can be obtained by strong reduction of u(vi), but in the air it oxidizes back to uo +22 . the pentavalent ion uo+2 can be reversibly formed by reduction of uo +22 , but it readily disproportionates into u(iv) and u(vi). the trivalent u3+ can be formed by reduction of u(iv) but it is unstable as it oxidizes in aqueous solution (greenwood and earnshaw, 1997). 2. pe and ph dependence of u oxidation states in natural waters the thermodynamic principles of advanced aquatic chemistry including modelling methods are fairly discussed in a series of recent monographs (benjamin, 2002; morel and hering, 1993; grenthe and puigdomenech, 1997). putting to data set the updated thermodynamic values concerning uranium hydroand carbonate species (guillaumont et al., 2003) and utilizing the freeware phreeqc version 2.15.0 (usgs, 2008) we calculated the proportions of u(iii), u(iv), u(v) and u(vi) concentrations in dependence of pe and ph introducing the following model conditions (fig. 1-4): total uranium: 0.00005 mmol dm-3; alcalinity: 3.0 mmol dm-3; calcium: 1.5 mmol dm-3; temperature: 298.15 k; thermodynamic data: u4+ + e = u3+ (log k = -9.353; δh = 102.098 kj) u4+ + 4 h2o = u(oh)4 + 4 h + (log k = -8.538; δh = 103.596 kj) u4+ + 5 h2o = u(oh)5 + 5 h + (log k = -13.147; δh = 115.395 kj) u4+ + 2 h2o = uo+2 + 4 h + + e (log k = -6.432; δh = 130.248 kj) u4+ + 2 h2o = uo +22 + 4 h + + 2e (log k = -9.217; δh = 144.055 kj) uo +22 + h2o = ou2oh + + h+ (log k = -5.250; δh = 46.087 kj) 2 uo +22 + 2 h2o = (uo2)2(oh) +2 2 + 2 h + (log k = -5.620; δh = 150.791 kj) 3 uo +22 + 5 h2o = (uo2)3(oh) + 5 + 5 h + (log k = -15.550; δh = -185.226 kj) uo +22 + co _23 = uo2co3 (log k = 9.94; δh = 5.000 kj) uo +22 + 2 co _23 = uo2 (co3) _2 2 (log k = 16.61; δh = 8.500 kj) uo +22 + 3 co _23 = uo2 (co3) _4 3 (log k = 21.840; δh = -39.200 kj) fig. 1. proportion of u(iii) species in model natural waters in dependence of pe and ph. nova biotechnologica 9-3 (2009) 305 fig. 2. proportion of u(iv) species in model natural waters in dependence of pe and ph. fig. 3. proportion of u(v) species in model natural waters in dependence of pe and ph. fig. 4. proportion of u(vi) species in model natural waters in dependence of pe and ph. 306 závodská, l. et al. 3. materials and methods 3.1 sediment and water sampling, sample site and sample points the sampling of the investigated sediments and water has been performed on november 20, 2008 according to iso 5667-12 (guidance on sampling of bottom sediments) and iso 5667-15 (guidance on the preservation and handling of sludge and sediment samples). the sample site has been chosen in close proximity of a former uranium mine adit in považský inovec mountain range (fig. 5). uranium mineralization in perm of považský inovec mts. (kálnica, selec) is stratiform type (rojkovič, 1980; ivanička et al., 2007). major elements of mineralization act in psammitic and psefitic rocks. increased accumulation of uranium and accompanying minerals arose due to clastic material acquisition and by precipitation from aqueous solution. an important source of uranium was volcanisms of quartz porphyry and partly exposed crystalline rocks. during sedimentation and diagenesis in the productive complex of strata occurred the accumulation of uranium and accompanying minerals and during the alpine orogeny their concentration in the form of lenses. the most common ore minerals are pyrite, uraninite and rutile. the main elements of mineralization are u, pb, cu, mo nova biotechnologica 9-3 (2009) 307 and coincident elements ni, co and partly y and v. sampling point 3 (n 48°44.81'; e 17°57.68) has been chosen directly at the groundwater outflow from the uranium mine, which flows to the stream prostredný potok. sampling points 2 (n 48°44.80'; e 17°57.68) and 1 (n 48°44.22'; e 17°57.32) have been chosen at the above mentioned stream, approx. 25 and 50 m respectively north-west from the outflow. 3.2 physical-chemical characterization of the sediment-water system the primary characterization of the investigated system – the measuring of the water column height, the ph and eh of water and sediment, the thickness of the sediment and the definition of the sediment colour have been accomplished in situ. the additional assays – the ph determination of the wateras well as the 0.01 mol dm-3 cacl2 extracts of the sediments, the sediments dry matter determination, the measuring of the water conductivity, the sedimentation test (for the sample taken at sampling point 3) as well as the granulometric analysis (for the sample taken at sampling point 1) – have been accomplished in the laboratory. the sedimentation test has been realized with 20 g air dry sediment in 100 cm3 graduated cylinder. for the wet granulometric analysis (utilizing water taken at the identical sampling point) 2.0 mm, 1.0 mm, 0.25 mm, 0.125 mm and 0.06 sieves have been applied and the fractions have been weighed after drying at laboratory temperature. the mineralization of the samples (sediments from sampling points 2 and 3 as well as the reference sediment gbw 07306) has been executed using the microwave sample digestion system multiwave 3000 (anton paar, austria). 0.25 g air dry sediments have been treated with 5 cm3 conc. hno3 and 2 cm3 conc. h2so4 at tmax= 496 k and p = 2.6 . 10 6 pa (sediment 2 and gbw 07306) as well as tmax= 449 k and p = 1.36 . 10 6 pa (sediment 3). the total uranium concentrations in mineralized sediments have been determined by icp-ms (hp – 4500, hewlett packard, usa) utilizing icp-ms vi (merck) calibration solutions and certified reference sediment tmda 62 (national water research institute, canada). the uranium concentrations in particular fractionation extracts have been determined by spectrophotometry according stn 75 7614 (water quality. determination of uranium), using uv-vis spectrophotometer cary 50 bio, varian, australia. the extraction fractionations of the sediments have been accomplished applying a slightly modified tessier type sequential extraction procedure. in order to study the influence of oxygen to the uranium mobility in the watersediment system we realized a time dependent aeration of investigated materials in contact with uranium contaminated water. 1 g of air dry sediment 3 has been placed in a test-tube and 8 cm3 of water has been added. to 1 g of sediment 2 and montmorillonite k-10 placed in the same type of test-tubes 8 cm3 of uranium acetate solution (uranium concentration 12 mg dm-3) has been added. using a simple laboratory aeration apparatus a time dependent aeration (1h, 1 day, 1 week) has been accomplished and after centrifugation (4000 rpm, 300 s) the modified tessier type sequential extraction has been carried out. the same experiment has been fulfilled, using argon atmosphere. 308 závodská, l. et al. 4. results and discussion the obtained results of the primary characterization of the investigated system are shown in table 1 (in situ determinations) and in table 2 (laboratory determinations). table 1. in situ determinations. h: water column height, th: sediment thickness, col: sediment colour, * water sampling points identical with 1, 2, 3 sediment sampling points. h [cm] th [cm] col ph (25°c) pe sediment 1 2 7.5 grey ––– –––– sediment 2 2 7.5 brown ––– –––– sediment 3 2 7.5 orange ––– 0.76 (8.7°c) water 1* ––– ––– –––– 8.15 + 2.96 (7.4°c) water 2* ––– ––– –––– 7.86 + 1.59 (7.5°c) water 3* ––– ––– –––– 7.40 + 0.35 (8.7°c) table 2. laboratory determinations. d: dry substance. extract ph d (1h, 105°c) h2o 0.01mcacl2 χ [μs cm-1] sediment 1 74.95% 7.33 6.93 ––– sediment 2 72.69% 7.90 7.52 ––– sediment 3 13.26% 7.85 7.42 ––– water 1* ––– ––– –––– 773 (17.9°c) water 2* ––– ––– –––– 887 (18.3°c) water 3* ––– ––– –––– 873 (18.7°c) moving away from the outflow we observed moderately increasing ph values of water, slightly decreasing ph values of 0.01 m cacl2 sediment extracts, as well as increasing oxidation-reduction potential. the mentioned facts are obviously connected with decreasing dissolved co2 and increasing dissolved o2 concentrations as well as with the subsequent oxidation of several metal ions causing production of their precipitates. sedimentation curves of sediment 3 (not shown) confirm the apparent and simply distinguishable homogeneity of the clayey sediment, which even after 3 days did not show any tendency to swell. the granulometric analysis of sediment 1 showed a substantial fraction, namely 56.8% of grains sized >2 mm, 30.5% of the grain fraction 0.25 – 1.0 mm, ~4.7% of the grain fraction 0.25 – 0.125 mm and ~4.5% of the grain fraction 0.125 – 0.06%. according the recent knowledge (breitner et al., 2008) uranium is preferentially bound to the finest sediment grains and therefore the experiments connected with the sequential extractions have been fulfilled with samples of the grain fraction 0.125 – 0.06 mm. nova biotechnologica 9-3 (2009) 309 icp-ms determinations of total uranium have been performed for groundwater outflow at sampling point 3, for sediment 2 and for sediment 3 in duplicate samples. we obtained the following results: 31.75±0.35 μg dm-3 for groundwater outflow; 38.0±2.71 μg g-1 for sediment 3 and 9.0±0.59 μg g-1 for sediment 2. uranium concentrations in particular fractions of sediment 2 and sediment 3 using the applied sequential extractions (modified tessier type procedure) are shown in table 3. table 3. uranium concentrations in the investigated sediment fractions using modified tessier type procedure. f0: water soluble fraction, f1: ion-exchangeable fraction, f2: carbonate-bound fraction, f3: fe/mn oxides-bound fraction, f4: organic matter-bound fraction. uranium concentration [μg g-1] fraction sediment 2 sediment 3 f0 –––– 1.550±0.533 f1 –––– 1.620±0.533 f2 0.789±0.725 12.935±0.559 f3 0.893±0.722 1.113±0.658 f4 –––– 1.742±0.532 1 2 3 4 5 6 0 10 20 30 40 50 60 70 m on tm or illo ni t se di m en t 3 se di m en t 2 u ra ni um p or tio n in p ar tic ul ar fr ac tio ns [% ] m on tm or illo ni t se di m en t 3 se di m en t 2 argono 2 + co 2 f0 f1 f2 f3 fr fig. 6. comparison of uranium fractionation in sediment samples and montmorillonite k-10 after 1 week aeration and argonation. f0: water soluble fraction, f1: ion-exchangeable fraction, f2: carbonate-bound fraction, f3: fe/mn oxides-bound fraction fr: residual fraction. considering the obtained results it is straightforward, that for sediment 3 the prevailing amount of uranium is in the carbonate-bound fraction. this finding is in accordance with the published papers (bunzl et al., 1998 and martin et al., 1998). for sediment 2 the same fraction markedly drops and in the same time the fe/mn oxides-bound fraction become the most uranium containing one. the mentioned facts are with high probability connected to the quick aqueous co2concentration fall in the water as well as with a consequent uranium species sorption on the stream sediments. 310 závodská, l. et al. via aeration/argonation experiments (outlined in section 3.2) we gained a valuable comparison of time dependent uranium fractionation in investigated sediments vs. in montmorrillonite k-10 with and without contact with air. fig. 6 illustrates the obtained results after 1 week of aeration and argonation respectively. 5. conclusions while the proportion of u(iii) species in uranium contaminated natural waters at pe -5 and ph 4 hardly reach 1% and u(v) species exist only in relatively narrow pe and ph range, a considerable portion of uranium may exist in u(iv) oxidation state, namely at relatively low oxidation-reduction potential (pe values from -5 to 0) and the main portion in u(vi) oxidation state at positive pe values. the uranium concentration of the investigated water outflow from the former uranium mine adit reached as much as ~31 μg dm-3. in the investigated conditions the uranium in water is present predominantly in u(vi) oxidation state. with raising distance from the spring the water has a tendency of increasing pe and decreasing ph values. in montmorillonite k-10 the carbonate-bound uranium fraction after 1 week of aeration reached ~22%. in aerated conditions uranium has been present in carbonate-bound fraction of investigated sediments in much higher concentration reaching ~40%. the presence of air in all cases gave rise to a measurable increase of uranium proportion in biologically available fractions. compared to montmorillonite k-10, where the influence of air has been smaller, in similar conditions the biologically available uranium fractions unambiguously increased reaching 30-35% after 1 week aeration. acknowledgements: we would like to express our sincere thanks to dr. adriana shearman for accomplishing the icp-ms determinations. references závodská, l., kosorínová, e., ščerbáková, l., lesný, j.: environmental chemistry of uranium. hej, env-081221-a, 2008, 1-19. szabó-nagy, a., závodská, l., mátel, ľ., lesný, j.: geochemistry and determination possibilities of uranium in natural waters. acta tech. jaurin., 2009, in press. greenwood, n.n., earnshaw, a.: chemistry of the elements. second edition. butterworth-heinemann, elsevier science, linacre house, jordan hill, oxford ox2 8dp, 1997. united states geological survay: phreeqc version 2.15.0, 2008. benjamin, m.m.: water chemistry. mcgraw-hill, singapore, 2002. morel, f.m.m., hering, j.g.: principles and applications of aquatic chemistry. john wiley & sons, usa, 1993. grenthe, i., piugdomenech, i.: modelling in aquatic chemistry. nea&oecd, france, 1997. guillaumont, r., fanghänel, t., fuger, j., grenthe, i., neck, v., palmer, d.a., rand, m.h.: update on the chemical thermodynamics of nova biotechnologica 9-3 (2009) 311 uranium, neptunium, plutonium, americium and technetium. chemical thermodynamics, vol. 5, elsevier, the netherlands, 2003. rojkovič, i.: geochemická charakteristika uránového zrudnenia v perme považského inovca. manuskript, geofond bratislava, 1980. ivanička, m., havrila, m., kohút, m. (editors): geologická mapa regiónu považský inovec a jv. časti trenčianskej kotliny. 1:50 000, štátny geologický ústav dionýza štúra, bratislava, 2007. breintner, d., turtiainen, t., arvela, h., vesterbacka, p., johanson, b., lehtonen, m., hellmuth, k.h., szabó, c.: multidisciplinary analysis of finnish esker sediment in radon source identification. sci. total environ., 405, 2008, 129-139. bunzl, k., kracke, w., schimmack, w., zelles, l.: forms of fallout 137cs and 239+240pu in successive horizons of forest soil. j. environ. radioact., 39, 1998, 55-68. martin, r., sanchez, d.m:, gutierrez, a.m.: sequential extraction of u, th, ce, la and some heavy metals in sediments from ortigas river, spain. talanta, 46, 1998, 1115-1121. microsoft word vaverkova nb 9-2.doc nova biotechnologica 9-2 (2009) 191 the possibility to enhance flavonoids production in rubia tinctorum l. callus cultures daniela kákoniová1, štefánia vaverková2 , desana lišková1, eva urgeová3, zuzana juráková1 1institute of chemistry slovak academy of sciences, dúbravská cesta 9, sk-845 38 bratislava, slovak republic (chemdaka@savba.sk) 2department of botany and pharmacognosy, faculty of pharmacy comenius university, kalinčiakova 8, sk-832 32 bratislava, slovak republic (vaverkova@fpharm.uniba.sk) 3faculty of natural sciences, university of ss. cyril and methodius, trnava, slovak republic abstract: production of flavonoids in madder callus culture (rubia tinctorum l.) was dependent on culture conditions and culture media composition. the content of flavonoids increased in calli maintained on media supplemented with naa (4 mg.l-1) or naa:bap (4 mg.l-1 a 1 mg.l-1) in 16 h photoperiod. flavonoids represented 2.08 – 2.25 % of callus dry mass. the presence of cd(no3)2 (3.1 or 31.0 mg.l-1 concentrations) negatively influenced callus growth, but enhaced the percentage of dry mass in callus cells. during 42 days of culture an increase of cadmium accumulation and even of flavonoids has been observed. the most considerable influence of cdcl2 or cd(no3)2 on flavonoids content has been shown in short-term experiments after 48 h of callus culture. more distinct influence has been observed under the treatment with cdcl2 (0.005 mg.l-1) in comparison with cd(no3)2. key words: cadmium, callus, growth, madder, secondary metabolites 1. introduction the effort to use natural resources of vegetal and animal origin supports detailed investigation of familiar plant species for discovery of their still unknown impact against negative factors of the environment. cultivation of medicinal plants is in the focus worldwide. this is evoked not only by the appearance of numerous civilization deseases, but also by the new look on prophylaxis and food health. prominent plant species contain secondary metabolites usable in food industry, cosmetics, and mainly in pharmaceutical industry. besides standard application and isolation of secondary compounds from natural resources, increasing significance win biotechnologies aimed on bioactive metabolites production and enhancement of their production abilities, predominantly plant cell cultures in vitro (pšenáková et al., 2003; vanisree and tsay, 2004; vanisree et al., 2004). cell and callus cultures represent a continual renewable source of plant biomass and unlimited resource of desired pharmaceutical products. madder (rubia tinctorum l.) is a medicinal plant (thurzová et al., 1983). secondary compounds isolated from its root have diuretic effect and come in use by the treatment of kidney stones and as an auxilliary means in medication of rachitis and 192 kákoniová, d. et al. anaemia. this plant, coming from the south of europe, was grown for red dye, alizarine. this drug contains also flavonoids, compounds with antioxidative effect. commercial importance of flavonoids and a need for renewable resources of valuable chemicals has lead to attempts in developing alternative systems for their production. different in vitro systems have been developed for flavonoids production, e.g., callus, cell suspension cultures, root and shoot cultures (jedinák et al., 2004). biotic and abiotic elicitors can enhance secondary metabolites production. the stimuli are perceived by receptors activating secondary messengers. these transmit signals into the cell through signal transduction pathways leading to gene expression and biochemical changes (sudha and ravishankar, 2002) resulting in compounds formation. the basis for successful elicitation of secondary metabolites is the choice of suitable elicitor, its concentration, and optimal time of treatment. many plant secondary metabolites are involved in the interaction of the plant with the environment. increased contamination of the environment by toxic metals has negative consequence for all kinds of organisms, including higher plants. toxic metals in high concentrations inhibit growth and development of plants and disturb or change their biochemical and physiological processes. cadmium is one of common industrial pollutants, harmful to plants already at low concentrations (nehnevajová, 2002; šupalová, 2004). the aim of this study was to detect the potential of madder (rubia tinctorum l.) callus cultures to produce flavonoids in dependency on culture media composition, physical conditions, combination and concentration of growth regulators, and the effect of cd-salts cd(no3)2 and cdcl2. 2. material and methods 2.1 cultivation of callus cultures callus cultures of madder (rubia tinctorum l.) belong to the collection of in vitro cultures at the institute of chemistry sas in bratislava. callus cultures were isolated from leaf segments of madder seedlings and cultured on modified murashigeskoog (ms) medium (1962) or on z medium (čierna et al., 1991) at 25 ± 1 °c, under 60 % relative air humidity, 16 h photoperiod, irradiance of 45-60 µmol m-2.s-1, or in the dark. the callus cultures were subcultured every four weeks. 2.2 growth parameters and statistics the growth dynamics (∆ri(j+7) = ri(j+7) rij, ri = ∆m/m0, ∆m = m – m0, m = fresh mass, m0 = initial mass of inoculum, j = day of culture) was statistically evaluated by student`s t-test and anova. in all experiments 10 samples were used. the experiments were repeated twice. 2.3 elicitation of flavonoids the possibility to increase the content of flavonoids has been examined on media supplemented with naa:bap in various ratios 2:0, 2:1, 4:0, 4:1 (mg.l-1) under 16 h nova biotechnologica 9-2 (2009) 193 photoperiod or in the dark, in the presence of cadmium salts: cd(no3)2 or cdcl2 in different concentrations (0.005 mg.l-1, 0.05 mg.l-1, 0.5 mg.l-1, 3.1 mg.l-1, and 31.0 mg.l1) during a short-term culture (24, 48, and 168 hours), during 42 days on ms solid media, or with liquid media on paper bridges. 2.4 determination of flavonoids content flavonoids were determined colorimetrically from lyophilized dry mass. callus cultures were collected during the cultivation period, lyophilized, homogenized, and pulverized. the drug was subsequently extracted with acetone, shaked with etoac and then the samples were evaluated at 425 nm on spekol carl zeiss – jena 2 by modified method of tůmová and rusková (1998). the average content of flavonoids was calculated from standard curve of quercetin (europ. formulary 1). 2.5 determination of cadmium content the content of cadmium in madder cells was analysed at the institute of geology, faculty of natural sciences, comenius university in bratislava, bratislava, slovakia by nuclear absorption spectrophotometry. 3. results and discussion callus cultures of madder (rubia tinctorum l.) isolated from leaf segments and cultivated on two different media (ms or z) showed similarity in growth and growth dynamics (fig. 1a, 1b). the content of flavonoids in cells altered as an answer on growth hormones in culture media and light period (16 h photoperiod or in the dark). their values oscilated between 1.65 and 2.25 % of callus dry mass (fig. 2). the highest values of flavonoids were determined in calli grown at 16 h photoperiod on media containing naa:bap in the ratio 4:0 or 4:1 (mg.l-1). in these cases flavonoids made up 2.08 up to 2.25 % of dry mass (fig. 2). plant growth hormones represent important and in many cases essential compounds of culture media as for callus cultures growth, so for secondary metabolites production (siatka, 1998). type and concentration of growth hormones are specific for every culture grown in vitro. their mutual combinations are determined experimentally. the highest amounts of flavonoids in bellis perennis l. callus culture were determined on media supplemented with 2,4-d in 0.1 and 1 mg.l-1 concentration, or with iaa in 0.1 mg.l-1, possibly also with naa (1 mg.l-1). lower or higher concentrations of growth hormones reduced the production of flavonoids (siatka, 1998). the content of flavonoids in rubia tinctorum l. callus cells depended on the photoperiod length and naa concentration, and the combination with bap in culture media. the highest values of flavonoids were detected in calli growing on media with naa (4 mg.l-1) or when naa (4 mg.l-1) was combined with bap (1 mg.l-1) and grown in 16 h photoperiod (fig. 2). it is known that some metals may positively affect the production of secondary metabolites (zheng and wu, 2004; rai et al., 2005). cadmium e.g. enhances the 194 kákoniová, d. et al. 0 0,5 1 1,5 2 2,5 3 0 7 14 21 28 35 42 day m /m 0 z ms a 0 0,2 0,4 0,6 0,8 1 0 7 14 21 28 35 42 day δ r i z ms b biosynthesis of ajmalicine in suspension cultures of catharanthus roseus during 24 – 48 h of cultivation (zheng and wu, 2004). fig. 1. rubia tinctorum l. callus culture growth (a), growth dynamics of rubia tinctorum l. callus culture (b). 0 0,5 1 1,5 2 2,5 1 2 3 4 5 6 7 8 media % o f f la vo n o id s ms z fig. 2. effect of ms and z modified media and physical culture conditions (16 h photoperiod/dark) on flavonoids content in callus cultures of rubia tinctorum l. naa:bap (mg.l-1) 1 – 2:0; 2 – 2:1; 3 – 4:0; 4 – 4:1 – dark; 5 – 2:0; 6 – 2:1; 7 – 4:0; 8 – 4:1 – 16 h photoperiod noticeable increase of rosmarinic acid in suspension cultures of melissa officinalis l. was observed at the end of the second subculture (4 weeks of culture) by šupalová (2004) when cultivated on media supplemented with 31.0 mg.l-1 cd(no3)2. in this case the content of rosmarinic acid was comparable with its content in intact plants. the presence of cd(no3)2 in 3.1 and 31.0 mg.l -1 concentrations influenced negatively madder callus growth (fig. 3a), but increased the % of dry mass after 42 days of culture (fig. 3b). the treatment of phyllanthus amarus with a cd-salt (higher than 50 ppm and up to 100 ppm) significanly inhibited their growth. decrease of dry mass, content of proteins, chlorophyll, and saccharides was evident. in contrast the content of starch nova biotechnologica 9-2 (2009) 195 -1 -0,5 0 0,5 1 1,5 2 0 7 14 21 28 35 42 day δ r i c cd1 cd2 a 0 2 4 6 8 7 14 21 28 35 42 day % o f d .m . c cd1 cd2 b 0 100 200 300 400 500 7 14 21 28 35 42 day c d μ g .g 1 cd1 cd2 c 0 0,5 1 1,5 2 7 14 21 28 35 42 day % o f f la vo no id s c cd1 cd2 d increased, similarly as therapeutically active compounds – phyllantine and hypophyllantine (rai et al., 2005). in madder cells cadmium accumulation corresponded with its concentration in culture media and duration of the treatment (fig. 3c). fig. 3. growth dynamics (a), percentage of dry mass (b), accumulation of cadmium (c) and content of flavonoids (d) of rubia tinctorum l. callus culture on ms medium supplemented with cd(no3)2. c – control; cd1 – 3.1 mg.l-1; cd2 – 31.0 mg.l-1 these results are supported also by the findings of nehnevajová (2002) in ginkgo biloba l. callus culture. the highest concentration of cd(no3)2 during 4 subcultures enhanced the toxic effect of this salt on callus growth parameters, callus pigmentation, cells plasmolysis, and cell wall irregular thickenings. in madder callus, at the 31.0 mg.l-1 cd(no3)2 concentration, the content of cd increased already on the 7th day of culture and this trend continued till the day 42 of culture on agar media (479 µg.g-1 d.m.) (fig. 3c). the production of flavonoids was time-shifted at both concentrations of the cd-salt compared with the control. the presence of 3.1 mg.l-1 cd(no3)2 caused moderate stimulation already after 21 days with the maximum value on the 35th day of culture. the highest values of flavonoids on media supplemented with the higher concentration (31.0 mg.l-1) of cd(no3)2 on 28 th day were determined (fig. 3d). production of flavonoids in madder callus cells cultured on paper bridges was positively affected by all concentrations of cdcl2 and cd(no3)2 tested, mainly after 24 and 48 h of culture. most significantly was this process affected by the concentration 0.005 mg.l-1 of cdcl2, when the content of flavonoids increased by 57-64 % in comparison with the control (fig. 4). 196 kákoniová, d. et al. 0 0,4 0,8 1,2 1,6 2 c 1 2 3 4 5 6 media % fl av o n o id s 24 h 48 h 168 h fig. 4. content of flavonoids in rubia tinctorum l. callus cultures grown on paper bridges. c control; 1 0.005 mg.l-1 cdcl2; 2 0.05 mg.l-1 cdcl2; 3 0.5 mg.l-1 cdcl2; 4 0.005 mg.l-1 cd(no3)2; 5 0.05 mg.l-1 cd(no3)2; 6 0.5 mg.l-1 cd(no3)2. during this short-term culture no growth or uptake of cd-salts by cells growing on paper bridges were observed. very diminutive uptake was determined at the 0.005 mg.l-1 concentration of cdcl2. this effect could be the result of ions interaction in liquid medium and of the short-term cd-salt treatment. tůmová and rusková (1998) have also ascertained a positive effect of cdcl2 as well as cuso4 on the production of flavonoids in ononis arvensis l. callus culture. they have observed that cdcl2 in 0.05 mg.l -1 or 0.5 mg.l-1 concentrations significantly increased flavonoids content after 48 h, but the lowest concentration (0.005 mg.l-1) affected it already after 24 h of culture. it can be concluded that plant growth hormones, and also cd-salts (in suitable combination and concentration) in connection with physical conditions and length of the treatment, enhance the production of secondary metabolites in madder (rubia tinctorum l.) cells cultured in vitro. acknowledgement: this work was supported by slovak grant agency vega, grant no. 1/4354/07, apvv-cost -0004-06, and cost action 859. references čierna, m., kákoniová, d., lišková, d.: a medium for rapid plant callus growth. biologia, 46, 1991, 271-272. european pharmacopoea (ph.eur.) 4-nd. ed. maissoneueve, france, 2000, 375-376 pp. nova biotechnologica 9-2 (2009) 197 jedinák, a., faragó, j., pšenáková, i., maliar, t.: approaches to flavonoid production in plant tissue cultures. biologia, 59, 2004, 697-710. murashige, t., skoog, f.: a revised medium for rapid growth and bioassays with tobacco tissue cultures. physiol. plant., 15, 1962, 473-497. nehnevajová, e.: effect of cadmium on growth parameters of ginkgo biloba l., thesis, comenius university, bratislava, 2002, 89 pp. [in slovak] pšenáková, i., faragó, j., vašková, l.: application possibilities of in vitro plant systems for the production of secondary metabolites. nova biotechnol. iii-2, 2003, 103-113. [in slovak] rai, v., khatoon, s., bisht, s.s., mehrotra, s.: effect of cadmium on growth, ultramorphology of leaf and secondary metabolites of phyllanthus amarus schum. and thonn. chemosphere, 61, 2005, 1644-1650. siatka, t.: effect of auxins on bellis perennis l. callus cultures growth and flavonoids production. čes. slov. farm., 47, 1998, 273-275. [in czech] sudha, g., ravishankar, g.a.: involvement and interaction of various signaling compounds on the plant metabolic events during defense response, resistance to stress factors, formation of secondary metabolites and their molecular aspects. plant cell tiss. org. cult., 71, 2002, 181-212. šupalová, a.: the influence of cadmium on growth parameters and content of rosmarinic acid in callus and suspension cultures of lemon balm (melissa officinalis l.), thesis, comenius university, bratislava, 2004, 113 pp. [in slovak] thurzová, ľ., kresánek, j., mareček, š., mika, k.: small atlas of medicinal plants, osveta, bratislava, 1983, 324-325 pp. [in slovak] tůmová, l., rusková, r.: effect of cdcl2 and cuso4 on flavonoids production in ononis arvensis l. cultured in vitro. čes. slov. farm., 47, 1998, 261-263. [in czech] vanisree, m., tsay, h.-s.: plant cell cultures – an alternative and efficient source for the production of biologically important secondary metabolites. int. j. appl. sci. eng., 2, 2004, 29-48. vanisree, m., lee, ch.-y., lo, s.-f., nalawade, s.m., lin, ch.y, tsay, h.-s.: studies on the production of some important secondary metabolites. bot. bull. acad. sin., 45, 2004, 1-22. zheng, z.u., wu, m.: cadmium treatment enhances the production of alkaloid secondary metabolites in catharanthus roseus. plant sci., 166, 2004, 507-514. microsoft word janecek 9-1 2009.doc nova biotechnologica 9-1 (2009) 5 amylolytic enzymes focus on the alpha-amylases from archaea and plants štefan janeček1,2 1department of biotechnology, university of ss. cyril and methodius, j. herdu 2, sk-917 01 trnava, slovak republic (stefan.janecek@ucm.sk) 2institute of molecular biology, slovak academy of sciences, dúbravská cesta 21, sk-845 51 bratislava, slovakia (stefan.janecek@savba.sk) abstract: amylolytic enzymes represent a group of starch hydrolases and related enzymes that are active towards the α-glycosidic bonds in starch and related polyand oligosaccharides. the three best known amylolytic enzymes are α-amylase, β-amylase and glucoamylase that, however, differ from each other by their amino acid sequences, three-dimensional structures, reaction mechanisms and catalytic machineries. in the sequence-based classification of all glycoside hydrolases (ghs) they have therefore been classified into the three independent families: gh13 (α-amylases), gh14 (β-amylases) and gh15 (glucoamylases). some amylolytic enzymes have been placed to the families gh31 and gh57. the family gh13 together with the families gh70 and gh77 constitutes the clan gh-h, well-known as the α-amylase family. it contains more than 6,000 sequences and covers 30 various enzyme specificities sharing the conserved sequence regions, catalytic tim-barrel fold, retaining reaction mechanism and catalytic triad. among the gh13 α-amylases, those produced by plants and archaebacteria exhibit common sequence similarities that distinguish them from the α-amylases of the remaining taxonomic sources. despite the close evolutionary relatedness between the plant and archaeal α-amylases, there are also specific differences that discriminate them from each other. these specific differences could be used in an effort to reveal the sequence-structural features responsible for the high thermostability of the α-amylases from archaea. key words: α-amylase, glycoside hydrolase families, sequence-structural features, archaebacteria, plants, evolutionary relatedness. 1. introduction starch is an important source of energy for a wide spectrum of animals (including humans), plants and microorganisms. it consists exclusively from glucose monomers that are linked by α-1,4and α-1,6-glycosidic linkages. amylose (15-25% of starch) is formed by α-1,4-linearly bound glucoses, whereas amylopectin (75-85% of starch) contains also the branching points with the α-1,6-linked glucoses (leveque et al., 2000b; bertoldo and antranikian, 2002). starch industry covers many well-developed and also recently established sophisticated technologies that utilize amylolytic enzymes. these amylases represent approximately 30% of the worldwide industrial enzyme production, the starch hydrolysis being considered to be the main way of their use (van der maarel et al., 2002). 2. amylolytic enzymes with regard to a complex structure of starch and related oligoand polysaccharides the starch-degrading organisms have to dispose by relevant 6 janeček, š. combination of starch hydrolases and related enzymes (legin et al., 1998; bertoldo and antranikian, 2002). these enzymes are in general called amylases. the amylolytic enzymes form a large group of starch hydrolases and related enzymes that are active towards starch, pullulan, glycogen and other related oligoand polysaccharides (vihinen and mantsala, 1989; pandey et al., 2000; janecek, 2009). it is a common way of binding of a glucose residue of the substrate in the enzyme active centre, termed conventionally as a substrate-binding subsite (davies et al., 1997), that is responsible for the activity of amylolytic enzymes. most of them belong to glycoside hydrolases (ghs) that constitute the individual gh enzyme families without mutual sequence similarities (henrissat, 1991). now the gh families are part of the cazy web-server (cantarel et al., 2009) that covers also other carbohydrate-active enzymes (fig. 1). fig. 1. carbohydrate-active enzyme (cazy) classification (http://www.cazy.org/). the individual proteins and enzymes are within the cazy server classified into four main groups of sequence-based families: (i) gh, glycoside hydrolases; (ii) gt, glycosyl transferases; (iii) pl, polysaccharide lyases; and (iv) ce, carbohydrate esterases. the cbm stands for the family classification of carbohydrate-binding modules. for details, see cantarel et al. (2009). the most known amylolytic enzymes are α-amylase (ec 3.2.1.1), β-amylase (ec 3.2.1.2) and glucoamylase (ec 3.2.1.3) that are, however, quite different from each other. they differ not only in their primary and tertiary structures, but also in their catalytic machineries and reaction mechanisms employed (janecek, 1994a; pujadas et al., 1996; coutinho and reilly, 1997). they have therefore been classified into different gh families: gh13 α-amylases, gh14 β-amylases, and gh15 glucoamylases (henrissat, 1991). nova biotechnologica 9-1 (2009) 7 the enzymatic hydrolysis of a glycosidic bond can be characterized by a general acid catalysis that requires two essential components: a proton donor (an acid) and a nucleophile (a base). according to the anomeric configuration of the resulting hydroxyl group with regard to conformation of the cleaved o-glycosidic linkage, two basic mechanisms exist for this hydrolysis (fig. 2): retaining or inverting (mccarter and withers, 1994). whereas α-amylase employs retaining mechanism (i.e. the products of its action are α-glucans), both β-amylase and glucoamylase are inverting hydrolases (i.e. they produce β-glucans). fig. 2. (a) retaining reaction mechanism of glycoside hydrolases (macgregor et al., 2001). the proton donor protonates the glycosidic oxygen and the catalytic nucleophile attacks at c1 leading to formation of the first transition state. the catalytic base promotes the attack of the incoming molecule roh (water in hydrolysis or another sugar molecule in trasnglycosylation) on the formation of the covalent intermediate resulting in a second transition state, leading to hydrolysis or transglycosylation product. (b) inverting reaction mechanism of glycoside hydrolases (sauer et al., 2000). the catalytic base (top) and acid (bottom) in the water-assisted hydrolysis of substrate leading to inversion of the configuration of the anomeric carbon. from the structural point of view (fig. 3), both α-amylase and β-amylase rank among the tim-barrel enzymes, i.e. they possess the (β/α)8-barrel catalytic domain, while glucoamylase adopts a helical version of catalytic tim-barrel, the so-called (α/α)6-barrel. within the cazy classification the α-amylases from the family gh13 with closely related families gh70 and gh77 constitute the clan gh-h that is wellknown as the α-amylase family (macgregor et al., 2001; cantarel et al. 2009). it is worth mentioning that some α-amylases with sequences and structures different from the main gh13 α-amylases have been placed to the family gh57 (janecek, 2005) and some amylolytic enzymes are present also in the family gh31 (nakai et al. 2005; kang et al., 2008). (b) (a) 8 janeček, š. fig. 3. three-dimensional structures of amylases. (a) gh13 α-amylase from aspergillus oryzae (pdb code: 2taa; matsuura et al., 1984); (b) gh14 β-amylase from soybean (1bya; mikami et al., 1993) and (c) gh15 glucoamylase from aspergillus awamori (1agm; aleshin et al., 1992). the catalytic machineries of gh13, gh14 and gh15 α-amylases, β-amylase and glucoamylases, respectively, are also different: whereas the enzymes from the family gh13 possess a catalytic triad formed by two aspartates and one glutamate (uitdehaag et al., 1999), both β-amylases (mikami et al., 1993) and glucoamylases (aleshin et al., 1992) have their catalytic machineries formed by two glutamic acid residues that are, however, not alignable due to mutual amino acid sequence differences (pujadas et al., 1996; coutinho and reilly, 1997). it thus could be summarised that amylases and related enzymes classified into the families gh13 (forming with gh70 and gh77 the clan gh-h), gh14, gh15 as well as gh31 and gh57 differ from each other by their amino acid sequences, threedimensional structures, catalytic machineries and reaction mechanism (janecek, 2009). 3. α-amylase enzyme family most of amylolytic enzymes are grouped in the α-amylase family (macgregor et al., 2001). it was originally recognised as a group of starch hydrolases and related enzymes (such as α-amylase, cyclodextrin glucanotransferase, neopullulanase, etc.) that exhibited sequence similarities and commonly predicted tim-barrel fold (macgregor and svensson, 1989; takata et al., 1992). within the sequence-based classification of ghs, it was originally established as the family gh13 (henrissat, 1991), but later the families gh70 and gh77 were added to form the presently well-accepted gh-h clan (macgregor, 2005; janecek, 2009). (a) domain b domain c (β/α)8-barrel (b) (β/α)8-barrel (c) (α/α)6-barrel nova biotechnologica 9-1 (2009) 9 3.1. clan gh-h the above-mentioned families gh13, gh70 and gh77 form the clan gh-h, i.e. the α-amylase family, which at present consists of 30 various enzyme specificities (table 1) and contains more than 6,000 sequences (cantarel et al., 2009). the members of the α-amylase family are not only hydrolases, but also transferases and isomerases. based on amino acid sequence similarities, even some heteromeric amino acid transporter proteins may be considered to be the non-amylolytic members of the clan gh-h (janecek et al., 1997) (fig. 4). not all family enzymes attack the glycosidic bonds in starch; they are active towards the analogous bonds in glycogen, pullulan and other related polyand oligosaccharides, like trehalose, sucrose, etc. (macgregor et al., 2001). whereas the family gh77 is a monospecific family, i.e. it contains only one enzyme specificity amylomaltase (alternative names 4-α-glucanotransferase or disproportionating enzyme; ec 2.4.1.25), the family gh70 consists of two specificties glucosyltransferase (glucansucrase; ec 2.4.1.5) and alternansucrase (ec 2.4.1.140), and the family gh13 is formed by all the remaining enzyme specificies (amylomaltase being also present). gh13 is thus taken as the main α-amylase family (macgregor et al., 2001). enzymes that are members of the α-amylase family have to obey the following four criteria (kuriki and imanaka, 1999; macgregor et al., 2001; janecek, 2002; van der maarel et al., 2002): (i) they act on α-glucosidic bonds (not only the α-1,4and α-1,6-linkages); (ii) they employ the retaining reaction mechanism; (iii) they contain from 4 up to 7 conserved sequence regions; and (iv) they possess the same catalytic machinery within the catalytic tim-barrel fold consisting of the aspartate residue near the end of the strand β4 (catalytic nucleophile), glutamate residue near the end of the strand β5 (proton donor) and aspartate residue near the end of the strand β7 (transition-state stabiliser). the conserved sequence regions (fig. 4) represent the short stretches of amino acid sequence that can be found in every α-amylase family member in equivalent positions and that contain the catalytic triad (asp206, glu230 and asp297; aspergillus oryzae α-amylase numbering; matsuura et al., 1984) and other functionally important residues (nakajima et al., 1986; janecek, 2002). these conserved sequence regions common for the entire clan gh-h may also be used as the sequence “fingerprints” since they contain amino acid residues exclusively specific for the individual enzyme specificities (janecek, 2008). 3.2. glycoside hydrolase family gh13 α-amylase is the most known and widely used enzyme of the gh-h clan. in general, α-amylases are endo-enzymes specific towards the α-1,4-glucosidic bonds, but there are also related gh13 exo-amylases, the so-called maltooligosaccharideproducing amylases (maltogenic α-amylase, maltotriohydrolase, maltotetraohydrolase, etc.), preferentially active at one side of the polysaccharide chain producing small oligosaccharides, such as maltose, maltotriose, maltotetraose, etc. (macgregor et al., 2001). 10 janeček, š. the α-amylase family members are multidomain proteins (fig. 3a) containing the main catalytic domain in the form of a parallel (β/α)8-barrel (domain a) that is interrupted by a usually small domain in the place of the loop 3 connecting the strand β3 with the helix α3 (domain b) and succeeded by the antiparallel β-sandwich domain (domain c). the α-amylase-type of the barrel was confirmed in all members of the αamylase family whose three-dimensional structure has already been determined (fig. 4). the (β/α)8-barrel of α-amylases was first revealed in the structure of taka-amylase a (matsuura et al., 1984), i.e. in the structure of the α-amylase from aspergillus oryzae. since this type of fold was first identified in triose-phosphate isomerase (tim), the (β/α)8-barrel is often simply called tim-barrel (farber and petsko, 1990). it is a barrel of eight inner parallel β-strands surrounded outside by eight αhelices (fig. 3a,b). table 1. the members of the α-amylase family (clan gh-h). enzyme class enzyme ec gh hydrolases α-amylase 3.2.1.1 13 oligo-1,6-glucosidase 3.2.1.10 13 α-glucosidase 3.2.1.20 13 pullulanase 3.2.1.41 13 amylopullulanase 3.2.1.1/41 13 cyclomaltodextrinase 3.2.1.54 13 maltotetraohydrolase 3.2.1.60 13 isoamylase 3.2.1.68 13 dextran glucosidase 3.2.1.70 13 trehalose-6-phosphate hydrolase 3.2.1.93 13 maltohexaohydrolase 3.2.1.98 13 maltotriohydrolase 3.2.1.116 13 maltogenic α-amylase 3.2.1.133 13 maltogenic amylase 3.2.1.133 13 neopullulanase 3.2.1.135 13 maltooligosyltrehalose hydrolase 3.2.1.141 13 maltopentaohydrolase 3.2.1.13 sucrose hydrolase 3.2.1.13 transferases amylosucrase 2.4.1.4 13 glucansucrase 2.4.1.5 70 sucrose phosphorylase 2.4.1.7 13 glucan branching enzyme 2.4.1.18 13 cyclodextrin glucanotransferase 2.4.1.19 13 4-α-glucanotransferase (amylomaltase) 2.4.1.25 13, 77 glucan debranching enzyme 2.4.1.25/3.2.1.33 13 alternansucrase 2.4.1.140 70 maltosyltransferase 2.4.1.13 isomerases isomaltulose synthase 5.4.99.11 13 maltooligosyltrehalose synthase 5.4.99.15 13 trehalose synthase 5.4.99.16 13 hatsa rbat protein --13 4f2hc antigen --13 a hats means the heteromeric amino acid transporter proteins. adapted from janecek (2009). nova biotechnologica 9-1 (2009) 11 fi g. 4 . s eq ue nc e fi ng er pr in ts o f th e αam yl as e fa m ily m em be rs . o ne r ep re se nt at iv e of e ac h en zy m e sp ec if ic ity is p re se nt ed . t he c at al yt ic tr ia d is h ig hl ig ht ed i n ye llo w a nd s ig ni fi ed b y as te ri sk s. t he o th er f un ct io na lly i m po rt an t re si du es c or re sp on di ng w ith h is 12 2, a rg 20 4, an d h is 29 6 of α -a m yl as e ar e al so c ol ou re d. t he w el lco ns er ve d as pa rt at e (b eg in ni ng o f th e st ra nd β 3) i s si gn if ie d by b la ck -a nd -w hi te in ve rs io n. t he r es id ue s co ns er ve d in a t le as t 50 % o f se qu en ce s ar e co lo ur ed w ith g re y ba ck gr ou nd . t he r ep re se nt at iv es o f he te ro m er ic am in o ac id tr an sp or te r pr ot ei ns ( h a t s) a re a ls o sh ow n. t he ‘ y ea r’ d en ot es th e ye ar o f th re edi m en si on al s tr uc tu re d et er m in at io n (i f an y) . a da pt ed fr om j a n e c e k (2 00 2) . 12 janeček, š. the active site of these enzymes is localised at the c-terminal end of the timbarrel (matsuura et al., 1984, qian et al., 1993; kadziola et al., 1994; linden et al., 2003). comparison of known tertiary structures of various α-amylase family members with sequence alignments have shown that differences in specificity result from different variation of substrate binding at the β->α loops (svensson, 1994; janecek, 1997). also the active-site cleft is not of the same shape in each case (kamitori et al., 1999; przylas et al., 2000), despite the fact it always contains the same catalytic triad accompanied, however, by several additional residues depending on a given enzyme specificity (matsuura, 2002). differences especially in the length, sequence and secondary structure have also been seen within the domain b protruding out of the catalytic tim-barrel in the place of the loop 3 (jespersen et al., 1991, 1993). it was pointed out that these differences may be directly related to enzyme specificity (janecek et al., 1997). with regard to domain c succeeding the catalytic tim-barrel, this domain could contribute to the overall catalytic domain stability by shielding the hydrophobic residues of the barrel (katsuya et al., 1998). as far as the conserved sequence regions of the α-amylase family are concerned (fig. 4), four of them (the regions i, ii, iii and iv) belong to the best known regions established more than 20 years ago, whereas the three additional ones (the regions v, vi and vii) were identified more recently. the former regions (friedberg, 1983; nakajima et al., 1986; macgregor et al., 2001), positioned near the c-termini of the β-strands β3, β4, β5 and β7 of the catalytic tim-barrel, contain most of the functionally important residues including the catalytic triad (fig. 4). the latter regions (janecek, 1992, 1994a,b, 1995, 2002), located near the c-terminal end of domain b and of β-strands β2 and β8, cover the features distinguishing the individual enzyme specificities from each other. even the absence of the fifth conserved sequence region, for example, may be used as a feature characteristic of a given specificity (janecek, 2000). although the basic arrangement of the α-amylase family members is the same counting the three domains a, b and c (fig. 3a), it should be taken into account that there are some family members that contain additional cand/or n-terminal domains, for example cyclodextrin glucanotransferase (klein and schulz, 1991) and neopullulanase (hondoh et al., 2003). they may play various and still not completely recognised functions, but most of them have been anticipated to be involved in binding starch (glycogen, pullulan) and related substrate analogues. these non-catalytic domains were in many cases confirmed to have this property and thus have been called starch-binding domains (penninga et al., 1995; sorimachi et al., 1997). it was found that starch-binding domain disrupts the starch surface and thus increases the effect of the amylolytic hydrolysis (southall et al., 1999). within the cazy server (fig. 1), these motifs have been classified into the cbm (carbohydratebinding module) families (cantarel et al., 2009). at present, nine families of starch-binding domains are known: cbm20, cbm21, cbm25, cbm26, cbm34, cbm41, cbm45, cbm48, and cbm53. the motifs from the family cbm20 belong to most intensively studied starch-binding domains (svensson et al., 1989; janecek and sevcik, 1999; rodriguez-sanoja et al., 2005; machovic and janecek, 2006a). based on a detailed bioinformatics analysis it was suggested nova biotechnologica 9-1 (2009) 13 to establish a common cbm clan from the families cbm20 and cbm21 (machovic et al., 2005) and the motifs classified recently into the families cbm48 and cbm53 could also join the proposed cbm clan (machovic and janecek, 2006b, 2008). 3.3. glycoside hydrolase families gh70 and gh77 the family gh70 contains the sucrose-utilising glucosyltransferases (glucansucrase and alternansucrase) that possess a circularly permuted version of the α-amylase-type catalytic tim-barrel (macgregor et al., 1996). the first element of the gh70-type barrel is the α-helix equivalent to helix α3 of the α-amylase-type tim-barrel, whereas the last element is the β-strand equivalent to strand β3 of αamylases (fig. 5). this means that instead of e1-h1-e2-h2….e8-h8 present in αamylases (and overall in both the families gh13 and gh77), in gh70 glucosyltransferases there is h3-e4-h4-e5….h2-e3, where e and h stand for βstrand and α-helix, respectively (macgregor et al., 1996). the glucansucrases are usually large multidomain proteins occurring exclusively in lactic acid bacteria (van hijum et al., 2006). fig. 5. the arrangement of the secondary structure elements in gh70 with respect to gh13 α-amylase type tim-barrel. (a) typical “ordinary” tim-barrel present in the members of the family gh13 (and also gh77); (b) circularly permuted version of the family gh70. the helices are represented by black rectangles and the strands are shown as arrows. the order of the helices in the gh13 (and gh77) is 12345678 from the nterminal end of the protein, whereas in the gh70 the order is 34567812. adapted from macgregor (2005). the structure/function relationships within the family gh70 and its relatedness to the main α-amylase family gh13 were recently elucidated by determining the tertiary structure of the gh70 glucansucrase from leuconostoc mesenteroides (pijning et (a) (b) 14 janeček, š. al., 2008) that has confirmed the previous predictions concerning the circular permutation (fig. 5). the solved structure interestingly revealed that the enzyme adopts the so-called “u-fold” domain arrangement so that 4 of the 5 domains are formed by combining an nand a c-terminal part of the polypeptide chain (dijkstra et al., 2007). the family gh77 contains only one enzyme specificity, the amylomaltase (table 1), known also as 4-α-glucanotransferase in bacteria (terada et al., 1999) and archaeons (kaper et al., 2005) or disproportionating enzyme (d-enzyme) in plants (takaha et al., 1993). they exhibit a lower degree of sequence similarity to the family gh13 (fig. 4) and the main feature characteristic for the gh77 members is the lack of domain c (przylas et al., 2000) succeeding typically the catalytic timbarrel in gh13 (fig. 3). the gh77 structure contains several, mainly α-helical insertions that can be divided into three subdomains (fig. 6): (i) subdomain b1 corresponds with gh13 domain b; (ii) subdomain b2 is unique for the gh77 amylomaltases; and (iii) subdomain b3 is equivalent to gh13 domain c (strater et al., 2002). fig. 6. three-dimensional structure of gh77 amylomaltase from thermus aquaticus (1cwy; przylas et al., 2000). the interest in the family gh77 was recently increased by revealing the putative amylomaltases from a few borreliae that exhibited in their amino acid sequences the non-gh77 features (godany et al., 2008). it was especially the arginine positioned two residues before the catalytic nucleophile in the conserved sequence region ii (fig. 4) that was recognized to be replaced naturally by a lysine in the gh77 amylomaltaselike protein from borrelia burgdorferi (machovic and janecek, 2003). this arginine was otherwise considered to belong to the four residues conserved invariantly throughout the α-amylase family, i.e. the entire clan gh-h (janecek, 2002). the exclusive (i.e. the non-gh77) sequence features present in gh77-like proteins from borreliae have already been confirmed as well as it was determined that the b. (β/α)8-barrel subdomain b2 subdomain b1 subdomain b3 nova biotechnologica 9-1 (2009) 15 burgdorferi gh77 amylomaltase-like protein exhibits a typical amylomaltase activity, i.e. the enzyme catalyzes both the hydrolysis of maltooligosaccharides and formation of their transglycosylation products (godany et al., 2008). based on the bioinformatics analysis of various gh77 real and hypothetical amylomaltases, some of the borrelial gh77-like proteins were suggested to exhibit an intermediary character within this family (janecek, 2008). 3.4. glycoside hydrolase families gh31 and gh57 the families gh31 and gh57 are not the members of the clan gh-h, i.e. they do not belong to the α-amylase family in terms as it is widely accepted (macgregor et al., 2001), but they both deserve some attention here since they contain similar enzyme specificities (α-amylase, α-glucosidase, amylopullulanase, 4-αglucanotransferase, branching enzyme, etc.). the family gh31 contains, in addition to the above-mentioned α-glucosidases (ec 3.2.1.20 similar to gh13), also α-xylosidases and α-glucan lyases (frandsen and svensson, 1998; lee et al., 2005; kang et al., 2008). although it employs the retaining mechanism (fig. 2a) and its members adopt the catalytic tim-barrel domain (fig. 7a) similar to that adopting in the α-amylase family (lovering et al., 2005; fig. 7. three-dimensional structure of (a) gh31 α-xylosidase from escherichia coli (1xsi; lovering et al., 2005) and (b) gh57 4-α-glucanotransferase from thermococcus litoralis (1k1w; imamura et al., 2003). ernst et al., 2006; sim et al., 2008) with even the corresponding catalytic nucleophile (rigden, 2002), the family gh31 has not joined the clan gh-h. one of the reasons is the difference in the proton donors used in gh31 and gh-h (b) (β/α)7-barrel domain ii (β/α)8-barrel domain b domain c (proximal) domain n domain c (distal) (a) 16 janeček, š. (matsuura et al., 1984; uitdehaag et al., 1999; lovering et al., 2005). based on a detailed bioinformatics study, an idea on the so-called remote homologies between the family gh31 and clan gh-h was proposed recently (janecek et al., 2007) indicating a possibility to create a level of evolutionary hierarchy higher than a clan. as far as the family gh57 is concerned, it contains several enzyme specificities that are also members of the main α-amylase family, only the α-galactosidase (ec 3.2.1.22) being different (janecek, 2005; murakami et al., 2006). it also employs the retaining mechanism, but due to a different catalytic domain an incomplete version of a tim-barrel, i.e. a (β/α)7-barrel (fig. 7b) and catalytic machinery (imamura et al., 2003; dickmanns et al., 2006) it should be evolutionarily more distantly related to gh13 than is the family gh31 (janecek, 1998). moreover, gh57 exhibits its own conserved sequence regions (zona et al., 2004) that are different from those characteristic for the clan gh-h (janecek, 2002). 4. α-amylases from archaebacteria and plants at present it is well-known and accepted that plant and archaeal α-amylases from the family gh13 are sequentially similar and evolutionarily related. this remarkable finding was first observed ten years ago (janecek et al., 1999; jones et al., 1999). before the first gh13 α-amylases from archaea became available, the plant αamylases were positioned in the evolutionary tree (fig. 8) on a branch next to the cluster of bacterial liquefying and intracellular α-amylases represented by bacilli and enterobacteria, respectively (janecek, 1994b). 4.1. similarities and differences the first detailed bioinformatics study focused on the archaeal α-amylases and their counterparts from a wide spectrum of remaining living organisms from bacteria and eucarya revealed (janecek et al., 1999) that the sequence features exclusive for the α-amylases from hyperthermophilic archaeons are present also and almost only in the plant α-amylases (fig. 9). these features are as follows (janecek et al., 1999): (i) ile107 (thermococcus hydrothermalis α-amylase numbering; leveque et al., 2000a) succeeding the conserved aspartate in the conserved sequence region region i (strand β3); (ii) (ala194)-trp195 at the beginning, tyr199 in the middle and gly202 at the end of the region ii (strand β4); (iii) ala219 succeeding the conserved tryptophane and tyr223-trp224 succeeding the catalytic proton donor (glu222) in the region iii (strand β5); (iv) ala286 in the region iv (strand β7); (v) ile196 in the region v (located within the loop3, i.e. domain b); (vi) ile42 succeeding the conserved glycine at the beginning and dipeptide pro48-pro49 at the end of the region vi (strand β2); and (vii) gln309 succeeding the conserved glycine at the beginning, tripeptide ile312phe313-tyr314 in the middle and asp316 at the end of the region vii (strand β8). it is worth mentioning that some of the above-mentioned residues have already been recognised as functionally important residues (kadziola et al., 1998; linden et nova biotechnologica 9-1 (2009) 17 fig. 8. the evolutionary tree of microbial (including fungi and yeasts), plant and animal α-amylases. the bacterial sources are abbreviated as follows: dicth, dictyoglomus thermophilum; micsp, micrococcus sp.; bacme, bacillus megaterium; escco, escherichia coli; salty, salmonella typhimurium; bacst, bacillus stearothermophilus; bacam, bacillus amyloliquefaciens; bacli, bacillus licheniformis; bacsu, bacillus subtilis; butfi, butyrivibrio fibrisolvens, xanca, xanthomonas campestris; aerhy, aeromonas hydrophila. the tree does not contain any archaeal α-amylase since at the beginning of 90s of the previous century no sequence of an archaeal α-amylase was available. the red arrow indicates the the cluster of plant αamylases. adapted from janecek (1994b). fig. 9. sequence fingerprints of α-amylases. the enzymes represent the individual taxonomic sources with focus on archaea and plants. the sequence features characteristic of the archaeal α-amylases are highlighted in black-and-white inversion. the catalytic triad is signified by asterisks and yellow highlighting. adapted from janecek (2008). 18 janeček, š. al., 2003). thus for example the glycine from the region ii (gly202 of the archaeal αamylase) serves as a specific ligand for calcium ion and the tryptophane from the region iii (trp224 of the archaeal α-amylase) forms a stacking interaction with one of the acarbose rings bound in the active site in the complex structure of barley αamylase with acarbose (kadziola et al., 1998). these residues should play the same roles in the structure of the archaeal α-amylase from pyrococcus woesei (linden et al., 2003). the close sequence similarity between the α-amylases from archaea and plants has evoked the idea on a possibility to reveal the factors responsible for the high thermostability of the archaeal α-amylases that exhibit the temperature optima around and above 80 oc (leveque et al., 2000b; bertoldo and antranikian, 2002). the plant enzymes are generally substantially less thermostable. it is worth mentioning that on the one side the archaeal and plant α-amylases contain the common sequence features that discriminate them from the remaining sources, but on the other side they have to possess the additional sequence features that should enable one to distinguish them from each other, e.g., the alanine from the region iv (ala286 of the archaeal α-amylase) that has no correspondence in the plant counterparts (fig. 4). such specific differences could be utilized in an effort to identify the molecular basis of high thermostability of the archaeal α-amylases via the approaches of site-directed mutagenesis and protein design. fig. 10. the evolutionary tree of α-amylases. the tree reflects the conserved sequence fingerprints of αamylases (fig. 9). adapted from janecek (2008). nova biotechnologica 9-1 (2009) 19 4.2. evolutionary relatedness the close evolutionary relatedness of the α-amylases from archaea and plants from the family gh13 is shown in figure 10. the gh13 as one of the largest gh families (cantarel et al., 2009) has recently been divided into the subfamilies (stam et al., 2006), the plant and archaeal α-amylases being placed into the subfamilies gh13_6 and gh13_7, respectively. with regard to the α-amylases most closely related to those from plants and archaea (fig. 10), these are the bacterial enzymes from bacillus licheniformis (yuuki et al., 1985) and escherichia coli (raha et al., 1992) that represent the liquefying and intracellular α-amylases, respectively, as observed originally (janecek, 1994b). it should be noted, however, that the close evolutionary relationships between the α-amylases from archaea and plants illustrated here only for a limited sample of living organisms (fig. 10) has been confirmed also in the more recent evolutionary trees comparing a wider spectrum of taxonomic sources including novel groups of α-amylases from bacteria (da lage et al., 2004) and fungi (van der kaaij et al., 2007). acknowledgements: this work was supported in part by the grants no. 1/4363/07 and 2/0114/08 from the slovak grant agency vega and the project av-4/2023/08 from the ministry of education of the slovak republic. references aleshin, a.e., golubev, a., firsov, l.m., honzatko, r.b.: crystal structure of glucoamylase from aspergillus awamori var. x100 to 2.2 å resolution. j. biol. chem., 267, 1992, 19291-19298. bertoldo, c., antranikian, g.: starch-hydrolyzing enzymes from thermophilic archaea and bacteria. curr. opin. chem. biol., 6, 2002, 151-160. cantarel, b.l., coutinho, p.m., rancurel, c., bernard, t., lombard, v., henrissat, b.: the carbohydrate-active enzymes database (cazy): an expert resource for glycogenomics. nucleic acids res., 37, 2009, 233238. coutinho, p.m., reilly, p.j.: glucoamylase, structural, functional, and evolutionary relationships. proteins, 29, 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university yahia farès of médéa, médéa 26000, algeria 3interdepartmental center for industrial agri-food research, university of bologna, cesena, italy 4department of agricultural and food sciences, university of bologna, bologna 33-40126, italy 5centro de referencia para lactobacilos (cerela), conicet, san miguel de tucumán, tucumán 4000, argentina  corresponding author: boubakri.kamel@univ-medea.dz article info article history: received: 20th november 2021 accepted: 7th january 2022 keywords: kaddid starter culture traditional fermentation weissella abstract kaddid is a dry-fermented meat product traditionally produced in north africa by spontaneous fermentation. as a reservoir of natural biodiversity, the identification and relevant traits of lactic acid bacteria (lab) were carried out from south-western algeria homemade samples. after a preliminary physiological and biochemical screening, 19 presumptive lab isolates were selected on the basis of antimicrobial compounds production. the isolates were identified by 16s rrna gene sequencing as weissella cibaria, w. confusa, w. paramesenteroides, pediococcusacidilactici, and enterococcus hirae. as predominant, the safety and technological characterization of weissella strains were performed. the production of antimicrobial and antifungal compounds was observed, while neither h2s, biogenic amines nor hemolytic activity were detected; antibiotic resistance was exhibited, however several strains were more susceptible to assayed antibiotics. technological characterization of weissella strains showed high acidification rates even in the presence of up to 10 % nacl, autolytic and proteolytic capacity however, no eps production and lipolytic activity were observed. strains characterization led to the selection of w. cibaria bk2, w. confusa bk6 and bk11 as well as w. paramesenteroides bk8 to be considered as possible candidates for use as starter culture for kaddid fermentation to improve and standardize this traditional meat product. introduction even today, traditional meat products are generally homemade as a mean to preserve meat to be consumed in times of scarcity. among traditional products, the appreciation of fermented meats is probably related to their unique and specific sensory properties and alleged rootedness in a socio-cultural context. meat products prepared in north african countries are usually dried or cooked because of the weather and are rarely smoked; they are produced from different meat (beef, lamb, goat and camel) depending on the geographic area. dried kaddid has been traditionally used as mailto:boubakri.kamel@univ-medea.dz nova biotechnol chim (2022) 21(2): e1269 2 ingredient to prepare different winter dishes as stews and soups (gagaoua and boudechicha 2018). in algeria, it is prepared by adding salt and spices to lamb meat cutting into thin strips, which are then hang on a string and exposed to the air until thoroughly dried and stored at room temperature; salt content in the final product ranges from 7 % to 12 % (bennani et al. 1995; benlacheheb et al. 2018). microbiological survey of dry-salted kaddid showed the presence of lactic acid bacteria (lab) in addition to microorganisms related to the product hygiene (bennani et al. 2000; ben belgacem et al. 2008, 2010; essid et al. 2009; benlacheheb et al. 2018). physicochemical features of kaddid during ripening such as ph, moisture, salt content and water activity are main modulators of microbiological evolution. it is known that the presence of lab induces desirable attributes to traditional fermented food products, enhancing their typical characteristics while conferring additional safety and health benefits. distinctive features derived from lab metabolic activities in salted meat will determine final quality of fermented products. in view to design novel functional starter cultures, it would be necessary to exploit the autochthonous lab with technological, functional and safety characteristics. a quick growth and high acidification rate in the presence of high salt content are the main criteria for strains selection by which a safe initial environment can be created and food pathogen and spoilage reduced (fusco 2015; fessard and remize 2017). from a safety point of view, the production of antibacterial and antifungal compounds during fermentation are desired features as these metabolites inhibit pathogen and spoilage proliferation. the lack of antibiotic resistance, virulence factors and aminogenesis among other traits, are also required (castellano et al. 2017). in addition, the united nations food and agriculture organization (fao)/world health organization (who) stated the importance to conduct a minimum safety assessment including several specific metabolite productions, toxin production, and potential hemolysis, even for microbial populations classified as gras (fao/who 2002). moreover, changes in meat and fat are responsible for the flavour in fermented meat. proteolysis and lipolysis by meat enzymes and lab will impact on the development of typical sensory characteristics by peptides and amino acids generation (fadda et al. 2010; vignolo et al. 2019). thus, the aim of this study was the identification of the lab population from algerian kaddid samples and traits related to technological and safety features of autochthonous isolated lab were investigated. experimental samples collection and lab isolation samples of homemade kaddid were collected from the southwestern region of algeria, namely tindouf (one sample from camel meat) and béchar (6 samples from lamp meat) provinces. approximately 400 g of ready to consume kaddid pieces from each producer were placed in sterile plastic bags and transported refrigerated to the laboratory for analyses. each sample (10 g) was suspended in 90 ml of sterile tryptone-salt diluents (tryptone 1 g.l-1; nacl 0.85 g.l-1; tween 80 1 ml.l-1), homogenized for 3 min (stomacher 400, seward, worthing, uk) and serially diluted. dilutions were then plated in duplicate on mrs and m17 (merck, darmstadt-germany) media, and microaerobically incubated at 30 °c during 72 h. an average of 20 – 25 colonies per kaddid sample were randomly picked from both media plates containing 100 – 300 colonies. gram-positive and catalase-negative bacteria (presumptive lab) were sub-cultured on the corresponding medium and stored in 25 % of glycerol at -80 °c for further use. physiological and biochemical characterization of lab sixty-three presumptive lab isolates were preliminarily identified according to von wright and axelsson (2012) and the scheme described by carr et al. (2002). growth at 10 ºc and 45 ºc during 7 d and 24 h, respectively, at ph 4 to 9.6 and in the presence of 4 to 10 % nacl were evaluated in mrs (bacilli) and m17 (cocci). production of gas (co2) from glucose (gibson and abdelmalek 1945) and arginine hydrolysis (møller 1955) were analyzed. for carbohydrate nova biotechnol chim (2022) 21(2): e1269 3 fermentation mevag medium (biokar diagnostic, allonne, france) supplemented with different sugars (table 1) was used, lab suspensions being inoculated by a central puncture and covered by a vaseline layer to promote anaerobiosis; after incubation (30 °c; 24 h) color changes due to the sugars utilization by bacteria were recorded. molecular identification genomic dna was extracted from pure lab cultures using instagene matrix (bio-rad laboratories inc., hercules, usa). molecular identification was performed as described by montanari et al. (2015). the partial 16s rrna gene sequence was amplified using the primers lpigf/lpigr (5’-tacgggaggcagcagtag3’ and 5’-catggtgtgacgggcggt-3’; eurofins genomics germany gmbh, ebersberg, germany). pcr amplifications were performed using taq dna polymerase kit from thermo fisher scientific (waltham, usa). reaction mixtures consisted of buffer 5x, 2 mm mgcl2, 50 mm each of the 4 deoxynucleoside triphosphates (dntp), 1.25 u of taq-polymerase, 0.5 mm of each primer, and 0.5 μl of appropriately diluted template dna in a final volume of 50 μl. amplification was performed on a biometra t3000 thermal cycler (analytik jena gmbh, jena, germany) with initial denaturation at 94 °c for 5 min, then 34 cycles at 94 °c for 1 min, 55.5 °c for 2 min, and 72 °c for 2 min, followed by final extension at 72 °c for 10 min. pcr products were separated by electrophoresis on 1.5 % (w/v) agarose gel (lonza, italy) stained with ethidium bromide (0.5 μg.ml-1). the 600 bp amplicons were eluted from an agarose gel, purified with the qiaquick pcr purification kit (qiagen, hilden, germany) and sequenced at the bmr genomics srl. sequencing facility (padova, italy) using the same primers as for amplification. sequence similarity searches were performed using blast network service (http://blast.ncbi.nlm.nih.gov/) and ez-taxon server (http://147.47.212.35:8080/). antimicrobial activity lab (63 strains) inter-species inhibitory capacity was first investigated by using the disc method described by tadesse et al. (2004) with modifications. overnight lab cultures (0.5 ml) used as indicators were mixed with 12 ml of melted and cooled mrs agar media, poured into plates, let solidify and dried. lab cultures were centrifuged (7,000 × g; 15 min) and the obtained cell free supernatants were used to impregnate sterile filter paper discs that were deposited on the seeded agar. on the other hand, the antibacterial activity of identified weissella isolates was evaluated by a semi-quantitative agar-spot-test as described by fontana et al. (2015) against gram positive and gram-negative bacteria (table 3). overnight lab cultures were centrifuged (7,000 × g; 15 min), and supernatants (5 µl) were spotted onto 10 ml of bhi agar (britania, argentina) plates (0.7 %) previously inoculated with 50 µl of each indicator strain. plates were incubated at 30 °c for 48 h and the presence of a clear inhibition zone around the spots was considered as a positive antagonistic effect. inhibitory activity was expressed as + (halos presence) or – (no halos) around the spot. positive antibacterial activity lab supernatants were neutralized (4n naoh) and treated with catalase (1,000 u.ml-1) (sigmaaldrich, st louis, usa) to determine the chemical nature of the inhibitory substance. antifungal activity against aspergillus flavus, penicillium expansum, and fusarium oxysporum albedinis was investigated by a modified agar diffusion assay (magnusson et al. 2003). petri plates containing potato dextrose agar (pda) were inoculated with the fungus and incubated at 25 °c during 48 h. after visible formation of conidiospores, they were collected and adjusted to 105 spores/ml of sterile saline solution. lab selected strains were streakinoculated on mrs agar plates and after incubation (30 °c; 48 h), plates were overlaid with 10 ml of pda soft agar (0.7 % agar) containing fungal spore suspensions (104.ml-1) and incubated aerobically (30 °c; 48h). plates were then examined for clear inhibition zones around the lab streaks and scored as – (no growth inhibition), + (1 – 5 mm growth inhibition), ++ (5 – 10 mm growth inhibition) and +++ (˃ 10mm growth inhibition). 3 http://blast.ncbi.nlm.nih.gov/ http://147.47.212.35:8080/ nova biotechnol chim (2022) 21(2): e1269 2 biogenic amines and h2s production the ability to decarboxylate amino acids used as precursor was tested according to bover-cid and holzapfel (1999). briefly, the plates with the agar medium, supplemented with histidine, tyrosine, ornithine, and lysine 1 % (w/v) were spotted with the active weissella (7 strains) and incubated anaerobically (30 °c; 2 – 5 d). growth of decarboxylating strains was easily recognizable because of a purple halo in the yellow medium. production of h2swas investigated on tsi (triple sugar iron) agar medium by a central puncture inoculation. after incubation (30 °c; 48 – 72 h), h2s production was confirmed by the blackening of the medium and gas bubbles in the agar (guiraud 2003). antibiotic resistance antibiotics recommended for the european food safety authority (efsa 2012) to identify bacterial strains with potential acquired resistance were used. ampicillin (amp; 0.032 – 16 g.ml-1), vancomycin (van; 0.25 – 128 g.ml-1), chloramphenicol (chl; 0.125 – 64 g.ml-1), gentamycin (gen; 0.5 – 256 g.ml-1), streptomycin (str; 0.5 – 256 g.ml-1), kanamycin (kan; 2 – 1024 g.ml-1), tetracycline (tet; 0.125 – 64 g.ml-1), erythromycin (ery; 0.016 – 8 g.ml-1) and clindamycin (cli; 0.032 – 16 g.ml1) were tested. the minimum inhibitory concentration (mic) of antibiotics was determined by the broth micro-dilution method reported by the iso 10932/idf 233 standard. the strains were classified as susceptible or resistant according to the cut-off values proposed by efsa (2012). a bacterial strain was defined as susceptible or resistant when it was inhibited or not, at a specific antimicrobial concentration equal or lower than the established cut-off value. hemolysin and gelatinase activity hemolysin activity was determined on columbia blood agar (oxoid) containing 5 % defibrinized horse blood after 48 h of incubation at 37 °c, both under aerobic and anaerobic conditions. the type of hemolysis (α, β or ɣ) was determined. staphylococcus aureus atcc25923 and escherichia coli atcc25922 were used as positive control for βand α–hemolysis, respectively. zones of clearing around colonies indicated -hemolysin production. gelatinase production was detected by inoculating lab onto freshly prepared peptone yeast extract agar containing gelatin (30 g.l-1; difco). plates were incubated overnight at 37 °c and cooled at room temperature for 2 h. the presence of turbid zone around the colonies was considered as positive result. growth and acidification selected weissella strains were inoculated (1 %) into mrs broth, incubated at 10, 30, 37 and 44 °c for 48 h and growth at od620 was measured. similarly, the growth of each strain was evaluated in mrs with ph adjusted to ph 4.5, 5, 6, 7, 8 and 9.6 and supplemented with 4, 6.5 and 10 % nacl. the od620 was measured at 0, 2, 4, 6, 24 and 48 h. acidification ability was evaluated as reported by ammor et al. (2005), using sausage-broth (sb) medium. eighty (80) ml of sb medium was inoculated with an overnight culture of each strain. the ph values and od620 were recorded after 0, 3, 6, 24, 48, 72 and 96 h of incubation at 30 °c using a ph meter and a spectrophotometer. autolytic activity and thermoresistance each strain was suspended in pbs buffer (ph 7) at a do620 : 0.2 and subjected to a freeze cycle (-20 °c for 24 h) and after thawing, strains were incubated at 30 °c for 24 h. autolytic activity was determined by the decrease percentage in absorbance at d620 after time interval (piraino et al. 2008) as %aa: (ai-at) × 100/ai, where aa: autolytic activity, ai: initial absorbance and at: absorbance after 24 h of incubation. autolysis was classified according to lactobacilli genus (ayad et al. 2004), ranged from 70 – 96 % (good), 40 – 69 % (low) and 0 – 39 % (poor). thermo-resistance was evaluated as reported by badis et al. (2004); lab strains inoculated in mrs broth were heated at 60.5 °c during 30 min, and then incubated at 30 °c for 24 to 48 h and the colonies in mrs agar were enumerated. 4 nova biotechnol chim (2022) 21(2): e1269 3 proteolytic and lipolytic activities five microliters (5 μl) of each lab strain suspended in pbs buffer (ph 7) were spot inoculated onto tryptone soy agar (tsa) supplemented with sterile skim milk (10 %) as described by guiraud (2003). after incubation at 30 °c for 5 d, the caseinolytic activity (measured in mm) was determined by the presence of a clear area around the spot. for lipolytic activity, the technique reported by mauriello et al. (2004) with minor modifications was used. one ml of lab overnight cultures was inoculated into 10 ml of a broth containing tryptone (1 % (w/v)), yeast extract (0.5 % (w/v)), nacl (3 % (w/v)), ph 7.0, supplemented with 4 % (w/v) lamb fat previously homogenized by vigorous shaking. after incubation at 30 °c for 7 d, free fatty acids were then determined. the lipids were extracted into 10 ml of petroleum ether by shaking for 1 min. the fatty acids of the upper phase were titrated with naoh (0.1 m) in ethanol using 1 % phenolphthalein-ethanol solution as indicator. results were expressed as % of oleic acid by a × n × 28.2/g, where a: ml naoh used for titration, n: naoh normality, 28.2: % of oleic acid equivalent weight and g: amount of lamb fat used. exopolysaccharides (eps) production active cultures of lab strains were spotted on mrs agar in which glucose was replaced by sucrose and incubated at 30 °c for 2 – 7 d. ropiness was examined by the presence of a ropy condition after touching the colony with a loop. statistical analysis agar assays were performed by duplicate and growth curves by triplicate. in the case of antibiotic resistance, media values were compared with cutoff points. the media and sd were calculated for growth data, results (means od ± sd) being evaluated by the application of anova to define differences and statistical significances were determined by the tukey test. results and discussion physiological and biochemical characterization of lab isolates sixty-three presumptive lab isolates (42 cocci and 21 bacilli) were subjected to a preliminary characterization. results showed that 10 % of the isolates produced gas from glucose (table 1). among homofermentative cocci/coccobacilli isolates, those tetrads-forming cocci (23.8 %) that grew at 10 °c and 40 – 45 °c, up to 10 % nacl but not at ph > 8.0 were presumed as pediococcus. however, chains-forming homofermentative cocci (47.7 %) that developed at the same temperatures, in a wider ph range (4.0 to 9.6) and up to 6.5 % nacl were assigned to enterococcus genus, differing from lactococci in that the latter are not able to grow at 40 – 45 °c. on the other hand, heterofermentative cocci/coccobacilli isolates (28.6 %) able to grow at 10 °c, up to 6.5 % nacl and ph between 4.5 and 8.0 (arginine mostly positive and variable growth at ph > 6.0, between 40 – 45 °c and nacl > 6.5 %) have been characterized as presumptive leuconostoc or weissella. concerning bacilli (21 %) involving homo and heterofermentative isolates would be assigned to lactobacillus or weissella genus with variable arginine hydrolysis, ability to grow between 40 – 45 °c in a wide range of ph and resistant to nacl and sugar fermentation capacity except for xylose. sugars fermentation for cocci/coccobacilli isolates exhibited variable carbohydrates fermentation; heterofermentative coccobacilli fermented cellobiose, fructose, maltose, mannose, sucrose, and xylose but not melibiose, raffinose, sorbitol and trehalose. based on phenotypic, morphologic and biochemical characterization, ph, temperature, salt tolerance and sugars fermentation, it can be preliminary suggested that cocci/coccobacilli isolates belong to pediococcus, enterococcus, leuconostoc, weissella and lactobacillus genera. these results agree with the lab from high saltcontaining fish and meat products (najjari et al. 2008; ben belgacem et al. 2010; belfiore et al. 2013). 5 nova biotechnol chim (2022) 21(2): e1269 2 molecular identification of isolates exhibiting antimicrobial activity after the first inter-lab species inhibition assay, selected isolates (19) were subjected to molecular identification. table 1. physiological and biochemical characterization of lab isolated from kaddid. physiological traits cocci/coccobacilli (42) bacilli (21) homofermentative heterofermentative homo/hetero microscopy cocci/ tetrads cocci/ chains coccobacilli single/pairs chains/ pairs co2 from glucose – – + +/– arginine hydrolysis +(v) +/– – +/– growth at 10 °c + + + + 45 °c + + +/– v nacl 4% + + + + 6.5% + + +/– + (v) 10% + +/– – (v) + (v) ph 4.5 + + + + 6.5 + + + (v) + 8.0 – + +/– v 9.6 – + – – d-glucose + + + + d-arabinose +/– +/– +/– +/– d-cellobiose – +/– + + d-fructose +/– + + + d-galactose +/– + +/– + d-lactose + + + + d-maltose – – + + d-mannose – + + + d-mannitol + – +/– + d-melibiose – +/– – + d-ribose + +/– + + d-raffinose +/– – – +/– d-sorbitol +/– +/– – +/– d-sucrose +/– + + +/– d-trehalose – + – + d-xylose +/– +/– + – + = positive; – = negative; +/– = more or less positive; v = variable. in parallel with the physiological/biochemical characterization, amplification of partial 16s rrna gene sequence allowed the identification of 15 isolates as weissella (w.) cibaria/confusa with a similarity level of 99 to 100 %, one isolate as w. paramesenteroides (similarity 99.87 %), two isolates as p. acidilactici (similarity > 99 %) and one isolate as e. hirae (similarity 99.77 %), (table 2). this result indicated that most of labs were heterofermentative, while only three strains were homofermentative. because weissella species constituted the major population among identified lab, they were used for further studies. high relatedness of w. cibaria and w. confusa observed in this study agrees with that described by lynch et al. (2015). however, based on differential capacity to ferment carbohydrates, w. cibaria was described to ferment arabinose but not galactose and ribose, while these latter were utilized by w. confusa (björkroth et al. 2002; quattrini et al. 2019). results from carbohydrates fermentation were used to complement molecular identification (table 1). thus, strains were distinguished as w. cibaria (bk1, bk2, bk3, bk9, bk10, bk13, bk18, bk19), w. confusa (bk4, bk5, bk6, bk7, bk11, bk12, bk16), w. paramesenteroides (bk8), p. acidilactici (bk14, bk17) and e. hirae (bk15) as shown in table 2. species of this genus have been isolated from a wide range of ecological niches including soil, plants, breast milk, oral cavity, urogenital and git tract of humans and animals as well as a huge variety of fermented foods (abriouel 6 nova biotechnol chim (2022) 21(2): e1269 3 et al. 2015; fusco et al. 2015; maldonado et al. 2018). from a technological point of view, weissella plays a key role in food fermentation based on vegetables and to a lesser extent in meat. however, the identification of w. cibaria, w. confusa and w. paramesenteroides from dry-salted algerian kaddid agrees with those reported during dry-cured sausages fermentation (fusco et al. 2015). indeed, w. cibaria and w. confusa were previously retrieved from portuguese fermented sausages, thai pork sausages (nham), morcilla de burgos and fermented fish (santos et al. 2005; srionnual et al. 2007; albano et al. 2009; kopermsub and yunchalard 2010; wongsuphachat et al. 2010). likewise, w. paramesenteroides was identified from italian fermented sausages (urso et al. 2006; papagianni and papamichael 2011). although w. cibariahas been first isolated from thai fermented meat (björkroth et al. 2002), together with w. confusa have been associated with a wide range of vegetable fermented products and their ability to use plant carbohydrates was reported (fusco et al. 2015). besides plant sugars utilization, w. confusa and w. paramesenteroides showed to use ribose, suggesting they also may grow in meat. table 2. lactic acid bacteria (lab) strains identified from dried salted algerian kaddid. lab isolates isolation source closest relative identity [%] accession no.* bk1 sk1 weissella cibaria 99.41 % mt158598.1 bk2 sk1 weissella cibaria 99.87 % mt012260.1 bk3 sk1 weissella cibaria 99.87 % mt012260.1 bk4 sk2 weissella confusa 100 % mk503640.1 bk5 sk2 weissella confusa 100 % mk503640.1 bk6 sk3 weissella confusa 99.76 % mk503640.1 bk7 sk3 weissella confusa 100 % mk503640.1 bk8 sk4 weissella paramesenteroides 99.87 % mn994365.1 bk9 sk4 weissella cibaria 99.75 % mt012260.1 bk10 sk5 weissella cibaria 99.55 % mt012260.1 bk11 sk5 weissella confusa 99.50 % mk503640.1 bk12 sk6 weissella confusa 99.88 % mk503640.1 bk13 sk6 weissella cibaria 99.65 % mt012260.1 bk14 sk6 pediococcus acidilactici 99.74 % cp050079.1 bk15 sk7 enterococcus hirae 99.77 % mt197246.1 bk16 sk7 weissella confusa 99.05 % mk503640.1 bk17 sk7 pediococcus acidilactici 99.88 % cp050079.1 bk18 sk7 weissella cibaria 100 % mt012260.1 bk19 sk7 weissella cibaria 99.75 % mt012260.1 sk – sample of kaddid. kaddid southwestern algerian samples were from: sk1, sk2, sk3 (béchar city), sk5 (beniounif), sk6 and sk7(igli) from béchar province, and sk4 from tindouf province. *sequence similarity searches were performed using blast networkservice (http://blast.ncbi.nlm.nih.gov/). antimicrobial activity in a first attempt to distinguish those isolates exhibiting inhibitory activity, from 63 lab isolates preliminarily assigned to different lab genera, 19 of them showed inter-species antagonistic activity (result not shown) suggesting the presence of antibacterial metabolite/s in the supernatant. indeed, when neutralized supernatants and catalase addition were evaluated, the inhibitory activity was suppressed indicating that organic acids or some compound of protein nature would be responsible for the antibacterial effect. the production of inhibitory metabolites active against food pathogens could be an important improvement for starter cultures and might be of interest in controlling meat fermentation, which naturally contain competing food-borne pathogens. therefore, as a dominant population, sixteen labs assigned to weissella genus were investigated for their antibacterial and antifungal activity against a range of pathogens and contaminants (table 3). results showed weissella isolates bk2, bk3 and bk19 as the highest inhibitory strains against the assayed pathogens. bacteriocin production by weissella species was widely reported, especially 7 https://www.ncbi.nlm.nih.gov/nucleotide/mt158598.1?report=genbank&log$=nucltop&blast_rank=2&rid=89bpjf6n01r https://www.ncbi.nlm.nih.gov/nucleotide/mt012260.1?report=genbank&log$=nucltop&blast_rank=1&rid=89dnr0xf016 https://www.ncbi.nlm.nih.gov/nucleotide/mt012260.1?report=genbank&log$=nucltop&blast_rank=1&rid=89efxj7z014 https://www.ncbi.nlm.nih.gov/nucleotide/mk503640.1?report=genbank&log$=nucltop&blast_rank=2&rid=89epeghv014 https://www.ncbi.nlm.nih.gov/nucleotide/mk503640.1?report=genbank&log$=nucltop&blast_rank=2&rid=89f7yzyh014 https://www.ncbi.nlm.nih.gov/nucleotide/mk503640.1?report=genbank&log$=nucltop&blast_rank=2&rid=89fp23gy01r https://www.ncbi.nlm.nih.gov/nucleotide/mk503640.1?report=genbank&log$=nucltop&blast_rank=2&rid=89fxm8by014 https://www.ncbi.nlm.nih.gov/nucleotide/mn994365.1?report=genbank&log$=nucltop&blast_rank=1&rid=89gnjhaw01r https://www.ncbi.nlm.nih.gov/nucleotide/mt012260.1?report=genbank&log$=nucltop&blast_rank=1&rid=89mtemfx014 https://www.ncbi.nlm.nih.gov/nucleotide/mt012260.1?report=genbank&log$=nucltop&blast_rank=1&rid=89n8wemv014 https://www.ncbi.nlm.nih.gov/nucleotide/mk503640.1?report=genbank&log$=nucltop&blast_rank=2&rid=89njnt5g016 https://www.ncbi.nlm.nih.gov/nucleotide/mk503640.1?report=genbank&log$=nucltop&blast_rank=2&rid=89pjr8fz014 https://www.ncbi.nlm.nih.gov/nucleotide/mt012260.1?report=genbank&log$=nucltop&blast_rank=1&rid=89rv1pyc01r https://www.ncbi.nlm.nih.gov/nucleotide/cp050079.1?report=genbank&log$=nucltop&blast_rank=1&rid=89st2gre014 https://www.ncbi.nlm.nih.gov/nucleotide/mt197246.1?report=genbank&log$=nucltop&blast_rank=1&rid=89t640s2016 https://www.ncbi.nlm.nih.gov/nucleotide/mk503640.1?report=genbank&log$=nucltop&blast_rank=2&rid=89tj232x014 https://www.ncbi.nlm.nih.gov/nucleotide/cp050079.1?report=genbank&log$=nucltop&blast_rank=1&rid=89tsx2w701r https://www.ncbi.nlm.nih.gov/nucleotide/mt012260.1?report=genbank&log$=nucltop&blast_rank=1&rid=89u1554w016 https://www.ncbi.nlm.nih.gov/nucleotide/mt012260.1?report=genbank&log$=nucltop&blast_rank=1&rid=89u7cp5h016 http://blast.ncbi.nlm.nih.gov/ nova biotechnol chim (2022) 21(2): e1269 2 with activity against other lab species (fusco et al. 2015). the exceptional inhibitory ability against e. coli, s. typhimurium and pseudomonas was in coincidence with that reported for weissella species (woraprayote et al. 2015; fessard and remize 2017). in addition, supernatants of the examined presumptive weissella exhibited a high inhibitory activity against l. monocytogenes scott a, gm1 and gm2 and l. innocua atcc51742 and dsm20649 as well as s. aureus atcc 29213 indicator strains, with inhibition zones between 8 to 20 mm, whereas enterococcus and pediococcus were not inhibited. the ability of weissella isolates to prevent listeria and staphylococcus growth agree with those reported for w. paramesenteroides, w. hellenicaand w. viridescens from pickles, sea foods and meat fermented products (papagianni and papamichael 2011; masuda et al. 2012; leong et al. 2013; chen et al. 2014; castilho et al. 2019). moreover, the antifungal activity of 10 out of 16 weissella isolates against fungal indicators (table 3) coincide with that reported for w. cibaria, w. confusa and w. paramesenteroides against other phytopathogenic or food fungal strains (trias et al. 2008; valerio et al. 2009; ndagano et al. 2011; bianchini et al. 2015; quattrini et al. 2019). the production of lactic and acetic acids by heterofermentative weissella may account for their great inhibitory activity, in agreement to fungal inhibitory compounds production reported by gerez et al. (2013). due to their antimicrobial activity, weissella have been found to act as foodbiopreservatives and probiotics in humans and animals (abriouel et al. 2015; fusco et al. 2015). the production of antimicrobial compounds is desired, thus the proliferation of pathogens or spoilage microorganisms can be controlled during fermentation. based on these antimicrobial features, w. cibaria bk2, bk3 and bk19, w. confusa bk4, bk6 and bk11, and w. paramesenteroides bk8 were selected to investigate their major safety and technological properties. safety evaluation although many lab species have been recognized as gras organisms by fda (1999) or have attained the qps status by efsa (2004), no weissella species were included. studies on antibiotic resistance profile of this genus are limited, and mic cut-off has not still defined by efsa. when weissella strains resistance/sensitivity to clinical antibiotics was investigated (table 4), a multiresistance pattern was found, this being in correlation with that described by abriouel et al. (2015). similar to other lab, w. cibaria, w. confusa and w. paramesenteroides exhibited intrinsic resistance to van (ouoba et al. 2008). however, additional high resistance to kan, gen and tet was exhibited for all weissella strains, strains bk3 and bk19 were also resistant to str and chl, this being in coincidence with those reported for strains isolated from chinese dry fermented meat product (wang et al. 2018) and fermented salted squid (le and yang 2018). similar resistance to gen and kan of w. cibaria strain from goat milk was described (elavarsi et al. 2014), and str resistance of w. cibaria and w. confusa from fruit/juices was also reported (xu et al. 2018). however, the investigated strains were sensitive to ery, which disagree with that found for w. cibariaof vegetable origin (xu et al. 2018; dentice maidana et al. 2019). antibiotic resistance patterns found here are related to the controversial nature of weissella genus reported by abriouel et al. (2015), and the lack of use as commercial starter so far (fessard and remize 2017). despite the resistance to aminoglycosides kan and gen, w. cibaria bk2 was the more sensitive among assayed strains. within the framework of food safety, weissella strains were also investigated for their hemolytic and gelatinase activity as well as biogenic amines production. results showed neither gelatinase nor -hemolytic activity was exhibited by weissella strains, only -hemolysis being observed. similarly, biogenic amines were not produced by the analyzed strains (data not shown). due to their controversial status, determination of these safety traits for weissella strains help in carefully selecting strains lacking pathogenic potential. technological characterization in view to select weissella strain/s to be used for kaddid fermetnation, several technological traits 8 nova biotechnol chim (2022) 21(2): e1269 3 were evaluated. the strains tested showed a good adaptation towards cultural stresses, such as temperature, nacl concentration and ph (table 4). acidification showed ph values between 2.10 and 2.37 units after four days, showing a decrease to 4.03 – 4.27 after 6 h of incubation at 30 °c, reaching final values (96 h) in the range of 3.80 – 4.10 (data not shown). the ph reduction is in correlation with the acid production by lab strains, w. paramesenteroides bk8 being the most acidogenic. the average acidification rate of assayed strains resulted in 0.55 units/day, which was higher than that of traditional kaddid (benlacheheb et al. 2018). as expected, optimal temperature for weissella strains was 30 °c reaching od620 between 1.96 and 2.11 at 48 h with an average growth rate of 0.47/h. when nacl concentration increased from 4 to 10 % a decrease in weissella growth from od620 of 1.68 to 0.06 was produced, w. paramesenteroides bk8 being the most resistant to 10 % of nacl (table 4). osmotic adaptation of strains correlated with their growth under the high salt concentration of kaddid. to prevent spoilage/pathogens proliferation, quick growth/acidification capacity is an important criterion for the selection of lab starter. in addition, the evaluation of enzymatic activities that could play a role in the flavor development, such as the release of intracellular enzymes by cell lysis (autolysis) showed values in the range of 4.23 – 8.08 %, while proteolytic activity was only exhibited by w. confusa bk11.autolysis of weissella strains at 24 h here obtained showed lower values compared to that reported for w. confusa strain isolated from indian fermented foods (sharma et al. 2018). all weissella strains showed to be thermoresistant when heated at 60.5 ºc during 30 min while no lipolytic activity was detected (data not shown). similarly, a lack of lipolytic activity was also reported for lactobacillus plantarum isolated from tunisian kaddid (essid et al. 2009), but were able to hydrolyze casein, contrarily to the results for w. cibaria strains in this study. w. cibaria has been reported to have an extensive peptidolytic activity (lynch et al. 2015); perhaps the use of casein as a protein source did not allow evidencing this activity. furthermore, the lack of h2s and eps production favor their use as starter culture in meat fermentation; even when the ability to produce eps is a common trait for w. cibaria and w. confusa (fusco et al. 2015; lynch et al. 2015; quattrini et al. 2019), formation of these compounds in meat products would lead to an indication of sensory spoilage. therefore, based on antimicrobial activity, antibiotic resistance patterns, growth, and acidification, nacl tolerance and moderate protein hydrolysis as well as the lack of virulence factors and adverse sensory traits, the strains w. cibaria bk2, w. confusa bk6 and bk11 as well as w. paramesenteroides bk8 may be selected as candidates to be used in the fermentation of algerian kaddid. conclusion microbiological examination of southwestern algeria dried and salted kaddid samples, was performed. antimicrobial activity and other safety traits of lab isolates were used to select those inhibitory against food pathogens and contaminants, with low antibiotic resistance, unable to produce virulence factors and not aminogenic. molecular identification showed weissella species as dominant population and in a lesser extent p. acidilactici and e. hirae. in view to use these strains as autochthonous starter and functional culture, weissella strains showing technological and safety traits allowed selecting w. cibaria bk2, w. confusa bk6 and bk11 as well as w. paramesenteroides bk8 as valuable candidates which may contribute not only to improve overall quality but also preserve typicality, which benefits for both producers and consumers. acknowledgements the authors thank the university yahia-fares in médéaalgeria, as well as the fellowship grant in italy, to perform some trials as molecular identification of strains. also, a particular thanks to algerian ministry of hight education and scientific researche (mhesr) for the scholarship longstay (pne 2018/2019, n° 256) at cerela-conicet, tucumán, argentina. conflict of interest the authors declare that they have no conflict of interest. 9 nova biotechnol chim (2022) 21(2): e1269 3 table 3. antimicrobial activity of weissella strains isolated from algerian kaddid. cfs – cell free supernatant. kaddid southwestern algerian samples sk1, sk2, sk3 (béchar city), sk5 (beniounif), sk6 and sk7 (igli) from béchar province, and sk4 from tindouf province. *antibacterial activity is expressed by inhibition zone diameter (mm); ** antifungal activity expressed as: – no growth inhibition), + (1 – 5 mm growth inhibition), ++ (5 – 10 mm growth inhibition) and +++ (˃ 10 mm growth inhibition). indicator microorganism isolated bacteria antibacterial and antifungal activity of bacterial cfs bk1 bk2 bk3 bk4 bk5 bk6 bk7 bk8 bk9 bk10 bk11 bk12 bk13 bk16 bk18 bk19 samples source sk1 sk1 sk1 sk2 sk2 sk3 sk3 sk4 sk4 sk5 sk5 sk6 sk6 sk7 sk7 sk7 gram (-)bacteria* escherichia (e.) coli algerian meat 10.5 2.5 6 e. coli atcc25922 salmonella (s.) bongori algerian meat 2.5 5.5 7.5 6.5 3 s. typhimurium atcc2572 11.5 5.5 7.5 7.5 6.5 8 7 4.5 12 klebsiella pneumoniae algerian kaddid (sk4) 10.5 4.5 2.5 10 citrobacter farmeri algerian kaddid (sk1) 5.5 4 pseudomonas (p). frederiksbergensis algerian kaddid (sk2) 11.5 4.5 6 7 14 p. aeruginosa atcc27853 9.5 8.5 4 5 acenitobacter baumanii atcc 19606 5 4 6 gram (+) bacteria* listeria (l.) monocytogenes scott a 8 9 11 14 8 9 11 15 10 9 12 19 18 15 16 16 l. monocytogenes atcc13932 l. monocytogenesgm1 italian chicken meat 9 15 14 15 15 13 10 12 13 14 9 8 12 15 12 14 l. monocytogenes gm2 italian chicken meat 6 7 11 14 13 10 13 14 14 14 12 8 10 7 13 15 l. monocytogenes atcc 15313 7.5 10 l. innocua atcc51742 10 16 13 11 12 13 10 13 13 12 13 13 13 10 15 15 l.innocua dsm20649 13 8 12 16 15 15 9 16 20 13 15 11 14 19 bacillus cereus atcc 10876 enterococcus (en.) faecalis atcc 49452 9 7 en. faecalis atcc 29212 en. hirae bk15 algerian kaddid (sk5) staphylococcus (s.) aureus atcc 25923 10 7 s. aureus atcc 29213 9 18 16 16 15 15 13 13 15 14 14 14 14 13 13 14 staphylococcus sp. algerian kaddid (sk3) 5 pediococcus acidilactici bk14 algerian kaddid (sk6) molds** penicillium expansum algerian wheat aspergillus flavus algerian wheat + +++ ++ +++ + + ++ fusarium oxysporum albedinis algerian dates + +++ +++ +++ +++ ++ ++ +++ 10 nova biotechnol chim (2022) 21(2): e1269 3 table 4. safety and technological characterization of weissella strains from algerian kaddid. *ph was determined in sb as ph (96 h) – ph (0 h). van – vancomycin; chl – chloramphenicol; gen – gentamycin; str – streptomycin; kan – kanamycin; tet – tetracycline. weissella strains antibiotic resistance ph* growth (od620) at 48 h autolytic activity [%] temperature [°c] nacl [%] 10 30 44 4 6.5 10 w. cibaria bk2 van/kan/gen 2.10 ± 0.02 0.13 ± 0.01 2.10 ± 0.40 1.10 ± 0.3 1.63 ± 0.12 1.23 ± 0.14 0.04 ± 0.00 6.03 ± 0.05 bk3 van/kan/chl/str 2.10 ± 0.01 0.15 ± 0.02 2.10 ± 0.08 1.87 ± 0.33 1.63 ± 0.32 1.23 ± 0.00 0.02 ± 0.01 6.06 ± 0.17 bk19 van/kan/gen/tet/chl 2.10 ± 0.00 0.15 ± 0.02 2.08 ± 0.11 1.85 ± 0.26 1.63 ± 0.17 1.23 ± 0.11 0.02 ± 0.0 8.08 ± 0.2 w. confusa bk4 van/kan/gen/tet 2.10 ± 0.03 0.15 ± 0.00 1.96 ± 0.23 1.87 ± 0.70 1.57 ± 0.09 1.23 ± 0.03 0.06 ± 0.01 4.23 ± 0.37 bk6 van/kan/gen 2.10 ± 0.11 0.19 ± 0.03 2.11 ± 0.07 1.85 ± 0.29 1.63 ± 0.44 1.23 ± 0.10 0.05 ± 0.00 4.23 ± 0.10 bk11 van/kan/gen 2.15 ± 0.07 0.13 ± 0.01 2.10 ± 0.17 1.68 ± 0.03 1.70 ± 0.05 1.35 ± 0.12 0.04 ± 0.01 5.75 ± 0.44 w. paramesenteroides bk8 van/kan/gen 2.37 ± 0.03 0.07 ± 0.00 2.10 ± 0.04 1.68 ± 0.15 1.99 ± 0.12 1.40 ± 0.14 0.18 ± 0.01 5.33 ± 0.21 11 nova biotechnol chim (2022) 21(2): e1269 3 references abriouel h, lavilla lerma l, casado muñoz m delc, pérez montoro b, kabisch j, pichner r, cho g-s, neve h, fusco v, franz chmap, gálvez a, benomar n (2015) the controversial nature of the weissella genus: technological 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tibor roháčik2, jana sokolovičová2 1department of chemistry, university of ss. cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic (filip.kraic@ucm.sk) 2selekt, research and breeding institute, bučany 591, sk-919 28 slovak republic abstract: the final goal of this work is development of new genotypes of wheat with better properties compared to the standard set. prediction of optimal descriptors and properties related to the production characteristics is performed using several statistical and chemometrical tools, like correlation analysis, principal component analysis, cluster analysis and linear discriminant analysis. optimisation of wheat genotypes is directed towards high food quality. key words: wheat genotypes, crop, correlation analysis, principal component analysis, cluster analysis. 1. introduction in the last two years a large number of data concerning various wheat genotypes, their properties and observations were prepared in a form of spreadsheets. they stemmed the databases, which are periodically complemented by several slovak breeding stations, state and private research institutions. the main part of the data in this work is from selekt, research and breeding institute, bučany. the evaluated wheat descriptors are of different character; they concern the plant itself (plant height, mass of thousand grains), possible diseases (rust, powdery mildew, fusariosis, septoriosis) as well as some laboratory results (content of gluten, swellingness, sedimentation test, etc.). diversity studies have already been performed on wheat using grain quality (högy et al., 2008; every et al., 2008), fysiological factors (reynolds et al., 2002; reynolds et al., 2004; goggin et al., 2004), and resistance against fungal diseases (hamzehzarghani et al., 2005; snijders, 2004). our previous chemometrical study revealed interesting latent relations among the soil quality (with regard to nutrition elements), content of nutrition elements in the vine leaves, vine crop and quality if the produced wine (kraic et al., 2008). success of that chemometrical data treatment encouraged us to investigate the present agruicultural problem by means of several statistical/chemometrical tools. 2. material and methods 2.1 description of the studied data seventy wheat samples were investigated; among them 16 samples from bučany (designated bu-108 to bu-124 but without bu-122); 13 was from trebišov (bu-108 to bu-124 but without bu-109, bu-110, bu-116, bu-119), 16 from malý šariš (bu-108 to 102 kraic, f. et al. bu-124 but without bu-117) and 17 was from pstruša (bu-108 to bu-124). in addition, the data from all mentioned agricultural locations contained 2 standard wheat strains named ilona and bardotka. the samples omitted from individual locations did not contain all measured (or observed) quantities therefore these samples with the missing values were not further statistically processed. all investigated samples were characterized by the following 6 variables – wet and dry gluten (denominated as wgluten, dgluten, resp.), prugar’s number (prugar) – which represents a relationship between wet gluten and swell gluten, swell (swell), sedimentation (sedimen) and viscosity (viscos). it should be noted that the names starting with capital letter and stressed by italics fonts denote the variables selected for further chemometrical processing. the wheat samples were splitted into two categories according to the value of two categorical variables representing two different classification criteria: (1) sample quality, by which the samples are distributed to four classes designated as a1 (best), a2, b1 and b2 (worst); this way of categorization was made by the agricultural experts in bučany research and breeding institute. (2) sample origin respecting four locations in slovakia, namely bučany, trebišov, malý šariš and pstruša. 2.2 multidimensional data analysis statistical calculations were performed using following techniques: correlation analysis, principal component analysis (pca), cluster analysis (ca) and linear discriminant analysis (lda). in calculations two contemporary software commercial packages were used: stagraphics plus 5.1 and sas jmp 7.0. 3. results and discussion 3.1 correlation analysis the output of correlation analysis is the correlation table, which contains pair (pearson) correlation coefficients expressing the strength of correlation between all possible pairs of variables. the entries of this table are symmetrical according to diagonal. the correlation table comprising mutual dependence of all pairs of six chemical or physico-chemical variables relevant to the wheat quality is summarized in table 1. the following conclusions may be drawn from the correlation table: (a) the highest correlation is between wgluten and dgluten. (b) very high correlations were found between wgluten and prugar as well as dgluten and prugar. (c) very significant correlations (rcrit ≥ 0.306 at p ≤ 0.01) are between the following pairs of variables: prugar and sedimen, swell and viscos, wgluten and sedimen, dgluten and sedimen, viscos and prugar, wgluten and swell (inverse dependence), and sedimen and viscos. (d) a significant correlation (at the 95 % or higher probability level, p ≤ 0.05) is between dgluten and swell (ireverse dependence), and prugar and swell. all hitherto mentioned correlation coefficients are larger or equal than the critical value of the correlation coefficient, rcrit = 0.184, and are marked by bold faces. (e) no significant correlation was proved in all other pairs of variables. nova biotechnologica 9(1) (2009) 103 table 1. pearson correlation coefficients exhibiting the strength of correlation between individual pairs of variables for 70 studied wheat samples. wgluten dgluten prugar swell sedimen viscos wgluten 1 dgluten 0.988 1 prugar 0.762 0.837 1 swell -0.376 -0.256 0.293 1 sedimen 0.452 0.468 0.497 0.073 1 viscos 0.024 0.069 0.389 0.474 0.305 1 critical values of the correlation coefficient (absolute values) for n = 70 are: rcrit = 0.198 (p=0.10), rcrit = 0.235 (p=0.05), rcrit = 0.306 (p=0.01); significant correlations are marked bold. 3.2 cluster analysis generally, the agglomeration process in cluster analysis may be performed either with the studied objects or variables (khattree and naik, 2000). in this work, the clustering was made for the studied six chemical/physico-chemical variables. the result of the performed cluster analysis is a dendrogram depicted in fig. 1. the basis for the performed calculations were the data of 6 selected variables characterizing 70 samples of the wheat strains at 4 quality levels and 4 research locations. ward’s method of clustering and squared euclidean distance was used in all calculations. two main clusters of the progressively agglomerated variables can be seen in fig. 1. the first cluster, connected at the lowest distance level, is formed by wgluten, dgluten, which are most similar, gradually connected to prugar and further to sedimen. the second main cluster is formed by swell and viscos. the variables forming the same cluster are most similar; the measure of mutual similarity is given by the distance on the vertical axis of dendrogram. the results of cluster analysis are in agreement with the outputs of correlation analysis. 3.3 principal component analysis in principal component analysis, pca, some natural grouping of the objects (the wheat samples in this work) and the studied variables (the sample characteristics) may be seen. the principal components, pcs, are calculated as the linear combinations of original variables (sharma, 1996; khattree and naik, 2000). according to the computed eigenvalues only three out of six principal components (pcs) were found important as their value was larger than 1, which is usually considered as the criterion of significancy. three kinds of graphical outputs are used in the pca, namely scatterplot showing the objects, the loadings plot showing the variables, and the biplot where both, the objects and variables are depicted together. the advantage of first two graphical representations is a possibility to obtain the 2d graph as well as the 3d illustration where usually the first two or three most important pcs are used as the axes. on the other hand, the biplot, even though plotted in two dimensions, provides some additional information about the studied problem. 104 kraic, f. et al. fig. 1. cluster analysis of 6 variables characterizing quality of 70 wheat samples obtained from all four research locations. software statgraphics plus 5.1. fig. 2. biplot pc2 vs. pc1 for 6 measured chemical descriptors and 70 samples from 4 localities (1 – bučany, 2 trebišov, 3 – malý šariš, 4 – pstruša). software spss 15. fig. 2 exhibits the biplot, which simultaneously represents the wheat samples (depicted here by the numbers) and six original quality descriptors, depicted by the rays starting from the origin and ending at the point determining the position of the corresponding variable. the samples are here categorized by four locations, namely bučany, trebišov, malý šariš and pstruša. even though pca method is not used for nova biotechnologica 9(1) (2009) 105 classification, high values of the second principal component, pc2, are observable for the samples from trebišov (2), which at the same time means that they are characterized by the highest swelling and viscosity factors. the factors mostly influencing the first principal component, pc1, are wet and dry gluten and prugar number (with relatively smaller contribution of sedimentation). 3.4 linear discriminant analysis linear discriminant analysis (lda) is a multivariate technique focused on separating distinct sets of objects into two or more populations and then allocating the objects, not readily known where they belong to, into one of the considered populations (sharma, 1996). its main goal is to ensure a maximal discrimination among the classes of objects. taking this into account, the original variables are linearly combined into discriminant functions, the number of which is equal to the number of the classes minus one (lankmayr et al., 2004). classification performance depends on the selected categorical target variable. if quality was used as the target variable (the categorization of wheat samples is described in part 2.1) then 94.3% of the originally grouped objects were correctly classified when the discrimination model was calculated and 92.9% of the objects were correctly classified using leave-one-out cross-validation method. it means that 5 objects out of 70 ones were categorized into a different category then supposed). classification of the wheat samples by locality was also successful when considering that four localities were used for categorization. leave-one-out cross-validation showed 82.9 % correct classifications. it is worth noting that in this case 25 % success corresponds to random categorization so that the classification success is clearly pronounced. 4. conclusions principal component analysis and cluster analysis allow display a natural grouping of the wheat samples. both methods revealed that six utilized variables can be divided into two groups: (1) wet and dry gluten, prugar number and sediment, (2) swelling and viscosity factors. the obtained results demonstrate a good applicability of the used multivariate statistical methods for graphical representation of the wheat samples in two dimensional visual display. wheat classification may be conveniently illustrated by linear discriminate analysis, which was proved as an appropriate multidimensional classification technique. further study on the investigated wheat samples using different measurement techniques and observations is under progress. references every, d., motoi, l., rao, p.s., shotner, s.c., simmons, l.d.: predicting wheat quality – consequences of the ascorbic acid improver effect. j. cereal sci., 48, 2008, 339-348. goggin, d.e., colmer, t.d.: wheat genotypes show contrasting abilities to recover from anoxia in spite of similar anoxic carbohydrate metabolism. j. plant physiol., 164, 2007, 1605-1611. 106 kraic, f. et al. hamzehzarghani, h., kushalappa a.c., dion, y., rioux, s., comeau, a., yaylayan, v., marshall, w.d., mathee, d.e.: metabolic profiling and factor analysis to discriminate quantitative resistance in wheat cultivars against fusarium head blight. physiol. mol. plant pathol., 66, 2005, 119-133. högy, p., fangmeier, a.: effects of elevated atmospheric co2 on grain quality of wheat. j. cereal sci., 48, 2008, 580-591. khattree, r., naik, d.n.: multivariate data reduction and discrimination. sas institute, cary, north carolina, usa, 2000. kraic, f., mocak, j., argay, m.: influence of nutrients in soil and vine leaves and meteorological factors upon vine crop and must. nova biotechnol., 8, 2008, 71-77. lankmayr, e., mocak, j., serdt, k., balla, b., wenzl, t., bandoniene, d., gfrerer, m., wagner, s.: chemometrical classification of pumpkin seed oils using uv–vis, nir and ftir spectra. j. biochem. biophys. meth., 61, 2004, 95-106. reynolds, m.p., trethowan, r., crossa, j., vargas, m., sayre, k.d.: erratum to “physiological factors associated with genotype by environment interaction in wheat“. field crop res., 85, 2004, 253-274. reynolds, m.p., trethowan, r., crossa, j., vargas, m., sayre, k.d.: physiological factors associated with genotype by environment interaction in wheat. field crop res., 75, 2002, 139-160. sharma, s.: applied multivariate techniques. wiley, new york, 1996. snijders, c.h.a.: resistance in wheat to fusarium infection and trichothecene formation. toxicol. lett., 153, 2004, 37-46. microsoft word mrazova_nb.doc nova biotechnologica 8-1 (2008) 65 computer-aided diagnosis of lung malignity using multidimensional analysis of tumour marker data viera mrázová1, ján mocák1, elena varmusová2, denisa kavková2 1department of chemistry, university of ss. cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic (viera.mrazova@ucm.sk) 2institute for tuberculosis and respiratory diseases, department of clinical chemistry, kvetnica, poprad, sk-058 87 slovak republic abstract: the aim of this work is assessing diagnostic performance of lung tumour markers. three clinical laboratory tests were used for indicating lung malignancy in order to verify or predict the patient’s diagnosis. the data set of 182 patients was examined and two main groups of the patient samples were created – 86 with diagnosed malignancy (confirmed by histology) and 96 with diagnosed benign tumours or tuberculosis. the following tumour markers were analyzed: carcinoembryonic antigen and cytokeratin 19 fragment, which were sampled in the pleural exudates, and the same tumour markers in serum. in addition, the patient’s age and the gender of the corresponding individual were used as further variables in the original data matrix. three laboratory tests were used for indicating lung malignancy in order to verify or predict the patient’s diagnosis not only by using the results of the chosen individual laboratory test but also applying multivariate statistical approach, which jointly utilizes all performed tests in the form of their optimal linear combination. key words: lung malignity, multidimensional analysis, tumour marker. 1. introduction diagnosis of any disease can be confirmed or predicted not only using appropriate laboratory tests but also using multivariate statistical analysis, which uses simultaneously all performed tests in the form of their optimal (usually linear) combination. this new way of enhancing the diagnostic effectiveness, advocated by us, is applied here to the results of laboratory analysis of lung tumour markers in serum as well as pleural effusion (exudate). pleural effusion is common for several kinds of lung illnesses in clinical practice. malignancy is one of the main causes of pleural effusion. greater than 90 % of malignant pleural effusions are due to metastatic disease, mainly from lung or primary breast malignancies. the initial diagnostic approach includes examinations: thoracocentesis, cytology, and biochemical laboratory tests. however, the sensitivity of these non-invasive techniques is considered to be only 40 %–70 %. to improve upon these rates, a number of tumour markers (tm) in the pleural fluid have been intensively evaluated. the most common markers found to be of diagnostic significance were carcinoembryonic antigen (cea), cancer antigen 15-3 (ca), cancer antigen 19-9, and cytokeratin 19 fragment (cyfra 21-1). cea was identified in 1965 and has been widely used during the follow up of various tumours i.e.: colorectal cancers (mroczko et al., 2007; duffy et al., 2007; 66 mrázová, v. et al. yamamoto et al., 2005), breast cancer (nicolini et al., 2008; chen et al., 2006; sölétormos et al., 2004). cyfra 2l-1 assay measures cytokeratin 19 fragment and his concentration is increased with the extent of the malignant disease in non-small cell lung cancer. the serum cyfra 21-1 distribution differs significantly according to histology, disease stage and performance status. lung cancer is the leading cause of cancer deaths in europe. levels of tumour markers, especially cea and cyfra 21-1, may help to establish the diagnosis of pleural malignancy (matsuoka et al., 2007; shitrit et al., 2005; okamoto et al., 2005; fuhrman et al., 2000). it should be added that the most effective positive test is histology of the appropriate tissue sample but this way is invasive and takes a long time. therefore the use of tm may prevent the loss of time necessary for medical treatment in urgent cases. 2. material and methods 2.1 description of the studied data tumour markers were determined at the institute for tuberculosis and respiratory diseases (itrd) in poprad kvetnica, slovakia. the data set of 182 patients was examined; two main groups of the patient samples were created – 86 malignant (with malignancy confirmed by histology) and 96 benign tumours or tuberculosis. the following tumour markers were analyzed in pleural effusion: cea (coded as excea), cyfra 21-1 (excyf) as well as in serum: (scea and scyf, respectively). in addition, the patient’s age (coded as age) and the gender of the corresponding individual (coded as sexn) were used as the variables in the original data matrix. when using classification multivariate statistical techniques, two values of the categorical classification variable dg (diagnosis) were used: 1 indicating malignant diseases and 2 for others. this categorization was made on the basis of known histology results. 2.2 multidimensional data analysis statistical calculations were performed using the principal components analysis (pca), cluster analysis (ca), the linear discriminant analysis (lda), and logistic regression (lr). several software commercial packages were used: stagraphics plus 5.1, spss 15 and jmp 6.0.2. 2.3 analytical procedures tumour markers were analysed by automatic analysers elecsys 1010 and elecsys 2010, which use immunoanalysis with electrochemically generated chemiluminiscent detection. for determinations in pleural effusion an original procedure was used developed at the itrd. nova biotechnologica 8-1 (2008) 67 3. results and discussion 3.1 principal component analysis (pca) the data set of the patients characterized by four variables, namely scea, excea, excyf and scyf was used for a preliminary study. in the way, described in detail in the part 3.1 it was found that the variable scyf is of the least importance. considering this as well as economical aspects the variable scyf was exclude from further studies. instead, the variable age, always accessible, was used in the detailed pca study. fig. 1. pca biplot showing 4 selected variables (excyf, excea, scea, age) and 182 objects – patient’s samples. software spss 15. pca reveals a natural grouping of the studied objects as well as the used variables in a reduced dimensional space (fig. 1). the first principal component (pc1) performs a linear combination of four original variables, optimized with respect to preserving maximal variance of the data. the variables are demonstrated in the exhibited pca biplot by the rays (connecting the variable position in the pc2 – pc1 plane with the origin). the numbers 1 and 2 represent the category where the investigated sample belongs (1 – malignant, 2 – non-malignant). the inspection of the biplot depicted in fig. 1 reveals that the pc1 axis represents malignancy. all tumour markers are positively correlated with the pc1, which is the proof that all patient samples with a high pc1 value are malignant and is in accordance with the observation that the malignant cases are located at high pc1 values. 3.2 cluster analysis (ca) among the clustering techniques, ward´s method with squared euclidean distance metrics was selected for variable clustering. the obtained results are in agreement with 68 mrázová, v. et al. clinical expectations: excea and scea are clustered with excyf so that all tumour markers indicating positive diagnosis result are together. variable age is clustered with sexn since it simply reflects the fact that the average age of women is higher than that of men. d is ta nc e 0 200 400 600 800 s c e a e x c e a e x c y f a g e s e x n fig. 2. cluster analysis of variables using ward`s method, squared euclidean. 182 patient samples with lung diseases. software statgraphics 5.1. 3.3 discriminant analysis with regard to the solved problem the main goals of the applied classification multivariate methods, namely the linear discriminant analysis (lda), quadratic discriminant analysis (qda), and logistic regression (lr) is: (1) to create diagnostic categories and the training data set using the entries of the individual samples with known diagnosis, (2) to elaborate a classification model using the categorized patient samples in the training set, (3) to perform the categorization of the not yet classified samples (belonging to the test set of data) into the selected classes. fig. 3. linear discriminant analysis of the samples denoted by the numbers on the vertical axis. df1 denotes the only discriminant function. 86 samples corresponding to malignancy confirmed by histology (dg=1) and 96 samples regarding benign tumours or tuberculosis (dg=2). software statgraphics 5.1. df1 n um be r dg 2 1 -0,6 1,4 3,4 5,4 7,4 9,4 0 40 80 120 160 200 nova biotechnologica 8-1 (2008) 69 figure 3 represents the lda graphical output, which shows that the non-malignant patient samples (numbers 1-96) are located in a narrow cluster at very negative values of the first discriminate function (df1) whilst the malignant samples (97-182) form a wide tailing cluster at higher df1 values, which is a typical behaviour in many clinical studies. the classification performance for different software packages providing the classification outputs is collected in table 1. the exhibited results of the classification performance regard three types of samples: (1) the training set samples (used for calculating the classification model), (2) the samples omitted from the training set in a step-by-step manner according to the leave-one-out procedure (which was applicable only using the spss software), (3) the samples creating a special test set, which were not included into the training set. tab. 1. classification results for various multivariate methods and software. spss jmp statgraphics classification method training set leave-1out test set training set test set training set test set lda true/all 139/182 137/182 26/30 139/182 26/30 139/182 26/30 % true 76.4 75.3 86.7 76.4 86.7 76.4 86.7 qda true/all 150/182 n/a 25/30 n/a n/a n/a n/a % true 82.4 – 83.3 – – – – lr true/all 163/182 n/a 27/30 163/182 27/30 n/a n/a % true 89.6 – 90.0 89.6 90.0 – – note: the number of the patient samples is given by denominator in the “true/all” ratio. decision upon malignity was predicted using four variables scea, excea, excyf, age except lr where also sexn was used. n/a means that the calculation was not possible when using the cited software. the predictive ability of the used multivariate methods is expressed by the results referring to the last two types of the samples. it is better for the lda (over 86 %) than the qda. however, the best results (90 %) were achieved by logistic regression, where in addition to the variables used in other techniques, the patient’s gender (woman/man) was used (in the form of the binary variable sexn). 4. conclusions principal component analysis and cluster analysis allow display a natural grouping of the samples belonging to the individuals treated for lung diseases. the obtained results demonstrate very good applicability of the used multivariate statistical methods for graphical representation and the samples classification in a reduced number of dimensions. patient’s diagnosis may be predicted or verified not only using the results of the selected individual laboratory test but also utilizing all performed laboratory tests jointly in the form of their optimal combination ensured by an appropriate multidimensional statistical technique. 70 mrázová, v. et al. references chen, ch.ch., hou, m.f., wang, j.y., chang, t.w., lai, d.y., chen, y.f., hung, s.y., lin, s.r.: simultaneous detection of multiple mrna markers ck19, cea, c-met, her2/neu and hmam with membrane array, an innovative technique with a great potential for breast cancer diagnosis. cancer lett., 240, 2006, 279-288. duffy, m.j., van dalen, a., haglund, c., hansson, l., holinski-feder, e., klapdor, r., lamerz, r., peltomaki, p., sturgeon, c., topolcan, o.: tumour markers in colorectal cancer: european group on tumour markers (egtm) guidelines for clinical use. eur. j. cancer, 43, 2007, 1348-1360. fuhrman, c., duche, j.c., chouaid, c., abd alsamad, i., atassi, k., monnet, i., tillement, j.p., housset, b.: use of tumor markers for differential diagnosis of mesothelioma and secondary pleural malignancies. clin. biochem., 33, 2000, 405-410. matsuoka, k., sumitomo, s., nakashima, n., nakajima, d., misaki, n.: prognostic value of carcinoembryonic antigen and cyfra 21-1 in patients with pathological stage i non-small cell lung cancer. eur. j. cardio-thorac., 32, 2007, 435-439. mroczko, b., groblewska, m., wereszczynska-siemiatkowska, u., okulczyk, b., kedra, b., laszewicz, w., dabrowski, a., szmitkowski, m.: serum macrophage-colony stimulating factor levels in colorectal cancer patients correlate with lymph node metastasis and poor prognosis. clin. chim. acta, 380, 2007, 208-212. nicolini, a., carpi, a., ferrari, p., rossi, g.: immunotherapy prolongs the serum cea-tpa-ca 15.3 lead time at the metastatic progression in endocrinedependent breast cancer patients: a retrospective longitudinal study. cancer lett., 263, 2008, 122-129. okamoto, t., nakamura, t., ikeda, j., maruyama, r., shoji, f., miyake, t., wataya, h., ichinose, y.: serum carcinoembryonic antigen as a predictive marker for sensitivity to gefitinibhis in advanced non-small cell lung cancer. eur. j. cancer, 41, 2005, 1286-1290. shitrit, d., zingerman, b., shitrit, a. b., shlomi, d., kramer, m. k.: diagnosis value of cyfra 21-1, cea, ca 19-9, ca 15-3, and ca 125 assay in pleural effusions: analysis of 116 cases and review of the literature. oncologist, 10, 2005, 501-207. sölétormos, g., nielsen, d., schioler, v., mouridsen, h., dombernowsky, p.: monitoring different stages of breast cancer using tumour markers ca 15-3, cea and tpa. eur. j. cancer, 40, 2004, 481-486. yamamoto, y., hirakawa, e., mori, s., hamada, y., kawaguchi, n., matsuura, n.: cleavage of carcinoembryonic antigen indeces metastatic potential in colorectal carcinoma. biochem. bioph. res. commun., 333, 2005, 223-229. zemanova nbc 12-2(1 nova biotechnologica et chimica 12-2 (2013) 100 doi 10.2478/nbec-2013-0012  university of ss. cyril and methodius in trnava synthesis and reactions of new derivatives of furo[3,2-b]pyrrole ivana zemanová, renata gašparová department of chemistry, faculty of natural sciences, university of ss. cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic (ivanazemanova@zoznam.sk) abstract: synthesis of methyl 4h-furo[3,2-b]pyrrole-5-carboxylate is taken place in two step synthesis. vilsmeier-haack reaction of 4h-furo[3,2-b]pyrrole-5-carboxylate 1 led to methyl 2-formyl-4h-furo[3,2b]pyrrole-5-carboxylate 4, which served as starting compound for synthesis of furo[3,2-b]pyrrole-2aldoxime 5 and methyl 2-[(4-oxo-2-thioxo-1,3-thiazolidin-5-ylidene)methyl]-4h-furo[3,2-b]pyrrole-5carboxylate 7. the hydrazinolysis of 1 was prepared by carbohydrazide 2, which subsequently reacted with aldehydes to form of derivatives 3. pyrazole derivatives 11 were prepared by the reaction of azlactone 9 with derivatives 10. reactions were carried out under microwave irradiation or at classical heating. key words: aldoxime, carbohydrazide, furo[3,2-b]pyrrole, microwave irradiation, hippuric acid 1. introduction during the past few decades many results have been published in the area of the synthesis of heterocyclic compounds containing furo[3,2-b]pyrrole skeleton (puterová et al., 2004) due to their biological activity (krutošíková et al., 1994; gorugantula et al., 2010). carboxhydrazides and their derivatives are interesting class of compounds, which exhibits antitubercular (jordão et al., 2011), antimicrobial (piaczonka et al., 2013), antifungal (telvekar et al., 2012), anticonvulsant and anti-inflammatory (ulloora et al., 2013) activities. the present paper is a continuation of previous research, which dealt with the synthesis and reactions of furo[3,2-b]pyrrole system (gašparová et al., 2005; gašparová et al., 2007). 2. material and methods melting points of products were determined on a kofler hot place and are uncorrected. 1h nmr spectra were obtained on a 300 mhz spectrometer varian gemini 2000 in cdcl3 or dmso-d6 with tetramethylsilane as the internal standard. the infrared spectra (ir) were taken on a ftir iraffinity-1 spectrophotometer using kbr technique. all microwave experiments were performed in a panasonic nn-e205 type microwave oven. the apparatus was adapted for laboratory applications; nhexane was used as coolant for the condenser. methyl 4h-furo[3,2-b]pyrrole-5carboxylate (4), 4h-furo[3,2-b]pyrrole-5-carbohydrazide (5) and methyl 2-formyl-4hfuro[3,2-b]pyrrole-5-carboxylate (7) were synthesized following the published procedures (krutošíková et al., 1994; gajdoš et al., 2005). bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:11 utc nova biotechnologica et chimica 12-2 (2013) 101 2.1. synthesis of compounds 3a-d the mixture of 4h-furo[3,2-b]pyrrole-5-carbohydrazide 2 (1.21 mmol), 5substituted furan-2-karbaldehyde (1.21 mmol) in ethanol (5 ml), and catalytic amount of 4-methylbenzenesulfonic acid was refluxed at 70-80°c for 0.5-1 h (scheme 1). after cooling, the solid product was filtered off, washed with ethanol and recrystallized from ethanol. 2.1.1 n'-{[5-(4-nitrophenyl)furan-2-yl]methylidene}-4h-furo[3,2-b]pyrrole-5 carbohydrazide (3a) yield 48 %; m. p 279-282 °c. calcd. for c18h12n4o5 (364.31) c, 59.34; h, 3.32; n, 15.38. found: c, 58.84; h, 3.24; n, 14.76 %. ir (kbr): 3350, 3140, 1650, 1594, 1510, 1330, 1275, 1137, 1075, 1022, 915, 852, 753, 656 cm-1. 1h nmr (dmso-d6): 11.71 (s,1h, nh); 11.54 (s, 1h, nh); 8.75 (d, 2h, j = 7.8 hz, h-11', h-7'); 7.78 (d, 1h, j = 4.5 hz, h-2); 7.73 (d, 2h, j = 8.4 hz, h-10', h-8'); 7.5 (s, 1h, h-7); 6.98 (s, 1h, h-6); 6.28 (d, 1h, j = 3 hz, h-3'); 5.88 (s, 1h, h-3). 2.1.2 n'-{[5-(4-methylphenyl)furan-2-yl]methylidene}-4h-furo[3,2-b]pyrrole-5carbohydrazide (3b) yield 53 %; m. p 207-210 °c. calcd. for c19h15n3o3 (333.34) c, 68.46; h, 4.54; n, 12.61. found: c, 67.80; h, 4.39; n, 12.40 %. ir (kbr): 3453, 3235, 3113, 1634, 1616, 1571, 1490, 1431, 1251, 1137, 1072, 1028, 986, 819, 724 cm-1. 1h nmr (dmso-d6): 11.58 (s,1h, nh); 11.59 (s, 1h, nh); 8.28 (s, 1h, h-7); 7.77 (d, 1h, j = 4.5 hz, h-2); 7.70 (d, 2h, j = 7.8 hz, h-11', h-7'); 7.31 (d, 2h, j = 8.4 hz, h-10', h8'); 7.07 (d, 1h, j = 3.3 hz, h-4'); 7.02 (m, 2h, h-6, h-3'); 6.60 (d, 1h, j = 3.9 hz, h3); 2.36 (s, 3h, ch3). bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:11 utc 102 zemanová, i. and gašparová, r. 2.1.3 n'-[(5-phenylfuran-2-yl)methylidene]-4h-furo[3,2-b]pyrrole-5-carbohydrazide (3c) yield 35 %; m. p 198-200 °c. calcd. for c18h13n3o3 (319.31) c, 67.71; h, 4.10; n, 13.16. found: c, 67.38; h, 3.96; n, 13.62 %. ir (kbr): 3331, 3124, 1631, 1471, 1441, 1358, 1305, 1273, 1135, 1075, 1022, 914, 806, 762, 734, 688, 646 cm-1. 1h nmr (dmso-d6): 11.53 (br, 2h, nh); 8.28 (s, 1h, h-7); 7.70 (m, 3h, h-2, h-7', h11'); 7.49 (m, 3h, h-10', h-8'); 7.37 (m, 1h, h-9'); 7.02 (d, 1h, j = 3 hz, h-4'); 7.04 (d, 1h, j = 3 hz, h-3'); 6.99 (s, 1h, h-6); 6.60 (d, 1h, j = 3.9 hz, h-3). 2.1.4 4-methyl-2-{[2-({2-[3-(trifluoromethyl)phenyl]-4h-furo[3,2-b]pyrrol-5yl}carbonyl)hydrazinylidene]methyl}-4h-furo[3,2-b]pyrrole-5-carboxylic acid (3d) yield 40 %; m. p 244-246 °c. ir (kbr): 3257, 2962, 2596, 1674, 1614, 1533, 1448, 1332, 1261, 1222, 1161, 1072, 957, 796, 694 cm-1. 1h nmr (dmso-d6): 11.84 (s,1h, nh); 11.66 (s, 1h, nh); 8.27 (s, 1h, h-7); 8.12 (m, 2h, h-7˝, h-9˝); 7.67 (m, 2h, h-10˝, h-11˝); 7.43 (s, 1h, h-6'); 7.25 (s, 1h, h-6); 7.04 (s, 1h, h-3'); 7.03(s, 1h, h-3); 6.82 (s, 1h, h-5'); 3.96 (s, 3h, ch3). 2.2 synthesis of methyl 2-[(hydroxyimino)methyl]-4h-furo[3,2-b] pyrrole-5-carboxylate (5) classical heating (a). to mixture of ethanol (26 ml) and water (8 ml) was added hydroxylamine hydrochloride (0.6 g, 9 mmol), sodium hydroxide (2 g, 50 mmol) and methyl 2-formyl-4h-furo[3,2-b]pyrrole-5-carboxylate 4 (0.38 g, 2 mmol) (scheme 1). the reaction mixture was stirred at room temperature for 24 h. the precipitate was filtered off, washed with water and recrystallized from methanol. microwave method (b). to mixture of ethanol (26 ml) and water (8 ml) was added hydroxylamine hydrochloride (0.6 g, 9 mmol) and methyl 2-formyl-4hfuro[3,2-b]pyrrole-5-carboxylate 4 (0.38 g, 2 mmol) (scheme 1). the reaction mixture was irradiated at 90 w for 13 min. after cooling, the solid product was filtered off, washed with water and recrystallized from methanol. yield: 50 % (a), 70 % (b); m. p 236-241 °c. calcd. for c9h8n2o4 (208.17): c, 51.93; h, 3.87; n, 13.46. found: c, 51.88; h, 3.89; n, 13.61 %. ir (kbr): 3290, 3145, 3084, 2960, 1678, 1458, 1315, 1273, 1220, 1124, 985, 920, 769 cm-1. 1h nmr (dmso-d6): 12.09 (d, 1h, j = 0.6 hz, oh); 11.88 (s, 1h, nh); 7.59 (s, 1h, h-6); 7.26 (d, 1h, j = 0.9 hz, h-3); 6.79 (d, 1h, j = 0.7 hz, ch); 3.81 (s, 3h, och3). 2.3 methyl 2-{[(benzyloxy)imino]methyl}-4h-furo[3,2-b]pyrrole-5carboxylate (6) the mixture of methyl 2-[(hydroxyimino)methyl]-furo[3,2-b]pyrrole-5-carboxylate 5 (3.3 g, 1.6 mmol), benzyl chloride (3.8 g, 30 mmol) and catalytic amount of sodium carbonate in acetone (200 ml) was refluxed for 48 h (scheme 1). sodium carbonate bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:11 utc nova biotechnologica et chimica 12-2 (2013) 103 was filtered off and the excess of benzylchloride was distilled under reduced pressure. ice water (100 ml) was added and the mixture was extracted with diethylether (2×50 ml). the organic layer was dried with sodium sulphate and the solvent was evaporated. yield: 20 %; m. p 224-227 °c. calcd. for c16h14n2o4 (298.29): c, 64.42; h, 4.73; n, 9.39. found: c, 64.01; h, 4.69; n, 9.12 %. 1h nmr (cdcl3): 11.72 (s, 1h, nh); 7.77 (s, 1h, h-6); 7.42 (m, 6h, ph); 6.77 (s, 1h, ch); 5.01 (s, 2h, ch2); 3.88 (s, 3h, och3). 2.4 synthesis of methyl 2-[(4-oxo-2-thioxo-1,3-thiazolidin-5-ylidene) methyl]-4h-furo[3,2-b]pyrrole-5-carboxylate (7) the mixture of methyl 2-formyl-4h-furo[3,2-b]pyrrole-5-carboxylate 4 (5 g, 26 mmol), rhodanine (7 g, 53 mmol) and sodium acetate (13 g) in glacial acetic acid (45 ml) was refluxed for 30 min. (scheme 2). the reaction mixture was poured into water (260 ml). the separated precipitate was washed with water (140 ml), ethanol (50 ml), diethylether (20 ml), and the solid product was recrystallized from acetone. yield: 70 %; m. p 296-298 °c. calcd. for c12h8n2o4s2 (308.33): c, 46.74; h, 2.62; n, 9.09. found: c, 46.44; h, 2.60; n, 8.88 %. 1h nmr δh (dmso-d6): 13.69 (brs, 1h, nh); 12.12 (s, 1h, nh); 7.51 (s, 1h, ch); 7.29 (s, 1h, h-6); 6.87 (s, 1h, h3); 3.83 (s, 3h, och3). 2.5 synthesis of 2-[(e)-2-carboxy-2-sulfanylethenyl]-4h-furo[3,2-b] pyrrole-5-carboxylic acid (8) the mixture of 2-[(4-oxo-2-thioxo-1,3-thiazolidin-5-ylidene)methyl]-furo[3,2b]pyrrole-5-carboxylate 7 (4 g, 1.5 mmol) and aqueous sodium hydroxide (7 g naoh in 18 ml h2o) was refluxed for 30 min. (scheme 2). after cooling, 20 m hydrochloric acid (24 ml) was added into the reaction mixture. the formed solid product was filtered off and recrystallized from methanol. yield: 80 %; m. p >350 °c for c10h7no5s (253.23). 1h nmr (dmso-d6): 11.74 (s, 1h, nh); 7.56 (s, 1h, h-6); 6.99 (d, 1h, h-3); 6.74 (dd, 1h, j = 2.7 hz, 1.1 hz, h7); 3.64 (brs, 1h, sh). bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:11 utc 104 zemanová, i. and gašparová, r. 2.6 synthesis of methyl 2-[(5-oxo-2-phenyl-1,3-oxazol-4(5h)-ylidene) methyl]-4h-furo[3,2-b] pyrrole-5-carboxylate (9) classical heating (a). the mixture of methyl 2-formyl-4h-furo[3,2-b]pyrrole-5carboxylate 4 (0.5 g, 2.6 mmol), hippuric acid (0.46 g, 2.6 mmol) and catalytic amount of fused potassium acetate (0.38 g, 38 mmol) in acetanhydride (12.5 ml) was refluxed for 1 h (scheme 3). after cooling, the reaction mixture was poured into ice water. the formed solid product was filtered off, washed with water and recrystallized from ethanol. microwave method (b). the mixture methyl 2-formyl-furo[3,2-b]pyrrole-5carboxylate 4 (0.5 g, 2.6 mmol), hippuric acid (0.46 g, 2.6 mmol) and catalytic amount of fused potassium acetate (0.38 g, 38 mmol) in acetanhydride (12.5 ml) was irradiated at 90 w for 12 min (scheme 3). the work-up was the same as above method a. yield: 80 % (a), 92 % (b); m. p 324-326 °c. calcd. for c18h12n2o5 (336.30): c, 64.29; h, 3.60; n, 8.33. found: c, 63.96; h, 3.55; n, 8.21 %. ir (kbr): 3286, 3140, 1786, 1768, 1689, 1631, 1500, 1450, 1396, 1288, 1247, 1219, 1132, 977, 854, 761, 702 cm-1. 1h nmr (cdcl3): 11.76 (s, 1h, nh); 7.61 (m, 5h, ph); 7.18 (s, 1h, h-6); 7.01 (s, 1h, h-3); 6.82 (s, 1h, h-7); 3.93 (s, 3h, och3). 2.7 synthesis of compounds (11a-b) the mixture of methyl 2-[(5-oxo-2-phenyl-1,3-oxazol-5(4h)-ylidene)methyl]-furo [3,2-b]pyrrole-5-carboxylate 9 (1.4 mmol) and corresponding carbohydrazide (1.4 mmol), acetic acid (10 ml) and catalytic amount of fused potassium acetate (0.4 g) was irradiated at 90 w for 17 min (scheme 3). after cooling, the solid product was filtered off, washed with water and recrystallized from ethanol. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:11 utc nova biotechnologica et chimica 12-2 (2013) 105 2.7.1 methyl 2-{[1-{[(2,3-dimethyl-4h-furo[3,2-b]pyrrole-5-yl)carbonyl]imino}-5-oxo -2-phenyl-4h-imidazol-4-ylidene]methyl}-4h-furo[3,2-b]pyrrole-5-carboxylate (11a) yield: 65 %; m. p 285-287 °c. calcd. for c27h21n5o6 (511.49): c, 63.40; h, 4.14; n, 13.69. found: c, 63.19; h, 4.35; n, 12.82 %. 1h nmr (dmso-d6): 11.78 (s, 1h, nh); 11.30 (s, 1h, nh); 10.14 (s, 1h, nh); 8.09 (m, 2h, h-2', h-6'); 7.62 (m, 3h, h3', h-4', h-5'); 7.26 (s, 1h, h-7); 6.87 (s, 1h, h-6˝); 6.86 (d, 1h, j = 1.9 hz, h-6); 6.68 (d, 1h, j = 1.8 hz, h-3); 3.78 (s, 3h, och3); 2.28 (s, 3h, ch3); 2.04 (s, 3h, ch3). 2.7.2 methyl 2-{[1-(phenylcarbonylimino)-5-oxo-2-phenyl-4h-imidazol-4-ylidene] methyl}-4h-furo[3,2-b]pyrrole-5-carboxylate (11b) yield: 74 %; m. p 310-314 °c. calcd. for c25h18n4o5 (454.43): c, 66.07; h, 3.99; n, 12.33. found: c, 65.78; h, 3.94; n, 11.78 %. ir (kbr): 3296, 1685, 1629, 1512, 1450, 1286, 1219, 1143, 817, 758, 698 cm-1. 1h nmr (dmso-d6): 12.07 (s, 1h, nh); 11.71 (s, 1h, nh); 8.05 (dd, 2h, j = 8.1 hz. j = 1.5 hz, h-2',h-6'); 7.91 (dd, 2h, j = 8.2 hz, j = 1.5 hz, h-3', h-5'); 7.66 (m, 6h, ar); 7.53 (s, 1h, h-6); 7.26 (s, 1h, h-7); 6.88 (s, 1h, h-3); 3.85 (s, 3h, och3). 3. results and discussion methyl 2-formyl-4h-furo[3,2-b]pyrrole-5-carboxylate 7 was routinely prepared by condensation of furan-2-carboxaldehyde with methyl azidoacetate in methanol in the presence of sodium methoxide giving methyl 2-azido-3-(furan-2-yl)propenoate, which underwent the cyclization in boiling toluene to give methyl 4h-furo[3,2-b]pyrrole-2carboxylate 4 (krutošíková et al., 1994). compounds 3a-d were formed by reaction with carbohydrazide 2 using corresponding aldehydes in 35-53% yield. the structures of compounds 3a-d were corroborated by the presence two singlets of nh protons at 11.84 and 11.53 ppm. ir spectra of 3a-d exhibit absorption bands of carbonyl group at 1631-1674 cm-1 and absorption bands of nh group at 3258-3453 cm-1. one of the most interesting results in the study is synthesis of methyl 2[(hydroxyimino)methyl]-4h-furo[3,2-b]pyrrole-5-carboxylate 5, which was prepared by reaction of methyl 2-formyl-4h-furo[3,2-b]pyrrole-5-carboxylate 4 with hydroxylamine hydrochloride in sodium hydroxide either by classical heating for 24 h in 50% yield or in microwave oven for 13 min. in 70% yield. the only one preparation of 4h-furo[3,2-b]pyrrole-2-aldoxime 5 has been described by gorugantula et al., 2010. in their study there was described the synthesis of 4h-furo[3,2-b]pyrrole-2aldoxime via 4-nitro-5-(2-phenylethenyl)furan-2-aldoxime palladium-catalysed reductive cyclization. reaction of aldehyde 4 with hydroxylamine has been described as useful method of nitrile synthesis (krutošíková et al., 1993), but in that case aldoxime 5 has not been isolated. 1h nmr spectrum displayed doublet signal of =noh proton at 12.09 ppm. doublet signal of ch proton occur at 6.79 ppm. ir spectrum of 5 shows the absorption bands of carbonyl group at 1678 cm-1 and of nh group at 3290 cm-1. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:11 utc 106 zemanová, i. and gašparová, r. reaction of 5 with benzyl chloride in acetone led to methyl 2{[(benzyloxy)imino]methyl}-4h-furo[3,2-b]pyrrole-5-carboxylate 6 in yield 20 % after 48 h of refluxed. 1h nmr spectra display singlet signal of nh proton at 11.72 ppm, multiplet signal of ph group at 7.42 ppm, singlet signal of ch2 bond at 5.01 ppm. the reaction of methyl 2-formyl-4h-furo[3,2-b]-pyrrole-5-carboxylate 4 with rhodanine afforded compound 7, which subsequently underwent hydrolysis to provide derivative 8 in 80 % yield. compound 8 display singlet signal of nh group at 1.74 ppm and broad signal of sh group at 3.64 ppm. signal cooh group is not occurring in the spectrum as a result of the rapid exchange hydrogen for deuterium. the reactions of azlactone 9 with carbohydrazides 10 were carried in acetic acid under microwave irradiation in the presence of potassium acetate to give compounds 11a-b in yields 65-74 %. compounds 11a and 11b display two or three singlets at 12.01–10.14 ppm in their 1h nmr spectra due to nh group. three singlets of nh groups of compound 11a appear at 11.78, 11.30 and 10.14 ppm. the characteristic bands observed at 1680 cm-1 and 3296 cm-1 in ir spectra correspond to the c=o and nh group. the structures of the prepared compounds were confirmed by 1h nmr and ir spectra. 4. conclusions derivatives 3 were obtained by the reaction of carbohydrazide 2 with heterocyclic aldehydes. methyl 2-formyl-4h-furo[3,2-b]pyrrole-5-carboxylate 4 served as the substrate for synthesis of furo[3,2-b]pyrrole-2-aldoxime 5 as well as derivatives 7, 9. the prepared furo[3,2-b]pyrrole-2-aldoxime 5 was used as starting compound for the condensation reaction with benzyl chloride to give a compound 6. the hydrolysis of compound 7 gave 2-[2-carboxy-2-sulfanylethenyl]-4h-furo[3,2-b]pyrrole-5-carboxylic acid 8. pyrazole derivatives 11 were prepared by the reaction of azlactone 9 with derivatives 10. acknowledgement: this work was supported by the slovak research agency under the contract no. vega 1/0233/12 references gajdoš, p., pavlíková, s., bureš, f., krutošíková, a.: 2-[3(trifluoromethyl)phenyl]furo[3,2-b]pyrroles: synthesis and reactions. cent. eur. j. chem., 3, 2005, 311-325. gašparová, r., moncman, m., horváth, b.: microwave assisted reactions of 2-[3-(trifluoromethyl)phenyl]-4-r1-furo[3,2-b]pyrrole-5-carboxhydrazides. cent. eur. j. chem., 6, 2007, 180-187. gašparová, r., zbojek, d., lácová, m., kráľová, k., gatial, a., horváth, b., krutošíková, a.: reactions of substituted furo[3,2b]pyrrole-5-carboxhydrazides and their biological activity. cent. eur. j. chem., 3(4), 2005, 622-646. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:11 utc nova biotechnologica et chimica 12-2 (2013) 107 gorugantula, p. s., martínez-carrero, m. g., dantale, w. s., söderberg, c. g. b.: palladium-catalyzed reductive n-heterocyclization of alkenyl-substituted nitroarenes as a viable method for the preparation of bicyclic pyrrolofused heteroaromatic compounds. tetrahedron, 66, 2010, 1800-1805. jordão, k.a., sathler, c. p., ferreira, f.v., campos, r. v., de souza, c.b.v.m., castro, c.h., lannes, a., lourenco, a., rodrigues, r. c., bello, l. m., lourenco, c.s.m., calvalho, s.l.g., almeida, c.b.m, cunha, c.a.: synthesis, antitubercular activity, and sar study of n-substitutedphenylamino-5-methyl-1h-1,2,3-triazole-4-carbohydrazides. bioorg. med. chem., 19, 2011, 5605–5611. krutošíková, a., dandárová, m., alföldi, j.: synthesis and reactions of furo[3,2-b]pyrrole type aldehydes. coll. czech. chem. commun., 58, 1993, 21392149. krutošíková, a., dandárová, m., alföldi, j.: substituted vinyl azides in the synthesis of condensed nitrogen heterocycles. chem. papers, 48, 1994, 268273. pieczonka, m. a., strzelczyk, a., sadowska, b., mlostoń, g., staczek, p.: synthesis and evaluation of antimicrobial activity of hydrazones derived from 3-oxido-1h-imidazole-4-carbohydrazides. eur. j. med. chem., 64, 2013, 389–395. puterová, z., sterk, h., krutošíková, a.: reaction of substituted furan-2carboxaldehydes and furo[b]pyrrole type aldehydes with hippuric acid. molecules, 9, 2004, 11-21. telvekar, n. v., belubbi, a., bairwa, k.v., satardekar. k.: novel n′benzylidene benzofuran-3-carbohydrazide derivatives as antitubercular and antifungal agents. bioorg. med. chem. lett., 22, 2012, 2343–2346. ulloora, s., shabaraya, r., ranganathan, r., adhikari, v.a.: synthesis, anticonvulsant and anti-inflammatory studies of new 1,4dihydropyridin-4-yl-phenoxyacetohydrazones. eur. j. med. chem., 70, 2013, 341– 349. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:11 utc microsoft word fecskeova et al. nb 2010.doc nova biotechnologica 10-2 (2010) 131 cloning and characterization of coba, one of vitamin b12 biosynthesis pathway genes from selenomonas ruminantium lívia fecskeová, peter pristaš, peter javorský institute of animal physiology, slovak academy of sciences, šoltésovej 4-6, košice, slovak republic (fecskeova@saske.sk) abstract: bacterial biosynthesis of vitamin b12 can occur via either aerobic or anaerobic route. while the aerobic pathway has been fully elucidated and understood, less is known about the anaerobic pathway. selenomonas ruminantium is thought to be the main producer of this vitamin in rumen environment and must use the anaerobic pathway. in our work we found one of the genes of vitamin b12 biosynthetic pathway of s. ruminantium, encoding for the cobalamin adenosyltransferase, enzyme taking part at the last steps of the synthesis process. deduced amino acid sequence showed the highest similarity to cobalamin adenosyltransferases of other ruminal anaerobic bacteria and that of species selenomonas. phylogenetic comparisons of coba protein sequences of several anaerobic bacteria of clostridiale order indicate possible horizontal transfer of this gene. key words: vitamin b12, cobalamin biosynthesis, selenomonas ruminantium 1. introduction one of nature’s structurally most complex small molecule, vitamin b12 or cobalamin, is an essential nutrient for humans and animals. it is used to treat pernicious anaemia and peripheral neuritis, and is used as a dietary supplement. while it is required in both prokaryotic and eukaryotic metabolism, only some bacterial and archaeal species are able to synthesize it de novo (rodionov et al., 2003). some prominent b12-dependent reactions in bacteria and archaea include the process of acetate formation in acetogenic bacteria, transfer of methyl group in methaneproducing archaea and anaerobic fermentation of 1,2-propanediol, ethanolamine and glycerol in enteric bacteria (marten et al., 2002). animals and humans require b12 as coenzyme for two enzymes only: methionine synthase for homocysteine methylation and methylmalonyl-coa mutase involved in oxidation of fatty acids and amino acids, respectively. plants and fungi are thought to neither synthesize, nor need it (duda et al., 1967). two different cobalamin synthetic pathways have been found an evolutionally older anaerobic pathway found in salmonella enterica or propionibacterium shermanii (roessner and scott, 2006) and a more recent aerobic route in pseudomonas denitrificans (battersby, 1994), which differ at the point of cobalt insertion. as the industrial production by chemical synthesis would be too expensive and technically demanding, vitamin b12 is produced industrially by biosynthetic fermentation processes, employing almost exclusively p. denitrificans and propionibacterium species (martens et al., 2002). selenomonas ruminantium, a gram-positive obligate anaerobe originally isolated from rumen of cattle, is one of the most numerous bacteria of the ruminal microbial 132 fecskeová, l. et al. population. considerable metabolic role it plays in rumen is given by its capability to convert succinate to propionate and to utilize lactate and many amino acids (ricke et al., 1996). previous research has showed that this bacterium is the main b12 contributor to the rumen environment (dryden et al., 1962), where its role is in the assimilation of propionic acid, a major fermentation product of the ruminal microflora, by b12-dependent methylmalonyl-coa mutase. 2. materials and methods 2.1 bacterial strain and growth conditions bacterial strain s. ruminantium s8 was cultivated anaerobically in the atmosphere of pure co2 in selective m10 broth medium (caldwell and bryant, 1966) with an addition of 10 % clarified rumen fluid, 0.1 % mineral solution and 0.1 % vitamin solution (clark and holms, 1976). fructose (4g/l) was used as the sole carbon source. 2.2 dna isolation and pcr reaction total dna from bacterial cells was isolated by sodium dodecylsulphate lysis and subsequent phenol extractions (pospiech and neumann, 1995). total dna was amplified in techne tc 3000 (usa) thermal cycler in 50 μl reaction mix containing 40 μmol/l each dntp, 20 pmol of each primer, 1x reaction buffer and 0.5 u of taq dna polymerase (invitrogen, netherland). pcr primers used were srdrecf (5´tctcgaaaatggggcgcagc3´) and srdrecr (5´tttgagamactcataa gtgcgcattc3´). initial denaturation step (95 °c 5 min) was followed by 35 cycles (94 °c 1 min, 58 °c 1 min, 72 °c 1 min) and a final incubation at 72 °c for 10 min. 2.3 molecular cloning and sequence analysis pcr amplicon was ligated into plasmid ptz57r/t (fermentas, lithuania) and escherichia coli er2267 competent cells were transformed with the ligation mixture. recombinant plasmid was extracted using the genejet plasmid miniprep kit (fermentas, lithuania) and the dna insert was sequenced. using the blast algorithm (altschul et al., 1990) at ncbi the obtained nucleotide sequence was subjected to homology search against nucleotide and protein database. for phylogenetic comparisons mega 4 software (tamura et al., 2007) was used. 3. results and discussion small plasmids of s. ruminantium were suggested to undergo recombination events during the rolling circle replication, when highly recombinogenic single-stranded plasmid intermediates form. recombination is proposed to rely on highly conserved, short dna sequences characteristic for many small rcr plasmids of s. ruminantium, nova biotechnologica 10-2 (2010) 133 such as the srsr elements (selenomonas ruminantium sequence repeats) (nakamura et al., 1999). during experiments on the possible role of srsr mediated recombination in the plasmid evolution and spreading in s. ruminantium using pcr and specifically designed primers amplifying interchangeable plasmid rep cassettes multiple amplicons were obtained. while most of the obtained amplicons contained plasmid derived sequences encoding for replication protein (not published yet), surprisingly in one case the complete coba gene encoding for cobalamin adenosyltransferase was present. after pcr reaction we obtained an approximately 800 bp amplicon, which we cloned and sequenced. while no significant similarity was observed at nucleotide level, the 780 bp dna fragment contained single orf encoding for a 178 amino acid protein with significant similarity to cob(i)alamine adenosyltransferase or cob(i)yrinic acid a,c-diamide adenosyltransferase, one of many enzymes of the b12 biosynthetic pathway. the sequence was submitted to genbank database under the accession number hq383925. comparison of the deduced amino acid sequence with the generalized structure of conserved domains of cobalamin adenosyltransferases (fig. 1) shows the presence of all conserved domains, within which each amino acid is conserved according to the generalized structure. we found the presence of two walker motifs type a and b, hydroxycobalamin binding site, atp binding site and homodimer interface. derived protein sequence showed the highest similarity to mitsuokella multiacida (65 % identity, 78 % similarity), megamonas hypermegale art12/1 (64 % identity, 79 % similarity), and s. flueggei atcc 43531 (62 % identity, 79 % similarity) coba sequences. phylogenetic comparison of several available coba genes of anaerobic bacteria (fig. 2) within the clostridiales order showed that s. ruminantium coba sequence groups together with other selenomonas spp. and related sequences. surprisingly this group of coba sequences is more related to the coba sequences of peptococcaceae family than to other members of veillonellaceae family, where s. ruminantium belongs to, indicating possible horizontal gene transfer of coba gene. fig. 1. schematic representation of selected motifs in s. ruminantium coba gene. the position of conserved amino acids characteristic for coba protein domains is indicated by blafl triangles. importance of bacterial production of vitamin b12 is given by its role in the elimination of some volatile fatty acids produced in the rumen. despite it very limited information is available on the genetic background of its production by ruminal selenomonads, which are the predominant suppliers of this vitamin to the rumen 134 fecskeová, l. et al. environment. so far, only one study has been performed investigating the b12 synthesis in s. ruminantium (anderson et al., 2001), in which the authors described five genes organized as an operon, encoding for enzymes acting in the first steps of b12 synthesis. a bifunctional gene, coba + hemd, coding for a protein with two catalylic functions – uroporphyrinogen iii synthase and uroporphyrinogen iii 2,7methyltransferase – was found and protein phylogenetic comparisons showed that this form of the enzyme is probably restricted to strictly anaerobic bacteria. the gene we describe here encodes for cobalamine adenosyltransferase, enzyme catalyzing one of the last steps of b12 biosynthesis. fig. 2. phylogenetic tree showing relatedness of s. ruminantium coba sequence (shown in bold). the tree was constructed using neighbour-joining algorithm implemented in mega 4 software. the sequence of alphaproteobacterium caulobacter segnis coba was used as an outgroup. considering the fact that the coba gene is located between highly conserved sequences found on s. ruminantium plasmids, which might carry out a recombinationmediated exchange of the gene or complete gene cassettes; and that protein phylogenetic comparisons also indicate possible horizontal transfer of this gene between different species, it is possible that a certain part encoding b12 pathway enzymes could have been gained in mechanisms of horizontal transfer. acknowledgment: this publication is the result of the projects no. 26220120001 and 26220120043 implementation supported by the research & development operational programme funded by the erdf. references altschul, s.f., gish, w., myers, e.w., lipman, d.j.: basic local alignment search tool. j. mol. biol., 215, 1990, 403-410. nova biotechnologica 10-2 (2010) 135 anderson, p.j., entsch, b., mckay, d.b.: a gene, coba + hemd, from selenomonas ruminantium encodes a bifunctional enzyme involved in the synthesis of vitamin b12. gene, 281, 2001, 63-70. battersby, a.r.: how nature builds the pigments of life: the conquest of vitamin b12. science, 264, 1994, 1551-1557. caldwell, d.r., bryant, m.p.: medium without rumen fluid for nonselective enumeration and isolation of rumen bacteria. appl. microbiol., 14, 1966, 794-801. clark, b., holms, w.h.: control of the sequential utilization of glucose and fructose by escherichia coli. j. gen. microbiol., 95, 1976, 191-201. duda, j., pedziwilk, z., zodrow, k.: studies on the vitamin b12 content of the leguminous plants. acta microbiol pol, 6, 1967, 233-238. dryden, l.p., hartman, a.m., bryant, m.p., robinson, i.m., moore, l.a.: production of vitamin b12 and vitamin b12 analogues by pure cultures of ruminal bacteria. nature, 14, 1962, 201-202. martens, j.-h., barg, h., warren, m.j., jahn, d.: microbial production of vitamin b12. appl. microbiol. biotechnol, 58, 2002, 275-285. nakamura, m., nagamine, t., ogata, k., tajima, k., aminov, r.i., benno, y.: sequence analysis of small cryptic plasmids isolated from selenomonas ruminantium s20. current microbiol., 38, 1999, 107-112. pospiech, a., neumann, b.: a versatile quick/prep of genomic dna from grampositive bacteria. trends genet., 11, 1995, 217-218. ricke, s.c., martin, s.a., nisbet, d.j.: ecology, metabolism, and genetics of ruminal selenomonads. crit. rev. microbiol., 22, 1996, 27-65. rodionov, d.a., vitreschak, a.g., mironov, a.a., gelfand, m.s.: comparative genomics of the vitamin b12 metabolism and regulation in prokaryotes. j biol. chem., 278, 2003, 41148-41159. roessner, c.a., scott, a.i.: fine-tuning our knowledge of the anaerobic route to cobalamin (vitamin b12). j bacteriol., 188, 2006, 7331-7334. tamura, k., dudley, j., nei, m., kumar, s.: mega4: molecular evolutionary genetics analysis (mega) software version 4.0. mol. biol. evol., 24, 2007, 1596-1599. nova biotechnol chim (2021) 20(2): e1010 doi: 10.36547/nbc.1010 1 nova biotechnologica et chimica formation of carnosine an ab initio study roman boča, beáta vranovičová department of chemistry, faculty of natural sciences, university of ss. cyril and methodius in trnava, nám. j. herdu 2, trnava 91701, slovakia  corresponding author: roman.boca@ucm.sk article info article history: received: 11th june 2021 accepted: 8th september 2021 keywords: carnosine histidine beta-alanine ab initio calculations molecular properties equilibrium constant note: used non-si units kcal mol-1 = 4.184 kj.mol-1, debye, d = 3.336 × 10-30 ams, bohr, a0 = 5.292 ×10 −11 m, angstrom, å = 10-10 m, atm = 101,325 pa abstract formation of carnosine from histidine and -alanine is studied by ab initio molcao-scf method followed by the perturbative configuration interaction (mp2) in vacuo. after the full geometry optimization at the scf level, the molecular properties were evaluated and followed by the vibrational-rotational analysis. consequently, the energy, entropy and free energy were evaluated for the reactants and products of the reaction histidine + -alanine → carnosine + h2o and finally, the equilibrium constant was enumerated. © university of ss. cyril and methodius in trnava introduction carnosine (beta-alanyl-l-histidine) is a simple peptide formed by the condensation reaction of histidine and -alanine (eq. 1). histidine + -alanine → carnosine + h2o (1) the molecular structures are viewed in fig. 1. carnosine is a substance with multi-beneficial effects (boldyrev et al. 2013). it is synthesized in organisms by the carnosine-synthase (eq. 2) atp + l-histidine + -alanine → adp + phosphate + carnosine (2) fig. 1. from top to bottom: structure of the histidine, alanine, and carnosine (zwitterionic forms) as extracted from the ccdc (cambridge crystallographic data centre). ccdc codes: 1889705, 1105698, and 1105666. colours: c – dark grey, n – blue, o – red, h – white. mailto:roman.boca@ucm.sk nova biotechnol chim (2021) 20(2): e1010 2 and it is metabolized by the canosinase. beneficial effects of the carnosine were proven in many areas and the most important of them are: prevention of neurodegeneration, improvement of memory, antidepresive action, and suppressing of cancer (schön et al. 2019). as carnosine penetrates the blood-brain barrier (bbb) and causes only little side effects, it possesses high utility potential. it serves also as a reservoir of histidine which is transformed to histamine by l-histidinedecarboxylase; the histamine itself does not penetrate bbb. experimental x-ray structure data for the reactants and products of the reaction (eq. 1) have been retrieved from the ccdc database (cambridge crystallographic data centre). these solid-state structures were used as an initial guess for the full geometry optimization in vacuo. for such a purpose the ab initio molcao-scf method was utilized using the 631g** basis set (hyperchem 2008). the dilemma of the zwitterionic versus amino forms in vacuo was solved by considering both of them. at the scf level a number of molecular properties were evaluated: the energies of the homo (the highest occupied molecular orbital) and lumo (the lowest unoccupied molecular orbital), the adiabatic ionization energy ei and electron affinity eeg based upon the positively and/or negatively charged open-shell system after geometry optimization, followed by the evaluation of the mulliken electronegativity  = (ei eeg)/2 and the pearson hardness  = (ei + eeg)/2 (pearson 1977; sen 1993). for the electroneutral molecule also the dipole moment p and the polarizability volume  (one-third trace of the polarizability tensor) were calculated at the scf level. the molecular electrostatic potential (politzer et al. 1985; politzer and murray 2002) was displayed as a 3d contour map on the isovalue surface of charge density; this shows the acidic/basic sites along the molecular skeleton suitable for nucleophilic and/or electrophilic interactions. the energetic properties were improved by a partial inclusion of the correlation energy by employing the 2nd-order perturbative configuration interaction using the moller-plesset partitioning (mp2). the above results have been compared with those obtained by the enlarged basis set 6-311g(d,p) after the full geometry optimization at the mp2 level. the optimized geometry has been a starting point for the full vibrational-rotational analysis yielding the corresponding energy levels. they enter the partition function allowing the evaluation of the thermodynamic functions, such as the internal energy u, entropy s, the free energy a and the gibbs energy g at the room temperature. results and discussion the mo-lcao-scf calculations started from the experimental solid-state geometry that is a zwitterionic form for histidine, -alanine and also carnosine. the full geometry optimization converged to the zwitterionic form (hereafter z) as displayed in fig. 2 for histidine. there exists a fivemembered ring h(nh2)cco with the short contact nh…o forming a bent hydrogen bond. the molecular electrostatic potential shows that the (h2n)h site is positively charged as opposite to the –coo residue. zwitterionic form amino acid form optimum geometry at the scf level start form the ccdc geometry (zwitterion), final zwitterionic form with the nh…o contact start from the reallocated hydrogen atom molecular electrostatic potential; contour 0.03 ea0 -1 fig. 2. optimized structure and molecular electrostatic potential for histidine. (a0 – bohr). in addition, the calculations were done for the amino-acid form (hereafter a) in which the nova biotechnol chim (2021) 20(2): e1010 2 hydrogen atom from the ammonium site was reallocated to the distant oxygen atom. for histidine this canonical form is a bit more stable by 17 kcal.mol-1 at the scf level and 10 kcal.mol-1 at the mp2 level (table 1). the molecular properties of the zand a-forms are almost analogous; the only marked difference exhibits the dipole moment that for the z-form is very high. the pearson hardness reflects the resistance of the molecule against the electron transfer and for the histidine it is high (155, 161 kcal.mol-1) relative to the series of other amino acids (vranovičová and boča 2021). table 1. calculated properties of histidine. a a all energy quantities in units of kcal mol-1. -alanine belongs to the simplest amino acids and it crystallizes in the zwitterionic form. however, the geometry optimization resulted in travelling of the hydrogen atom from the nh3 + site to the –coo– residue where a six-membered ring (h2n)cccoh is formed with the bent n…ho hydrogen bond (fig. 3). the ground state molecular energy for the zand aforms are almost identical, favouring the a-form only by 0.6 kcal.mol-1 (table 2). the calculated molecular properties are very similar, again except the dipole moment. the molecular electrostatic potential is rather unique with a positive tail at the ho– edge pointing to the negatively charged nh2– group. the hardness is high: 160 and 167 kcal.mol-1. for this small molecule the geometry optimization was performed also at the mp2 level. the final geometry is almost identical with that fixed at the scf level and it is stabilized by only 2 kcal.mol-1. zwitterionic form amino acid form optimum geometry at the scf level start from the ccdc geometry (zwitterion), final amino acid form with the n…ho contact start from the reallocated hydrogen atom molecular electrostatic potential; contour 0.03 ea0 -1 fig. 3. optimized structure and molecular electrostatic potential of -alanine. table 2. calculated properties of -alanine. a a all energy quantities in units of kcal.mol-1. zwitterion amino acid homo -215 -201 lumo 101 116 e+ -342,138 -342,136 e0 (optimized geometry) -342,323 -342,340 e− -342,220 -342,252 ei(scf) 185 204 eeg(scf) 103 88 m(scf) 41 58 p(scf) 144 146 e+(mp2) -343,183 -343,177 e0(mp2) -343,399 -343,409 e−(mp2) -343,305 -343,318 ei(mp2) 216 232 eeg(mp2) 94 91 m(mp2) 61 70 p(mp2) 155 161 dipole moment p/debye 12.99 6.20 polarizability /å3 75.6 75.6 surface area s /å2 321 325 volume v/å3 475 482 zwitterion amino acid homo -261 -247 lumo 116 124 e+ -201,788 -201,778 e0 (optimized geometry) -201,985.2 -201,985.8 e− -201,878 -201,890 ei(scf) 197 208 eeg(scf) 107 96 m(scf) 45 56 p(scf) 152 152 e+(mp2) -202,361 -202,351 e0(mp2) -202,593 -202,591 e−(mp2) -202,505 -202,496 ei(mp2) 232 240 eeg(mp2) 88 95 m(mp2) 72 72 p(mp2) 160 167 dipole moment p/debye 6.75 2.97 polarizability /å3 40.7 40.5 surface area s/å2 242 242 volume v/å3 331 331 3 nova biotechnol chim (2021) 20(2): e1010 2 the molecule of carnosine during the geometry optimization becomes folded as shown in fig. 4. zwitterionic form amino acid form optimum geometry at the scf level start from the ccdc geometry (zwitterion) with spatially separated nh3 + and coo groups start from the reallocated hydrogen atom molecular electrostatic potential; contour 0.03 ea0 -1 fig. 4. optimized structure and molecular electrostatic potential of carnosine. table 3. calculated properties of carnosine. zwitterion [kcal.mol-1] amino acid [kcal.mol-1] homo -162 -200 lumo 38 115 e+ -496,423 -496,451 e0 (optimized geometry) -496,552 -496,619 e− -496,526 -496,540 ei(scf) 129 168 eeg(scf) 26 79 m(scf) 51 44 p(scf) 77 123 e+(mp2) -496,846 -496,870 e0(mp2) -498,113 -498,171 e−(mp2) -496,959 -496,967 ei(mp2) 1,267 1,301 eeg(mp2) 1,154 1,204 m(mp2) 56 48 p(mp2) 1,210 1,252 dipole moment p/debye 25.24 4.95 polarizability /å3 113.8 112.3 surface area s/å2 438 445 volume v/å3 677 689 the a-form is preferred against the z-form by 67 and 58 kcal.mol-1, respectively. the inclusion of the correlation energy via the mp2 method causes a dramatic increase of the ionization energy, electron affinity and consequently the pearson hardness. the effect to the mulliken electronegativity is small (table 3). the molecule of water possesses rather high ionization energy and electron affinity (table 4). the calculated ionization energy ei(mp2) = 283 matches the experimental value of 291 kcal.mol-1. the pearson hardness p(mp2) = 202 kcal.mol -1 refers to the class of hard molecules. table 4. calculated properties of water.a homo -312 lumo 135 e+ -47,455 e0 (optimized geometry) -47,706 e− -47,577 ei(scf) 251 eeg(scf) 129 m(scf) 61 p(scf) 190 e+(mp2) -47,547 e0(mp2) -47,830 e−(mp2) -47,708 ei(mp2) 283 eeg(mp2) 122 m(mp2) 80 p(mp2) 202 dipole moment p/debye 2.15 polarizability /å3 4.87 surface area s/å2 116 volume v/å3 117 a experiment: ei (vertical) = 12.62 ev = 291 kcal.mol -1. all energy quantities in units of kcal.mol-1. the free energies of the reactants and products allow determining the overall change a(t) for the reaction (eq. 1) which enters the equilibrium constant lnk = -a/rt. as evident from table 5, for the amino-acid forms at the scf level there is a ~ 0 at 300 k which yields k ~ 1. this value leads to the conclusion that the formation of carnosine and its hydrolysis via eq. 1 are equally probable processes. this result gives a thermodynamic (not kinetic) predisposition to the carnosine hydrolysis. hydrolysis of carnosine has been observed as an enzyme-assisted process (pegova et al. 2000). the results obtained in an analogous way but using the enlarged basis set 6-311g(d,p) and mp2optimized geometry gave almost the same results as evident from table 5. with expectations, all 4 nova biotechnol chim (2021) 20(2): e1010 2 molecular energies are a bit lower. amino acid and zwitterionic forms of histidine, -alanine, and carnosine are close in energy. with g = -0.32 kcal mol-1 the equilibrium constant reads k = exp (-g/rt) = 1.14. table 5. energies, entropies, and free energies of the reactants and products at 300 k.a histidine -alanine carnosine h2o reaction (eq.1) scf level, 6-31g** e0, z-form -342,323 -201,985.2 -496,552 -47,706 50.2 e0, a-form -342,340 -201,985.8 -496,619 -47,706 0.8 u, 300 k -342,225 -201,908 -496,444 -47,689 0 s, 300 k 0.0984 0.0785 0.1283 0.0450 -0.0036 a, 300 k -342,254 -201,932 -496,483 -47,703 0 evib 113.4 75.8 172.9 14.6 -1.7 erot 0.89 0.89 0.89 0.89 0 etrans 0.89 0.89 0.89 0.89 0 svib 0.0283 0.0138 0.0544 0 0.0123 srot 0.0290 0.0253 0.0317 0.0103 -0.0122 strans 0.0411 0.0394 0.0422 0.0347 -0.0036 mp2 level, 6-31g** e0, z-form -343,399 -202,593 -498,113 -47,830 49 e0, a-form -343,409 -202,591 -498,171 -47,830 -1 mp2 level, 6-311g(d,p) (5d, 7f) e0, z-form -344,886 -203,472 -500,247 -48,046 65.4 e0, a-form -344,885 -203,470 -500,307 -48,046 1.57 u, 300 k -344,782 -203,396 -500,141 -48,031 6.73 s, 300 k 0.1084 0.0804 0.1365 0.0465 -0.0058 g, 300 k, 1 atm -344,805 -203,420 -500,181 -48,044 -0.32 a energies in kcal mol-1, entropies in kcal k-1 mol-1. z – zwitterion, a – amino acid form. conclusions ab initio mo-lcao-scf calculations show that the amino acid forms of the -alanine, histidine, and carnosine are more stable than the zwitterionic form in vacuo. the large pearson hardness of the carnosine means that it is very resistant against the electron transfer. the formation of the carnosine from the -alanine and histidine via eq. 1 is an equally probable process as its hydrolysis, k ~ 1. acknowledgments grant agencies of slovakia are acknowledged for the financial support (projects vega 1/0013/18, apvv 16-0039 and itms no 313011asn4). conflict of interest the authors declare that they have no conflict of interest. references boldyrev aa, aldini g, derave w (2013) physiology and pathphysiology of carnosine. physiol. rev. 93: 18031845. cambridge crystallographic data centre, https://www.ccdc.cam.ac.uk/. hyperchem (2008) molecular modeling system, ver. 8.0.6. hypercube inc. pearson rg (1977) chemical hardness, wiley-vch, weinheim, 210 p. pegova a, abe h, boldyrev a (2000) hydrolysis of carnosine and related compounds by mammalian carnosinases. compar. biochem. phys. 127: 443-446. politzer p, murray js (2002) the fundamental nature and role of the electrostatic potential in atoms and molecules. theor. chem. acc. 108: 134-142. 5 https://www.ccdc.cam.ac.uk/ nova biotechnol chim (2021) 20(2): e1010 2 politzer p, laurence pr, jayasuriya k (1985) molecular electrostatic potentials: an effective tool for the elucidation of biochemical phenomena. envir. health persp. 61: 191-202. sen, kd (1993) chemical hardness. in clarke mj et al. (eds.), structure and bonding, springer-verlag, berlin heidelberg, pp. 268. schön m, mousa a, berk m, chia wl, ukropec j, majid a, ukropcová b, de courten b (2019) the potential of carnosine in brain-related disorders: a comprehensive review of current evidence. nutrients. 11: 1196. vranovičová b, boča r (2021) ab initio study of the biogenic amino acids. j. mol. model. 27: 355. 6 microsoft word luptakova et al 2010-1.doc nova biotechnologica 10-1 (2010) 23 metals recovery from acid mine drainage alena luptakova1, magdalena balintova2, jana jencarova1, eva macingova1, maria prascakova1 1department of mineral biotechnologies, institute of geotechnics of the slovak academy of sciences, watsonova 45, košice, sk-043 53, slovak republic (luptakal@saske.sk, jencarova@saske.sk, macingova@saske.sk, prascak@saske.sk) 2institute of building and environmental engineering, civil engineering faculty, technical university of košice, vysokoškolská 4, košice, sk-042 00, slovak republic (magdalena.balintova@tuke.sk) abstract: the objectives of the present work give the results view of some physicochemical, chemical and biological-chemical methods for the heavy metals removal from acid mine drainage (amd). the background of the studied physicochemical methods was the adsorption by turf, chemical methods the heavy metals precipitation by the neutralization with naoh. the principles of the biological-chemical methods were the bioprecipitation by the applications of sulphate-reducing bacteria (srb), the sorption by the bacterially produced iron sulphides and sorption by brown coal bio-modified by micromycetes. key words: acid mine drainage, neutralization, bioprecipitation, sorption, biosorption 1. introduction acid mine drainage (amd) is unique among industrial contaminants on the subject of mainly the mining industry of the sulphide minerals. amd generation proceeds increased considerably after the closure of mines. acid mine waters have low ph-values, and typically high concentrations of sulphates, iron and non-ferrous metals (kontopoulos, 1988), which serve as buffering systems. development of cost-effective and sustainable remediation solutions for the mine water problem has been the subject of extensive review. in addition to monitored natural attenuation, the two broad philosophies which have been pursued in the treatment and abatement of mine water pollution include measures directed towards prevention at source, usually involving physical intervention of one form or another, and measures directed at the resulting effluent, including active or passive remedial systems. both active and passive systems may be implemented using physicochemical, chemical or biological-chemical treatment technologies (skousen et al., 1998; kadukova and stofko, 2006a). nowadays is pay attention to physical, chemical and biological methods for the selective recovery of metals from amd. these methods constitute the possibility of the recovery metals in the suitable forms for commercial value. current research of heavy metals removal in water environment is aimed to application of natural materials as well as industrial wastes that are regarded as cost effective sorbents 24 luptakova, a . et al. (garcia sanchez et al. 1999). among the most often tested sorbents of heavy metals belong: zeolite, carbonate, clays, turf, oxide and hydroxide of iron. deorkar and tavlarides (1998) development of amd physicochemical treatment by application of an adsorption process comprised of inorganic chemically active adsorbents to selectively recover of fe, cu, zn, cd and pb from amd without neutralization. jacke and diebold (1983) evaluated the chemical treatment of amd on the ground of metal recovery from amd by addition of sulphides followed by oxidation and selective titration. cu and zn precipitated as sulphides and fe, al, mn and mg were recovered as hydroxides. tabak et al. (2003) conducted the biotreatment of amd by selective sequential precipitation to recover metals as hydroxides and sulphides. for the metals removal from amd can be used different biosorbents on the base of sawdust, algae, microscopic fungi, biogenous ferrous sulphides biomass and etc. (kadukova and stofko, 2006b; kadukova and vircikova, 2003). in slovak republic there are some localities with existing amd generation conditions. our previous research demonstrates the amd critical values in the abandoned cu – fe ore deposit smolnik (luptakova et al., 2006). it is necessary to develop methods for their treatment. that was the reason for starting a systematic monitoring of geochemical development in acid mine drainage in 2004 in order to prepare a prognosis in terms of environmental risk and use of these waters as an atypical source of a wide range of elements. on this account was our research oriented on the development suitable methods or their combination for the amd effluent treatment from deposit smolnik. we studied some physicochemical, chemical and biological-chemical methods. heavy metals model solutions and amd from smolnik were used for experiments. the background of the used physicochemical methods was the adsorption by turf brush peatsorb. experiments of the chemical methods were oriented on to study of the metals selective precipitation in the hydroxides form by the neutralization with naoh. the principle was the endpoint titration. the backgrounds of the biological-chemical methods were the bioprecipitation by the applications of sulphate-reducing bacteria (srb), the sorption by the bacterially produced iron sulphides and sorption by brown coal modified by different micromycetes strains. the metabolic process of srb is the anaerobic reduction of sulphates by the formation of hydrogen sulphide reacting in the water with cations of metals forming little soluble sulphides. investigated was the process of the heavy metals precipitation by bacterially produced hydrogen sulphide with the combination of the metals precipitation by sodium hydroxide at the various amd ph values. in the literature this methods is named as the selective sequential precipitation (ssp) (tabak et al., 2003). besides srb application gives rise to fe sulphides (fexsy) with the magnetic properties, which are suitable bio-sorbents of heavy metals and are utilizable for amd treatment in combination with the magnetic separation. for the heavy metals removal from solutions also unconventional sorbents prepared from brown coal by micromycetes were used. it was studied bio-modification of brown coal sorption materials with the aim to enhance its sorption properties. the micromycetes (aspergillus niger, aspergillus clavatus, nova biotechnologica 10-1 (2010) 25 penicillium glabrum and trichoderma viride) have been selected for biological activation of coal samples. 2. material and methods 2.1 model solutions stock solutions of each metal: cu(ii) containing 30-300 mg/l, zn(ii) containing 30-300 mg/l and cd(ii) containing 50-100 mg/l were prepared by dissolving cuso4.5h2o, znso4.h2o and 3cdso4.8h2o of analytical grade in distilled water. 2.2 acid mine drainage the experiments were conducted with amd coming from the abandoned and flooded deposit of smolnik (slovak republic). the average values of ph and the major metals composition of acid mine drainage was following: ph 3.9, so4 2 2 938 mg/l, fe 307 mg/l, mn 26 mg/l, cu 5 mg/l, zn 11 mg/l, al 77 mg/l. 2.3 adsorption metals by turf based on our previous results, where various adsorbents were tested (balintova and kovalikova, 2008) for our study of cu, fe, al, zn ions removal from acid mine drainage by adsorption, turf brush peatsorb (reo amos slovakia) was used. the dependence of cu, fe, al, zn concentration decreasing on time (1, 3, 5 and 10 min), was investigated under dynamic conditions using turf brush peatsorb. to intensify the adsorption process, sample of amd was continuously stirred with 5 g of turf brush peatsorb. in filtrate was determined ph (mettler toledo) and cu, fe, al, zn by colorimeter dr 890 (hach lange). 2.4 metals precipitation by naoh the precipitation by 1m naoh solutions was used for the removal of metals as hydroxides from amd. experiments were carried out by raw amd samples of 100 ml and each were titrated to ph end points ranging from 5 to 9 using 1m naoh. when the preset ph end point was reached, the titrated solution was filtered to precipitated metals removing. during titration the amd solution was continuously stirred, the ph was monitored and the concentration of metals was determined too. 2.5 metals precipitation by biogenic h2s and naoh for the production of the bacterially h2s the cultures of srb (genera desulfovibrio) were used. these bacteria were isolated from a mixed culture obtained from the potable mineral water (gajdovka spring, the locality kosice-north, slovakia). 26 luptakova, a . et al. this biological-chemical method contains several process steps and can be divided in to these main steps, as well as: the bacterially h2s production by srb; the heavy metals precipitation by the bacterially produced h2s; the heavy metal sulphides separation by the filtration; the setting ph of the filtrate from previous steps by 1m naoh (the precipitation of metals as hydroxides); the heavy metal hydroxides separation by the filtration; the subsequent precipitation of the heavy metals by bacterially produced h2s. values of ph for the heavy metals precipitation were assigned on the ground of the study of the orientation conditions for the selected metal removal from amd by precipitation using naoh and our previous works and enumerations (luptakova et al., 2003). the concentration of metals was determined by atomic absorption spectrometry using spectrometer aa-30 varian instrument. a glass ph electrode combined with the reference ag/agcl electrode was used to measure ph. digital phmeter gprt 144 agl was used. 2.6 sorption of metals by bacterially produced iron sulphides the preparation of biogenic sulphides was realized in the bioreactor filled with 400 ml of modified nutrient medium dsm-63 and inoculated with 100 ml of a culture of srb during 21 days at 30°c under anaerobic conditions. these conditions were generated by introducing an inert gas (n2) and chemically with sodium thioglycolate. the ph of the medium was adjusted to the value 6.8 with sodium hydroxide. preparation was realized under 2 different modes. during discontinuous mode the bioreactor worked without addition of fresh nutrient medium. during semicontinuous process of preparation the bioreactor worked 4 days in batch mode and then 3 days in continuous mode (i.e. fresh medium was supplied into reactor). batch sorption experiments were performed in 100 ml erlenmeyer flasks with the sorbent dose 1 g/l. sampling was conducted during 90 minutes. the concentration of zinc and cadmium was determined by atomic absorption spectrometry. 2.7 sorption by bio-modified brown coal the cultures of selected micromycetes were grown in sabouraud agar medium. suspension was injected (5 ml) of every 14-day-old culture spores in sab to the 10 g of brown coal mixed with 10 ml of sab medium. the cultivation was executed in the dark at ambient temperature. the leaching process took 7 weeks. after leaching, the suspensions were filtered, washed with distilled water, dried and prepared for adsorption experiments. all the adsorption experiments were conducted at ambient temperature in a laboratory shaker. metal solutions of known concentrations were introduced into the glass erlenmeyer bottles containing defined amounts (10 g/l) of the adsorbent. the bottles were shaken horizontally and the adsorbent was removed by filtration after 1 hour adsorption. the equilibrium concentrations of heavy metals were determined by atomic adsorption spectroscopy and the metal uptake was calculated from the difference. the langmuir adsorption isotherms have been constructed and the maximum adsorption capacity of the adsorbents has been nova biotechnologica 10-1 (2010) 27 determined. for cu(ii) sorption the ph reached 5, as cu(ii) ions undergo hydrolysis reactions in water and form insoluble aqueous complexes with increasing ph. zn(ii) sorption experiments were performed at ph 7 for the same reason as in case of cu(ii) adsorption. 3. results and discussion 3.1 adsorption metals by turf table 1 documents the physical-chemical method studies and there are also given the results of ph measuring in amd turf brush mixture depending on time and influence of adsorption processes on cu, fe, al, zn concentrations in individual samples. from the results follows, that it is possible to decrease the cu, fe, al and zn concentrations in polluted surface water by physical adsorption. the highest turf brush efficiency was observed for zinc removal, where the decrease of concentration in solution was 95.71%. then follows copper (decreasing in amd about 55.88%), iron (21.19%) and aluminium (15.6%). based on experimental results we can also state that chosen adsorbent have not influenced the ph increasing above 4 that is connected with precipitation of metals. table 1. dependence of cu, fe, al and zn removal from amd versus adsorption time. cu fe al zn adsorption time ph [mg/l] amd 3.95 1.36 358.2 54.5 17.5 1 min 3.10 0.86 347.8 52.7 1.5 3 min 2.95 0.61 353.3 46.4 1.2 5 min 2.97 0.61 333.5 46.2 1.0 10 min 2.93 0.60 282.3 46.0 0.75 3.2 metals precipitation by naoh the results of the titration test amd by 0.2m naoh documents fig. 1. it is a documentation of the titration curve and elemental amd analysis. the titration curve of amd can be divided into a number of by its different slopes. it shows that the optimum ph for metals precipitation is different for each metal: for al – ph 5; for cu – ph 6; for zn – ph 7; for fe – ph 8; for mn – ph 9. table 3 demonstrates results of metals precipitation by naoh that is titration of amd to ph end points for the individual metals ranging from 5 to 9 using 1m naoh. as it is seen from table 2 was removed 97% of al at ph 5; 99.9% of cu at ph 6; 99.9% of zn at ph 7; 99.9% of fe at ph 8 and 99.9% of mn at ph 9. initial assumption about precipitation of followed metals up to ph 9 has been confirmed. 28 luptakova, a . et al. 3.3 metals precipitation by biogenic h2s and naoh the selective sequential precipitation of heavy metals form amd sample was performed in two interconnected bioreactors with a capacity 1000 ml (the first bioreactor) and 250 ml (the second bioreactor), which operated at the semi-continual conditions. using the operating conditions and obtained results of the selective sequential precipitation of heavy metals form amd sample illustrated in table 3. the bacterially produced hydrogen sulphide by srb at ph 3.9 (initial ph of amd), 4.5 and 6.0 realized the selective sequential precipitation of cu, zn and fe, respectively (i.e. steps 1, 3 and 5). al and mn were precipitated as aluminium and manganese hydroxide at ph 6.0 and 9.0, respectively (i.e. steps 4 and 6). fe was precipitated predominantly as hydroxide (steps 2, 4 and 6). fig. 1. titration curve and metal amd analysis of amd from the deposit of smolnik. table 2. precipitation of al, cu, zn, fe and mn in ph dependence (initial ph of amd – 3.9). ph al (mg/l) cu (mg/l) zn (mg/l) fe (mg/l) mn (mg/l) 3.9 58.8 1.38 6.88 338.6 22.88 5 0.4 0.65 6.75 268.8 22.88 6 0.4 <0.02 5.38 9.8 22.88 7 0.4 <0.02 <0.03 2.5 20.38 8 0.4 <0.02 <0.03 <0.03 12.25 9 0.4 <0.02 <0.03 <0.03 0.03 table 3. metals precipitation by bacterially produced h2s and naoh (initial amd ph – 3.9). step 1. step 2. step 3. step 4. step 5. step 6. ph 3.9 4.5 4.5 6.0 6.0 9.0 precipitating agent h2s naoh h2s naoh h2s naoh removed metals cu fe, al zn al, fe fe mn, fe form of removed metals (solid phase) cus fe(oh)3 al(oh)3 zns al(oh)3 fe(oh)3 fes mn(oh)2 fe(oh)2 filtrate composition concerning of metals presence (liquid phase) fe, al, zn, mn fe, al, zn, mn fe, al, mn fe, mn fe, mn ----- nova biotechnologica 10-1 (2010) 29 3.4 sorption of metals by bacterially produced iron sulphides fig. 2 shows sorption of cadmium and zinc ions from model solutions by iron sulphides during 90 minutes by semi-continuous and discontinuous sorbents, when initial concentration of metal ions in model solutions was 50 mg/l. 0 5 10 15 20 25 0 10 20 30 40 50 60 70 80 90 time [min] so rp ti on [ m g/ g ] cd-ss (50) cd-ds (50) zn-ds (50) zn-ss (50) fig. 2. sorption of cadmium and zinc ions from model solutions. the quantities of metal ions that iron sulphides captured from 100 ml of solution are in calculation on 1 g weights of dry the sorbent. we can see that the sorption value for cadmium after 90 minutes for semi-continuous sorbent (cd-ss) is 21.96 mg/g and 21.83 mg/g for discontinuous sorbent (cd-ds). values of zinc sorption are 9.49 mg/g for semicontinuous sorbent (zn-ss) and 5.22 mg/g for discontinuous sorbent (zn-ds). 0 5 10 15 20 25 30 35 40 45 50 0 10 20 30 40 50 60 70 80 90 time [min] so rp ti o n [ m g /g ] cd-ss (100) cd-ds (100) zn-ds (100) zn-ss (100) fig. 3. sorption of cadmium and zinc ions from model solutions. 30 luptakova, a . et al. fig. 3 compares sorption of zinc and cadmium ions during 90 minutes by semicontinuous and discontinuous sorbents, when initial concentration of metal ions in model solutions was 100mg/l. in this case the highest value was obtained for zinc sorption by semi-continuous sorbent (zn-ss) 43.13 mg/g and the lower value belong to cadmium sorption by semicontinuous sorbent (cd-ss) 22.75 mg/g. 3.5 sorption by bio-modified brown coal fig. 4 presents adsorption isotherms of copper and zinc adsorption by biomodified coal adsorbents. experimental data were fitted by langmuir equation. the correlation coefficient ranged from 0.96 to 0.99. experimental results showed that maximum increase of metals uptake for biologically activated brown coal was achieved by the activation by penicillium glabrum (sample s3), i.e. 8.8 mg cu(ii)/g of sorbent and 14.3 mg zn(ii)/g of sorbent. 0 50 100 150 200 0 2 4 6 8 10 cu adsorption q [m g/ g] c e [mg/l] coal + a. niger coal + a. clavatus coal + p. glabrum coal + t. viride coal 0 50 100 150 200 0 2 4 6 8 10 coal + a. niger coal + a. clavatus coal + p. glabrum coal + t. viride coal zn adsorption q [m g/ g] c e [mg/l] fig. 4. langmuir adsorption isotherms of cu (a) and zn (b) adsorption on brown coal treated by different microorganisms. the results of adsorption experiments showed that selected type of sorbent preparation had positive influence on sorption properties of activated material and prepared sorbents had good affinity to selected metals. obtained results confirmed that there is a possibility to prepare the sorbents by new non-conventional methods and the obtained results appear as promising for the research and development in utilisation of non-energetic coal. 4. conclusions the major metal ions in the amd from the abandoned and flooded deposit of smolnik (slovak republic) were fe, al, ca and mg, among which fe and al were potentially valuable, while others such as cu, zn and mn were present as minor metals at significantly low concentrations. the value of ph, contend of fe, al, zn, cu, mn nova biotechnologica 10-1 (2010) 31 and mg of amd did not meet the effluent limitation of nv sr no. 296/2005 z.z. up to now amd was not treated at the site. results of the amd titration test document that the titration curve can be divided into four ranges (i to iv). its show the different optimum ph for metals precipitation of each metal: for al – ph 5; for cu – ph 6; for zn – ph 7; for fe – ph 8; for mn – ph 9. the metals precipitation using 1m naoh confirms that was removed 97% of al at ph 5; 99.9% of cu at ph 6; 99.9% of zn at ph 7; 99.9% of fe at ph 8 and 99.9% of mn at ph 9. metals removal by precipitation is possible up to ph 9. the study of the selective sequential precipitation and bio recovery of metals from aforementioned amd was realized by the combination of the metals precipitation by the bacterially produced hydrogen sulphide and the precipitation of metals by sodium hydroxide at the various values of ph amd. for the removal of cu and zn in the form of sulphides were received excellent results. was not come to good results point of view of the fe, al and mn the selective precipitation, because was determined the co-precipitation of fe and al or fe and mn. obtained results can be used for suggestion of technology for selective metal recovery from acid mine drainage from smolnik. the base this technology will be the combination of chemical and biological agent application. acknowledgements: this work was supported by the slovak research and development agency under the contract no. apvv-51-027705 and bilateral project apvv sk-cz-0105-07. references balintova, m., kovalikova, n.: removal of heavy metals from acid mine drainage using adsorption methods. proceedings of the 8th international scientific conference modern management of mine producing, geology and environmental protection sgem 2008, albena, 2008, 155-160. boonstra, j., van lier, r., janssen, g., dikman, h., buisman, c.j.n.: biological treatment of acid mine drainage. proceedings of the 13th international biohydrometallurgy symposium, biohydrometallurgy and the environment toward the mining of the 21st century ii., ibs, madrid, 1999, 559-566. deorkar, n.v., tavlarides, l.l.: adsorption process for metal recovery from acid mine waste: the berkeley pit problem. environ. prog., 17, 1998, 120-125. foucher, s., battaglia-brunet, f., ignatiadis, i., morin, d.: treatment by sulfate-reducing bacteria of chessy acid-mine drainage and metals recovery. chem. eng. sci., 56, 2001, 1639-1645. garcia sanchez, a., alavarez ayuso, e., jimenez de blas, o.: sorption of heavy metals from industrial waste water by low-cost mineral silicates. clay miner., 34, 1999, 469-477. janke, d.r., diebold, f.e.: recovery of valuable metals from acid mine drainage by selective titration. water res., 17, 1983, 1639-1645. kadukova, j., vircikova, e.: minerálne biotechnológie iii., biosorpcia kovov z roztokov, všb tu ostrava, 2003, isbn 80-248-0244-9. 32 luptakova, a . et al. kadukova, j., stofko, m.: environmentálne biotechnológie pre hutníkov, equilibria, košice, 2006a, isbn 80-8073-496-8. kadukova, j., stofko, m.: biosorption of heavy metals ions from aqueous solutions. environmental research trends, nova publishers, 2006b, isbn 160021-556-4. kalin, m., fyson, a., wheeler, n.w.: the chemistry of conventional and alternative treatment systems for the neutralization of acid mine drainage. sci. tot. environ., 366, 2006, 395-408. kontopouls, a.: acid mine drainage control. in: castro, s.h., vergara, f., sánches, m.a. (eds.) effluent treatment in the mining industry. university of concepcion, chile, 1988, 57-118. luptakova, a., kusnierova, m., bezovska, m., fecko, p.: the selective precipitation of heavy metals by sulphate-reducing bacteria. proceedings of the 15th international biohydrometallurgy symposium, nereus congress and conferences, athens, greece, 2003, 665-672. luptakova, a., kusnierova, m., slesarova, a.: environmental risks and impact of old mine loads in the slovak republic. proceedings of 2nd international conference on environmental research and assessment, university of bucharest, centre for environmental research and impact studies, bucharest, 2006, 254-257. skousen, j., rose, a., geidel, g., foreman, j., evans, r., hellier, w.: a handbook of technologies for avoidance and reclamation of acid mine drainage, morgantown, wv: national mine land reclamation center, west virginia university, 1998. tabak, h.h., scharp, r., burckle, j., kawaharai, f.k., govind, r.: advances in biotreatment of acid mine drainage and biorecovery of metals: 1. metal precipitation for recovery and recycle. biodegradation, 14, 2003, 423436. veeken, a.h.m., rulkens, w.h.: innovative developments in the selective removal and reuse of heavy metals from waste-waters. water sci. technol., 47, 2003, 9-16. microsoft word ubaldini_luptakova 2010-1.doc nova biotechnologica 10-1 (2010) 15 application of biohydrometallurgical processes for heavy metals removal from acid mine drainage stefano ubaldini1, alena luptakova2, eva macingova2, roberto massidda1, pietro fornari1 1instituto di geologia ambientale e geoingegneria, cnr, rome, italy, (stefano.ubaldini@igag.cnr.it) 2institute of geotechnics, slovak academy of sciences, slovakia (luptakal@saske.sk) abstract: the main scope of this study was to remediate acid mine drainage (amd) by application of biohydrometallurgical processes, environmentally friendly, to remove heavy metals such as zn, cu, mn, cd, al and fe. the processes studied have been electrowinning and bioprecipitation. the samples utilised were collected from the zinc mine located in italy and from a cooper – iron ore deposit in slovakia. by electrochemical experiments, high metals removal, with a low energetic consumption, has been achieved: in particular, by zn electrodeposition, it was possible to achieve 95-99% zn removal. culture of sulphatereducing bacteria (srb) of genera desulfovibrio sp. was used for the bioprecipitation tests. the precipitation kinetic of metals at the original ph of aforementioned amd by srb has been investigated. this method has been performed in two interconnected reactors. achieved results indicate the 98-99% selective elimination of cd from amd italian mine, and the 98-99% selective elimination of cu from amd slovak mine by bacterially produced h2s. both the electrowinning and bioprecipitation processes have been demonstrated the technical feasibility to decrease the heavy metals concentration. the experimental work has been carried out in the framework of the agreement of scientific cooperation between the institute of environmental geology and geoengineering of the cnr, italy and the institute of geotechnics of slovak academy of sciences, slovakia (years 2007-2009). key words: heavy metals, biohydrometallurgical processes, acid mine drainage, desulfovibrio sp. 1. introduction in contrast to most organic pollutants, heavy metals are never degraded. the only ways to remedy heavy metals-polluted lands are stabilization or extraction using the suitable methods (veglió et al., 2003; kadukova and stofko, 2006); beolchini et al., 2007). various methods are used for redevelopment of soils and waters in the world (apha, 1989), but any of them are universal (pagnanelli et al., 2003; bálintova and kovaliková, 2008; ubaldini et al., 2009). classical treatments for the removal of heavy metals from contaminated waters are precipitation with lime or more expensive chemicals (epstein, 2003). however, these methods present negative drawbacks the production of secondary wastes (e.g. lime precipitation generates high volumes of solid wastes) (ubaldini et al., 2009). there is a need for new and low-cost technologies in the field of elimination metals from environment. with respect to involved proposition various authors have studied, at laboratory scale, the application of physicochemical and biological-chemical processes. between the innovative and unconventional technologies belong for example the electrowinning and the bioprecipitation. electrowinning process is 16 ubaldini, s. et al. currently used at large scale to purify process solutions and to recover precious metals. microorganisms play important roles in the environment fate of heavy metals (ronald, 1995) with a multiplicity of physical, chemical and biological mechanisms effecting transformations between soluble and insoluble phases (beolchini et al., 2009a; beolchini et al., 2009b). the biggest environmental problems relating to mining and processing activities in the worldwide is the formation and treatment of acid mine drainage (dikman and buisman, 1999). the source of acid mine drainage (amd) is the residues of mining activity mainly after the mining of deposits containing of sulphide minerals. amd contains sulphuric acid, metals in the soluble form and its ph can be very low (ubaldini et al., 2006a). in italy and slovakia there are some localities with existing amd generation conditions (ubaldini et al., 2007a; ubaldini et al., 2007b). 2. materials and methods 2.1 samples the investigation has been carried out at laboratory scale by synthetic solutions, starting from amd from the zinc mine located in montevecchio mine (italy) and slovak mine located in smolník. the amd characterisation is reported in tables 1 and 2. table 1. composition of the amd italian sample in mg/l. zn cd cu ni as sb pb mn fe so4 2 1600 3.50 0.50 4.00 0.006 0.005 0.076 86 190 1800 table 2. composition of amd slovak sample in mg/l. zn cd cu ni as al pb mn fe so4 2 10.13 0.1 4.31 0.32 0.042 79.50 0.019 20 270 2938 2.2 physical-chemical process: electrowinning nitric acid (hno3) has been added to the synthetic solution, with the aim to oxidise fe2+ to fe3+. in a subsequent step, sodium hydroxide (naoh) was added to reach ph 4.0. successively, the deposit has been separated by filtration. electrowinning tests have been performed in a cylindrical glass laboratory cell of 200 cm3 volume according to ubaldini et al., 2008. the cell was connected to a potentiostat-galvanostat. with the scope to study the electrodeposition kinetic, liquid samples of 3 cm3 have been whit drawn and submitted to chemical analysis by icpms, while the purity of the solid deposit was determined by x-ray diffraction technique (xrd). metallic content of the deposit was analysed by icp-ms. nova biotechnologica 10-1 (2010) 17 2.3 biological-chemical processes: bioprecipitation the cultures of srb (genera desulfovibrio sp.) were used which were isolated from a mixed culture obtained from the potable mineral water (luptakova et al., 2002; luptakova et al., 2008). scanning electron micrographs of sulphatereducing bacteria is reported in figure 1. the precipitation of heavy metals form amd sample was performed in two interconnected bioreactors with a capacity 1000 ml (the first bioreactor) and 250 ml (the second bioreactor) (ubaldini et al., 2006a; luptakova et al., 2008a). the heavy metals concentration in the liquid samples taken from the bioreactor was determined by atomic absorption spectrophotometry. the qualitative analysis of precipitates obtained by bacterial produced hydrogen sulphide was realized by energy dispersive spectrometry (eds) analysis. samples of precipitates were dried and coated with gold prior to the eds analysis. fig. 1. scanning electron micrographs of sulphate-reducing bacteria (desulfovibrio sp.) (luptakova et al., 2002). 3. results and discussion 3.1 physical-chemical process: electrowinning preliminary precipitation step has been carried out before electrowinning. during this phase, also al deposition has been achieved. the liquor prepared was treated by using an electrowinning lab-scale operation, to verify the technical feasibility of the metals deposition. the average results of the electrowinning tests on montevecchio (initial ph 4.6) and smolnik samples (initial ph 3.5), show that, after 30’, zn deposit was of low quality. after 1 h, zn deposit was uniform, while on counter electrode surface mno2 deposited. manganese deposited to the anode as mno2 and to the cathode as mn +. after 2 hours, 90-95% of the metals have been removed by a quantitative cathodic deposition. the high grade purity of the metallic deposit has been achieved, such as it was demonstrated from the results of analysis conducted by xrd. at the end of the processes, all the metals concentrations decrease under the recommended limit suggested from ec (data not shown here) (ubaldini et al., 2006a; ubaldini et al., 2006b; ubaldini et al., 2006c). table 3 and table 4 show the main results of zn electrowinning from synthetic solution (amd italian and slovak 18 ubaldini, s. et al. samples, respectively), while table 5 shows the results attained after chemical precipitation by naoh (amd from slovak sample). table 3. main results of zn electrowinning of synthetic solution (amd italian sample). time (min) r (%) η* (%) e* (kwh/kg) 90 97.98 21.65 16.23 120 99.85 13.05 30.21 * η faradic current efficiency, e energetic consumption table 4. main results of zn electrowinning of synthetic solution without chemical precipitation (amd slovak sample). time (min) r (%) η* (%) e* (kwh/kg) 90 92.18 20.10 17.13 120 96.89 11.92 31.21 * η faradic current efficiency, e energetic consumption table 5. main results of zn electrowinning of synthetic solution after chemical precipitation (amd slovak sample). time (min) r (%) η* (%) e* (kwh/kg) 90 97.07 25.94 12.00 120 99.71 14.99 24.91 * η faradic current efficiency, e energetic consumption 3.2 biological-chemical processes: bioprecipitation during the metals bioprecipitation at the original ph of aforementioned amd, only the precipitation of cd (in the case of the amd sample from montevecchio mine) and cu (in the case of amd sample from smolnik adit pech) were observed. 0 1 2 3 4 5 6 0 100 200 300 0 50 100 150 200 cd ni cu zn fe m n c on ce nt ra tio n of c u, n i a nd c d [m g/ l] c on ce nt ra tio n of f e an d m n [m g/ l]; zn [m g/ l]. 1 01 time of biop recip itation [min] fig. 2. precipitation of heavy metals by biologically produced h2s by srb from amd italian mine at original ph value of amd. nova biotechnologica 10-1 (2010) 19 fig. 2 presents that at ph 4.6 cd was effectively recovered from amd of montevecchio mine using biologically produced h2s. after 30 minutes the concentration of cd was 0.03 mg/l. on the basis of the results of eds qualitative analysis, cd was precipitated in the form cadmium sulphides. in the event of the amd smolnik at ph 3.5, the initial copper concentration 4.31 mg/l was decreased to less than 0.05 mg/l after 4 hours (fig. 3). eds qualitative analysis of precipitates demonstrates that cu was precipitated in the form sulphides cus. concentration changes of other metals (zn, fe, ni, mn), were not significant or remained without changes in case of both aforementioned amd. 0 0,5 1 1,5 2 2,5 3 3,5 4 4,5 5 0 100 200 300 t ime of bioprecipit at ion [min] 0 5 10 15 20 25 30 cu ni cd zn fe m n c on ce nt ra tio n of z n an d m n [m g/ l]; fe [m g/ l]. 1 01 c on ce nt ra tio n of c u, n i a nd c d [m g/ l] fig. 3. precipitation of heavy metals by biologically produced h2s by srb from amd – slovak mine at original ph value of amd. 4. conclusions by application of biohydrometallurgical processes, the technical feasibility to decrease the heavy metals concentration on the amd studied has been determined. in particular, through electrowinning, it was possible to achieve high zn removal with a low energetic consumption, while bioprecipitation process demonstrates the selective precipitation of heavy metals by srb from the amd samples. at original ph value of amd from italian mine was achieved only the precipitation of cd. from amd of slovak mine was achieved only the precipitation of cu at original ph value. obtained results indicate the 98-99% elimination of cd or cu by bacterially produced h2s. acknowledgements: this work was supported by italian national council researches under cnr project n. 6.1.132.48.2, under project cnr rstl n. 0042.0005 and by slovak research and development agency under the contract n. apvv-51-027705. moreover, the authors are grateful to ms. emanuela tempesta for helpful collaboration during the experimental work. 20 ubaldini, s. et al. references apha: standard methods for the examination of water and wastewater. 17th edition, american public health association, usa, washington d. c., 1989. 1. balintova, m., kovalikova, n.: testing of various sorbents for copper removal from acid mine drainage. chem. listy, 102, (2008), 343-344. beolchini, f., ubaldini, s., passariello, b., gul, n., ture, d., veglió, f., danovaro, r., dell’anno, a.: bioremediation of dredged sediments polluted by heavy metals. adv. mat. res., 20-21, 2007, 307-310. beolchini, f., dell’anno, a., de propris, l., ubaldini, s., cerrone, f., danovaro, r.: autoand heterotrophic acidophilic bacteria enhance the bioremediation efficiency of sediments contaminated by heavy metals. chemosphere, 74, 2009a, 1321-1326. beolchini, f., fonti, v., ferella, f., ubaldini, s., vegliò, f.: nickel, vanadium and molybdenum extraction from exhaust lc-finer catalysts by biohydrometallurgical technologies. proceedings of the 1st international conference biotechnologies and metals 2009. kosice, slovak republic, september 24th – 25th, 2009b, 11-14. dikman, h., buisman, c.j.n.: biological treatment of acid mine drainage. in: biohydrometallurgy and the environment toward the mining of the 21st century. amils r., ballester a. 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6.78 for garden soil), ec (ss 7.80 ds.m.-1; gs 0.32) and ex na+ (ss 8.81 cmol.kg-1; gs 0.4181 cmol.kg-1) was observed in the saline soil while there was a decrease in organic carbon, total nitrogen and available phosphorus in saline soil. proximate analysis of c. maxima and t. occidentalis leaves revealed that fiber, carbohydrate, and caloric value were slightly reduced in saline soil treatments while ash, protein and lipids contents were slightly increased. amf inoculation and pm application had significant effect on proximate composition of these plant leaves but caloric value which was significantly (p ≤ 0.05) increased in non-saline soil treatments. physiological parameters such as leaf turgid weight (ltw), leaf relative water content (lrwc), vigor index (vi), and salt tolerance index (sti) were significantly reduced by salinity, while electrolyte leakage (el) was higher in saline soil treatments than nonsaline soil treatments. however, inoculation with amf in combination with pm amendment significantly increased ltw, lrwc, vi, and sti in both saline and non-saline soil treatments above single treatment with mycorrhizal species and poultry manure. however, el reduced with mycorrhizal inoculation. the results of this work have shown that amf and pm can enhance plants ability to tolerate salinity possibly through some morphological and physiological changes which improved water and nutrients uptake. introduction soil salinity is a term used to describe the amount of mineral salts present in soil (shan 2009). the mineral salts constitute a mixture of electrolytes. the major cations in saline soils include na+, ca2+, mg2+, and k+. the major anions include clˉ, so4 2-, hco3-, co3 2-, and no3-. these constituents are mailto:abdelhak.rhouma@gmail.com nova biotechnol chim (2022) 21(1): e1170 2 usually reported in units of mg/l (ppm), mmol.l-1 or mmol charge.l-1 (meq.l-1) in solution extracted from a soil saturated with water (tanji 2002). salinity is often measured as electrical conductivity (ec), a measure of the ability of a substance to conduct electricity. the natural factors contributing to salinization of soils include weathering of rocks, deposition of oceanic salts, topographical factor, groundwater table fluctuation, salt lake, scald, fallow period, and flood water. however, the major contributors to soil salinization are weathering of parental rocks, oceanic salt deposition, and groundwater table fluctuation. rocks are mostly rich in sodium and other salts (saxena et al. 2017). the most common man-made factors contributing to salinization are the irrigational water and the use of chemical fertilizers and pesticides. irrigation is an important factor in the crop productivity. therefore, the use of high salt-containing water for crop irrigation and poor management practices for appropriate leaching of salts lead to the accumulation of salts and deteriorate the crop fields (zhu 2007). salinity not only decreases the agricultural production of most crops, but also, as a result of its effect on soil physicochemical properties, adversely affects the associated ecological balance of the area. the harmful impacts of salinity include: low agricultural production, low economic returns due to high cost of cultivation, reclamation management, soil erosion due to high dispersibility of soil, ecological imbalance due to halophytes and marine life forms from fresh water to brackish water, poor human health due to toxic effects of elements such as b, f, and se (hu and schmidhalter 2002; ashok et al. 2012). crop species show a spectrum of responses to salt, although all have their growth, and eventually, their yield reduced by salt. salt effects are the combined result of the complex interaction among different morphological, physiological, and biochemical processes (ashok et al. 2012). salinity may directly or indirectly inhibit cell division and enlargement and finally the growth of the whole plant. in addition to these factors, some other factors like water deficit (drought stress), ion toxicity, ion imbalance and soil compaction may cause growth reduction, injury of foliage, nutrient deficiencies, destruction of soil structure which ultimately hampers the growth of the plant. some above ground visible morphological symptoms of plants are marginal yellowing/browning of foliage, premature fall of leaves, twig and branch die back, loss of vigor and stunted growth (ashok et al. 2012). the high concentration of salts in soil may induce three types of stresses: osmotic, ionic or oxidative, which drastically affect plant growth and productivity (saxena et al. 2017). osmotic stress leads to altered water potential, thereby reducing the water use efficiency of plant due to induction of physiological drought conditions (saxena et al. 2017). ionic stress causes disruption of ion homoeostasis at both cellular and whole-plant levels, oxidative stress elicits release of reactive oxygen species, which inhibit cell growth and plant metabolism. experiments carried out to understand amf-salinity interaction revealed that mycorrhizal fungi reduce negative effects of these stresses and promote plant growth (wu et al. 2006; zuccarini and okurowska 2008; evelin et al. 2009; wu et al. 2010a, 2010b). plants encounter a variety of biotic and abiotic stresses, which cause significant structural and functional changes that will result in decreased yield and vegetative traits (plant height, shoot length, number of branches, fresh and dry biomass, etc.) (agha et al. 2021; matrood and rhouma 2021; sofy et al. 2021a). in the other hand, salinity is among the most significant threats hindering global food security. arbuscular mycorrhizal fungi and poultry manure (practice alone or in combination) were commonly used for agricultural production for their abilities to improve plant health to salinity stress (solaiman et al. 2020; zhang et al. 2020; sallam et al. 2021; sofy et al. 2021a, 2021b). arbuscular mycorrhizal (am) fungi are among the most common soil fungi and the majority of plant species have associations with am fungal species (selvaraj and chellappan 2006). it is thought that about 80 % of vascular plants form am associations (hodge 2000). mycorrhizal fungi can help plants to survive and grow under different environmental conditions, and also help plants increase their reproductive output (bolandnazar et al. 2007). the basic elements of the symbiosis are that the plant provides the mycorrhiza with carbohydrates while the fungi enhance the plant’s uptake of certain nutrients needed for growth nova biotechnol chim (2022) 21(1): e1170 3 (selvaraj and chellappan 2006). it has been estimated that in compensation for the additional nutrients and water provided by mycorrhizas, a plant must provide 20 % of its fixed carbon to the roots for mycorrhizal establishment and maintenance of the association (ebrahim 2014). little information is available about the influence of combination poultry manure/arbuscular mycorrhizal fungi on yield and quality of cucurbits. elmer and pignatello (2011) and blackwell et al. (2015) pointed out that poultry manure application and arbuscular mycorrhizal fungi could serve as a sustainable nutrient alternative to chemical fertilizer. this is due to the potential of the fungi to utilize unavailable organic nutrients and increase the efficiency use of nutrients through improved nutrients uptake, which might enhanced plant growth and yield (elmer and pignatello 2011; blackwell et al. 2015). earlier researchers have clearly documented the positive effect of organic amendments in combination with arbuscular mycorrhizal fungi (hammer et al. 2014, 2015) on plant growth and improve nutrients uptake (abdullahi et al. 2015; solaiman et al. 2019). solaiman et al. (2020) pointed out that the cucumber growth responses to poultry manure application and arbuscular mycorrhizal symbiosis showed better plant growth and yield of cucumber and reduced the negative impact of stress salinity. this combination also improved the nutrient uptake and soil fertility of sandy soils (mickan et al. 2016; paymaneh et al. 2018; solaiman et al. 2020). this research was undertaken to investigate the effect of salt stress on the proximate composition and physiological parameters of two different cucurbits (telfairia occidentalis and cucurbita maxima) and determine ways of ameliorating its effect using arbuscular mycorrhizal species and poultry manure. experimental study area saline soil and salt water were collected from the saline ecosystem of iwuochang, ibeno local government area (latitude 4.56°n and longitude 7.57°e), akwa ibom state, nigeria, with an annual rainfall of about 4,021 mm and mean temperature variation of 22 – 31 ºc. the experiment was set up in a safe and secured environment at mbioto 1, etinan local government area (latitude 4.51°n and longitude 7.50°e), akwa ibom state, nigeria, with an annual rainfall of about 4,000 mm and mean temperature variation of 26 – 36 ºc (aksg 2008). non-saline soil for the control and nonsaline treatments was obtained from a farmland in mbioto 1, etinan local government area; fresh water was used for watering the non-saline and control treatments. a map showing the saline water/soil collection and experimental set-up locations is presented in fig. 1. fig. 1. map showing saline water/soil collection and experimental set-up locations (source: field data). experimental design this experiment was set up in a randomized complete block design and arranged in three blocks of 108 pots each for each species of cucurbits (c. maxima and t. occidentalis). this gave a total of 12 treatments (table 1) for each species with nine replicates totaling 108 combinations for each nova biotechnol chim (2022) 21(1): e1170 2 species of cucurbits. this experiment was carried out in 1 march 2020 in a greenhouse. table 1. experimental design. treatments meaning smpsalinity, mycorrhiza, poultry s+ mp+ salinity, mycorrhiza, poultry s+ m+ p(gg) + salinity, + mycorrhiza (g. geosporum), poultry s+ m+ p(ri) + salinity, + mycorrhiza (r. irregularis), poultry s+ mp+ + salinity, mycorrhiza, + poultry s+ m+ p+ (gg) + salinity, + mycorrhiza (g. geosporum), + poultry s+ m+ p+ (ri) + salinity, + mycorrhiza (r. irregularis), + poultry sm+ p(gg) salinity, + mycorrhiza (g. geosporum), poultry sm+ p(ri) salinity, + mycorrhiza (r. irregularis), poultry sm+ p+ (gg) salinity, + mycorrhiza (g. geosporum), + poultry sm+ p+ (ri) salinity, + mycorrhiza (r. irregularis), + poultry smp+ salinity, mycorrhiza, + poultry planting the experimental soils were steam sterilized in the oven in bits for 2 h at 100 ºc to kill weed seeds and soil microorganisms and sieved through a 2 mm mesh to remove pebbles. the poultry manure used in this research consists of moisture (39.69 %), n (2.47 %), p2o5 (2.84 %), k2o (1.84 %). treatments consisted of 1 kg of poultry manure per pot. am fungi glomus geosporum and rhizophagus irregularis (60 – 65 spores per 5 g) were purchased from international institute of tropical agriculture (iita) ibadan, nigeria. matured seeds of cucurbita maxima and telfairia occidentalis were obtained from akwa ibom state agricultural development project (akadep) in etinan. the obtained seeds were selected to eliminate infected seeds. five seeds each of c. maxima and t. occidentalis were sown in each of the pots filled with about 10 kg of sterilized soils. arbuscular mycorrhiza fungi were inoculated by placing 25 g of soil/root fragments containing 60 – 65 spores per 5 g in planting hole at 15 cm depth, before planting the c. maxima and t. occidentalis. following seedling emergence, the plants inoculated were allowed to establish for up to 15 d before being treated with the first dose of saline water. this was to ensure the establishment of am colonization and avoid sudden plant death due to salinity shock. the roots treatment with saline water (100 ml) using an erlenmeyer flask (250 ml) on the two cucurbits species was performed 1 d after the establishment of the mycorrhizal symbiosis and the treatments were spaced every 3 d until the end of the trial (30 june 2020). assessments were conducted 90 d after the treatment (with poultry manure and am fungi). at the end of trial (30 june 2020), 27 plants (3 plants × 9 replicates) per treatment and per block were assessed for each cucurbit species (c. maxima and t. occidentalis). physico-chemical properties of experimental soils soil samples were taken using a 7-cm-diameter soil auger. a total of 108 samples per block were collected in sterile polythene bags. for each block, samples were mixed together into a single one. nine soil samples (500 g) per block (3 blocks) and per replicate (3 replicates) were collected from each treatment after and before the trials and brought to the laboratory. the soil samples were taken and air-dried at room temperature and ground in a wooden mortar to pass through a 2 mm mesh sieve and stored in labelled bags. sub-samples were taken from each soil sample and analysed for physico-chemical properties of the soil. soil samples were analysed following the standard procedures outlined by the association of official analytical chemist (aoac 2005) procedure for wet acid digestions (rhouma et al. 2019). soil physicochemical properties (ph, total nitrogen (%), available phosphorus (mg.kg-1), silt (%), clay (%), sand (%), ex. ca (cmol.kg-1), ex. mg (cmol.kg-1), ex. na. (cmol.kg-1), ex. k. (cmol.kg-1), organic carbon (%), exchangeable acidity (meq/100 g), ecec (cmol.kg-1), base saturation 4 nova biotechnol chim (2022) 21(1): e1170 2 (%) and electrical conductivity (ec) (ds.m-1) were determined for each samples (rhouma et al. 2019). analysis of water samples nine water samples (1,000 ml) per replicate (3 replicates) were collected from saline (water used in treatment) and freshwater). a total of 27 samples were collected in sterile glass bottles (2,000 ml) and brought to the laboratory. water ph, electrical conductivity, and total dissolved solid (tds was measured using portable ph/ec/tds/temperature combined (hi 991301, hanna instruments ltd., leighton, uk). dissolved oxygen was measured using digital portable analyzer jpb-607a portable dissolved oxygen analyzer (tech instrumentation inc., elizabeth, usa). biological oxygen demand (bod5), total alkalinity, acidity, chloride, calcium, nitrate, sulphate, phosphate, magnesium, sodium and potassium concentration was determined by the conventional method of the association of official analytical chemists (aoac 2005). salinity was determined using digital salt meter, which measures the salinity of seawater in parts per thousand (rhouma et al. 2017). determination of proximate content the determination of ash, lipid, carbohydrate and crude fibre was carried out using the standard methods described by cella and watson (2000) and adeola et al. (2010). caloric value was determined using a bomb calorimeter. physiological parameters electrolyte leakage was calculated using the formula (shi et al. 2006): ec1/ec2. values of fw, tw, and dw were used to calculate lrwc using the formula (eq. 1; kaya et al. 2003): (1) to determine the turgid weight (tw), leaves were soaked in distilled water inside a closed petri dish. leaf samples were weighed periodically after gently wiping the water from the leaf surface with tissue paper until a steady state was achieved. the turgid weight of the leaves was determined by weighing the soaked leaves on a weighing balance and weight recorded (kaya et al. 2003). plant vigor index in each treatment was calculated using the formula (eq. 2; maisuria and patel 2009): vigor index = root length + shoot length × percentage emergence )%( (2) plant salt tolerance index (psti) was calculated using the formula of jaarsma et al. (2013) (eq. 3): (3) statistical analysis all data in the present study were subjected to analysis of variance (anova) using statistical package for social sciences (spss) and data are presented as standard error of mean (± sem) of triplicate experiments. the student’s t-test was used to determine the significant difference between means of the soil and water parameters analyzed. the differences between the means were separated and compared using the duncan’s multiple range tests. however, a probability level of p ≤ 0.05 was considered statistically significant. results and discussion analysis of the saline and garden soils used in this study revealed significant variations in their soil physico-chemical parameters (p ≤ 0.05). significant increase in parameters such as ph (7.75), ec (7.80 ds.m-1) and ex na+ (8.81 cmol.kg-1) was observed in the saline soil while there was a decrease in organic carbon (1.61 %), total nitrogen (0.49 %) and available phosphorus (24.66 mg.kg-1) in saline soil (p ≤ 0.05) (table 2 and 3). this observation is in line with the work of miller and gardiner (2007) who reported an increase in ph and ec in saline soils in new jersey due to salt stress. deleke and akomolafe (2013) also made similar findings as they observed an increase in ph, ec and ex na+ in saline soils and a decrease in organic carbon, organic matter, total nitrogen and phosphorus in salinity influenced soils in nigeria. soil organic 5 nova biotechnol chim (2022) 21(1): e1170 3 carbon content is influenced by two opposing factors: reduced plant inputs and reduced rates of decomposition (garg and manchanda 2008). this might be responsible for the significant decrease in the soil oc, total n and p observed in this work. high concentrations of salts in soil, especially na+ ions drastically affect the basic structure of soil (garg and manchanda 2008). the presence of na+ ions in the cation exchange complex makes the soil compact and subsequently decreases soil porosity and aeration, which hampers plant growth and hinders their productivity (garg and manchanda 2008). the presence of the salts of calcium and magnesium forms a white crust on the soil surface that changes soil water osmotic potential; therefore, plants growing in saline soils face salt-induced physiological drought conditions. salinity impairs plant’s major processes such as photosynthesis, protein and lipid metabolism, nutrient acquisition, and ion homeostasis. indeed, water moves out of the plant due to salt-induced osmotic stress, which makes the plant dehydrated and eventually leads to the death of the plant (evelin et al. 2011). table 2. physicochemical properties of the experimental soils. s/no. parameters soil before treatment with saline water soil after treatment with saline water 1. ph 6.78b 7.75a 2. total nitrogen [%] 2.27a 0.49b 3. available p. [mg.kg-1] 36.31a 24.66b 4. silt [%] 4.00b 5.60a 5. clay [%] 4.20b 12.00a 6. sand [%] 92.04a 82.40b 7. ex. ca [cmol.kg-1] 5.25a 2.97b 8. ex. mg [cmol.kg-1] 4.36a 3.80b 9. ex. na [cmol.kg-1] 0.41b 8.81a 10. ex. k. [cmol.kg-1] 6.98a 1.48b 11. organic carbon (%) 5.61a 1.61b 12. exchangeable acidity (meq/100g) 3.56a 3.20b 13. ecec [cmol.kg-1] 20.56a 20.26b 14. base saturation [%] 82.68b 84.20a 15. ec. (ds.m-1) 0.32b 7.80a * significant at p ≤ 0.05, ex – exchange, ecec – effective cation exchange capacity, ec – electrical conductivity. table 3. water analysis of the experimental irrigation water. s/no. parameters saline water (water used in treatment) fresh water 1. ph 7.70a 6.70b 2. ec [µs.cm-1] 3080.00a 27.70b 3. tds 1021.00a 11.00b 4. acidity [mg.l-1 as caco3] 80.00 b 95.40a 5. alkalinity [mg.l-1 as caco3] 138.00 a 53.20b 6. do [mg.l-1] 6.40b 7.60a 7. bod [mg.l-1] 3.20b 2.80a 7. sulphate [mg.l-1] 102.31a 1.91b 9. phosphate [mg.l-1] 0.09a 0.04b 10. nitrate [mg.l-1] 0.06b 2.82a 11. cl[mg.l-1] 2560.13a 55.23b 12. ca2+ [mg.l-1] 55.71b 106.20a 13. mg2+ [mg.l-1] 120.20b 232.81a 14. na+ [mg.l-1] 1027.00a 0.11b 15. k+ [mg.l-1] 6.42b 8.40a 16. salinity [ppt] 33.21a 0.32b * significant at p ≤ 0.05, ec – electrical conductivity, do – dissolved oxygen, bod – biological oxygen demand, tds – total dissolved solids. 6 nova biotechnol chim (2022) 21(1): e1170 3 proximate analysis of c. maxima and t. occidentalis leaves revealed that fibre, carbohydrate and caloric value were slightly reduced in saline soil treatments while ash, protein and lipids contents were slightly increased (table 4 and 5). amf inoculation of c. maxima and t. occidentalis and poultry manure application had some significant effect on proximate composition of these plant leaves but caloric value which was significantly increased in non-saline soil treatments (p ≤ 0.05) (table 4 and 5). proximate composition of c. maxima and t. occidentalis such as carbohydrate, caloric value and fibre were significantly reduced with salinity, while ash, protein and lipids increased in saline soil treatments compared to non-saline soil treatments. however, inoculation of c. maxima and t. occidentalis with arbuscular mycorrhizal fungi (amf) (r. irregularis and g. geosporum) in conjunction with soil amelioration with poultry manure (pm) increased some proximate composition of c. maxima and t. occidentalis. proximate analysis of c. maxima and t. occidentalis leaves increased dramatically for the plants treated with g. geosporum+manure poultry (ash 18.48 – 17.09 %, respectively; fibre 15.20 – 20.11 %, respectively; protein 8.81 – 8.21 %, respectively; lipid 8.38 – 6.88 %, respectively; cho 49.12 – 47.71 %, respectively; caloric value 297.60 – 281.41 kcal, respectively) and r. irregularis + manure poultry (ash 17.54 – 17.02 %, respectively; fibre 14.67 – 19.82 %, respectively; protein 8.22 – 8.41 %, respectively; lipid 6.94 – 6.66 %, respectively; cho 50.03 – 48.09 %, respectively; caloric value 318.71 – 289.00 kcal, respectively) even in the presence of salinity (table 4 and 5). it can be concluded from the results of this study that c. maxima plants tolerate better the salinity when treated with g. geosporum+manure poultry. we concluded that the addition of r. irregularis in combination with poultry manure to soil optimally improved the studied parameters of t. occidentalis in water stress conditions (table 4 and 5). increase in ash, protein and lipids have also been reported by uddin et al. (2017) in clinacanthus nutans with increasing salinity. the findings in this study agree with the results of ali et al. (2014) on portulaca oleracea, hibiscus sabdariffa and sorghum bicolor, kekere (2014) in a. hypogea, uzun et al. (2013) and kapoor and srivastava (2010) who reported that increasing salinity levels tended to enhance crude protein synthesis. the increase in crude lipid content of c. maxima and t. occidentalis in response to salinity may be because plants have some level of tolerance at these salinity levels or due to accumulation of compatible solutes (uddin et al. 2017). these results agree with those previously reported on p. oleracea by teixeira and carvalho (2009) and oenothera biennis by heuer et al. (2002). they observed increased total fat content in plants exposed to moderate saline environment. table 4. effects of arbuscular mycorrhizal fungi (amf) inoculation on the proximate composition of c. maxima grown in saline soil and ameliorated with poultry manure. treatments ash [%] fibre [%] protein [%] lipid [%] cho [%] caloric value [kcal] smp*16.06 ± 0.66b 16.11 ± 0.38a 8.95 ± 0.21b 6.54 ± 0.15b 52.33 ± 4.55a 314.73 ± 10.51c s+ mp0.00 ± 0.00c 0.00 ± 0.00b 0.00 ± 0.00c 0.00 ± 0.00c 0.00 ± 0.00c 0.00 ± 0.00g s+ m+ p(gg) 18.65 ± 1.24a 16.21 ± 0.33a 10.71 ± 1.61a 8.22 ± 0.25a 46.21 ± 3.42b 242.71 ± 8.41f s+ m+ p(ri) 18.40 ± 0.71a 15.72 ± 0.61a 9.20 ± 0.75a 8.61 ± 0.34a 48.07 ± 3.11b 257.10 ± 8.11e s+ mp+ 19.06 ± 1.62a 15.68 ± 0.46a 11.24 ± 1.22a 8.68 ± 0.29a 45.34 ± 2.05b 239.12 ± 6.34f s+ m+ p+ (gg) 18.48 ± 1.44a 15.20 ± 0.51a 8.81 ± 0.61b 8.38 ± 0.41a 49.12 ± 4.12a 297.60 ± 6.81d s+ m+ p+ (ri) 17.54 ± 1.34a 14.67 ± 0.25a 8.22 ± 0.57b 6.94 ± 0.38b 50.03 ± 4.48a 318.71 ± 9.66c sm+ p(gg) 16.76 ± 0.84b 15.49 ± 0.35a 7.97 ± 0.43b 6.61 ± 0.31b 53.17 ± 4.33a 320.12 ± 10.67c sm+ p(ri) 16.24 ± 0.69b 16.01 ± 0.42a 7.77 ± 0.64b 6.58 ± 0.50b 53.40 ± 4.37a 322.50 ± 10.81c sm+ p+ (gg) 15.45 ± 0.51b 14.81 ± 0.29a 8.96 ± 0.72b 6.62 ± 0.34b 54.16 ± 4.71a 332.13 ± 12.12b sm+ p+ (ri) 16.28 ± 0.75b 14.77 ± 0.32a 8.06 ± 0.76b 6.48 ± 0.34b 54.41 ± 4.21a 351.00 ± 14.32a smp+ 16.79 ± 0.65b 14.58 ± 0.45a 8.09 ± 0.59b 7.92 ± 0.51b 51.02 ± 3.55a 298.30 ± 9.42d *mean of three replicates ± sem. means within of each column followed by different letters are significantly different at p < 0.05 according to duncan’s multiple range test. s(no salinity), m(no mycorrhiza), p(no poultry manure), s+ (plus salinity), m+ (plus mycorrhiza), p+ (plus poultry droppings), (gg) – glomus geosporum, (ri) – rhizophagus irregularis, 0.00 (means the plants were dead). 7 nova biotechnol chim (2022) 21(1): e1170 2 table 5. effect of arbuscular mycorrhizal fungi (amf) inoculation on the proximate composition of t. occidentalis grown in saline soil and ameliorated with poultry manure. treatments ash [%] fibre [%] protein [%] lipid [%] cho [%] caloric value [kcal] smp*17.20 ±1.51b 20.17 ± 2.78a 8.74 ± 0.15a 6.81 ± 0.57a 47.08 ± 3.58a 298.16 ± 6.45b s+ mp21.43 ± 1.91a 23.11 ± 2.88a 8.67 ± 0.31a 8.27 ± 0.66a 38.52 ± 2.94b 197.14 ± 4.88f s+ m+ p(gg) 18.96 ± 0.52b 21.22 ± 1.94a 8.21 ± 0.25a 7.08 ± 0.4a 45.45 ± 3.42a 246.30 ± 6.12d s+ m+ p(ri) 17.47 ± 0.78b 21.43 ± 1.81a 8.87 ± 0.38a 6.71 ± 0.49a 45.52 ± 3.64a 275.28 ± 5.14c s+ mp+ 22.00 ± 1.24a 21.77 ± 1.57a 8.77 ± 0.42a 8.25 ± 0.67a 39.21 ± 3.11b 202.11 ± 3.88e s+ m+ p+ (gg) 17.09 ± 0.64b 20.11 ± 1.45a 8.21 ± 0.33a 6.88 ± 0.35a 47.71 ± 3.31a 281.41 ± 5.74c s+ m+ p+ (ri) 17.02 ± 0.45b 19.82 ± 1.39a 8.41 ± 0.47a 6.66 ± 0.42a 48.09 ± 4.01a 289.00 ± 6.14c sm+ p(gg) 16.42 ± 0.64b 18.76 ± 1.43a 7.91 ± 0.51a 6.21 ± 0.29a 50.70 ± 3.69a 301.10 ± 7.22b sm+ p(ri) 16.53 ± 0.51b 18.64 ± 0.84a 7.61 ± 0.39a 6.11 ± 0.43a 51.11 ± 4.12a 307.42 ± 7.31a sm+ p+ (gg) 17.06 ± 0.48b 18.65 ± 1.44a 7.66 ± 0.45a 6.06 ± 0.28a 51.57 ± 4.24a 309.40 ± 6.48a sm+ p+ (ri) 16.22 ± 0.33b 18.70 ± 0.87a 7.25 ± 0.42a 6.21 ± 0.57a 51.62 ± 4.1a 311.10 ± 7.24a smp+ 17.03 ± 0.66b 19.76 ±1.46a 7.84 ± 0.37a 5.29 ± 0.61a 50.08 ± 3.82a 299.90 ± 6.75b *mean of three replicates ± sem. ameans within of each column followed by different letters are significantly different at p < 0.05 according to duncan’s multiple range test. s(no salinity), m(no mycorrhiza), p(no poultry manure), s+ (plus salinity), m+ (plus mycorrhiza), p+ (plus poultry droppings), (gg) – glomus geosporum, (ri) – rhizophagus irregularis, 0.00 (means the plants were dead). measured physiological parameters of c. maxima and t. occidentalis such as leaf turgid weight (ltw), leaf relative water content (lrwc), salt tolerance index (sti) and vigor index (vi) were significantly reduced in saline soil treatments when compared to the control, while electrolyte leakage increased in saline soil treatments (p ≤ 0.05) (table 6 and 7). amelioration of the saline soil with poultry manure alone also enhanced the physiological parameters of c. maxima and t. occidentalis. inoculation with amf alone or together with poultry manure amelioration significantly increased performance of the physiological parameters in the two test plants both in saline and non-saline soil treatments during the first and second cropping seasons (p ≤ 0.05) (table 6 and 7). ltw, lrwc, sti and vi were all significantly higher in amf inoculated and poultry manure ameliorated c. maxima plants grown in non-saline soil (p ≤ 0.05) (table 6 and 7). table 6. effects of arbuscular mycorrhizal fungi (amf) on the physiological parameters of c. maxima grown in saline soil ameliorated with poultry manure. treatments leaf turgid weight (ltw) [g] leaf relative water content (lrwc) [%] salt tolerance index [sti] vigour index (vi) [%] electrolyte leakage (el) [ds.m-1] smp*0.67 ± 0.06b 38.00 ± 2.51c 1.00 ± 0.01a 7481.00 ± 7.04h 0.81 ± 0.24c s+ mp0.00 ± 0.00d 0.00 ± 0.00d 0.00 ± 0.00d 0.00 ± 0.00l 0.00 ± 0.00d s+ m+ p(gg) 0.26 ± 0.11c 36.00 ± 1.24c 0.36 ± 0.08c 1,303.00 ± 6.06i 2.22 ± 0.67a s+ m+ p(ri) 0.23 ± 0.20c 36.36 ± 1.66c 0.29 ± 0.06c 956.00 ± 8.13j 2.31 ± 0.38a s+ mp+ 0.21 ± 0.09c 30.00 ± 1.02c 0.28 ± 0.12c 856.00 ± 4.90k 2.52 ± 0.44a s+ m+ p+ (gg) 0.68 ± 0.12 b 44.78 ± 2.42b 0.71 ± 0.33b 8,037.00 ± 9.02f 1.66 ± 0.14b s+ m+ p+ (ri) 0.69 ± 0.34 b 42.65 ± 1.57b 0.71 ± 0.24b 7,897.00 ± 8.37g 1.51 ± 0.16b sm+ p(gg) 0.70 ± 0.30b 44.93 ± 3.10b 1.04 ± 0.67a 9,465.00 ± 9.53c 0.72 ± 0.20c sm+ p(ri) 0.69 ± 0.27b 45.59 ± 1.67b 1.03 ± 0.75a 8,378.00 ± 8.86d 0.91 ± 0.48c sm+ p+ (gg) 0.74 ± 0.61b 45.21 ± 2.01b 1.06 ± 0.54a 10,088.00 ± 10.75b 0.85 ± 0.44c sm+ p+ (ri) 0.93 ± 0.84a 51.09 ± 3.44a 1.14 ± 0.68a 10,583.00 ± 12.15a 0.67 ± 0.28c smp+ 0.68 ± 0.22b 44.78 ± 1.97b 1.01 ± 0.24a 8,099.00 ± 7.14e 0.83 ± 0.41c *mean of three replicates ± sem. ameans within of each column followed by different letters are significantly different at p < 0.05 according to duncan’s multiple range test. s(no salinity), m(no mycorrhiza), p(no poultry manure), s+ (plus salinity), m+ (plus mycorrhiza), p+ (plus poultry droppings), (gg) – glomus geosporum, (ri) – rhizophagus irregularis, 0.00 (means the plants were dead). 8 nova biotechnol chim (2022) 21(1): e1170 2 table 7. effects of arbuscular mycorrhizal fungi (amf) on the physiological parameters of t. occidentalis grown in saline soil ameliorated with poultry manure. treatments leaf turgid weight (ltw) [g] leaf relative water content (lrwc) [%] salt tolerance index [sti] vigour index (vi) [%] electrolyte leakage (el) [ds.m-1] smp*0.89 ± 0.51a 56.58 ± 3.11b 1.00 ± 0.01c 11,984.00 ±3.68f 0.51 ± 0.24c s+ mp0.51 ± 0.20c 37.78 ± 1.05d 0.28 ± 0.08g 662.00 ± 3.80k 2.06 ± 0.97a s+ m+ p(gg) 0.66 ± 0.32b 49.09 ± 1.57c 0.48 ± 0.10f 8,784.00 ± 2.09i 1.91 ± 0.11b s+ m+ p(ri) 0.71 ± 0.55b 47.37 ± 1.22c 0.50 ± 0.25f 9,265.00 ± 6.00h 1.76 ± 0.21b s+ mp+ 0.63 ± 0.19b 52.73 ± 1.67b 0.61 ± 0.33e 8,265.00 ± 4.33j 2.01 ± 0.40a s+ m+ p+ (gg) 0.83 ± 0.22a 57.75 ± 2.15b 0.88 ± 0.51d 10,602.00 ± 7.09g 1.27 ± 0.22b s+ m+ p+ (ri) 0.85 ± 0.46a 60.27± 1.97a 1.02 ± 0.66c 12,169.00 ± 2.64e 1.14 ± 0.31b sm+ p(gg) 0.88 ± 0.75a 63.38 ± 2.28a 1.21 ± 0.58b 13,248.00 ± 4.64h 0.47 ± 0.26c sm+ p(ri) 0.91 ± 0.69a 66.67± 2.11a 1.23 ± 0.64b 13,665.00 ± 1.95c 0.49 ± 0.34c sm+ p+ (gg) 0.95 ± 0.56a 68.49 ± 3.15a 1.37 ± 0.69a 13,901.00 ± 2.84b 0.52 ± 0.58c sm+ p+ (ri) 0.99 ± 0.87a 70.67 ± 3.47a 1.40 ± 0.81a 14,183.00 ± 8.28a 0.48 ± 0.61c smp+ 0.89 ± 0.61a 57.89 ± 2.30b 1.07 ± 0.55c 12,201.00 ± 7.38l 0.53 ± 0.42c *mean of three replicates ± sem. ameans within of each column followed by different letters are significantly different at p < 0.05 according to duncan’s multiple range test. s(no salinity), m(no mycorrhiza), p(no poultry manure), s+ (plus salinity), m+ (plus mycorrhiza), p+ (plus poultry droppings), (gg) – glomus geosporum, (ri) – rhizophagus irregularis, 0.00 (means the plants were dead). el was however, highest in sole poultry manure ameliorated saline soil treatments. a similar trend was observed in t. occidentalis, except for el which was highest in pure saline soil non-fertilized with poultry manure and uninoculated with amf in the first cropping (table 6 and 7). the symbiotic association of g. geosporum+manure poultry applied on c. maxima and t. occidentalis plants allows better leaf turgid weight (0.68 – 0.83 g, respectively), leaf relative water content (44.78 – 57.75 %, respectively), salt tolerance index (0.71 – 0.88, respectively), vigour index (8,037 – 10,602 %, respectively), and electrolyte leakage (1.66 – 1.27 ds.m-1, respectively) underwater stress conditions; whose t. occidentalis plants are more tolerant to water salinity. also, the highest value of leaf turgid weight (0.69 – 0.85 g, respectively), leaf relative water content (42.65 – 60.27 %, respectively), salt tolerance index (0.71 – 1.02, respectively), vigour index (7,897 – 12,169 %, respectively), and electrolyte leakage (1.51 – 1.14 ds.m-1, respectively) was obtained when the c. maxima and t. occidentalis plants are treated with r. irregularis+manure poultry under water stress conditions; whose t. occidentalis plants are more tolerant to water salinity (table 6 and 7). foliar na+ accumulation in of c. maxima and t. occidentalis had corresponding significant reduction on some physiological parameters such as leaf turgid weight (ltw), leaf relative water content (lrwc), salt tolerance index (sti), vigour index (vi) and electrolyte leakage (el) of c. maxima and t. occidentalis (p ≤ 0.05) (fig. 2 and 3). amelioration with poultry manure showed some improvements in these physiological parameters in the two test plants. inoculation of c. maxima and t. occidentalis with amf in non-saline soil treatments showed significant increase in physiological parameters when compared to the control and saline treatments (p ≤ 0.05) (fig. 2 and 3). ltw, lrwc, sti, vi and el were improved when the plants were treated with g. geosporum+manure poultry and r. irregularis+manure poultry underwater stress conditions. we can conclude that these treatments enhanced the studied parameters of t. occidentalis in water stress conditions (fig. 2 and 3). physiological parameters of c. maxima and t. occidentalis such as leaf turgid weight (ltw), leaf relative water content (lrwc), vigour index (vi) and salt tolerance index (sti) were significantly reduced by salinity, while electrolyte leakage (el) was higher in saline soil treatments than non-saline soil treatments. however, inoculation of c. maxima and t. occidentalis with amf (r. irregularis and g. geosporum) in conjunction with poultry manure amendment significantly increased their leaf turgid weight 9 nova biotechnol chim (2022) 21(1): e1170 2 (ltw), leaf relative water content (lrwc), vigor index (vi) and salt tolerance index (sti) in both saline and non-saline soil treatments above single treatment with mycorrhizal species and poultry manure (p ≤ 0.05). however, electrolyte leakage (el) reduced with mycorrhizal inoculation. fig. 2. comparative assessment of the influence of foliar na+ accumulation on leaf turgid weight, leaf relative water content, salt tolerance index, vigour index and electrolyte leakage of c. maxima. 10 nova biotechnol chim (2022) 21(1): e1170 2 fig. 3. comparative assessment of the influence of foliar na+ accumulation on leaf turgid weight, leaf relative water content, salt tolerance index, vigour index and electrolyte leakage of t. occidentalis. the increasing of the studied parameters in the cucurbit plants with application of arbuscular mycorrhizal fungi and poultry manure could be attributed to two processes: (i) through increased 11 nova biotechnol chim (2022) 21(1): e1170 2 nutrient transport found in the poultry manure through the arbuscular mycorrhizal fungi and (ii) direct connection between cucurbits plant and mycorrhizal hyphal network. arbuscular mycorrhizal fungi and poultry manure application are widely claimed to be able to aid plants under soil salinity conditions. cyril et al. (2014), and adebisi and adewole (2019) showed that organic manures particularly poultry manure, mixed with arbuscular mycorrhizal fungi had positive effects in increasing red amaranth yield and improving crop quality under saline conditions. abusuwar (2018) reported that the arbuscular mycorrhizal fungi coupled with poultry manure enhanced leaf area, number of leaves per plant, plant height, fresh and dry biomass, yield and nutritive value of forage crops grown in saline soils and irrigated with saline water. mickan et al. (2016) poultry manure applied to the agricultural soils with the presence of am fungi stimulated growth of extra-radical hyphae in soil and increased mycorrhizal colonization of roots. based on the understanding of these interactions, it has been claimed that am fungi can be more important to plant growth and yield than poultry manure (mickan et al. 2016; solaiman et al. 2019, 2020; zhang et al. 2020). over the last couple of decades, the universal symbiosis between arbuscular mycorrhizal fungi and cucurbits is such an old tie that, perhaps, enabled the establishment of plants in land (rouphael et al. 2015; chen et al. 2017) by boosting photosynthesis, plant growth, nutrient acquisition and decreasing membrane leakage and reactive oxygen species under condition of salinity stress (cavagnaro et al. 2015; liu et al. 2016; sofy et al. 2021a). this symbiosis had been reported 400 million years ago (selosse et al. 2015). several research studies have reported the efficiency of am fungi to impart growth and yield enhancement in plants under salinity stress (abdel latef and chaoxing 2014; talaat and shawky 2014). wang et al. (2018) have noted considerable improvement in fresh and dry biomass, and n concentration of root and shoot due to mycorrhizal inoculation under saline conditions. chen et al. (2017) revealed that the stem diameter, plant height, dry weight, root to shoot ratio of cucumber seedlings inoculated with glomus sp., and rhizophagus sp. were improved greatly compared with the non-inoculated control. the same authors showed that glomus sp., and rhizophagus sp. increase the nutrient concentration, net photosynthetic rate, chlorophyll content, root activity, light saturated rate of the co2 assimilation, maximum carboxylation rate and maximum ribulose-1,5-bis-phosphate regeneration rate. moreover, arbuscular mycorrhizal fungi can significantly improve plant nutrient uptake and resistance to several abiotic stress factors particularity salinity stress (sun et al. 2018; begum et al. 2019). liu et al. (2016) documented that the am fungi inoculation could effectively enhance the cucumber growth and other cucurbit crops, which is closely associated with the secondary metabolism in plants. notably, yang et al. (2014) and he et al. (2017) showed a positive stimulatory effect of glomus spp., and rhizophagus spp. on peanut and tomato in terms of photosynthetic characteristics, growth and hormone status. yadav et al. (2013) found that the inoculation of gloriosa superba with glomus sp. can interact synergistically and maximize benefits, resulting in root length, higher leaf area and colchicine content. it is widely believed that arbuscular mycorrhizal fungi have been considered as an alternative to inorganic fertilizers in the near future (ortas 2012), which is probably why am fungi enhanced plant tolerance to abiotic factors (plassard and dell 2010). qiu et al. (2019) documented that the soil application of arbuscular mycorrhizal fungi could improve the chemical and biological properties of soil and enhance their nutrient levels and enzymatic activities. a prominent role of such am fungi application is to transfer nutrients, (organic carbon in the form of sugars and lipids) (jiang et al. 2017; luginbuehl et al. 2017). amiri et al. (2017) revealed that am fungi-pelargonium graveolens symbiosis increased the concentrations of n, p, and fe under drought stress. gomez-bellot et al. (2015) reported the levels of p, ca, and k in euonymus japonica have been enhanced under salinity stress due to instant am fungi attachment. in addition, am fungi application improved p and n contents in plant tissues of chrysanthemum morifolium (wang et al. 2018) and increased seedling biomass by enhancing intercellular co2, p, and n contents and water content in leymus chinensis (jixiang et al. 2017). furthermore, hashem et al. (2018) documented that the synthesis of jasmonic acid, salicylic acid, and several important inorganic nutrients and the total concentrations of p, ca2+, n, 12 nova biotechnol chim (2022) 21(1): e1170 3 mg2+, and k+ were higher in the arbuscular mycorrhizal fungi-treated cucumis sativus plants compared with those in the un-inoculated plants under salt stress conditions. ali and hassan (2014) reported that under salt stress because of inadequate water uptake, rwc was significantly decreased in relation to salinity in chamomile herb. shou-jun et al. (2014) also reported that under no saline condition, leaf relative turgidities in nonmycorrhizal and mycorrhizal plants remained at comparatively steady-state level from 53.75 % to 54.56 % throughout the experiment. mycorrhizal inoculation led to relatively higher leaf turgidity compared to non-mycorrhizal plants in this study. the phenomenon is ascribed to improved hydraulic conductivity of plants with a longer root and an altered root system morphology induced by am fungi (shou-jun et al. 2014). sheng et al. (2008) reported that plants inoculated with amf maintain relatively higher water content compared with uninoculated plants. inoculation with amf often results in increased nutrient uptake, accumulation of an osmo-regulator, an increase in photosynthetic rate and water use efficiency, suggesting that salt stress alleviation by amf results from a combination of nutritional, biochemical and physiological effects (evelin et al. 2009). sofy et al. (2021a) proved that the combination of arbuscular mycorrhizal and organic amendment is the most effective in decreasing the damaging impacts of salt on spinach plants by increasing the up-regulation of antioxidants, morphological and physiological parameters (shoot and root length, fresh and dry biomass, membrane stability index, relative water content, mineral contents, chlorophyll content, total soluble protein content and endogenous phytohormones (auxin, abscisic acid, gibberellins, salicylic acid and jasmonic acid)) and decreasing membrane leakage and reactive oxygen species. mumtaz et al. (2013) reported that electrolyte leakage was enhanced with increasing salinity levels as compared to the control in salt sensitive cucumber plants as compared to the salt tolerant cultivar. this observation has been reported by other investigators in cucumber (kaya et al. 2001), rice (lutts et al. 1996), tomato (atilla 2014) and sugar beet (ghoulam et al. 2002). agha et al. (2021) and sofy et al. (2021b) documented that the bacteria combination was the most efficient in reducing the harmful effects of salt on soybean and pea plants by boosting antioxidant upregulation and lowering membrane leakage and reactive oxygen species. a major effect of environmental stress (i.e., salt, drought) on plant is membrane modification, which results in cell membrane perturbed function or total dysfunction. changes in membrane leakage and injury can be measured by the extent of el (electrolyte leakage) in tissues (atilla 2014). the positive effects of am fungi inoculation may result in improving integrity, vigour and stability of the membrane since the membrane permeability has been found to be reduced by am fungi inoculation. plants inoculated with amf have been shown to maintain a lower electrolyte concentration than the non-mycorrhizal ones and hence maintain membrane stability (garg and manchanda 2008; ali and hassan 2014). poultry manure has been widely used as fertilizers for centuries. this manure contains not only the basic nutrients required by crops, but also trace elements. it is rich in mineral elements, essential nutrients n, p, and k, and other nutrients that can stimulate microbial activity and healthy plants, ameliorate seed germination, increase vegetative traits, reduce the negative impact of salinity, increase the percent root colonization of arbuscular mycorrhizal fungi, improve the physical and chemical properties of the soil (structure, texture, porosity, etc.), maintain the balance of soil nutrient, improve nutrient absorption, increase root vitality, increase fertilizer retention, enhance yields, and participate in the addition of organic matter to organically-deficient soils (mufwanzala and dikinya 2010; revell et al. 2012; awad 2016; pandian et al. 2016; sikder et al. 2019; sistani et al. 2019; solaiman et al. 2020; zhang et al. 2020; sallam et al. 2021). hirzel et al. (2018) showed that the highest values of available p and exchangeable k, s, ca and mg were obtained using poultry manure in saline soil, whereas ph and salinity (electrical conductivity) reported the lowest values. adeleye et al. (2010) documented that poultry manure application enhanced soil physicochemical properties by decreasing soil bulk density and temperature, and increasing exchangeable ca, mg, k, total porosity, soil moisture retention capacity, total n, soil organic matter, available p 13 nova biotechnol chim (2022) 21(1): e1170 2 and lowered exchange acidity under salinity conditions. conclusion soil salinity is one of the most severe abiotic stresses affecting plant establishment, growth and production worldwide as observed in this study. results of this study revealed that salt stress negatively affected physicochemical properties of the saline soil when compared to the garden soil, thus resulting in negative effects on growth parameters, proximate composition and physiological parameters of c. maxima and t. occidentalis. the effects of mycorrhizal symbiotic association on c. maxima and t. occidentalis showed improvements on the growth of the test plants. using different mechanisms c. maxima and t. occidentalis by itself or in association with arbuscular mycorrhizal fungi and poultry manure can tolerate or survive soil salinity. however, in the presence of the fungi, plant ability to resist the stress increases as a result of morphological and physiological changes and improved vigour, extensive network of the mycorrhizal plant roots and enhanced nutrient uptake are all among the processes that made the mycorrhizal inoculated plants to survive under salt stress. t. occidentalis showed better salt tolerance indices on individual parameters and overall salt tolerance index. given the importance of these strategies, arbuscular mycorrhizal fungi/poultry manure application has important implications under pot experiments. hence, field and greenhouse trials aimed at understanding the effectiveness, efficiency and durability of these strategies are suggested for future studies. conflict of interest the authors declare that they have no conflict of interest. references abdel latef aa, 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institute of science and technology, ulsan 44919, republic of korea 2department of chemistry, m. r. degree college, fort, andhra pradesh 535002, india 3department of chemistry, s.v.r.m college nagaram, guntur, andhra pradesh 522268, india 4chemistry of natural and microbial products department, pharmaceutical industries division, national research centre, dokki, giza 12622, egypt  corresponding author: bodduramakrishna87@gmail.com article info article history: received: 1st august 2021 accepted: 8th november 2021 keywords: lichens natural products secondary metabolites abstract lichens have attracted considerable interest since ancient time due to their medicinal properties. lichen produce a variety of orcinol-based compounds such as xanthones, anthraquinones, dibenzofurans, depsides, and depsidones. several related compounds have shown potent bioactivities as antiviral, antioxidant, anti-herbivore, insecticidal, antifungal, and anticancer. lichens have been employed as traditional medicines, and these are continuing to be of great interest for their biotechnological potential. the purpose of this review was to systematically evaluate the literature on the orcinol based biologically active secondary metabolites of lichen. introduction lichens are extraordinary self-supporting symbiotic microorganisms, formed by both alga (cyanobacteria) and fungi. this association is very useful for both organisms. the alga carries chlorophyll and is called photobiont. the fungi build the structure of the lichen thalli, the partner may be referred to as the mycobiont (de priest 2004). alga produces primary metabolites by photosynthesis (sugars, amino acids, carotenoids, and starch) for fungus growth and, which in turn gives a surface to the algae for the protection against dehydration (podterob 2008). the fungus and the alga are in a mutualistic relation and they are capable of dealing with ecological conditions, that neither of them would be able to survive on its own (margulis and barreno 2003; bates et al. 2011). some lichenized fungi synthesized secondary metabolites without photobiont under certain conditions, for example the lichen lecanora dispersa contains 2,7-dichlorolichexanthone as the main secondary metabolite, but cultured spore isolates, growing in absence of the alga, produced from lichen genus pannarin (leuckert et al. 1990). a lichen thalli consist of cortex layers, algal layer and medulla. naturally, lichens grow in a very slow and radial manner that is measured in millimeters per year. lichen produces different secondary metabolites (sms), and most of them occur exclusively in this symbiotic organism (boustie and grube 2005; jayanthi et al. 2012; xu et al. 2016). mailto:bodduramakrishna87@gmail.com nova biotechnol chim (2022) 21(1): e1075 2 during the complex metabolic interaction between mycobiont and photobiont, the mycobiont produce important secondary metabolites and accumulate as extracellular tiny crystals on the external sides of the hyphae. lichen-derived secondary metabolites are small and complex molecules, which represent about 20 % of lichens total dry weight (muggia et al. 2009). they act as protectors of the thalli against attacks by pathogens, herbivores, competitors, and different external abiotic conditions including high uv irradiation. approximately 1,050 lichen secondary metabolites have been extracted and identified to date. most well-known lichen substances are members of phenolic compounds such as dibenzofurans, anthraquinones, depsides, depsidones, depsidones, triterpenes, gamma lactones, and pulvinic acid derivatives. lichens synthesized sms, mainly acetylpolymalonate pathway (app), shikimic acid pathway (sap) and mevalonic acid pathway (map) (culberson and armaleo 1992; çobanoğlu et al. 2016). the polyketide biosynthetic pathway seems to be in charge of majority of the phenolic lichen compounds, while pulvinic acid derivatives derived from shikimic pathway and the abundance of di and triterpenoids, carotenoids, steroids found in lichens are synthesized via the mevalonate pathway (stocker-wörgötter 2008). on the other hand, secondary metabolites originated from the fungal partner of the lichen, are placed on the surface of the fungal hyphae. most of these fungal secondary metabolites are phenolics, crystalline in nature and soluble in organic solvents. however, the carbon is essential for lichen secondary substances biosynthesis and is obtained by the algal partner during photosynthesis. the carbohydrates involved in this process depend mainly on the algae itself and are mostly glucose and sugar alcohols (polyols) (el-garawani et al. 2020). orcinol based lichen secondary metabolites orcinol and its derivatives have been considered the most common mono-hydric phenolic compounds found in lichens (stepanenko et al. 2002; férnandez-morano et al. 2015; moreira et al. 2015). as shown in fig. 1, the major orcinol based compounds of lichens are produced by the polyketide route. in this pathway, two coenzymes such as acetyl-coa and malonyl-coa are utilized in lichen substances biosynthesis. particularly, orcinol-based secondary metabolites produced by orsellinate type of cyclization. orsellinic acid and its homologues are the most existing mononuclear structural units of polyketide-related lichen substances. orcinol type of secondary metabolites (orcinol and orsenillic acid based derivatives, e.g. lecanoric acid, montagnetol, trivaricacid, gyrophoric acid, evernic acid, methyl orsenillate, and erythrin) (subba rao and seshadri 1941; boustie and grube 2005; thadhani et al. 2011). β-orcinol type of secondary metabolites (β-orcinol and β-orsenillic acid based derivatives, (e.g. diffractic acid, pannarin, stictic acid, atranorin and vicanicin acid (kathirgamanathar et al. 2004; papadopoulou et al. 2007). fig. 1. biosynthesis of orcinol based lichen secondary metabolites. nova biotechnol chim (2022) 21(1): e1075 5 depsides depsides are phenolic compounds, constructed through intermolecular esterification of two or more orsenillic acid units. for example, the carboxylic acids of one unit are joined to the hydroxyl para to the carboxylic acid of the second unit, such esterification leads to para-depside. if the esterification occurs through meta hydroxyl with respect to the carboxylic acid called meta-depside (seshadri 1944; elix and wardlaw 1986). some of the important examples of this class are lecanoric acid, gyrophoricacid, erythrin, etc. depsidones depsidones are the important class of oxygenated heterocyclic compounds derived from lichen species. depsidones consist of both ester and ether linkage synthesized from the depsides. the depsidones biosynthesis involves oxidative coupling of depsides, which are normally biosynthesized from the condensation of orsellinic acid and orcinol derivatives. however, depsidones biosynthesis may actually operate through a depside intermediate pathway (hirayama et al. 1974; llah et al. 1993). some of the important examples of this class are diploicin, psoromic acid, virensic acid, and norstictic acid. dibenzofurans dibenzofurans are essentially unique to lichens, produced via the polyketide pathway. dibenzofurans are formed by carbon-carbon coupling and cyclodehydration of two phenolic units (orcinol and orsenillic acid derivatives). notable examples of this class are didymic acid, pannaric acid, schizopeltic acid, subbidymic acid, and usnic acid (millot et al. 2016). xanthones lichens produces poly-substituted aromatic xanthones, formed through internal cyclization of a single folded polyketide chain. majority of the lichen xanthones are synthesized via folding of a polyketide intermediate, which results in formation of structures having a methyl group in position 8. both, aldol condensation and claisen-type cyclization yield a benzophenone intermediate that might then dehydrate to form the central pyrone core. two different series of xanthones are resulting according to this folding pattern. this biosynthetic scheme gives rise to the common oxygen substitution pattern of lichexanthone and norlichexanthone (rezanka et al. 2003; masters and bräse 2012; lepogam and boustie 2016). some of the important examples of this class are lichexanthone, nor lichexanthone and arthothelin. biphenyls in lichens, biphenyls form via phenolic couplings of two methyl pholoroacetate to phoneunits, followed by o-methylation of hydroxyl groups. since the mechanism for carbon bond formation between two mono-aromatic units is common in lichens, as exemplified in the usnic acids, dibenzofurans, and depsidones formation. it is interesting to note that contortin is the only lichen biphenyl known so far. another compound also formed from two mono aromatic units bound by a carbon-carbon linkage is the diphenyl methane, bis(2,4-dihydroxy-6-n-propylphenyl) methane, which are found in protousnea sp., eg. contortin (rezanka et al. 2003). biological activity of orcinol based lichen secondary metabolites in nature, lichen fungi grow under the most extremely different ecological conditions. lichenized fungi produce variety of low molecular weight orcinol based secondary metabolites possess several biological activities, including antibacterial, anti-fungal, anti-oxidant, anti-diabetic, anti-cancer, and anti-inflammatory activities (lawrey 1986; boustie and grube 2005; shukla et al. 2010; shrestha and clair 2013). however, lichens are pharmaceutically unexplored secondary metabolites. extracts and isolated compounds from different lichen species antimicrobial activities. from literature surveys, it was found that lichen genus such as usnea, parmelia, parmotrema, cetraria, pseudevernia and hypogymnia showed potent antimicrobial and antifungal activities (türk et al. 2006; kamal et al. 2015; özyiğitoğlu et al. 3 nova biotechnol chim (2022) 21(1): e1075 2 2017). the major metabolites gyrophoric acid (1), stenosporic acid (2) isolated from the lichen, xanthoparmelia pokornyi showed antimicrobial activity towards some known food borne bacteria and fungi. these acid derivatives showed significant anti-microbial activity again sleight organisms (candan et al. 2006). methyl-β-orcinol carboxylate is an orcinol derivative isolated from the lichen, everniastrum irrhatum, tested against polyene and azole-resistant strains of candida albicans and capable of inhibiting drug-resistant strains in a dose dependant manner (candan et al. 2006). new dibenzofuran derivatives (3 – 5) obtained from the cladonia incrassate showed anti-bacterial activity against s. aureus organism. the major metabolites, (-)usnic acids (3), didymic acid (4) and condidymic acid (5) (fig. 2), were found to be potent molecules (mic : 7.5 µg.ml-1). phenonip was used as a positive control (ic50: 150 µg.ml-1) in this assay (dieu et al. 2014). fig. 2. structures of 1-5. hirtusneanoside a (6) was first extracted from the usnea hirta by rezanka and sigler (2007) and found to be an l-rhamnose-o-deoxyglycoside of an unsymmetrical dimeric tetra-hydro xanthone. it is potent when tested against staphylococcus aureus and bacillus subtilis (rezanka and sigler 2007). depside anziaic acid (7) was discovered from lichen (hypotrachyna sp.) as an inhibitor for both yersinia pestis and escherichia coli topoisomerase i and it was also found to act as an inhibitor of human topoisomerase ii (with little effect on human topoisomerase i), an important enzyme in cancer processes (lin et al. 2013). some lichen compounds such as (+) usnic acid (8), vicanicin (9), and diffractic acid (10) were identified as anticancer molecules (fig. 3). usnic acid, a di-benzo furan derivative, isolated from cladonia lepidophora lichen species. it is one of the well-studied lichen secondary metabolite, showed potent anti-cancer activity against hct116 and hela cancer cell lines with ic50 values of 17.7 µm and 23.7 µm respectively, and was found to be more active than the standard etoposide (ic50 = 40.3 µm). vicanicin (9) showed moderate anticancer activities against hct-116, hela and mcf7 cell lines (cocchietto et al. 2002). evernic acid (11) and physodic acid (12) were isolated from the acetone extract of evernia prunastri and pseudevernia furfuracea showed cytotoxicity against femx (human melanoma) and ls174 (human colon carcinoma) cell lines. particularly, physodic acid (12) exhibited the better cytotoxic activity (ic50 values of 19.52 for fem xcell line and 17.89 µg.ml-1 for ls 174) (kosanić et al. 2013). fig. 3. structures of 6-12. a new di-phenyl ether (13) and secalonic acid d (14) were isolated from the lichen, diploicia canescens and evaluated for their anti-cancer activity against the b16 murine melanoma cells. the di-phenyl ether (ic50 = 0.25 µm) and secalonic acid (ic50 = 0.28 µm) showed anti-cancer activity similar to standard etoposide (ic50 0.28 µm) against b16 cell line (millot et al. 2009). (-)usnic acid (15), a dibenzofuran derivative 4 nova biotechnol chim (2022) 21(1): e1075 5 isolated from different lichens genera such as cladonia, usnea, hypotrachyna, ramalina, evernia, lecanora, parmelia and most extensively studied lichen compound in search of anticancer agents (lumbsch et al. 1995; cocchietto et al. 2002; cansaran-duman et al. 2008). it has been shown moderate to potent proliferative activities against multiple cell lines, such as l-929 mouse fibroblast cells, k-562 human leukemia cells, hela human cervix carcinoma, femx human melanoma, ls174 human colon carcinoma 37 and uacc-62 human melanoma cells (schinkovitz et al. 2014). (-)usnic acid and m-scrobiculin were extracted from the lichen lobaria scrobiculata and exhibited cytotoxicity against hl-60 cells. both the isolated compounds showed ic50 values of 7.6 and 1.7 µm for (15 and 16 in fig. 4). doxorubicin was positive control in this assay (ic50 = 0.04µm). fig. 4. structures of 13-16. anti-oxidants inhibit undesirable oxidation processes by reacting with free radicals (reactive oxygen species) and their ability to protect the body from damage caused by oxidative stress. most of the secondary metabolites have been identified as phenolic compounds in lichens, which are strong antioxidants. some orcinol based secondary metabolites such aslobariellin and methyl haematommate isolated from l. pallida and s. strictum var. compressum exhibited promising antioxidants, able to prevent skin and neurodegenerative damage caused by oxidative stress. depsidones such as norstictic acid (17), fumarprotocetraric acid (18) and methyl haematommate (19) isolated from the lichen usnea articulata showed better superoxide anion scavenging activity with ic50 566 and 580 µm, respectively, than standard quercetin (ic50 = 754 µm) (lohézic-le dévéhat et al. 2007). orsellinic acid (20) and methyl orsellinate (21) were isolated from parmotrema stuppeum and heterodermia obscurata together with methyl-β-orcinol carboxylate (22). significant activity was observed for both the compound in the β-carotene-linoleate model system and in the nor assay (jayaprakasha and rao 2000; thadhani et al. 2011). the paradepsides lecanoric acid (23), erythrin (24) and the meta-depside sekikaic acid (25), along with the depsidone lobaric acid (26) showed exceptionally potent radical scavenging activity in the sor assay (fig. 5). interestingly, the ic50 values of the sekikaic acid (81.9 µm) lecanoric acid (91.4 µm) and lobaric acid (97.9 µm) were found lower than standard propylgallate standard (106 µm) (fig. 5). fig. 5. structures of 17-26. taborga et al. (2016) reported the new prenylated orcinol derivatives (27-29) from the direct reaction between orcinol and geraniol in the presence of bf3oet as catalyst. the cytotoxic activity of synthesized compounds was in vitro investigated against various cancer cell lines including (ht-29, pc-3, mdamb231, du-145). all the tested compounds were found to exhibit anti-cancer activity. orsellinates were synthesized by alcoholysis of lecanoric acid, a natural product isolated from the lichen parmotrema tinctorum. increasing the aliphatic alkyl chain at the ester functionality of orsellinic acid causes enhancement nova biotechnol chim (2022) 21(1): e1075 2 in the cytotoxic activity. the ethyl, propyl, butyl and pentanyl orsellinates (30 – 33) showed lc50 values range from 495 – 31 µm against brine shrimp (artemia salina) (gomesa et al. 2006). among tested ones, pentanyl orsellinate (33) possess potent inhibitory activity, whereas standard podophyllotoxin showed cytotoxicity15 µm. lichen genus parmelia is a rich source for depsides (aravind et al. 2014). atranorin (34) and diffractaic acid (35) isolated from the parmelia nepalensis and parmelia tinctorum, showed highly potent inhibitory activity against leukotriene b4 biosynthesis by a non-redox mechanism with ic50 values 6 and 8 µm respectively (fig. 6). nordihydroguaiaretic acid and anthralin were used as standard inhibitors (ic50 = 0.4 and 37 µm respectively) (kumar and müller 1999). fig. 6. structures of 27-35. conclusion from the above review it is evident that the orcinol form is an important building block for several phenolic compounds isolated from lichens. orcinol has very useful functionalities like phenolic, hydroxyl, and one methyl group, which are enable for a wide range of chemical transformations. chemical modification of orcinol is expected to elaborate wide range of diverse analogs and hybrid molecules. due to their structural diversity these compounds are expected to exhibit newer and enhanced biological 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(a) 13: 199-202. taborga l, espinoza l, moller a, carrasco h, cuellar m, villena j (2016) antiproliferative effect and apoptotic activity of linear geranyl phenol derivatives from phloroglucinol and orcinol. chem biol interact. 247: 2229. thadhani vm, choudhary m, ali s, omar i, siddique h, karunaratne v (2011) antioxidant activity of some lichen metabolites. nat. prod. res. 25: 1827-1837. türk h, yilmaz m, tay t, türk a, kivanç m (2006) antimicrobial activity of extracts of chemical races of the lichen pseudevernia furfuracea and theirphysodic acid, chloro atranorin, atranorin, and olivetoric acid constituents. z naturforsch. c. 61: 499-507. xu, m, heidmarsson s, olafsdottir e, buonfiglio r, kogej t, omarsdottir s (2016) secondary metabolites from cetrarioid lichens: chemotaxonomy, biological activities and pharmaceutical potential. phytomed. 23: 41-59. 7 microsoft word maresova 9-1 2009.doc nova biotechnologica 9-1 (2009) 73 zinc uptake and distribution in ivy (hedera helix l.) leaves jana marešová1, miroslav horník1,2, martin pipíška1,2, jozef augustín1,2 1department of biotechnology, university of ss. cyril and methodius, nám. j. herdu 2, trnava, sk-917 01, slovak republic (hornikm@ucm.sk) 2consortium for environmental biotechnology and environmental chemistry, hlavná 418, špačince, sk-919 51, slovak republic abstract: detached leaves of ivy (hedera helix l.) were used as a model for the study of zinc uptake and transport in vascular plants. by the uptake via the surface of fully immersed leaves in 25 % hoagland nutrient media (hm) spiked with 65zncl2 (50 µmol/dm3 zncl2), concentration in leaves 4.98 µg zn/g (dry wt.), i. e. 2.6 µg zn/dm2 leaf area after 7d exposition were obtained. by the uptake via immersed stalks of not immersed (transpiring) leaves concentrations up to 370 µg zn/g (dry wt.) were obtained. when zn enters into detached leaves via the surface of immersed leaf blades, zinc is uniformly distributed in leaf blades and leaf stalks. when zinc enters detached leaves via immersed stalks of non-immersed transpiring leaves, only small part of zinc is transported to leaf blades and the prevailing part remains in leaf stalks. stalks act as a trap, able to prevent other leaf tissues against inhibitory effects of high zn concentrations. mineral nutrient salts in solutions mobilize zn trapped in leaf stalks and facilitate zn transport by transpiration stream to leaf blades, what means that zn in stalks is bound in ion-exchageable forms. keywords: zinc, 65zn, foliar uptake, distribution, hedera helix. 1. introduction foliar uptake of mineral nutrients is of practical importance in agriculture and the problem was well described in numerous patents, periodicals and reviews (marschner, 1995). zinc is an essential nutrient as a trace element for animals, plants, and microorganisms. studies with wheat showed good transport of zn from stalks and leaves to developing grain (pearson et al., 1995; 1996), as well as from one root to another (pearson and rengel, 1995), indicating involvement of phloem transport. the movement of foliar applied zn to plant roots was demonstrated in small number of studies (haslett et al., 2001). radiotoxic 65zn is produced, sometimes in copious quantities, by neutron activation of stable zn in nuclear reactors. due to its half-life (τ = 244 d) and biological mobility, 65zn can be transported through food chains to man. 65zn may be taken up through leaves and roots by plants and its uptake is strongly influenced by nuclide form and soil properties (brambilla et al., 2002). english ivy (hedera helix l.) is a common, easily available plant species, possesing a number of advatages and its leaf ultrastructure is well described (canet et al., 1996; gilly et al., 1997). ivy leaf cuticle was used as a suitable model to investigate cuticular permeability. chamel (1986) described the fine structure and permeability of ivy leaf cuticles in relation to foliar development and after selective chemical treatments and determined the relationship between structure and permeability. 74 marešová j. et al. our previous papers were oriented on the bioaccumulation of 137cs, 60co and 65zn from nutrient solutions and translocation in vascular plants (horník et al., 2007; barátová et al., 2006). the objective of this study was to quantify the uptake of zinc by detached leaves of ivy (h. helix l.) submerged in solutions spiked with 65zncl2 in short-time laboratory experiments. two pathways of zn uptake and translocation, i.e. from stalks to leaf blades and from leaf blades to stalks were compared under the same experimental conditions. we used detached ivy leaves fully immersed in zncl2 solutions, instead of spraying, in order to eliminate differences in uptake values caused by different droplet volumes and contact surface areas, described by mercer (2007) and by other researchers. 2. materials and methods 2.1 plant material ivy branches (h. helix l.) were collected during spring months from freely grown garden vegetation. the upper part of branches were cut from a wild ivy plant, washed repeatedly in deionized water and used for experiments. leaves of about 0.2 – 0.3 g fresh weight and of leaf area 11.5 12.5 cm2 were used in experiments. fig. 1. photo of ivy leaves in experiments. characteristic signs: short stalks; shallow sinus; well developed veins; terminal, lateral and basal lobes. a. leaf stalks immersed in nutrient media in petri dishes; b. only leaf blades immersed in nutrient media in petri dishes. 2.2 bioaccumulation experiments 2.2.1 uptake via stalks of detached transpiring leaves leaf stalks (1.5 cm) were immersed in 10 ml 25% hoagland medium (hm, hoagland, 1920) supplemented with 5 µmol/dm3 zncl2 spiked with 65zncl2 and incubated in a cultivation room, at 22±2°c under illumination with artificial light (2 000 lx) in 12h/12h light/dark period (fig. 1a). the full-strength hm medium a b nova biotechnologica 9-1 (2009) 75 consisted of following molar concentrations of salts (in mm): mgso4.7h2o – 1.5; kno3 – 4.0; cacl2 – 4.0; nah2po4.2h2o – 1.87; na2hpo4.12h2o – 0.13; feso4.7h2o – 0.06; nano3 – 4.0; nh4cl – 3.17; nh4no3 – 2.0; h3bo3 – 0.14; na2moo4.2h2o – 0.0025; mnso4.5h2o – 0.21; znso4.7h2o – 0.023; cuso4.5h2o – 0.033. 2.2.2 uptake via surface area of immersed detached leaves leaf blades of detached leaves were fully immersed in 10 ml of 25% hm supplemented with 5µmol/dm3 zncl2 spiked with 65zncl2 in plastic petri dishes covered with lids (fig. 1b), under the conditions described in the previous paragraph. non-immersed leaf surfaces provided transpiration and respiration. at the end of experiments, leaves were carefully rinsed in deionized water and dried at 60°c to a constant weight and the incorporated radioactivity was measured by gammaspectrometry. bioaccumulation experiments were carried out in duplicate series. 2.3 radiometric analysis a gamma spectrometric assembly using the well type scintillation detector 54bp54/2-x, nai(tl) (scionix, the netherlands) and data processing software scintivision 32 (ortec, usa) were used for 65zn determination in plants and solutions. counting time of 600 s allowed to obtain data with measurement errors <2%, that do not reflect other sources of errors. a standardized solution of 65zncl2 (50 mg/dm3 65zncl2 in 3 g/dm 3 hcl) with specific radioactivity 4,901 mbq/cm3 was obtained from the czech institute of metrology (prague, czech republic). 2.4 speciation modeling the prediction of zn speciation in the aqueous systems was performed using the visual minteq (version 2.53) program. this speciation model allows the calculation of the composition of solutions for specified conditions (ph, ionic strength, concentration, temperature). 3. results and discussion leaf water repellency of adaxial or abaxial surfaces is a main limiting factor in spray application processes (watanabe and yamaguchi, 1991; holder, 2007). the permeability of the cuticle to water and to lipophilic organic molecules increases with mobility (diffusion coefficients) and solubility (partition coefficients) of these compounds within the transport-limiting barrier of the cuticles and this process is well described. significantly less is known about the permeability of the cuticle to ionic compounds. however, this is also of major significance in agriculture since, in foliar nutrition, elements such as zinc and copper can be sprayed as foliar fertilizers on leaf surfaces. in order to be effective, these ions have to penetrate the lipophilic cuticle. recently, significant progress has been achieved in measuring cuticular penetration (lin et al., 2007; schlegel et al., 2005; franke et al., 2005). 76 marešová j. et al. the aerial surfaces of higher plants are covered with a cuticle, with the exception of stomata openings. the cuticle is an extracellular, lipidic covering layer, forming the interface between the plant and environment. the cuticle represents the main barrier to the penetration of foliar-applied water soluble compounds such as mineral foliar fertilizers. the waxy leaf surface is hydrophobic and therefore surfactants are a common component of foliar formulations used for increasing the leaf wettability and to prolong the contact time of spray solutions with leaf surfaces. since charged molecules carry hydration shells (stein, 1967), they are not soluble in the lipophilic cutin and wax domains of the cuticles. according to viougeas et al. (1995) the cuticle mass of ivy leaves increases with increasing age from 234 to 539 µg/cm2. waxes increases from 12.3 to 18.6% of cuticle mass from young to old leaves. percentages of cutin and non-lipid constituents do not vary significantly with leaf age. they represent approximately 58 and 26% of the cuticle mass, respectively. cuticle thickness increases 12-fold during leaf growth to reach 4.25 µm for mature leaves. an outer lamellate zone gradually merging from an inner reticulate zone the thickness of which increases with leaf growth is characterized by a constant thickness of 0.2 µm. intracuticular wax is localized in lamellae. electron-dense fibrillae observed in the reticulate zone are made of non-lipid components (viougeas et al., 1995). we can suppose, that zn uptake data via leaf surface will be strongly dependent on the age of leaves used in experiments, due to the fact, that cuticle is the major barrier for nutrient leaf uptake. 3.1 zn uptake via stalks detached leaves are frequently used for studies of long distance transport in vascular systems of higher plants. the main advantage of such studies is in the elimination of selective effect of root system on different compounds, which takes place in transport studies via root systems of hydroponically grown plants. in our study, stalks of detached leaves of ivy (h. helix) were immersed in zncl2 solutions and both, the adaxial and abaxial leaf surfaces were in contact with atmosphere. in this case the only driving force of zn uptake was water transport driven by transpiration. we found that under given conditions, the uptake of zn was proportional to the initial zn2+ concentration c0 within the range ≤ 50 µmol/dm 3. at c0 = 50 µmol/dm 3 zncl2, concentrations of zn2+ 370 µg/g and 3.1 µg/g of dry weight of leaf stalks and leaf blades, respectively, were obtained. it means that zinc entering the plant tissues via stalks is distributed by vascular system into leaf blades only in limited extent, reaching a specific concentration ratio of [zn]stalks /[zn]blades = 120 : 1 (fig. 2a). which chemical components of stalk tissues are responsible for immobilization of zn2+ ions via xylem vessels will require more detailed study. 3.2 zn uptake via leaf surfaces for the zn foliar uptake study in our experiments we used detached ivy leaves, fully immersed in zncl2 solutions. this approach eliminates the differences in foliar nova biotechnologica 9-1 (2009) 77 uptake from sprayed solutions caused by different droplet volumes and contact surface areas of sprayed solutions, described by mercer (2007). under experimental conditions both adaxial and abaxial leaf surfaces were in contact with zncl2 solution and transpiration as the main driving force does not participate on zn influx into leaf tissues. influx of nutrients via leaf surfaces is a characteristic route for nutrient uptake by plants without efficient root systems, such as mosses and submerged aquatic plants. under such conditions the amount of zinc taken up by ivy leaves increased with increasing zn concentration in solutions, however the amount of zinc in leaf tissues represented only 33.7% of that accumulated via leaf stalks. data in fig. 2b demonstrate, that zinc entering plant tissues via leaf surfaces is distributed by vascular system into stalks, reaching the concentration ratios of [zn]stalks /[zn]blades from approximately 1 : 1 to 2 : 1. however this ratio will depend on the zinc concentration in solution. according to kramer and kozlowski (1979) and lin et al. (1995) the mobility of absorbed elements depends on their concentration in plants. 0 10 20 30 40 50 0 100 200 300 400 z n [μ g/ g] c 0 zncl 2 [μmol/dm3] leaf blades leaf stalks a 0 10 20 30 40 50 0 100 200 300 400 leaf blades leaf stalks z n [μ g/ g] c 0 zncl 2 [μmol/dm3] b fig. 2. zn concentration (µg/g, dry wt.) in leaf stalks (......) and leaf blades (____) of ivy leaves (h. helix l.) after 5 d exposition in 2.4; 5.0 and 50 µmol/dm3 zncl2 in 25% hm spiked with 65zncl2 (310 kbq/dm3). a. uptake via immersed stalks of transpiring leaves. b. uptake via surface of fully immersed leaves. cultivation at 12h/12h light/dark period (2 000 lx), ph 6.0 and 22±2°c. wet weight of leaves [g/10 ml]: a. 0.29±0.01 (±sd); b. 0.27±0.01 (±sd). leaf area [cm2]: a. 14.6±0.75 (±sd); b. 13.7±0.99 (±sd). b. transpiration 3.32 ± 0.74 cm3.dm-2.d-1 (±sd). total zn uptake via leaf surfaces was by one order lower comparing with zn uptake via xylem path of stalks of detached leaves. this is a consequence of the existence of diffusion barriers on the leaf surfaces, mainly cuticular membrane and waxes and due to the absence of transpiration stream. the driving force for zn uptake across the leaf surface is a concentration gradient on the water/leaf interface. similarly as in the case of zn uptake via leaf stalks (fig. 2a), also in the case of zn uptake via leaf blade surfaces of fully immersed leaves (fig. 2b), zn uptake increased with increasing initial zn concentration c0. however total zn uptake expressed as specific concentration in µmol/g was 9.4 times lower in stalks and 2.8 times higher in leaf blades. 78 marešová j. et al. 3.3 effect of nutrient salts distribution of zinc entering the leaves of ivy via vascular system of stalk of detached leaves immersed in nutrient medium spiked with 65zncl2 was dependent on inorganic nutrient concentration (fig. 3). when zn is taken up from low nutrient salt media, i.e. < 50 % hm, substantial part of zinc remains immobilized in stalks. 0 25 50 75 100 0 10 20 30 40 50 z n [n m ol /g ] hoagland concentration [%] a 0 25 50 75 100 0,0 0,2 0,4 0,6 0,8 1,0 x m ol ar fr ac tio n hoagland concentration [%] b fig. 3. influence of nutrient salt concentration on zn uptake and distribution in leaf stalks and leaf blades of ivy (h. helix l.). uptake via immersed stalks of transpiring leaves. data after 6 d exposition in diluted hm spiked with 65zncl2 (310 kbq/dm3) at initial zn concentration c0: 1.1; 1.7; 2.3 and 3.4 µmol/dm3. cultivation at 12h/12h light/dark period (2 000 lx), ph 5.5 and 22±2°c. data expressed as a: zn concentration in ivy leaves [nmol/g, dry wt.]; b: zn molar fraction in leaf blades (x = [zn]blades/ [zn]total ; -■-■-■-) and leaf stalks (x = [zn]stalk/ [zn]total ; -●-●-●-). biomass of the whole ivy leaves (stalks + blades) in experiments (g/10 ml, wet wt.): 0.64±0.06 g (±sd). leaf blade area of transpiring leaves: 20.03±1.26 cm2 (±sd). transpiration rate: 3.33 ± 0.74 cm3.dm-2.d-1 (±sd). when zn is taken up from solutions of high nutrient concentrations (> 50 % hm), zinc is nearly completely transported from stalks to the leaf blades (fig. 4). we can conclude that zinc entering the leaves via stalk xylem is bound on components of xylem vascular system by reversible ionic bond. zinc can be replaced from binding sites by ions showing higher activity for binding sites, present in the vascular system. to answer the question which binding sites in xylem vessels play a decisive role in zn binding in xylem of individual plant species will require more detailed study. our hypothesis is supported by published data describing zinc interaction in other plant tissues. straczek et al. (2008) used chemical extractions and exafs spectroscopy for the study of zn distribution in whole roots and isolated root cell walls of tobacco plants. their results showed that the cell walls of roots exhibited a distribution of zn from water soluble to non-exchangeable zn form. in whole roots, zn was bound with oxalate and other cooh/oh groups: the first species was probably intracellular while the second was attributed to zn bound to the cell walls and, to a lesser extent, to intracellular organic acids. zn-phosphate was also identified, and this species was cuso4 extractable. it probably resulted from chemical precipitation in the apoplast, and explained the steady increase in exchangeable root zn observed in tobacco roots during the culture. nova biotechnologica 9-1 (2009) 79 0 20 40 60 80 100 0 2 4 6 8 10 12 14 16 18 [z n] st al ks : [z n] le af b la de s hoagland concentration [%] fig.4. distribution of zn in stalks and blades of ivy leaves after 6 d uptake via immersed stalks of transpiring leaves, expressed as the [zn]stalks : [zn]blades ratio. calculated from data in fig. 2. zinc, in optimal concentration, is a typical micronutrient which is necessary for normal metabolism of all plant cells. on the other side, in supra-optimal concentrations, zinc can cause serious damages in metabolically active cells, mainly in leaves. our data support the idea, that leaf stalk can act as a barrier able to retard transport of zn ions entering the leaf via xylem path. this barrier may be less efficient in the presence of higher salt concentrations moving in the root to shoot direction. 3.4 the effect of ph the membrane permeability can be affected by solution ph, mainly by influencing the driving forces via electrical potential and by change of the properties of the solutes by dissociation. the cuticles are polyelectrolytes and their isoelectric point is around ph 3 (schönherr and huber, 1977). above this point, when ph increases, the cuticles carry fixed negative charges. these charges are also an important characteristic affecting the water content of the polymer matrix via swelling. the ph dependence of zn uptake via ivy leaf surface is shown in fig. 5. below ph 3.0, i.e. below the isoelectric point of cuticle, zn uptake was minimal, increasing up to ph 4 and showing plateau up to ph 6. the next increase of zn uptake is evident at ph > 6 what coincides with decrease of zinc concentration in bioavailable zn2+ form and formation of zinc ionic forms. 3.5 the effect of temperature our experiments did not confirm the dependence of zinc uptake by ivy leaf surface on temperature within the range from 4 to 37°c (results not shown). this problem will require more detailed, mainly kinetics studies. experiments with isolated cuticular membranes described by schönherr and luber (2001) showed that different forms of water and lipophilic substances, inorganic ions and charged organic 80 marešová j. et al. molecules penetrate the isolated cuticular membranes independently of temperature. schreiber (2005) concluded that ionic compounds use aqueous polar path of diffusion, whereas lipophilic molecules move along the lipophilic wax and cutin domains. water, as a small but uncharged molecule, can use both paths. 3 4 5 6 7 8 0 0,2 0,4 0,6 0,8 1 0 2 4 6 8 m ol ar fr ac tio n ph z n up ta ke [% ] zn uptake [%] zn2+ znso 4 znhpo 4 zn(oh)+ zn(oh) 2 10 fig. 5. the ph dependence of zn uptake via the surface of fully immersed ivy leaves (-■-■-■-) and molar fraction of zn species in solutions at given ph values. uptake data after 5 d exposition in 5.0 µmol/dm3 zncl2 in 25% hm, spiked with 65zncl2 (130 kbq/dm3). initial ph values adjusted by adding 0.05 m naoh. leaf wet weight biomass [g/10 ml]: 0.22±0.017 (±sd). leaf area [cm2]: 9.86±0.88 (±sd). presented molar fractions of zn species at given ph are calculated by the visual minteq program. 4. conclusions experiments with ivy leaves as a model plant leaves showed that total zn uptake from zncl2 solution via immersed leaf surface is by one order lower, comparing to zn uptake via xylem path of immersed stalks of detached leaves under the same conditions. zn uptake increased with increasing initial zn concentration up to c0=50 µmol/dm3 zncl2 in both cases. zinc entering the plant tissues via leaf stalks remains bound mainly in stalk and was transported by vascular system into leaf blades only in limited extent. in the last case the specific concentration ratio [zn]stalks /[zn]blades was 120-times higher, compared with the case of zinc entering plant tissues via leaf surfaces. zn uptake was minimal below ph 3, increasing at ph 3 – 5, showing plateau at ph 6 – 7 and next rapid increase at ph 7. our experiments did not confirm the dependence of zinc uptake by ivy leaf surface on temperature. more detailed study is necessary for understanding all factors influencing the efficiency of foliar uptake of mineral nutrients from foliar fertilizers. references barátová, z., sekáčová, 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of xylem transport affects zn and mn transport into developing wheat grains of cultured ears. physiol. plantarum, 98, 1996, 229-234. schlegel, t.k., schönherr, j., schreiber, l.: size selectivity of aqueous pores in stomatous cuticle of vicia faba leaves. planta, 221, 2005, 648-655. 82 marešová j. et al. schönherr, j., huber, r.: plant cuticles are polyelectrolytes with isoelectric points around three. plant physiol., 59, 1977, 145-150. schönherr, j., luber, m.: cuticular permeation of potassium salts: effects of humidity, anions and temperature. plant soil, 236, 2001, 117-122. schreiber l.: polar paths of diffusion across plant cuticles: new evidence for an old hypothesis. ann. bot., 95, 2005, 1069-1073. stein, w.d.: the movement of molecules across cell membranes. academic press, new york, 1967, 369 pp. straczek, a., sarret g., manceau, a., hinsinger, p. geoffroy, n., viougeas, m.a., rohr, r., chamel, a.: structural changes and permeability of ivy (hedera helix l.) leaf cuticles in retention to leaf development and after selective chemical treatments. new phytol., 130, 1995, 337-348. watanabe, t., yamaguchi, i.: evaluation of wettability of plant leaf surfaces. j. pestic. sci., 16, 1991, 491-498. nova biotechnol chim (2022) 21(2): e1337 doi: 10.36547/nbc.1337 1 nova biotechnologica et chimica elucidation of antibacterial activity of bacillus sp. and alcaligenes sp. metabolites against multidrug-resistant bacteria faheem ullah1, sadir zaman1, waheed ullah1,, shandana ali3, muhammed qasim1, niaz muhammad1, momina mehmood1, navid ali1, niamat khan2 1department of microbiology, kohat university of science and technology, kohat 26000, khyber pakhtunkhwa, pakistan 2department of biotechnology and genetic engineering, kohat university of science and technology, kohat 26000, khyber pakhtunkhwa, pakistan 3department of zoology, kohat university of science & technology kohat 26000, khyber pakhtunkhwa, pakistan  corresponding author: waheedwazir@gmail.com article info article history: received: 22nd december 2021 accepted: 1st july 2022 keywords: antibacterial activity cholistan desert inhibitor minimum inhibitory concentration secondary metabolites abstract different resistance mechanisms are involved in exhibiting resistance to different groups of antibiotics. researchers are searching for new therapeutic options to encounter the emerging trend of microbial resistance. bacteria were isolated from the extreme environment of cholistan desert and were screened for characterization. potential metabolites that showed broad-spectrum activity were partially purified using silica gel chromatography and determined their minimum inhibitory concentration. a collection of 50 bacterial isolates from soil samples was screened for metabolite production and among them isolate r19 of bacillus sp. and isolate a8 of alcaligenes sp. had high similarity with strong antimicrobial metabolite producers. the growth of a8 was stable at slight acidic ph while r19 was best at neutral ph. similarly, the best growth of a8 was observed at 37 °c while r19 at 35 °c. minimum inhibitory concentration of purified compounds of bacillus sp. were determined at concentration range of (3.12 – 100 %) against multidrug-resistant (mdr) strains of shigella, enterobacter aerogenes, staphylococcus aureus, pseudomonas aeruginosa, escherichia coli, and klebsiella pneumonia and produced 10 – 25 mm zone of inhibition. metabolites of alcaligenes sp. were sufficient to inhibit the growth of all selected mdr bacteria at concentrations 12.25 – 100 % and shows 10 – 20 mm zone of inhibition. bacillus sp. and alcaligenes sp. can be used as producers of potential antibacterial metabolites. proper utilization of selected metabolites can be helpful in combating emerging drug resistant pathogenic bacteria. in addition, further proteomic analysis and structural insight should be considered to elaborate their active ingredients and its efficacy. introduction microbes are potential sources of different types of important active metabolites. in search of potential metabolites producer microbial strains, several studies have been conducted to explore different habitats for potential metabolites producer microbes. it can be deduced from different studies that microbes of diverse environments carrying strong antimicrobial potential according to andayani et al. (2015), observed by others (masand et al. 2018; rajasabapathy et al. 2020). microbial metabolites due to their increasing applications have allure the attention of scientists to mailto:waheedwazir@gmail.com nova biotechnol chim (2022) 21(2): e1337 2 explore different untouched sites for potential metabolites producer microbes kumar et al. (2018). metabolites have various therapeutic applications in the treatment and eradication of different types of bacterial, fungal and parasitic diseases demain (1999). in pre-antibiotic era, the treatment of infectious diseases was challenging due to unavailability of antibiotics adedeji (2016). the discovery and commercialization of penicillin give new hope because morbidity and mortality associated with infectious diseases were reduced in infected population. unfortunately, with passage of time resistant strains like emergence of methicillin resistant staphylococcus aureus (mrsa), vancomycin resistant enterococci and multidrug resistant (mdr) strains of gram negative bacteria were reported worldwide particularly in developing world hesse and adhya (2019). world health organization estimates that annually millions of people lost their lives due to drug-resistant bacterial strains. according to shrivastava et al. (2018) the world health organization enlist priority pathogens for which new and effective drugs need to be explored having bactericidal activity. among these pathogens, carbapenem resistant strains are global threats le thanh dong and espinoza (2020). carbapenems drugs are considered the last choice for treatment of mdr bacteria. recently, few extreme drug resistant (xdr) strains of salmonella sp. were isolated from infected patients in pakistan, which revealed resistance to most of the available drugs including ampicillin, chloramphenicol, trimethoprim-sulfamethoxazole, ciprofloxacin, and ceftriaxone while fortunately sensitive to azithromycin and carbapenems rasheed et al. (2019). in relation to the resistance, the induction of new effective drugs rate is low as compared to previously approved drugs that lose their efficacy ribeiro da cunha et al. (2019). to tackle antibiotic resistance issue, scientists are trying to explore new avenues for the isolation of potential metabolite producer microbes having strong inhibitory potential. bacillus a gram positive spore forming bacteria, having potential to cope harsh environment has been frequently isolated from extreme habitats nicholson et al. (2000). their secondary metabolites exhibit strong antibacterial activity and many of their compounds have been commercialized to use as antibiotics such as bacteriocins morikawa et al. (1992). beside bacillus, actinomycetes, fungi are also sources of antibiotics singh et al. (2019). in the current scenario, researchers demonstrate key interest in bacterial characterization from the unexplored harsh environment like deserts and marine with the hope to explore strong bioactive metabolites producer strains according to abdelkader et al. (2018); observed by cita et al. (2017). indeed, by 2008, more than 100 specialized metabolites had been isolated and identified from microorganisms isolated from such habitats. in addition, in the previous decade, 129 putative strains, producing 186 drug gable metabolites, were isolated from extreme strata sayed et al. (2020). the current study was conducted for the exploration of antibacterial metabolites producer bacterial strains from the unexplored habitat of cholistan desert (punjab, pakistan) with harsh environmental conditions like high temperature, scarcity of nutrients and water depletion. experimental collection and isolation of bacteria from soil samples samples from different locations of cholistan desert were collected in sterile bottles using standard procedure as previously described by elbendary et al. (2018). all samples were brought to the medical laboratory, department of microbiology, kust and were stored at -80 °c for further analysis. all samples were serially diluted up to 10-9 in sterilized distilled water. aliquot of 100 µl was spread from last three dilution on tryptone soya agar (tsa) and nutrient agar (na) and plates were incubated for 48 h at 37 °c. after incubation different colonies appeared on different culture media. resistant bacterial strains profile mdr bacterial strains of p. aeruginosa, e. coli, e. aerogenes, k. pneumonia, s. aureus, and shigella sp. were obtained from medical laboratory, department of microbiology, kohat university of science and technology. to assess the nova biotechnol chim (2022) 21(2): e1337 3 antibacterial potential of broth extract of metabolite producer strains, its inhibitory effects were screened against the resistant pathogens. all the selected bacterial strains revealed resistance toward different antibiotics like penicillin, cephalothin, tetracycline, amoxicillin, cefoperazone, ceftriaxone, and cefepime based on clsi guidelines. evaluation of antibacterial activity of cell-free extract isolated bacteria were grown in luria bertani broth (lb) for 5 to 7 days in shaking incubator at 170 rpm and 30 °c. after incubation, centrifugation was performed, and supernatants of each broth were filtered. the cell-free filtrates were assayed for antibacterial activity using well diffusion assay oskay (2011). growth optimization at different temperature and ph the isolates were incubated in nutrients broth at various temperatures like 5, 10, 15, 20, 25, 30, 35, 40, 45, 50, 55, 60, 65, 70, and 75 °c. growth conditions were optimized at different ph 3.0, 4.0, 5.0, 6.0, 7.0, 8.0, 9.0, and 10.0. the results were recorded using spectrophotometer at 600 nm od. for proper growth, ph of the media was adjusted according to bacterial needs as previously described khalil et al. (2009). extraction of antibacterial metabolites bacterial isolates from desert soil samples (n = 50) were screened for their antibacterial metabolites production. among these isolates, a8 and r19 exhibit broad-spectrum activity against mdr bacteria and were selected for further analysis. an equal amount of ethyl acetate was added to the extracted filtrate and then metabolites were concentrated using rotary evaporator. bacterial metabolites were purified using silica gel column chromatography, chloroform/methanol in the ratio of (100 : 0, 80 : 20, 60 : 40, 50 : 50, 40 : 60, 20 : 80, 0 : 100) as an eluent. further each fraction were concentrated using rotary evaporator rao et al. (2007). minimum inhibitory concentration (mic) determination of antibacterial metabolites activity of each fraction of selected metabolites was examined on mueller hinton agar (mha) against drug resistant strains by using agar well diffusion process. fractions of best restraining were selected for mic determination against resistant pathogens. active fractions (2 ml) were considered 100 % and were serially diluted into two-fold to make 50 %, 25 %, 12.5 %, 6.25 %, and 3.125 %, and concentration respectively. further 100 μl from each concentration was used for the mic determination. biochemical and molecular characterization of metabolites producer strains strong metabolites producer strains were biochemically characterized using standard procedures of (rahimnahal et al. 2017; marathe et al. 2018). for molecular characterization, dna from the selected active antimicrobial metabolites producers strains were extracted by standard phenol chloroform method (neumann et al. 1992) using overnight culture. pcr reactions were carried out for the amplification of 16s rrna gene using universal primers forward primer 5'agagtttcctggctcag-3' and reverse primer 5'-aaggaggtgatccagcc-3' (lim et al. 2016). pcr conditions were set for amplification of 16s rrna gene. the thermal cycling reactions were performed as: initial denaturation at 94 °c for 5 min, then 25 cycles of 94 °c for 1 min, 50 °c for 40 s and 72 °c for 60 s and final extension was 72 °c for 5 min. the amplified products of pcr of the selected isolates were confirmed on 2 % agarose by adding 3.5 μl ethidium bromide as a staining dye and visualized by the digital gel doc system (analytik jena system, jena, germany). the products were subjected to sequencing and reactions were conducted at macrogene (seoul, south korea) using the universal 16s rrna forward primer. the resulted sequences were extracted using bioedit software. ncbi blast analysis was performed for sequence alignment. moreover, phylogenetic tree was constructed using mega 7 software. nova biotechnol chim (2022) 21(2): e1337 3 results antibacterial activities of a8 and r19 metabolites soil samples (n = 50) were screened for their antibacterial metabolites production and among these isolates a8 and r19 were expressed broad spectrum activity against resistant bacterial culture and were selected for further analysis. morphologically isolate a8 stained gram-negative rod shape while r19 was identified as grampositive rod shape and was also spore positive fig. 1. biochemically both isolates were catalase, oxidase, sugar fermenting, and motility recorded positive. a b fig. 1. morphological study of the selected isolates from cholistan desert. a – culture of bacteria on nutrient agar; b – pink colour shows gram negative bacteria; c – the blue colour shows gram positive bacteria. growth optimization of selected isolates on different temperature and ph best growth of selected isolate a8 was observed at 37 °c and lowest growth were observed at 15 °c. similarly isolate r19 have shown maximum growth at temperature 35 °c as shown in fig. 2a. similarly, ph also has a huge impact on the bacterial growth. a8 shows maximum growth at neutral ph while r19 showed maximum activity at ph 9.0. both isolates growth was restrained at acidic ph as shown fig. 2b. gram negative rods culture of bacteria gram positive rods c 4 nova biotechnol chim (2022) 21(2): e1337 3 0 0.2 0.4 0.6 0.8 1 1.2 1.4 o p ti c a l d e n s it y ( o d ) temp = temperature (°c) effect on growth at different temperature a8 r19 0 0.5 1 1.5 ph 3.0 ph 4.0 ph 5.0 ph 6.0 ph 7.0 ph 8.0 ph 9.0 ph 10.0 o p ti c a l d e n s it y ( o d ) ph effect on growth at different ph a8 r19 fig. 2. effects of temperature (a) and ph (b) on growth of isolates (a8 and r19). mic determination of isolate a8 collected through silica gel at different concentrations. the metabolites activities of strain a8, after silica gel purification, were observed for antibacterial activity against shigella, s. aureus, e. aerogenes, p. aeruginosa, e. coli, and k. pneumonia mdr strains respectively at different concentration as shown in table 1 and fig. 3. isolate a8 metabolites has the maximum zone of inhibition against mdr shigella and s. aureus of about 25 mm, 24 mm, respectively. similarly, it has strong inhibitory activity toward p. aeruginosa and 19 mm zone of inhibition while in case of e. aerogenes 20 mm zone of inhibition was recorded. while less inhibitory activity was observed against e. coli and k. pneumonia. a b 5 nova biotechnol chim (2022) 21(2): e1337 3 fig. 3. antibacterial activity of a8 isolate against (a) klebsiella pneumonia, (b) e. coli, (c) e. aerogenes, (d) s. aureus, (e) shigella, (f) p. aeruginosa. fig. 4. antibacterial activity of r19 isolate against (a) k. pneumonia, (b) e. coli, (c) e. aerogenes, (d) s. aureus, (e) shigella, (f) p. aeruginosa. table 1. inhibition zones of a8 metabolites against selected bacterial strains at different concentration. tested bacterial strains 3.15 % [mm] 6.25 % [mm] 12.5 % [mm] 25 % [mm] 50 % [mm] 100 % [mm] shigella --13 15 22 25 s. aureus --10 12 21 24 e. aerogenes ---11 14 20 p. aeruginosa --10 15 17 19 e. coli ---11 12 15 k. pneumonia ----14 15 antibacterial activity of r19 isolate the antibacterial activity of r19 metabolite was observed against shigella, s. aureus, e. aerogenes, p. aeruginosa, e. coli, and k. pneumonia mdr strains at different concentration as shown in (table 2, fig. 4). r19 bacterial metabolites were more effective against all selected resistant bacterial strains as compared to a8. it has shown a strong inhibitory pattern from lower to higher concentration against shigella and e. aerogenes. at lower concentration (3.12 %) it produced 10 mm zone of inhibition while at higher concentration (100 %) it generated 19 mm and 20 mm zone of inhibition against selected mdr strains respectively. similarly, it has strong inhibitory action against mdr e. coli at concentration (50, 100 %) and manifest 19 mm and 23 mm zones of inhibition toward selected strains. further their action against other tested isolates including k. pneumonia and p. aeruginosa revealed 16 – 18 mm zone of inhibition at concentration (100 %) as shown in table 2. 6 nova biotechnol chim (2022) 21(2): e1337 3 table 2. inhibition zones of r19 metabolites against selected bacterial strains at different concentration measured in diameter (mm). test bacterial strains 3.12 % [mm] 6.25 % [mm] 12.5 % [mm] 25 % [mm] 50 % [mm] 100 % [mm] shigella 10 13 15 16 18 19 s. aureus -8 9 12 16 20 e. aerogenes 10 11 12 13 14 20 p. aeruginosa -8 9 11 15 18 e. coli -5 6 10 19 23 k. pneumonia ---10 15 16 molecular characterization of a8 and r19 strains using 16s rrna gene further identification of both a8 and r19 metabolite producer strains were characterized through pcr amplification of 16s rrna gene, size 1399 bp, as shown in fig. 5. amplified product of a8 and r19 were sequenced at macrogen (seoul, south korea) using forward primer. homology analysis of both isolates were conducted at ncbi blast and there were 97.7 % identity with alcaligenes sp. for a8 isolate and 98.3 % identity with bacillus sp. for r19. based on sequencing results, phylogenetic trees were constructed using mega7 for the selected isolates (a8 and r19) as shown in fig. 6 and 7. fig. 5. gel image of amplified product of 16s rrna gene. lane l shows ladder, lanes a8 and r19 bacterial isolates a8 and r19, respectively. fig. 6. r19 phylogenetic tree using mega7. 7 nova biotechnol chim (2022) 21(2): e1337 2 fig. 7. a8 phylogenetic tree using mega. discussions to combat extending bacterial resistance, exploration of new drugs is indispensable of a current scenario. scientists are in search of new metabolites that have strong potential to address resistant strains. soil harbour diverse microbial community which has potential to cherish strong antibacterial potential. previously bacterial isolates particularly bacillus sp. have been reported from different habitats having strong antibacterial activity. in recent study efforts were made to explore microbial community for potential of strong antibacterial compounds, from diverse environmental conditions. deserts have diverse environmental conditions and have mixed microbial flora. cholistan desert of pakistan has wide range of microbial community and have potential to cope with challenging environmental conditions amin et al. (2020). in current study two isolates (a8 and r19) emerged as strong antibacterial metabolites producer strains that have been characterized based on ribotyping which revealed that a8 showed 97.74 % sequence similarity to alcaligenes sp. and r19 unveil 98.33 % sequence similarity to bacillus sp. similar active producer strains have been screened from the unexplored unique habitat of mountain himalaya which produced strong antibacterial metabolites according to hussain et al. (2018). according to das et al. (2018) study, streptomyces strains were isolated from protected forest land and most of these isolated strains carried broad spectrum antibiotic activity and were stable at 37 °c while some of the isolated strains were stable 42 °c. a8 and r19 isolate showed broad spectrum activity, against mdr clinical bacterial strains. maximum growth of a8 and r19 isolates were observed on normal nutrient media. other growth conditions like temperature and ph were also analysed, isolates that the best grown at temperature 37 ℃ and the lowest below 20 ℃ have been recorded. our result are in line with the study conducted by bharali et al. (2011) in which the alcaligenes sp. isolates growth was documented at 42 °c. a8 showed maximum growth at neutral ph while r19 was most stable at slight alkaline ph. these results confirmed previously reported by farag et al. (2019) in which metabolites of bacillus manifest promising activity was observed at slight alkaline ph. in recent development, growth of mdr strains of shigella and e. aerogenes were restricted at concentration of 3.12 % of the partially purified compound of bacillus sp. similarly, for s. aureus, p. aeruginosa and e. coli were determined 6.25 % while 25 % for k. pneumonia. the partially purified metabolites of isolated strain of bacillus sp. exhibited promising activity against gram negative bacteria and it has also excellent inhibitory activity against s. pyogenes mtcc 442, b. cereus, e. faecalis, and s. epidermidis atcc 12228. 8 nova biotechnol chim (2020) 19(2): 124-137 similarly, ramachandran et al. (2014) isolated bacillus sp. from soil samples and found a strong producer of metabolites that showed strong effective against broad-spectrum microbes. the metabolites of alcaligenes sp. manifest strong activity at lowest concentration (12.25 %) against shigella, s. aureus and p. aeruginosa while at concentration (25 %) growth of e. aerogenes and e. coli were inhibited. a thermophilic strain of alcaligene sp. was isolated from petroleum contaminated soil having potency of antibacterial activity against bacillus sp., k. pneumonia, e. coli, p. aeruginosa, and s. aureus observed by bharali et al. (2011). similarly, isolated strains of alcaligenes sp. were reported from common effluent treatment plant which demonstrated antibacterial activity against mdr enterobacter sp. and serratia sp. being supported by the production of active a nucleoside antibiotic according to kapley et al. (2016). bacillus sp. are predominantly soil bacteria and can be found in different other habitats that their existence in soil in huge numbers as a result of their capacity to form resistance endospores and develop bioactive compounds which promote their resistance to variable environmental conditions reported by onajobi et al. (2020). a study reported by abd sharad et al. (2016) of the alcaligenes sp. isolated from marine habitat has strong antibacterial activity at 3 mg.ml1 against resistant bacteria. conclusions metabolites of alcaligenes sp. (a8) and bacillus sp. (r19) have shown the maximum zone of inhibition against mdr clinical bacterial strains. the active fractions of alcaligenes sp. metabolites revealed strong inhibitory effects against all resistant pathogens. this study provides initial layout for researchers and drug developers to further characterize active ingredients. furthermore, its growth was optimized on the best ph and temperature that will be helpful in extraction and stability of metabolites. proper utilization of selected metabolites can be helpful in combating emerging drug resistance mess in pathogenic bacteria. in addition, further proteomic analysis and structural insight should be considered to elaborate their active ingredients and its efficacy. acknowledgements this study was a part of ms research project. we extend our gratitude to department of microbiology, kohat university of science and technology for providing lab facilities for conducting this research. conflict of interest the authors declare that they have no 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methodius in trnava flavonols hplc analysis, in vitro biological activities in selected humulus lupulus l. genotypes maria maliarova1, tibor maliar2, jana girmanova1, jozef lehotay1, jan kraic2 1department of chemistry, faculty of natural sciences, university of ss. cyril and methodius in trnava, j. herdu 2, trnava, sk-917 01, slovak republic 2department of biotechnologies, faculty of natural sciences, university of ss. cyril and methodius trnava, j. herdu 2, trnava, sk-917 01, slovak republic (maria.maliarova@ucm.sk) abstract: the humulus lupulus l. is well known as necessary raw material for beer production. the main structural classes of chemical compounds identified from hop cones include terpenes, bitter acids, prenylated chalcones, and flavonol glycosides. they were subjects of presented work. the content of quercetin was found in the range 490 – 1092 µg/g and that of kaempferol from 218 to 568 µg/g of the dry hop cones. the content of isorhamnetin was very low in all varieties. from biological activities in vitro point of view, relative high level of inhibition activity was observed for six hop genotypes – zlatan, lučan, and the oswald's clones 31, 70, 71, 72, 114 on both enzymes thrombin and urokinase, but without correlation to analyzed flavonols content. in spite of this, antioxidant activity, measured by both the bclm and hpe methods, was found high and seem to be in correlation with content of analyzed flavonols. particularly the oswald's clone 114 expressed very potent biological activities. in general, obtained results indicate that hop cones are valuable material also for other application others than beer production. key words: humulus lupulus, saaz, quercetin, kaempferol, isorhamnetin, biological activity in vitro 1. introduction the hop plant (humulus lupulus l., cannabinaceae) is well-known throughout the world as the raw material for brewing industry. the female inflorescences (the hop cones, strobili lupuli) are used in the beer production especially to add bitterness (stevans et al., 1999). the main structural classes of compounds identified from the hop cones include: terpenes (compounds with sedative effect), bitter acids (prenylated derivatives of phloroglucinol, which posses antibacterial and antioxidant effects) and finally polyphenols, including flavonoids, prenylated flavonoids, and polyphenolic acids with antioxidant, antibacterial activity (krofta et al., 2008; zanoli and zavatti, 2008; nesvadba and krofta, 2009). it is well now that flavonoids exhibit a broad spectrum of pharmacological effects, especially anti-inflammatory and antioxidant activity, antimutagenic and anticarcinogenic activities but also inhibition activity on various proteolytic enzymes including enzymes involved in coagulation and fibrin clot digestion processes as thrombin and urokinase are (middleton et al., 2000; maliar et al., 2004). thrombin is key enzyme in process of fibrin clot formation of the coagulation cascade mechanism, partially different from the trypsin by the specific p1´ region bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:18 utc 130 maliarová, m. et al. cleaving peptide bond between arginine and any bulky aromatic residue (onaya et al., 1998). thrombin is pathophysiological promoter of coagulation disorder diseases and attractive target for perspective thrombolytics. urokinase (plasminogen activator of the urokinase type) is key enzyme responsible for activation of plasmin cascade leading to digestion of needless fibrin clot after wound or vessel closing and healing. urokinase is very specific serine-proteinase preferring cleaving peptide bonds beside lysine residue (schmitt et al., 1997), pathophysiological promoter of the oncological diseases with significant metastasis and attractive target for new oncolytics by the metastasis blocking mechanism. the hop is rich for flavonolglycosides, which have monoor di-saccharide bonded in position 3. segawa et al. have identified quercetin glycosides and kaempferol glycosides in the hop cones by mass spectrometry (segawa et al., 2006). the flavonolglycosides hydrolysis release free aglycons – flavonols from monoor disacharides (fig. 1). quercetin is formed from the glycosides of rutin, isoquercitrin and isoquercitrin malonate under acidic condition. kaempferol is formed from similar glycosides – kaempferol rutinosid, astragaline and astragalin malonate. isorhamnetin was also identified in the hop cones after enzyme hydrolysis (wojdylo et al., 2007). during brewing, the flavonols are extracted from hop to beer. the final content of flavonols in beer depends on both, the raw material and the brewing process conditions. however, acid hydrolysis takes place most frequently (alekseeva et al., 2004; proestos et al., 2006; stalikas, 2007). simultaneous acid hydrolysis and extraction of flavonols was firstly described by hertog for fresh and frozen vegetables (hertog et al., 1992). additional options are microwave assisted acid hydrolysis (nuutila, 2005) or enzyme hydrolysis by glycosidases (wojdylo et al., 2007). rutin quercetin isoquercitrin isoquercitrin malonate h+ h+ h+ fig. 1. structures of quercetinglycosides and their acid hydrolysis product. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:18 utc nova biotechnologica et chimica 12-2 (2013) 131 physical and chemical properties of flavonols provide important knowledge for selection of the condition for hydrolysis, separation and detection. 1-octanol/water partition coefficient – logp values and solubility in water are given in the table 1. table 1. 1-octanol/water partition coefficients and solubility in water values of selected flavonoids. log p solubility in water flavonol experimental data prediction by alogps experimental data [mg/ml] prediction by alogps [mg/ml] rutin 0.21 0.15 0.125 3.54 quercetin 1.82 ± 0.32 1.81 0.06 (16 ºc) 0.26 isorhamnetin not available 1.80 not available 0.15 kaempferol 3.11 ± 0.54 1.99 not available 0.10 despite of the fact, that these values are available by various chemical software, experimental data are most precious (rothwell et al., 2005). solubility of aglycones in water is lower than the solubility of glycosides therefore it is necessary to perform hydrolysis of glycosides in water-alcohol solutions. saaz is the former german name of the czech town žatec, known by the hop cultivation. nevertheless, it denotes also a hop variety, classified as one of the four true noble varieties used in production of pilsner style beer. this semi-early red-bine hop, belonging to the old middle european aroma group of hops, originates from the clonal selection in original hops widespread within the saaz and auscha regions. saaz variety is grown in nine clones. its typical property is fine balanced bitterness and the high level of total polyphenols. in fact, in the literature, does not existed sufficient analysis results about flavonols content, especially for these hop genotypes, typical for mentioned region, as well as any indication to biological effect is missing. the aim of this work was firstly: investigation of the content of individual flavonols in the hop clones saaz, secondly – estimation of several biological activities on in vitro level, eventually specification of any relation between flavonols content and biological activity. for the first purpose the hplc analysis was selected and three steps were necessary to accomplish this work: (1) selection of optimal conditions of the glycoside hydrolysis and extraction of flavonols. (2) selection of the optimal mobile phase and the most suitable column with the stationary phase. (3) description of the basic validation characteristics of the flavonols determination. (4) elaboration of analysis of natural samples. secondly, selected assays on in vitro level, carried out with the same hop cone extract samples, aimed to attempt to formulate any relations. 2. materials and methods 2.1 chemicals methanol (hplc gradient grade) was purchased from sigma-aldrich. hydrochloric acid and formic acid (both p.a. purity) were purchased from mikrochem. ultra pure water was prepared with simplicity 185, millipore. standards for hplc: quercetin, kaempferol and isorhamnetin were purchased from sigma-aldrich. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:18 utc 132 maliarová, m. et al. 2.2 calculation of physico-chemical properties the log p values were calculated by alogps 2.1 software accessible on-line on internet (vccl, 2011). 2.3 plant material plant material of dried hop cones was provided by the research institute of plant production piešťany, slovak republic and hop research institute žatec, czech republic. 2.4 hplc analysis the chromatographic apparatus consisted of a model 1525 binary hplc pump, a model 2487 dual λ absorbance detector, a model 2707 autosampler, a model 1500 heather column, and software empower 2 (waters, milford, ma, usa). the optimization of hplc conditions of flavonoids determination in hop extract was performed with the following colons: symmetry® c18, 4.6 x 75 mm, 3.5 μm, x terra® ms c18, 4.6 x 30 mm, 2.5 μm, x bridgetm c18, 4.6 x 50 mm, 3.5 μm (waters, milford, ma, usa). the mobile phase was composed from methanol and ultra-pure water with 0.1 % formic acid. the wavelength 360 nm was selected for detection of all investigated flavonols (quercetin, kaempferol and isorhamnetin). 2.5 enzyme inhibition assays analyses of thrombin, and urokinase inhibition activity in hop cones extracts was determined by simple photometry method using microplate reader opsys (dynex, usa), with following chromogenic substrates: n-α-benzoyl-phenylalanyl-valylarginine-paranitroanilide (bpva-pna) for thrombin, and n-glycine-arginineparanitroanilide dihydrochloride (gapna.2hcl) for urokinase, respectively. substrates were cleaved by thrombin and urokinase according to described methods (erlanger et al., 1961; geiger et al., 1991), released free paranitroaniline was detected at wavelength 410 nm. microplates were prepared manually by gradual dissolution of the substrate -inhibitor mixture. each well (three parallel wells were used for each sample) contained buffer solution with 0.6 mm substrate, 1% dmso (v/v), and tested sample diluted 200 times. control wells contained dmso. reaction was started by adding of enzyme solution (thrombin – 150 nih units.mg-1, urokinase – 500 plough units, respectively) in tris-hcl buffer, ph 7.6, without ca2+ ions and other activators. reaction temperature was 25 °c, data scanning time 1 min and 61 min. the optical density difference ∆od (od61.st.min – od1-st.min) was measured for each sample. the percentage expression of the inhibition activity was calculated in according with equation (eq. 1) and then related to standard epigallocatechin gallate (egcg) and expressed in mg of egcg equivalent (egcgeq.). % inhibition activity = ((1 – (∆od sample/∆od control))*100) (1) bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:18 utc nova biotechnologica et chimica 12-2 (2013) 133 2.6 antioxidant assays bclm (β-carotene linoleate model) is simple model of antioxidant activity in vitro (ohshima et al., 1998). this method quantifies ability of the sample to prevent lipoperoxidation under lipophilic conditions. 2 mg of β-carotene were dissolved in 20 ml of chloroform. 4 ml of this solution were added to the evaporation bank with 40 mg of linoleic acid and 400 mg of tween-40. chloroform was completely evaporated using rotary vacuum evaporator at 50°c and residue was mixed with 100 ml of deionized water to produce β-carotene linoleate emulsion. 230 µl of this emulsion were mixed with 20 µl of tested extract sample in microplate wells. microplates were incubated at 50°c for 90 minutes and the reaction mixtures were measured on β-carotene content decrease at 490 nm. control wells contained pure water and standard wells contained, 90 mm solution of egcg in dmso. this method of antioxidant activity was carried out to use an endpoint photometric measurement of a dual wavelengths mode by using a microplate reader type mrx (dynex). measured data were processed by same way and related to standard epigallocatechin gallate (egcg) and expressed in mg of egcg equivalent (egcgeq.). the second method of determination of antioxidant activity was method of hydrogen peroxide elimination (hpe), based upon the catalytical effect of horse radish peroxidase with combination with fenol red in according to method described by pick and keisari (1980) modified by rakotoarison et al. (1997). 10 µl of tested extract sample was mixed with 10 µl h2o2 and immediately filled to 100 µl by phosphate buffer pbs (ph = 7.4). prepared reaction mixture was subjected to incubation for 15 minutes in thermostat under 37°c. after incubation 100 µl of fenol red solution (0.2 mg/1ml) contained horse radish peroxidase (17 u/1ml) was added and then incubated 15 minutes under room temperature. the reaction is terminated by addition 5 µl 1n naoh (1 n) and od630nm was detected by microplate reader. measured data were processed by mentioned way and related to standard epigallocatechin gallate (egcg) and expressed in mg of egcg equivalent (egcgeq.). 2.7 antimicrobial activity extract samples were tested using microplate dilution method using sterile microplates with u shape wells. microplate preparing: filling columns 2, 3, 4, 5, 6, 7, 8, 9, 10 with 100 μl of cultivation medium with inoculum. then 180 μl of this mixture was added to the column 1, together with 20 μl of tested extract samples. then is carried out the dilution by gradual transfer of 100 μl z from the wells of column 1 to the column 2, mixing then to column 3, 4 ….12. in the columns there are following titer values of tested samples (from the column 1 to column 12): 10, 20, 40, 80, 160, 320, 640, 1280, 2560, 5120, 10240. cultivation medium was nutrient broth with inoculum adapt to 0.04 – 0.06 mcfarland units, for yeast and molds was used malt broth with inoculum adapt to 105 cell per 1 ml using bürker chamber. microplates were cultivated under following conditions: bacterial species for 24 hours bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:18 utc 134 maliarová, m. et al. at 37°c, yeasts 24 – 48 hours at 22°c (24 – 48 hours), and molds 114 hours at 22°c. thirty microliters of 0.02% tetrazolium blue (ttb) solution were added after cultivation and after 30 minutes of incubation under same conditions were microplates measured and evaluate. blue formazane product released by microorganism mitochondrial dehydrogenase has been observed in wells with cell proliferation. the last well without color effect is value of mic parameter expressed in titer scale. 3. results and discussion 3.1 hplc analyze of flavonols in hop cone extracts at first, the simultaneous acid hydrolysis and extraction of flavonols was optimized with regard to concentration of hydrochloric acid, hydrolysis time, and proportion of methanol in the solution (fig. 2). the optimized conditions of hydrolysis of the hop cones are as follows: 1.2 mol/l solution of hydrochloric acid during 1 hour hydrolysis in 50 % methanol-water solution. fig. 2. optimization of the simultaneous acid hydrolysis and extraction of flavonols from hop cones conditions, (♦) quercetin, (■) kaempferol. relation of the retention factor k of flavonols to methanol portion (%) in mobile phase, (♦) quercetin, (■) kaempferol, (▲) isorhamnetin. a good separation was achieved if the composition of mobile phase was 40 – 45 % methanol in water with addition of 0.1 % formic acid. further decrease of the methanol content leads to prolongation of the total analysis time. consequently, the best conditions for hplc separation of flavonols are as follows: mobile phase 0.1% (w/v) formic acid in water and methanol (57:43), flow rate 1 ml/min, column temperature 45°c. under these conditions and using the optimized stationary phase (discussed in the next paragraph) the total analysis time is 6 min. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:18 utc nova biotechnologica et chimica 12-2 (2013) 135 different stationary phases were compared in the final step to obtain the best resolution of the analyzed compounds. when using the columns symmetry and x terra a shift of the retention time tr of the analytes was observed. the shift of the retention time did not appear when the column x bridge was used. the hplc chromatogram obtained with the mentioned best column, optimally selected mobile phase and further optimized conditions is demonstrated on fig. 3. a u 0,000 0,005 0,010 0,015 minutes 0,0 1,0 2,0 3,0 4,0 5,0 6,0 fig. 3. representative hplc chromatogram of a real extract sample: humulus lupulus oswald clone 114. denotation of peaks: i quercetin, ii kaempferol, isorhamnetin detected only in traces. column xbridge, mobile phase 0.1 % formic acid in water/methanol (57:43). basic validation characteristics of the hplc flavonols determination – calibration equation, linear range, coefficient of determination, lod and loq are summarized in table 2. table 2. selected validation characteristics for the hplc determination of three flavonol aglycones. flavonols calibration equationa linear range [μg/ml] r2 b lod c [μg/ml] loqc [μg/ml] quercetin y = 17275x – 960.3 0.134 – 8.16 0.9997 0.0726 0.090 kaempferol y = 18287x – 636.1 0.0437 – 3.18 0.9997 0.0509 0.0745 isorhamnetin y = 14955x + 43.94 0.025 – 0.100 0.9937 0.0272 0.0572 a y = peak area, x = concentration of standard in μg/ml b r2 − coefficient of determination for 8 data points in calibration curves. two parallel measurements were made for each calibration standard. c lod − limit of detection, loq − limit of quantification. before hplc analysis of the particular hop plant material it is important to verify the stability of three investigated important flavonols in the solution during hydrolysis. therefore the solutions of flavonols were subjected to model hydrolysis (reflux, 1.2 mol/l hcl in 50 % water/methanol solution for 2 hours). the model solutions were analyzed in 15 min intervals. flavonols concentration was not significantly i ii bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:18 utc 136 maliarová, m. et al. changed during 60 min, however, after 105 min a significant decrease of the concentration of all three flavonols was observed (not presented in this paper). in the application part of this study seven varieties of saaz, harvested during year 2009, were analyzed: zlatan, lučan, and the oswald clones 31, 70, 71, 72, 114 (table 3). the content of quercetin was found in the range 489 – 1092 µg/g and that of kaempferol 218 – 568 µg/g of the dry hop cones. the content of isorhamnetin was very low in all varieties, which caused a relatively high rsd values. it is worth to compare that the similar quercetin content was found in the hop cones of variety „sbornyi“ − 1000 μg/g of the dry hop matter (alekseeva et al., 2004). to discuss about obtained results it is very difficult because there are no published papers about analysis of hope cone from žatec region, moreover there are several papers aimed to identification of flavonols by ms without quantification (magalhães et al., 2010). table 3. contents of flavonols and biological activity of dry hop cones. concentration of the saaz clones of humulus lupulus l. in [μg/g] ± % sd flavonols lučan zlatan oswald clone 31 oswald clone 70 oswald clone 71 oswald clone 72 oswald clone 114 quercetin hplc [μg/g] ± sd 783.3 ± 2.9 783.3 ± 2.4 792.8 ± 0.8 771.3 ± 7.2 489.5 ± 9.7 822.9 ± 3.6 1091 ± 4.2 kaempferol hplc [μg/g] ± sd 284.8 ± 4.0 338.5 ± 2.3 396.7 ± 3.3 402.3 ± 8.4 217.7 ± 7.6 314.0 ± 5.8 568.0 ± 6.1 isoramnetin hplc [μg/g] ± sd traces traces traces 21.4 ± 13.8 16.5 ± 6.8 traces traces 3.2 biological assays of hop cone extracts in vitro the same sample of extract from hop cones were subjected to several assays in vitro, especially to two test of antioxidant activity, either test of inhibition activity on thrombin as potential pathophysiological promoter of cardiovascular coagulation diseases or test of inhibition activity to urokinase as expression of ability to suppress processes of metastasis and onco-transformed cell spreading. fig. 4 presents mentioned biological activities of six hop cones extracts (zlatan, lučan, oswald's clones 31, 70, 71, 72, 114). there is evident (fig. 4) relative high level of inhibition activity on both enzymes, higher on thrombin for lučan, zlatan and oswald's clones k-70, 71, and for urokinase in case of k-72 and k-114. these indicated certain level of ability to block undesired processes of coagulation cloth formation and extracellular matrix degradation in relation to cardio-vascular diseases or metastasis formation, respectively. these results do not correlate with amount of estimated flavonols what could be explained by the in vitro effect of other active compounds – extractives from hop cones – bitter acids, terpens and others. it was published that the 8-prenylnaringenin (8-pn) as one component of hop extract inhibits platelet aggregation induced by thrombin (di vito bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:18 utc nova biotechnologica et chimica 12-2 (2013) 137 et al., 2012) but comparison to complex hop cones extract it is not possible, not published yet. fig. 4. inhibition activities on thrombin (ia_thrombin), urokinase (ia_urokinase), expressed by egcg equivalent in mg/g of native matter, further antioxidant activities by bclm method (aox_bclm) and by hpe method (aox_hpt), expressed as trolox equivalent in mg/g of native matter for six different hop genotypes. all tested categories are on the level of statistical significance with p<0,1 to control. opposite this, antioxidant of hop, hop extract, hop cones were published relatively frequently (lermusieau et al., 2001; yamaguchi et al., 2009; tronina et al., 2013), but differences in applied methods by various labs does not allow systematic comparison. similarly, level of the antioxidant activity is relative high, but intensively varied between tested samples, the highest for genotype k-114 and the lowest level has been observed for genotype k-71, what indicates rough correlation to flavonoid content. concerning to obtained results flavonoids seem to be major compounds of hop cone extracts responsible for antioxidant effect by both used methods. image about biological activity of hop cones extract was completed by test of antimicrobial activity towards g+ bacterial species staphylococcus aureus, gbacterial species pseudomonas aeruginosa and escherichia coli, yeast candida albicans and two cereal fungal pathogens fusarium graminearum. and pyrenophora teres. the results presents following table 4. from the results it is evident high level of antimicrobial activity to cereal pathogen pyrenophora teres, and relatively low activity to clinical bacterial pathogens and yeast with myceliar form candida albicans. from the comparison point of view between tested hop cones extract samples are statistically not significant differences. in fact, several papers published antibacterial effect of hop extracts (natarajan et al., 2008; leite et al. 2013) but certain level of antibacterial effect could be explained by flavonols too (waage and hedin, 1985; sivasothy et al., 2013). bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:18 utc 138 maliarová, m. et al. generally we can conclude that hop cones and preparations from them are valuable raw material with significant biological activities expressed in vitro. table 4. antimicrobial activities of six hop cones extract samples to selected microbial species. antimicrobial activity mic (titer) genotype lučan zlatan k-31 k-70 k-71 k-72 k-114 staphylococcus aureus 20 10 10 10 10 10 10 pseudomonas aeruginosa 10 10 10 10 10 10 10 escherichia coli 20 10 20 20 20 20 10 candida albicans 40 10 10 20 20 20 20 fusarium graminearum 10 10 10 10 10 10 10 pyrenophora teres 80 160 20 20 80 160 20 4. conclusions the rp-hplc method reported here represents a simple and rapid technique for simultaneous determination of important flavonol aglycones as quercetin, kaempferol and isorhamnetin contained in the hop cone extracts. for seven tested saaz clones, this is the first report regarding the conditions of the hplc determination of flavonols. the highest content of quercetin and kaempferol was determined in oswald's clone 114. in general, obtained results indicate surprisingly high degree of biological activities expressed in vitro and finally conclusion that hop cones are valuable material for other applications, others than beer production. acknowledgements: this work was realized under support of the project vega 1-0233-12 and vega 11188-12. the authors are thankful to prof. ing. jan mocak, drsc.† for this valuable discussion an encouragement in this research direction. references alekseeva, m.a., éller, k.i., arzamastsev, a.p.: determining polyphenolic components of common hop by reversed – phase hplc. pharm. chem. j. 38, 2004, 687 – 689. di vito, c., bertoni, a., nalin, m., sampietro, s., zanfa, m., sinigaglia, f.: the phytoestrogen 8-prenylnaringenin inhibits agonistdependent activation of human platelets. biochim. biophys. acta. 1820, 2012, 1724-1733. erlanger, b.f., kokowsky, m., cohen, w.: the preparation and properties of two new chromogenic substrates for 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j. ethnopharmacol. 116, 2008, 383 – 396. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:18 utc nova biotechnol chim (2022) 21(2): e1319 doi: 10.36547/nbc.1319 1 nova biotechnologica et chimica evaluation of extracellular cellulolytic potential of selected natural strains of a novel fungus sordaria fimicola isolated from evolutionary canyon under submerged fermentation wajiha zaka ansari1,2,, asifa irshad kayani3, amjid khan2, amir muhammad khan2, saman shahid1, zainab shahzadi1 and hanan mukhtar1 1department of botany, lahore college for women university, near wapda flats, jail rd, jubilee town, lahore 54000, punjab, pakistan 2department of botany, university of mianwali, mianwali, university rd mianwali 42200, punjab, pakistan 3department of botany, kinnaird college for women, 93 jail rd, g.o.r. i, lahore 54000, punjab, pakistan  corresponding author: wajihazaka44@gmail.com article info article history: received: 10th december 2021 accepted: 24th march 2022 keywords: cellulase enzyme activity evolutionary canyon optimization purification submerged fermentation abstract industrial biotechnology has a great emerging demand and sustainable expansion for mankind to utilize a variety of biodegradable material for the production of various alternative energy resources such as biogas and bioethanol. researchers are interested in exploitation of novel fungal strains for the production of extracellular cellulase from the last few decades. this study was designed to assess the extracellular cellulase production potential of novel fungal strains of sordaria fimicola first isolated from the evolution canyon, three located on south facing slope with xeric (s1, s2, s3) and other three on north facing slope with mesic (n5, n6, n7) environmental conditions. based on initial and secondary screening two hyper producer strains from each slope were selected. the best activity for s2 was 3.125 u/ml and n6 exhibited 2.829 u/ml under optimized conditions of 14 d of incubation at 30 oc, ph 6.0, 1 ml inoculum and with 2% substrate (carboxy-methyl cellulose) concentration. among the tested carbon and nitrogen sources, glucose proved to be best for both strains with s2 exhibiting maximum activity. peptone and beef extract proved to be the best nitrogen sources for s2 and n6 respectively. the cellulase after characterization for temperature and ph showed slightly thermophilic nature. the cellulase was partial purification the highest cellulase activities as surviving in more xeric conditions which contribute more resistive and productive features in those microorganisms living in the harsh environment. introduction extracellular cellulases are the most important group of enzymes that hydrolyze lignocellulosic biomass to glucose subunits. cellulases are composed of three main components: exoglucanases, endoglucanases, and βglucosidases (behera and ray 2016). hydrolytic cellulase converts lignocelluloses to sugars by the process of fermentation. cellulose is composed of long polymers of β 1-4, linked glucose units and forms a proper crystalline structure. cellulose, hemicellulose, and lignin are hydrolyzed by the complete action of extracellular cellulase (fang and xia 2015; hansen et al. 2015). enzymes isolated from microorganisms are gaining much attention due to their potential for various mailto:wajihazaka44@gmail.com nova biotechnol chim (2022) 21(2): e1319 2 industrial applications. industrially, there are in great demand as compared to intracellular enzymes because of their cost-effectiveness as well as their high stability (adrio and demain 2014). many researchers are always interested in exploring the new potential fungal strains for the enhancement of cellulase production to complete the industrial enzyme demand in future. the enzymes isolated from the fungi are generally regarded as safe (gras) as compared to bacteria because they are cheap, easy to culture and more economical (kumar 2020). the production of biofuel and bioethanol from lignocellulosic material is a potential application of cellulase which is widely used in internal combustion engines as a good substituent for gasoline (kuhad et al. 2011; gusakov and sinitsyn 2012). sordaria fimicola is a well-known homothallic coprophilous fungus that regulates the nutrients in the herbivore dung. it was first isolated from the evolutionary canyon of israel. evolutionary canyon is considered as the model microsite to study the environmental changes and the adaptive behavior of the species (pavlíček et al. 2008). a dramatic biotic contrast is displayed by the two opposite slopes which are 100 – 400 m apart from each other. african slope or south facing slope (sfs) exhibit more tropical conditions due to high solar radiation, high temperature, and more xeric conditions, more fluctuating and more heterogeneous, as they have savannah-like biota. on the contrary, the european slope or the nort facing slope (nfs) display a temperate environment, mesic conditions, lush green vegetation and maquis live-oak brushwood (nevo 2006; arif et al. 2017). s. fimicola is commonly found in animal dung and rotting vegetation, also present on wood, seed, and soil because of its slightly thermophilic nature. they are considered as the important control agents and a potential source to produce enzymes and antibiotics (lamb et al. 1998). the fermentation technology used has a significant impact on the success of cellulase production. a variety of fermentation techniques are available for cellulase production; however, the most used technologies are submerged and solid-state fermentation (sajith et al. 2016). initially enzymes were obtained from submerged fermentation due to easy handling and greater control of various physical and chemical environmental factors (ahmed et al. 2017). on the contrary, ssf decreases the cost of enzyme production and improves the yield (hareesh et al. 2016). but ssf is labor intensive and needs a longer lag time, large inoculum size due to which the current research was conducted on submerged fermentation (gowthamana et al. 2001). the aim of this report is to study the extracellular cellulase production from sordaria fimicola under smf (submerged fermentation) by optimizing various physical and chemical parameters, characterization for ph and thermo-stability and partial purification by salting out and dialysis. experimental fungal sample collection and sub-culturing six different strains (s1, s2, s3, n5, n6, and n7) of sordaria fimicola were collected from fungal culture bank, university of the punjab, lahore, pakistan. all the samples were made identified and stored at 4 oc before use. after sample collection, all the strains were sub-cultured immediately on potato dextrose agar. fungal strains were inoculated in form of small discs in triplicates. all the cultures were incubated at 25 oc in incubator. screening of fungal samples for extracellular cellulase primary screening of cellulase was carried after the growth of all strains of sordaria fimicola. the media provided for growth was prepared by adding 2 % carboxy-methyl cellulose as a substrate with potato dextrose agar and incubated with ph 5.5 at 25 oc for ten days. after ten days of incubation, all the plates were flooded with congo red stain for 15 – 30 min. the plates were washed with distilled water and then 1m nacl solution was added in all petri plates for 15 – 20 min. the zone of cellulase hydrolysis was clearly appeared around each colony of fungus. the zone of hydrolysis was measured in cm (khokhar et al. 2012; pavani et al. 2013). nova biotechnol chim (2022) 21(2): e1319 3 production of extracellular cellulase under submerged fermentation (smf) potato dextrose broth was supplemented with 2 % cmc as substrate was used for cellulase production in submerged fermentation. fungal isolates were inoculated in a 100 ml shake flask with 25 ml of cellulase production medium (pdb and 2 % cmc). all the fungal isolates were inoculated with 1 ml of fungal spore suspension containing 105 spores. all the flasks were incubated in shaking incubator for 14 – 21 d in triplicates at 30 oc with the ph 5.0. the samples were withdrawn at regular intervals for determination of enzyme activity through spectrophotometer at 540 nm (sajith et al. 2016). optimization of fermentation cultural conditions and extracellular cellulase production different parameters were taken for the production optimization of extracellular cellulase such as temperature (20 oc, 30 oc, and 40 oc), ph (4.0, 5.0, and 6.0), incubation period (7, 14, and 21 days), inoculum concentration (spore suspension of 0.5 ml, 1 ml, 1.5 ml, 2 ml, 2.5 ml, and 3 ml), substrate concentration (0.5 %, 1 %, 2 %, 3 %, and 4 % cmc), carbon sources (glucose, maltose and lactose) and nitrogen source such as peptone, beef extract and ammonium sulphate). all the experiments were done in triplicates and values are with ± standard deviation (okoye et al. 2013; saini et al. 2017). crude enzyme extraction after optimization with each cultural condition, 25 ml of filtrate from all the samples was collected and centrifugation was performed at 6,000 rpm for 15 min. the supernatant was taken as crude enzyme and further used for enzyme assay. biomass of mycelia was also calculated (karthikeyan et al. 2011). cellulase activity by carboxy-methyl cellulase (cmcase) assay dns method was used for the determination of enzyme activity (miller 1959). in this method, during the standard reaction conditions, 1 ml of crude enzyme was incubated with 1 ml of 1 % cmc as a substrate in 0.1m sodium acetate buffer for 30 min at 40 oc in water bath. the reaction was stopped by adding 3 ml dns (dinitrosalicylic acid) reagent. optical density was measured at 540 nm by spectrophotometer. one cellulase unit was determined as the amount of enzyme that releases 1 micromoles of glucose per minute (martins et al. 2008). total protein estimation bradford protein assay method was used to determine the protein concentration for all samples of fungus in the crude enzyme. 1ml of crude enzyme was reacted with 2 ml of bradford reagent and the mixture was kept at room temperature for 45 min. total protein of crude enzyme after optimization with each parameter was calculated at the absorbance of 595 nm (bradford 1976). characterization of crude enzyme the cellulase enzyme produced under optimized condition was characterized to check the optimum ranges of ph (4.0, 4.5, 5.0, 5.5, 6.0, 6.5, 7.0, 7.5, and 8.0) and temperature stability (30, 35, 40, 45, 50, 55, and 60 oc) (hamdan and jasim 2018). partial purification of crude cellulose the crude enzyme was partially purified by salting out with ammonium sulfate and dialysis. the enzyme collected after salting out and dialysis was assessed for protein estimation and enzyme activity to check the folds of purification. salting out was carried out by taking 20 ml of crude enzyme and brought to 80 % saturation with the solid ammonium sulfate. the mixture was placed overnight at 4 oc in a magnetic stirrer. centrifugation of the mixture was performed for 15 minutes at 6,000 – 8,000 rpm. the pellet formed was dissolved in 50 mm sodium acetate buffer having ph of 5.5. after salting out, the enzyme was subjected to determine the enzyme activity (elakkiya and nova biotechnol chim (2022) 21(2): e1319 2 muralikrishnan 2014). the enzyme collected after ammonium sulfate precipitation was dialyzed in a dialyzing bag. 8 ml of enzyme was dialyzed against 30 mm sodium acetate buffer with three different changes of buffer. the enzyme collected after dialysis was assessed for protein estimation and enzyme activity to check the folds of purification (hafiz et al. 2011). statistical analysis all the experimental work was carried out in triplicates. for statistical analyses of data statistix program, version 8.1 was used, and data were analyzed for analysis of variance (anova) using lsd p ≤ 0.05. mean values were separated (p ≤ 0.05) and represented by different letters both in tables and figures along with ± standard error. results and discussion primary screening of extracellular cellulase from fungal samples the cellulolytic potential of fungal strains was observed for the primary screening of cellulases by congo red method. a clear zone of hydrolysis was observed around each colony (fig. 1). all the fungal strains show extracellular cellulose activity. among s strains, s2 was observed as the hyper-producer and show the maximum zone of hydrolysis around its colony which was 4.81 cm. in the case of n strains, n6 shows the maximum zone of hydrolysis measured was 4.52 cm. it was concluded that both the strains have the potentiality for cellulase production. the results are similar with the findings of el-nahrawy et al. (2017), they selected twenty isolates of aspergillus tubingensis. all the isolates showed zone of hydrolysis ranges from 1.14 – 4.1 cm. the highest zone of hydrolysis was produced by f7 which was 4.1 cm. fig. 1. clear zone of hydrolysis (cm) shown by six different strains of s. fimicola in pda containing cmc. 4 nova biotechnol chim (2022) 21(2): e1319 3 secondary screening of six different fungal strains for extracellular cellulases under submerged fermentation submerged fermentation was chosen rather than solid state fermentation as the liquid medium is easy to handle and does not require extra labor work as in case of solid-state fermentation. initially, all the strains were cultured in broth for fermentation. it was carried for only confirmation of results which were achieved by the primary screening of cellulase enzyme. the results showed in (fig. 2) that among all the natural strains of s. fimicola, only s2 and n6 were observed as the hyper-producer celluloytic strains and the enzyme activities of s2 and n6 were 0.875 u/ml and 0.825 u/ml respectively and were selected for further investigations. submerged fermentation is an aerobic fermentation process that provides a long culture period. during submerged fermentation adequate oxygen, cell growth and metabolism are maintained (gomathi et al. 2012; jiang et al. 2013). fig. 2. secondary screening for extracellular cellulase production from six different strains of s. fimicola by smf. means followed by different letters are significantly different according to anova, lsd at p ≤ 0.05 (least significant difference). optimization of cultural conditions for cellulase production under submerged fermentation by two selected strains of s. fimicola the enzyme production was optimized under different parameters such as ph, temperature, time of incubation, inoculum size, substrate concentration, carbon, and nitrogen sources. effect of different temperature on enzyme activity temperature is a crucial factor for the growth of microorganisms. results showed (fig. 3a) that the optimum temperature was 30 oc for cellulase production in submerged fermentation for both the strains. s2 revealed maximum enzyme activity (0.95 u/ml) as compared to n6 (0.8 u/ml) because s2 survive in harsh conditions which will ultimately contribute to high yield. the results of the current study confirmed that s. fimicola is slightly thermophilic in nature. findings of this study agree with irfan et al. (2016) and kumar et al. (2012) who reported 30 oc optimum temperature for endoglucanase production. higher temperature ranges from 50 to 60 oc causes denaturation of the enzyme. the optimum temperature for cellulase production also depends on the strain variation (murao et al. 1988). effect of different ph on enzyme activity the effect of ph was determined for cellulase production, and the highest enzyme activity was shown by s2 (1.175 u/ml) and n6 (1.025 u/ ml) at ph 6.0 (fig. 3b). among s2 and n6, s2 revealed the highest enzyme production than that of n6. similar findings were reported that initial medium ph of 6 is suitable for maximum cellulase production (juhasz et al 2004; akinola et al 2012). extreme low and high ph cause instability of enzyme as they are protein which generally denatured at very extreme ph (nidetzky et al. 1998). effect of incubation period on enzyme activity the incubation period was determined by checking the enzyme activity from 3 to 21 d. the optimum production for both the strains showed the ideal incubation period was 14 d (fig. 3c). s2 showed more enzyme activity (1.15 u/ ml) as compared to n6 (0.975 u/ ml) after 14 days of incubation. according to el-hadi at al. (2014), the ideal incubation period for production of cmcase from aspergillus hortai was 96 h under submerged fermentation. but in case of s. fimicola, it completes its life cycle in 10 d of incubation. 5 nova biotechnol chim (2022) 21(2): e1319 3 therefore, the incubation of s. fimicola is different from a. hortai to produce extracellular cellulase enzyme. fig. 3. optimization of cultural conditions (a) effect of different temperature, (b) effect of different ph, (c) effect of different incubation period, (d) effect of different inoculum concentrations, (e) effect of different substrate (cmc) concentrations (f) effect of carbon sources (g) effect of nitrogen sources. means followed by different letters are significantly different according to anova, lsd at p ≤ 0.05 (least significant difference). 6 nova biotechnol chim (2022) 21(2): e1319 3 effect of inoculum concentration on enzyme activity inoculum of 1ml in both strains of fungus yields more enzyme production. s2 showed more enzyme activity as 1.175 u/ml as compared to n6 as 0.9 u/ml (fig. 3d). enzyme activities of both strains decrease until 3ml of inoculum due to the decrease in microbial growth. microbial growth decreases due to competition for space and nutrient among the cells which causes nutrient depletion (omojasola et al. 2008). decreased inoculum size may not be enough for the growth initiation of the species which directly affects the enzyme production. irfan et al. (2011) reported that aspergillus niger showed highest cmcase production with 3 % inoculum level. effect of substrate concentration on enzyme activity cellulase activity was observed at different substrate concentrations (fig. 3e) and it was observed that 2 % cmc act as the ideal substrate concentration for both the strains of s. fimicola for the highest production of extracellular cellulase. s2 showed maximum enzyme activity (1.174 u/ml) than that of n6 (0.983 u/ ml) at 2 % substrate concentration. similar results were reported from the findings of irfan et al. (2010). it reduces after a certain percentage of the substrate due to extra availability of nutrients and increased biomass and as a result, minimization in the metabolic activity. supplementation of excessive substrate concentration causes high viscosity and decreases the probability of the substrate to bind with the active side of the cellulase enzyme (nagah et al. 2016). effect of carbon source on enzyme activity the effect of carbon sources was studied by adding 2 % of three different carbon sources namely, sucrose, glucose, and lactose into the culture medium. among these the glucose proved to be the best carbon source (fig. 3f) resulted in producing high yield for the enzyme in s2 (1.296 u/ ml) and for n6 (1.042 u/ ml). the other two carbon sources cause a reduction in enzyme activity. similar results were obtained by the findings of nathan at al. (2014) that only the glucose results in maximum cellulase yield as compared to the other carbon sources. irfan et al. (2016) reported that fermentation medium supplemented with glucose results in high yielded cellulases from trichoderma harzianum. effect of nitrogen source on enzyme activity effect of nitrogen source on cellulase activity revealed (fig. 3g) that highest production of cellulase was attained by adding peptone in culture medium in case of s2 (1.241 u/ml) and beef extract in case of n6 (0.978 u/ml). ammonium sulfate is considered as the lowest enzyme-producing nitrogen source in case of both the fungal strains. the results are in accordance with the work of acharya et al. (2008) who reported that the maximum yield of cellulase is produced by adding organic solvents such as peptone and yeast extract in the medium. prasanna et al. (2016) and kathiresan and manivannan (2010) investigated that penicillium sp produced maximum cellulase enzyme when cultivated in the liquid broth containing yeast extract. characterization of cellulase crude cellulase enzyme produced under optimized conditions was also characterized for ph and temperature stability. the results revealed that it has the ph ranged from 4.5 to 5.5 (fig. 4a) and temperature optima ranged from 40 to 50oc (fig. 4b). several studies have reported that endoglucanases remain active at the temperature ranges from 50 – 70 oc (bai et al. 2013; boonchuay et al. 2016). for example, endoglucanase from a. niger z10 shows thermal stability at 40 oc (coral et al. 2002). karboune et al. (2008) reported the optimum temperature of 65 oc for cmcase from penicillium funiculsoum. the thermostability and ph stability of cellulase production also depend upon the strain variation of the microorganism. rahnama et al. (2016) revealed that trichoderma harzinum has maximum enzyme stability at ph of 4.5. picart et al. (2007) reported the optimum ph of 4.5 for 7 nova biotechnol chim (2022) 21(2): e1319 2 carboxymethyl cellulase from penicillium sp. 1.68 2.25 2.93 3.03 2.53 2.39 1.83 1.42 1.73 2.64 2.32 2.16 1.83 1.62 0 1 2 3 4 5 6 30 35 40 45 50 55 60 e n z y m e a c ti vi ty (u /m l) temperature oc n6 s2 b fig. 4. characterization of cellulose. (a) enzyme stability at different ph. (b) enzyme stability at different temperature. means are significantly different according to anova, lsd at p ≤ 0.05 (least significant difference). partial purification of crude cellulase cellulase produced under optimized cultural conditions was partially purified. from the results (table 1), it was observed that the purification fold increases 2.7 folds in case of s2 and 1.5 folds in n6 with yield 80.2 % and 79 % respectively after dialysis. jabbar et al. (2008) purified endoglucanases from gymnoascella citrina by gel filtration chromatography and the result revealed that purification fold increases 27.3 folds with 25.5 % yield. sulyman at al. (2020) confirmed that the purification of cellulase from aspergillus niger increases 68.1 folds when crude enzyme was treated with sephadex g-100 gel filtration. table 1. different enzyme activities and specific activities of crude enzyme, enzyme after partial purification were estimated and their folds of purification were also determined. purification step enzyme activity [u/ml] specific activity [u/mg] yield [%] purification folds s2 n6 s2 n6 s2 n6 s2 n6 crude enzyme 3.03 1.88 1.07 1.16 100 100 1 1 salting out 2.78 1.67 2.32 1.39 91 88 2.2 1.2 dialysis 2.43 1.49 2.86 1.72 80.2 79 2.7 1.5 conclusion the researchers are interested in isolating novel fungal strains and exploring their potential to produce extracellular enzymes at a low cost to complete the industrial enzyme demand in future. the conducted research study demonstrates the first-time production of cellulase enzyme from s. fimicola. it was accomplished that s2 strain resulted in maximum cellulose production under optimized conditions by using submerged fermentation technique because it developed greater resistivity due to more harsh conditions. the biomass of both strains increased up to 14 days on incubation. after that, it starts decreasing due to nutrient depletion. the enzyme shows a slightly thermophilic and acidic nature when characterized for ph stability and thermostability. the partially purified enzyme shows purification folds greater than that of crude enzyme. the results showed that s. fimicola is a good potential fungal strain and can be exploited on an industrial scale to production second8 nova biotechnol chim (2022) 21(2): e1319 3 generation biofuel by degrading agro-industrial wastes or lignocellulosic biomass at a low cost. conflict of interest the authors declare that they have no conflict of interest. references acharya pb, acharya dk, modi ha (2008) optimization for cellulase production by aspergillus niger using saw dust as substrate. afr. j. biotechnol. 7: 4147-4175. adrio jl, 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with the regeneration of protoplasts. we found that protoplasts are formed directly in cultivation media under submerged conditions in the presence of lytic enzyme. actinophage μ1/6 endolysin and lysozyme were used in this study. streptomyces strains were cultivated in several media with glycine and lytic enzyme for 24 and 48h. the highest amounts of protoplasts (about 3 x 107 cfu/ml of cultivation medium) together with the highest regeneration (95%) and transformation frequency (about 2 x 106 – 107 cfu/µg dna) were obtained reproducibly in yeme medium with high sucrose content. s. aureofaciens b96, as hardly transformable strain because of difficulties with protoplast preparation and their further regeneration, was used in this study. the same procedure was applied to s. lividans 66 tk24 and s. coelicolor a3(2), streptomycetes model strains, to confirm the general use of this method. moreover, such cultivation process was appropriate for additional quick isolation of either chromosomal as well as plasmid dna that could be further used in recombinant dna techniques. keywords: streptomyces, protoplasts, transformation, lysozyme, actinophage µ1/6 endolysin 1. introduction streptomyces are unusual among bacteria in growing as mycelial colonies with sporulating aerial hyphae. they are known for degradation of numerous macromolecules and synthesis of a wide range of antibiotics and other commercially important secondary metabolites. the complex life cycle of these bacteria includes formation of substrate mycelia, aerial hyphae and spores (pigac and schrempf 1995). the study of the genetics of streptomyces is important not only because of many antibiotics, but also because its differentiation and its regulation of secondary metabolism are of basic interest (ochi 1982). the preparation and regeneration of protoplasts are major steps following genetic manipulations such as fusion, transfection and transformation of streptomyces species. despite there have been reports of “natural” transformation and transfection of streptomyces cultures, there is no such system generally applicable to most species (kieser et al. 2000). besides transfection and transformation, there have been further means of plasmid transfer described. intergeneric conjugation, using escherichia coli as a donor, allows constructing and manipulating recombinant plasmids in e. coli and subsequently transferring them into streptomyces (paranthaman and 36 brnáková, z. et al. dharmalingam 2003; hou et al. 2008). further alternative to using chemicals for promoting an uptake of dna by cells is electroporation. protoplasts of s. venezuelae and some other streptomycetes, formerly not transformable by the standard protocol, were successfully transformed by electroporation (pigac and schrempf 1995). in addition, protoplast fusion is widely used for genome shuffling among interspecies and intergenetic microorganisms (imada et al. 2002; el-gendy et al. 2008; xu et al. 2008). though, the most of aforementioned methods require preparation of protoplasts and their successful regeneration. it has been found that the regeneration frequency of the protoplasts varies according to the species used and high regeneration frequency is limited to a narrow range of streptomyces species (shirahama et al. 1981, imada et al. 2002). for the further study of genes in various streptomyces it was necessary to develop procedures for efficient protoplast regeneration and plasmid transformation remembering also the potential presence of the restriction-modification system (matsushima and baltz 1985; matsushima et al. 1987; godány et al. 1991; muchová et al. 1991). the aim of this study was to try the effect of lytic enzymes, mainly actinophage μ1/6 endolysin, on protoplast preparation during cultivation under submerged conditions. up to now, this kind of procedure has not been reported. this work describes an easy and effective method for preparation of protoplasts from streptomyces species, mainly streptomyces aureofaciens b96, by cultivation in liquid medium containing lysozyme or actinophage μ1/6 endolysin. furthermore, cultivation with lytic enzyme facilitates the isolation of chromosomal and plasmid dna. 2. materials and methods 2.1 bacterial strains and plasmids streptomyces strains used in this study: s. aureofaciens b96 (collection of microorganisms, institute of molecular biology sas bratislava); s. coelicolor a3(2), and s. lividans 66 tk24 (hopwood et al. 1985). shuttle promoter-probe vector pkj2 (nazarov et al. 1990) was used as a control for transformation of protoplasts. 2.2 culture conditions and solutions streptomyces sp. were cultivated in tsb (tryptone soya broth powder, oxoid; containing 0.7% glycine), tssb (tsb + 10.3% sucrose, 0.7% glycine, serva), nb (nutrient broth no. 2, imuna šarišské michaľany; containing 0.7% glycine), nbs (nb + 10.3% sucrose and 0.7%glycine), yeme (prepared according to kieser et al. 2000, containing 0.7% glycine), sterile p buffer (prepared according to kieser et al. 2000) and 25% peg 1000 in t buffer (prepared according to kieser et al. 2000), lysozyme water solution (applichem, 40mg/ml, filter sterilized), actinophage μ1/6 endolysin (farkašovská et al. 2003, 5mg/ml), appropriately dried plates no. 16m (10.3% sucrose, 1.5% dextrin, 0.001% urea, 0.005% nacl, 0.005% k2hpo4, nova biotechnologica 8-1 (2008) 37 0.005% mgso4, 0.5% peptone, 0.1% beef extract, 2ml/l trace element solution (kieser et al. 2000) and 3% agar, ph 7.2). solutions used further in this study: thiostrepton (calbiochem, 50mg/ml in dmso), te buffer (10mm tris-hcl, ph 8, 1mm edta), neutral phenol-chloroform (1:1, equilibrated with te buffer, ph 8), acid phenol-chloroform (1:1, equilibrated with water), 3m sodium acetate ph 4.8. 2.3 growth of streptomyces mycelium for protoplasts preparation 10 ml of sterile media containing lysozyme (serva, final concentration 1mg/ml and 2mg/ml, respectively) or actinophage μ1/6 endolysin (final concentration 0.15mg/ml and 0.3mg/ml, respectively) in 100ml erlenmeyer flasks were inoculated with 200μl of dense spore suspension (prepared according to kieser et al. 2000). the lytic enzyme (lysozyme or endolysin) was added either immediately with inoculum or after 8h of incubation. flasks were incubated at 30°c on rotary shaker for 24 and 48 hours while testing the suitable medium for protoplast preparation. in the next step, 10 ml of tsb with glycine, but without lytic enzyme, was inoculated with 1ml of dense spore suspension. the flasks were incubated at 30°c on rotary shaker for 20 – 24 hours. after that, 1x106 of colony forming units (cfu) were used as inoculum to 25 ml of yeme medium with lytic enzyme (apart from the control flask) and incubated for 24 and 48 hours. the culture medium was poured into screw cap bottle and centrifuged. the supernatant was discarded and the pellet was suspended in 10 ml of p buffer. suspension was filtered through cotton wool (using a filter tube) and transferred into a plastic tube. the protoplasts were collected by centrifugation at 2800 rpm. pellet was resuspended in 500μl of p buffer. 2.4 transformation of protoplasts transformation of protoplasts with pkj2 plasmid dna was done according to hopwood et al. (1985) rapid small-scale procedure and plated on 16m agar plates (regeneration medium, 10.3% sucrose, 1.5% dextrin, 0.001% urea, 0.005% nacl, 0.005% k2hpo4, 0.005% mgso4, 0.5% peptone, 0.1% beef extract, 2ml/l of trace element solution (hopwood et al. 1985) and 3% agar, ph 7.2). after 20h incubation at 30°c the agar plates were overlaid with 1ml of thiostrepton (300μg/ml water solution), dried and incubated at 30°c for 2 – 3 days. 2.5 isolation of streptomyces “total” dna 1ml of medium after 24 and 48h incubation was centrifuged and neutral phenolchloroform was added to supernatant. the extraction from phenol-chloroform was repeated until the white interface was seen. the dna was precipitated from supernatant by adding 1/10 volume of 3m sodium acetate and 1 volume of isopropanol. after incubation at room temperature and centrifugation, the pellet was 38 brnáková, z. et al. washed by 96% ethanol and dried slightly. then, the pellet was dissolved in 50μl of te buffer and the presence of isolated dna was confirmed by 0.9% agarose gel electrophoresis using ethidium bromide detection. 2.6 isolation of plasmid dna for this part of work, pkj2 transformants of s. aureofaciens, s. lividans and s. coelicolor were used as inoculum. 1ml of culture medium after 24 and 48h incubation was centrifuged and acid phenol-chloroform was added to supernatant. mixture was vortex mixed and centrifuged. the supernatant was removed, leaving the white interface behind. 1/10 volume of 3m unbuffered sodium acetate and 2 volumes of 96% ethanol was added to supernatant and mixed. mixture was incubated at –20°c and then centrifuged. the pellet was dissolved in 500μl of te buffer and the solution was extracted by neutral phenol-chloroform until no white interface was seen. 1/10 volume of 3m unbuffered sodium acetate and 2 volumes of 96% ethanol was added to supernatant and mixed. mixture was incubated at –20°c and then span. the pellet was dissolved in 25μl of te buffer, visualized in 0.9% agarose gel electrophoresis using ethidium bromide detection and 5μl of such solution was used for transformation into protoplasts. 3. results and discussion 3.1 protoplasts preparation polyethylene glycol (peg)-mediated plasmid transformation of protoplasts had allowed the rapid development of gene cloning in various streptomyces species, particularly in s. lividans 66, s. ambofaciens, s. coelicolor a3(2), s. fradiae, and s. rimosus, as well as in some others (pigac and schrempf, 1995). this transformation procedure has been generally applicable to several streptomyces species, although it has been necessary to optimize growth and establish the optimal conditions for protoplast formation and regeneration. moreover, the transformation of the fragile protoplasts has been tedious and frequently not reproducible; thus, numerous streptomyces strains could not be proven to be transformable. preparation of protoplasts is essential for further genetic manipulations, such as transformation, transfection (kieser et al. 2000), electroporation (pigac and schrempf, 1995) or protoplast fusion (xu et al. 2008), known so far. furthermore, there has been considerable interest in the use of the intergeneric conjugation as a means of plasmid transfer, using e. coli as a donor (voeykova et al. 1998; hou et al. 2008). despite all possibilities, transformation stayed the most applied method, and many problems with transformation and protoplast regeneration of streptomyces species still preserved. strain development and genetic analysis of several important streptomycetes has been hindered by the apparent lack of natural fertility, the lack of transduction or transformation, and by restriction-modification systems. restriction endonuclease activities, having role in the protection of the bacterial genome, can nova biotechnologica 8-1 (2008) 39 complicate genetic manipulation of the bacterium by affecting transformation efficiency and stability of recombinant dna (apichaisataienchote et al. 2005). several methods have been designed in an attempt to improve protoplasts preparation and regeneration in streptomyces, including glycine treatment of mycelia, use of mixture of lytic enzymes, and supplementation of metal ions and osmotic stabilizers (yang and lei, 2001). our studies showed that cells could be transformed at a high frequency when the recipient streptomycetes protoplasts are formed by treatment with lytic enzyme during the cultivation. in this work, s. aureofaciens b96, hardly transformable streptomyces strain, and model strains, s. coelicolor and s. lividans, were used for setting the conditions for protoplast preparation during the cultivation process. streptomyces under submerged conditions enter the log phase before 24h, stationary phase between 24 and 96 h, and declining phase after 96h of incubation. it was reported that streptomyces protoplast formation was high in the early stationary phase and decreased in the late stationary phase (kieser et al. 2000; yang and lei, 2001). in addition, protoplast formation also increased in the decline phase, likely due to the autolysis of mycelia and partial damage of the cell wall. rodicio et al. (1978) found that protoplasts were yielded in young mycelia treated with lysozyme, even when the glycine was not added during the growth period. however, protoplast formation in old mycelia required the presence of glycine during the cultivation. therefore, mycelium grown at the late log to the middle stationary phase treated with lysozyme was effective for protoplast preparation. in our study, glycine was used in all media as a factor increasing susceptibility to the action of agents degrading the cell wall. s. aureofaciens was cultivated in various media with addition of lytic enzyme. the numbers of formed protoplasts, counted in bürker counting chamber, are shown in tables 1 and 2. table1. effect of lytic enzymes on number of s. aureofaciens b96 protoplasts in various media. lytic enzymes were added to media after 8h of incubation. protoplast concentration is in cfu/ml of medium. lysozyme endolysin 1 mg/ml 2 mg/ml 0.15 mg/ml 0.3 mg/ml medium 24h 48h 24h 48h 24h 48h 24h 48h nb + gly -------- nbs + gly 2×106 2×106 --4×106 4×106 4×106 4×106 tsb + gly 4×106 2×106 4×106 2×106 8×106 8×106 8×106 8×106 tssb + gly 12×106 8×106 14×107 12×106 16×107 14×106 16×106 14×106 there were too few protoplasts formed, when the lytic enzyme was added immediately into the cultivation media (less than100 cfu/ml). more effectual results were when the lytic enzymes were added after 8h incubation of streptomyces culture (table 1; 2×106-1×107 cfu/ml). under these conditions, the best results were acquired in tssb medium (12–14×106 cfu/ml), where additional sucrose was added to form hypertonic environment. moreover, if nb and nbs media were compared, there were no protoplasts observed in media without any osmotic stabilizer. however, the formation of protoplasts was influenced by the composition of cultivation media. nb 40 brnáková, z. et al. is a complex cultivation medium and was not suitable for streptomyces aureofaciens. optimal protoplast formation was obtained by treatment of mycelium with lytic enzyme during cultivation in yeme medium (1000mm sucrose, table 2). however, s. aureofaciens grew with much difficulties in such hypertonic medium and needed to be pre-cultivated overnight in tsb medium, where its growth was very extensive. table 2. effect of lytic enzymes on number of s. aureofaciens b96 protoplasts in yeme medium. the inoculum was 20-24h fresh culture pre-cultivated in tsb+gly medium. protoplast concentration is in cfu/ml of medium. lysozyme endolysin time of cultivation 1 mg/ml 2 mg/ml 0.15 mg/ml 0.3 mg/ml 24h 24×106 26×106 29×106 30×106 48h 26×106 29×106 31×106 31×106 the concentrations of lytic enzymes were selected according to preliminary studies in our laboratory and related to lysozyme they were consistent with the results of kieser et al. (2000) standard protocols for protoplast preparation. mycelium was grown in yeme medium with glycine for 48 hours. for comparison, protoplasts were prepared also by procedure described in kieser et al. (2000) with 1mg/ml of lysozyme for s. lividans or s. coelicolor and 2mg/ml of lysozyme s. aureofaciens (table 2), respectively. the amounts of prepared protoplasts were comparable to those formed by cultivation directly with lytic enzyme in yeme medium (approximately 50×107 cfu/ml in the case of s. lividans or s. coelicolor, and 30×107 cfu/ml in the case of s. aureofaciens). the reproducible results from liquid cultivation with lytic enzymes are summarized in tables 2 and 3. there was not a significant difference among the final protoplast amounts, when the different concentrations of lytic enzyme were used directly in media during the cultivation process. in this study, even the lower concentration (1mg/ml of lysozyme and 0.15 mg/ml of actinophage endolysin) was enough for protoplast formation. table 3. effect of lytic enzymes on number of s. lividans 66 tk24 and s. coelicolor a3(2) protoplasts in yeme medium. protoplast concentration is in cfu/ml of medium. lysozyme (2 mg/ml) endolysin (0.3 mg/ml) time of cultivation s. lividans s. coelicolor s. lividans s. coelicolor 24h 48×106 45×106 50×106 51×106 48h 50×106 49×106 51×106 51×106 following the cultivation, protoplasts were centrifuged, washed by p-buffer and filtrated to remove possible mycelia. the important fact was not to dilute cultivation medium because of osmotic instability of protoplasts. after centrifugal concentration at 2800 rpm, protoplasts were ready for transformation. in this state, acquired amounts of s. aureofaciens protoplasts were 25×109/ml and 25×1010/ml, 5×1010/ml and 4×1011/ml in the case of 1mg/ml and 2mg/ml of lysozyme; 0.25mg/ml and 0.5mg/ml of endolysin used, respectively. protoplast regeneration frequency is estimated by the ratio of cell number to protoplast number. it was reported before, that the cell regeneration from protoplasts nova biotechnologica 8-1 (2008) 41 of streptomyces depended on the medium components, age of mycelia, dehydratation of plates and culture temperature. it was also found that the presence of non-protoplast mycelium fragments could affect the cellular regeneration from protoplasts (yang and lei, 2001). regeneration medium, no. 16m was suitable for all streptomyces strains tested in this study, and protoplasts were regenerated after 2-3 days of incubation at 30°c. the regeneration frequencies were about 95% for s. aureofaciens, 94.3% and 94% for s. lividans and s. coelicolor, respectively. but in general, because of the diversity of streptomyces, the composition of the regeneration media has to be optimized for each strain. 3.2 transformation of protoplasts in past years, polyethylene glycol (peg)-mediated plasmid transformation of protoplasts had allowed the rapid development of gene cloning in various streptomyces species. although this transformation procedure is generally applicable to several streptomyces species, it is necessary to optimize growth and establish the optimal conditions for protoplast formation and regeneration. moreover, the transformation of the fragile protoplasts is tedious and frequently not reproducible; thus, numerous streptomyces strains could not be proven to be transformable (mellouli et al. 2004). peg induces plasmid transformation in streptomyces species apparently by interacting with cytoplasmic membrane structure, thus allowing plasmid dna uptake (garcia-dominguez et al. 1987). protoplasts of s. aureofaciens b96, in this study, were transformed by pkj2 plasmid dna. thiostrepton resistance marker is well expressed in s. aureofaciens and suggested good selection of transformants based on the resistance to this antibiotic. when the protoplasts of s. aureofaciens were prepared following the method developed for s. lividans and s. coelicolor by hopwood et al. (1985), the extremely low initial transformation frequency with plasmid dna was observed (less than 100 transformants per µg dna). despite, the frequencies in s. lividans and s. coelicolor were between 106–107 cfu/µg of plasmid dna. alike in the case of media without or with 300mm sucrose, there was only little transformation frequency with plasmid dna (5-10%). the highest transformation efficiency was observed when s. aureofaciens was cultivated with lytic enzyme in yeme medium (1000mm sucrose, pre-cultivated in tsb medium with glycine). protoplast numbers after concentration were 25×109 cfu/ml and 25×1010 cfu/ml in the case of 1mg/ml and 2mg/ml of lysozyme; 5×1010/ml and 4×1011/ml when 0.25mg/ml and 0.5mg/ml of endolysin was used, respectively. not only the best results in protoplast formation were in such osmotic medium, but also the regeneration of the protoplasts was more than 95% and the transformation frequency was comparable to s. lividans and s. coelicolor used in this study (in all cases the transformation frequencies were reproducibly about 2×106 – 107 cfu/μg dna). these results corresponded to the results published previously for s. lividans and s. coelicolor (kieser et al. 2000) and the other streptomyces strains (shirahama et al. 1981; matsushima and baltz 1985; and more). there was an irrelevant difference in transformation frequency regarding to concentrations of lytic enzymes used in cultivation media and 42 brnáková, z. et al. the type of plasmid. neither the size nor the origin of the plasmid dna played the role in this study. the preliminary studies in our lab showed that transformation frequency did not depend on the size of the cloning vector (data not shown). despite s. aureofaciens b96 protoplasts were stable after storing at -70°c under any condition used, they were not transformable any more. they always had to be prepared fresh. opposite, s. lividans and s. coelicolor protoplasts, prepared in the same way as aforementioned s. aureofaciens, were stable at -70°c in p buffer for at least six months. 3.3 isolation of “total” and plasmid dna there are various procedures of streptomyces dna isolation (kieser et al. 2000). in general, the first step for dna isolation is the lysis of the cell walls. they require treatment with sds or sarkosyl, then incubation with lysozyme at 30° or 37°c with periodical trituration. this step takes usually long time and sometimes not all of the mycelia are lysed. furthermore, the regeneration and transformation ability of protoplasts depends on the way of preparation in many cases. all dna isolation methods in this study were simplified procedures according to kieser et al. (2000). they were not such time-consuming, as the step of cell wall lysis was excluded. visually, except for the yeme with high sucrose content, all media were viscous after cultivation with lytic enzyme. there were only a few protoplasts after cultivation in these media, so we assumed that the most of them broke and intracellular content with dna split into the medium. after that, no lysis was needed and the whole isolation was based only on extraction from phenol, phenol-chloroform and on alcohol precipitation. if hypertonic medium was used for cultivation, like yeme, it was better to dilute the medium either with water or 10.3% sucrose to let the protoplasts break and split inner content into the medium. it was also possible to isolate plasmid dna from such cultivation media. the only difference was the extraction from acid phenol-chloroform at first. consequently, the plasmid dnas were purified like total dna. plasmid dnas isolated by this procedure were able to transform repeatedly into streptomyces protoplasts. according to one’s needs, by addition of the lytic enzyme into medium during cultivation it is possible to acquire protoplasts with high regeneration and transformation frequency or isolate chromosomal and plasmid dna. this procedure is applicable to protoplast preparation from many streptomyces species, even from hardly transformable industrial strains, when high concentration of sucrose, as osmotic stabilizer is added into liquid medium. this method is easier, more effective and not so time-consuming than developing and optimizing new procedures. additionally, chromosomal dna and plasmid dna isolations are very easy and quick, as the cell lysis step is excluded. acknowledgements this work was supported by a grant from vega no. 2/0121/08. the work has been carried out in compliance with current laws governing genetic experimentation in the slovak republic. nova biotechnologica 8-1 (2008) 43 references apichaisataienchote, b., altenbuchner, j., 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pristamycin by genome shuffling. appl. microbiol. biotechnol., doi: 10.1007/s00253-008-1540-0. yang, s.-s., lei, c.-m.: formation and regeneration of protoplasts for protease production in streptomyces rimosus. j. microbiol. immunol. infect., 34, 2001, 8– 16. microsoft word kraic nb 9-2.doc nova biotechnologica 9-2 (2009) 217 determination and classification of pollutants in waste water filip kraic1, zuzana királyová2, ján mocák1,2 1department of chemistry, university of ss. cyril & methodius in trnava, j. herdu 2, trnava, sk-917 01, slovak republic (filip.kraic@ucm.sk) 2institute of analytical chemistry, slovak university of technology, bratislava, sk-81237, slovak republic abstract: this paper deals with waste waters produced by industrial producers during recent three years. its main purpose is to evaluate the data monitored from discharges of three leather plants where eight traditional variables (cod, bod, insoluble matters, ph, and the concentrations of ammonia, total nitrogen, chromium and sulphides) were regularly analyzed and quantified. chemometrical and statistical methods were approved as very useful tools for characterization and classification of various kinds of water samples considering the environmental and metrological aspects. for this purpose, multivariate (multidimensional) techniques of data analysis and correlation analysis were especially very useful. the mentioned techniques are used in this work to (1) reveal the concealed interrelations of the monitored characteristics of waste waters, (2) compare the results of individual waste water producers and find the most important polluting source during a long time period, and (3) derive some generally valid conclusions regarding the observed results. key words: waste water, pollutants, multivariate data analysis 1. introduction pollution of the rivers and seas jeopardizes production of oxygen in water. a severe pollution source is the water waste pollution. waste water is coming into environment as a consequence of the industrial and agricultural production and the town activities. it has an unhealthy influence on human and environment. contaminations present in waste water contain various inorganic and organic matters. the most important variables, which characterize the water quality and indicate the extent of pollution are the concentrations of chromium (coded cr in further text), total nitrogen (coded ntot), ammonium (nh4), and sulphide (s2). together with chemical oxygen demand, cod, (coded chsk according to the slovak designation), biological oxygen demand, bod5, (coded bsk5 according to the slovak designation), water acidity (ph), and amount of insoluble matters (im) they were regularly monitored at the output from three industrial sites in the same slovak town during the years 2006, 2007 and (partly) 2008, which has created the measurement basis for the performed research. due to their potential environmental danger, discharges from the leather plants have to be regularly monitored. the most dangerous environmental factor is here the content of chromium, which is very toxic in the oxidation state +vi, therefore most part of cr(vi) is trapped in the technological process. also further above mentioned factors must be regularly monitored not only by the plant laboratory but also by an independent accredited analytical laboratory. when the limiting values are exceeded, the level of the respective factor must be immediately properly adjusted. 218 kraic, f. et al. characterization and classification of various kinds of water samples from the environmental and metrological aspects was effectively performed using various chemometrical and statistical methods (vončina et al., 2007; šnuderl et al., 2007; kannel et al., 2007; kraic et al., 2008). therefore in this work several multidimensional (multivariate) techniques of data analysis were used. 2. material and methods 2.1 sampling the waste water samples originated from three relatively similar industrial production sites. the sampling was done once a week by the analysts from a nearby accredited laboratory where the required measurements were made. the following 8 variables were monitored and analyzed: chsk, bsk, ph, im, ntot, nh4, cr and s2 (their codes are explained above). the sampling procedures and laboratory analyses were described in detail in our previous papers (királyová et al., 2008a; 2008b). to prevent changes in waste water samples, the analyses started two hours after sampling, which was faciliated by closeness of the analytical laboratory to the monitoring sites. 2.2 analysis cod (chsk) was measured by the spectrophotometrical dichromate method; bod5 (bsk5) was determined after treatment of analyzed water with manganese dioxide by iodometric thiosulphate determination of the present mn(iv). the ph value was measured potentiometrically using a glass electrode. insoluble matters (im), separated on an appropriate filter and filtered off, were dried at 105 °c until the constant weight and determined gravimetrically. ammonia was distilled off from the analyzed water and determined spectrophotometrically using the nessler reagent. for the total nitrogen determination, inorganic and organic nitrogen was oxidized by persulphate and mineralized in sulphuric acid. the formed nitrate reacted with 2,6dimethylphenol (in sulphuric and phosphoric acid medium) and the resulted 4-nitro2,6-dimethylphenol was determined spectrophotometrically. chromium was selectively determined by inductively coupled plasma optical emission spectrometry. sulphide anion was determined by back iodometric titration using thiosulphate standard solution. 2.3 multidimensional data analysis statistical calculations were performed using the following techniques: correlation analysis, principal component analysis (pca), cluster analysis (ca) and linear discriminant analysis (lda). in the performed calculations three contemporary software commercial packages were used: stagraphics plus 5.1, spss 15.0 and sas jmp 7.0. nova biotechnologica 9-2 (2009) 219 3. results and discussion 3.1 correlation analysis the output of correlation analysis is the correlation table, which contains the pair (or pearson) correlation coefficients expressing the strength of correlation between all possible pairs of variables. tab. 1 shows the calculated correlation table. the entries of this table are symmetrical according to diagonal. the following conclusions can be derived from the correlation table: (a) the highest correlation is between chsk and bsk5. (b) very high correlations exist between chsk and ntot, bsk5 and ntot, as well as chsk and im. (c) considerably significant correlations (rcrit ≥ 0.258 at p ≤ 0.01) exist between im and ntot, bsk5 and im, im and ph, as well as nh4 and s2. (d) significant correlations (at the 95 % or higher probability level, p ≤ 0.05) exist between bsk5 and ph, as well as im and nh4 (where both dependences are inverse). all correlation coefficients in table 1, which are larger or equal than rcrit = 0.184 are marked by bold faces. (e) no significant correlation was proved in all other pairs. table 1. pearson correlation coefficients exhibiting the strength of correlation between individual pairs of variables variable chsk bsk5 im ph nh4 ntot cr s2 chsk 1 bsk5 0.7606 1 im 0.5255 0.3195 1 ph 0.0025 -0.2352 0.2890 1 nh4 0.0058 0.0389 -0.1923 0.0786 1 ntot 0.6386 0.5766 0.4338 0.1337 0.0284 1 cr -0.0473 -0.0326 0.1056 -0.0942 -0.0982 -0.0052 1 s2 0.0986 0.0329 0.1808 -0.1102 -0.2694 0.0155 0.0973 1 note: 81 studied objects, i.e. 27 averaged month values were measured at the discharge of three leather plants. critical values of the correlation coefficient (absolute values): rcrit = 0.144 (p = 0.1), rcrit = 0.184 (p = 0.05), and rcrit = 0.258 (p = 0.01) for n = 81. significant correlations are marked bold. 3.2 principal component analysis in principal component analysis, pca, some natural grouping of the objects (the waste water samples in this work) and the studied variables might be seen. the principal components, pcs, are calculated as the linear combinations of original variables (sharma 1996; khattree and naik 2000). according to the computed eigenvalues only three principal components (pcs) were found important; their value was larger than 1, which is usually considered as the criterion. three kinds of graphical outputs are used in the pca, namely the scatterplot showing the objects, the loadings plot showing the variables, and the biplot where all objects and variables are depicted together. the advantage of first two outputs is the possibility to obtain not only the 2d graph but also the 3d one, where usually the first two and three most important pcs are used as the axes, respectively. on the other hand, the biplot, even though plotted in two dimensions, provides more complex information about the studied problem. 220 kraic, f. et al. fig. 1 exhibits the biplot, which simultaneously represents the samples, depicted here by the numbers, and eight originally utilized chemical descriptors, depicted by the rays starting from the origin and ending at the point determining the variable position. the samples are here categorized according to the sampling site located at the discharge of the plants 1, 2 and 3, respectively. from the position of variables in the plane pc2 – pc1 the following outcomes can be deduced: (a) variables chsk (cod), bsk5 (bod5) and ntot provide similar information about the sampled waste water. this is well understandable especially for the first two variables since they are highly correlated; the possibility to convert mutually their values has already been discovered. (b) similarity (interdependence) of nh4 and ph proves the role of ammonia in changing the ph value of waste water. (c) the opposite position of cr with respect to ph testifies that they are antagonists; a high level of chromium is reached at lower ph, and vice versa. the achieved pca results are in accord with the described outputs of cluster analysis introduced in further text. fig. 1. biplot pc2 vs. pc1 for 8 measured chemical descriptors and 81 waste water samples coming out from the discharges of three leather plants (coded by numbers 1, 2 and 3). software spss 15.0. when looking at the sample positions in fig. 1, it can be concluded that high sulphide and cr concentration values are characteristic for the waste coming from the second plant. on the other side, high ph and nh4 values are characteristic mainly for the third and partly for the first plant. since the samples belonging to the plant 2 are localized at low (mostly negative) values of chsk, bsk and ntot, it can be concluded that samples from plant 2 exhibit generally low values of these variables. the nova biotechnologica 9-2 (2009) 221 occurrence of negative variable values in the pca is caused by the performed variable standardization, in which the corresponding mean is subtracted from the original variable values and the result is divided by the corresponding standard deviation (e.g. the zero value is achieved for the original mean value of the variable). 3.3 cluster analysis generally, the clustering process in cluster analysis may be performed either with objects or variables (khattree and naik 2000). clustering in this work was made concerns the studied eight variables. the result of the performed cluster analysis is a dendrogram depicted in fig. 2. the basis for the performed calculations were data on 81 objects representing 27 average month data measured at 3 sampling sites (discharges of three leather production plants) for each of eight investigated variables. in these calculations ward’s method of clustering and squared euclidean distance were used. in fig. 2 three clusters of closely related variables can be seen. the first cluster is formed by chsk, bsk, connected further to ntot and im. the second cluster is formed by ph and nh4, and the third cluster contains cr and s2. the variables forming the same cluster are most similar; the measure of their mutual similarity is given by distance, which represents the vertical axis of the dendrogram. the results of cluster analysis are in a good agreement with the outputs of correlation analysis and principal component analysis. fig. 2. cluster analysis of 8 variables measured in waste water analysis of 81 samples obtained during 27 months (average values at 3 sampling sites). software statgraphics plus 5.1. chsk and bsk denote cod and bod5, respectively. 3.4 linear discriminant analysis linear discriminant analysis, lda, is a supervised learning method, in which the classification model is calculated using the data belonging to the training set where the 222 kraic, f. et al. categorization of all samples is known before the calculation starts. in the first step (training), the classification model is calculated, by which the studied objects (waste water samples in this case) are re-categorized so that the object (sample) category is either confirmed or the object is assigned to another category (sharma, 1996; vandeginste et al., 1998; khattree and naik, 2000). the success in classification is calculated by the ratio of the correctly classified objects to their total number. then, in the second step, the developed model is used for classification of the objects, which are not included into the training set. they belong either to the test data set, which is utilized for validation of the discriminant model, or the category of the investigated data is completely unknown so that the main goal of lda is prediction of the object category. table 2. evaluation of linear discriminant analysis classification of the waste water samples divided into categories given by the sampling location (plants 1, 2 and 3). predicted group membership evaluated data success by plant no. 1 2 3 total training set count 1 17 0 10 27 2 0 27 0 27 3 4 0 23 27 % 1 63.0b 0 37.0 100.0 2 0 100.0b 0 100.0 3 14.8 0 85.2b 100.0 cross-validateda count 1 14 0 13 27 2 0 26 1 27 3 6 0 21 27 % 1 51.9c 0 48.1 100.0 2 0 96.3c 3.7 100.0 3 22.2 0 77.8c 100.0 a in leave-one-out cross validation, each object was classified by the model derived from all objects other than that one. b in total 82.7 % of original grouped cases were correctly classified. c in total 75.3% of cross-validated grouped cases were correctly classified. in this work, the samples were separated into three categories, assigned by the plant releasing waste water. the classification results are summarized in table 2. the lda results testify that the waste water from plants 1 and 3 have a similar level of pollutants therefore the categorization of the samples from these two sources is often interchanged, e.g. 10 samples belonging to plant 3 were classified into group 1 (plant 1), as shown in the first line of the table. on the other hand, 100 % of the samples from plant 2 were classified correctly when the training set is considered and a 96.3 % success was obtained when performing leave-one-out validation. according to the position of the samples belonging to three plant discharges with respect to the first discriminant function expressing the overall pollutant concentration in the lda nova biotechnologica 9-2 (2009) 223 diagram (not shown here) it was proved that the worst pollutant is plant 1, the best cleaning procedures were applied in plant 2. an attempt was also made to see the seasonal effect on the waste water pollution in the lda output. therefore all data were divided into four categories according to the year seasons: spring (march, april, may), summer (june, july, august), autumn (september, october, november) and winter (december, january, february). the nominal categorical variable season was created with 4 classes spring, summer, autumn and winter and used as the discrimination criterion. the separation of the data by four seasons was not well demonstrated. however, the winter and autumn data were displayed at higher values of the first discriminant function, df1, which reflects the extent of pollution since df1 may be explained as the total concentration of the polluting substances. much more successful was seasonal categorization of the data into two parts: the warmer part of the year (spring and summer) and the colder part (autumn and winter). in this case the success of discrimination was 76.5 % for the training set and 66.7 % for the leave-one-out validation. in both cases the discrimination results are unambiguously significant. at the same time it means that in cold months the total level of pollution of the waste water from all three investigated plants is larger than in the year season when the temperature is higher. 4. conclusions the waste water characteristic parameters, namely cod (chsk), bod (bsk5), insoluble matters, ph, ammonium, total nitrogen, chromium, and sulphides were monitored at the discharge of three industrial plants of the same town during almost three years. the obtained analytical values were statistically evaluated and mutual relations and the trends of the individual waste water descriptors were discovered. in total, the most important source of pollution was the industrial plant number 1. with respect to the year seasons, more polluted waste waters are expected in cold months. acknowledgement: the support of this work by slovak grant agencies by means of grants vega 1/1005/09, vvce-0004-07 and apvv-0057-06 is highly acknowledged. references kannel, p.r., lee, s., kanel, s.r., khan, s.p.: chemometric application in classification and assessment of monitoring locations of an urban river system. anal. chim. acta, 582, 2007, 390-399. khattree, r., naik, d.n.: multivariate data reduction and discrimination. sas institute, cary, north carolina, usa, 2000. királyová, z., kraic, f., mocák, j.: study of pollutants in waste water. in: 28. proceedings of industrial toxicology 2008. tatranská štrba, slovakia, june 1820, 284-289. királyová, z., šnuderl, k., kraic, f., mocák, j.: determination and classification of pollutants in waste water. acta chim. slovaca, 1, 2008, 143-152. 224 kraic, f. et al. kraic, f., mocák, j., fiket, ž., kniewald, g.: icp ms analysis and classification of potable, spring, and mineral waters. chem. pap., 62, 2008, 445– 450. sharma, s.: applied multivariate techniques. wiley, new york, 1996. šnuderl, k., simonič, m., mocak, j., brodnjak-vončina, d.: multivariate data analysis of natural mineral waters. acta chim. slov., 54, 2007, 33-39. vandeginste, b.g.m., massart, d.l., buydens, l.m.c., de jong, s., lewi, p.j., smeyers-verbeke, j.: handbook of chemometrics and qualimetrics: part b, elsevier, amsterdam, 1998. vončina, e., brodnjak-vončina, d., mirkovič, n., novič, m.: chemometric characterisation of the quality of ground waters from different wells in slovenia. acta chim. slov., 54, 2007, 119-125. microsoft word riekkola-vanhanen 2010-1.doc nova biotechnologica 10-1 (2010) 7 talvivaara sotkamo mine – bioleaching of a polymetallic nickel ore in subarctic climate marja riekkola-vanhanen talvivaara mining company plc.,talvivaarantie 66, 88120 tuhkakylä, finland (marja.riekkola-vanhanen@talvivaara.com) abstract: the main activity of the talvivaara mining company plc. is the development and exploitation of the talvivaara deposits in sotkamo, finland using bioheapleaching. the talvivaara deposits comprise one of the largest known sulphide nickel resources in europe with 1004 million tonnes of ore, sufficient to support anticipated production for a minimum of 45 years. the mine started in late 2008 and will have an annual nickel output of approximately 50,000 tons when it reaches full production. in addition, the mine will also produce zinc (approximately 90,000 tpa), copper (approximately 15,000 tpa) and cobalt (approximately 1,800 tpa) as by-products of the process. the viability of bioheapleaching technology for the extraction of nickel has been demonstrated in a large on-site pilot trial using talvivaara ore. the three year pilot has shown that the leaching process also works well in the subarctic climatic conditions of eastern finland. keywords: bioheapleaching, nickel, zinc, copper, cobalt, talvivaara 1. introduction the talvivaara deposits are located in the southern part of the kainuu belt in eastern finland. they comprise two different polymetallic orebodies, which are located approximately three kilometres apart. the deposits are outcropping and relatively easy to mine. the mineral resources have been classified by australian jorc code with 0.07% ni cut-off at 1004 million tons, containing 0.23% of nickel, 0.51% of zinc, 0.13% of copper and 0.02% of cobalt. the black schist ore and the possible utilization of the deposits have been extensively studied for over 20 years. it was quickly apparent from the ore dressing tests that a usable nickel concentrate was not achievable due to the high graphite content of the ore. chemical and biological leaching options had to be considered as potential options (riekkola-vanhanen, 1999). talvivaara black schist ore contains pyrrhotite, pyrite, sphalerite, pentlandite, violarite, chalcopyrite and graphite. the main silica containing phases are quartz, mica, anorthite and microcline. in addition to nickel, zinc, copper and cobalt the ore contains about 0.3 % of manganese, 10 % of iron, 9 % of sulphur, 8 % of carbon and 50 % of sio2. the distribution of nickel in different sulphides is pentlandite 71 %, pyrrhotite 21 % and pyrite 8 %. the distribution of cobalt is pentlandite 11 %, pyrrhotite 26 % and pyrite 63 %. all copper is in chalcopyrite and zinc in sphalerite. 2. production process overview. the mining method at talvivaara is large scale open pit mining. materials handling covers all physical ore processing steps from the primary crusher to 8 riekkola-vanhanen, m. the heaps. after one and one-half years of bioleaching on the primary pad, the leached ore will be reclaimed, conveyed and restacked onto the secondary heap pad. after secondary leaching, the barren ore will remain permanently in the secondary heaps. in the metals recovery process, the metals will be precipitated from the pregnant leaching solution (pls) using hydrogen sulphide. the resulting products will be intermediates to be transported for further processing in refineries operated by the company’s customers. fig. 1. talvivaara process chart. open pit mining. annual ore production is approximately 22 million tons. sufficient areas to extend the pit will be prepared in subsequent years, normally a year prior to when mining is scheduled to commence. any overburden or moraine not required for road, perimeter wall or other construction, will be stockpiled for later use in rehabilitation. ore and waste are extracted using conventional large scale open pit drill and blast methods. a fleet of self-propelled diesel hydraulic track drill rigs are used. fragmentation by blasting is preferred to crushing because of lower costs. it is also beneficial to create more fracturing at blasting stage, and it increases the surface area and therefore improves leaching solution entry and consequently leaching efficiency. as a result, the drilling pattern and hole sizes are on average smaller than in mines with similar production rates. materials handling and bioheapleaching. materials handling in talvivaara cover all the physical ore processing steps from the primary crusher to the final locations on the secondary heaps. during the process, the ore is crushed and screened in four stages. after primary crushing, the ore is conveyed to the following crushing stages nova biotechnologica 10-1 (2010) 9 and screening and is agglomerated for bioheapleaching. at this stage of leaching no inoculum from a bacteria farm is added. agglomeration takes place in a rotating drum, where pls is added to the ore in order to consolidate the fine ore particles with coarser ore particles. this preconditioning step makes the ore permeable to air and water for bioheapleaching. after agglomeration, the ore is conveyed and stacked eight meters high on the primary heap pad for one and one-half years of bioheapleaching. the heap pad is equipped with piping, laid on the bottom of the pad, through which lowpressure fans supply air to the stacked ore. from the top, the heap is irrigated with leaching solution, which is collected from the bottom of the heap. a ten percent side flow is taken for metals recovery and the rest of the solution is diluted with pure water in order to keep the amount of solution constant. fig. 2. pls ponds, bioheap and metals plant after one and one-half years of leaching on the primary pad, the leached ore is expected to be reclaimed, conveyed and restacked onto the secondary heap pad, where it will be leached further in order to recover metals from those parts of the primary heaps, where leaching solution has had poor contact. such areas include, for example, the slopes of the heaps and areas between channels formed by the circulating leaching solution. at this stage the main part of copper and cobalt will be recovered, too. after secondary leaching, the barren ore is expected to remain permanently on the secondary heaps. metals recovery. in the metals recovery process, the metals are precipitated from the pls using hydrogen sulphide. the resulting products are intermediates, such as copper and zinc sulphides and a mixed nickel cobalt sulphide. these intermediates are 10 riekkola-vanhanen, m. transported for further processing in refineries operated by talvivaara’s customers. the recovery process also produces gypsum as a secondary product which will be collected and remain in a separate pond on the mining site. water management. the water management plan for the talvivaara project area includes all relevant pipelines, ponds and pump stations related to the processes outside the metals recovery plant area. it also includes surface water management, effluent treatment and other surface water construction projects. water management plays an important role at the operation. the most important component is the recycling of the leaching solution from the irrigation pond to the heap and thereafter to the pls pond. from the pls pond, approximately 90 per cent of the solution is recycled back to irrigation to increase the metal grade, while about 10 per cent is lead to metals recovery. after metals precipitation, the remaining solution goes into the raffinate pond to ph adjustment and is reused to irrigate the heaps. land and infrastructure. prior to construction of the pilot operation in 2005, the talvivaara deposits had no existing mining facilities. the development of the infrastructure and services included: • access roads, internal roads and railway; • power supply; • fuel services; • drinking water supply/water management; • metal recovery facility and • sewage and waste management. the first construction phase commenced in february 2007 with construction of roads to allow good access to the site and between the construction areas. the majority of all earthworks were completed by the end of 2008. the talvivaara sotkamo mine operational area totals 61 km2. 3. bioheapleaching at talvivaara bioleaching. bioheapleaching has been chosen for the talvivaara sotkamo mine based on its favourable capital and operational costs and the good performance data obtained with the technology in earlier trials with the talvivaara ore. talvivaara’s application of the bioheapleaching technology has its origins at outokumpu research, where it has been developed in conjunction with talvivaara ore since 1987. all the rights relating to the accumulated research and development data on bioheapleaching were transferred to talvivaara in connection with the acquisition of the mining licenses in february 2004. talvivaara has developed bioheapleaching and metals recovery from leaching solutions in collaboration with tampere, helsinki and lappeenranta universities of technology and omg kokkola chemicals ltd. the research and development work has been partly funded by the finnish funding agency for technology and innovation, through capital loans and grants since early 2004. the company has also benefited from the european union funded bioshale project. for example, gsf and talvivaara set up, as part of the bioshale project, a 110 tonne pilot trial in march 2005 nova biotechnologica 10-1 (2010) 11 to test bioheapleaching of talvivaara ore. the trial was successfully started in -20ºc conditions, thus serving as an important indicator of the feasibility of the process in subarctic conditions prior to moving to larger scale on-site trials (riekkolavanhanen, 2005). smaller scale laboratory trials have provided the company with an understanding of the key parameters of bioheapleaching e.g. particle size, ph value, temperature, oxidation and aeration rate. the ph of the bulk solution is an important parameter in bioleaching processes. the acid ph range from 1.5 to 3 is normally considered to be non-selective against any specific ironand sulphur-oxidizing acidophiles that may be potentially useful in biological leaching systems. the ph value used has to be chosen in a way to ensure maximum leaching of valuable metals but also to minimize the leaching of unwanted impurities from the ore. dissolution of silicate has to be avoided, because it can create solution flow barriers by formation of amorphous, gelatinous precipitates (dopson et al., 2008). at talvivaara the ph value has to be kept over 1.5 in order to prevent silicate precipitation. in order to validate the bioheapleaching process on a larger scale, a demonstration scale on-site pilot study was commenced at talvivaara in may 2005 (riekkolavanhanen, 2007; puhakka et al., 2006). heap irrigation was started in august 2005 and metals recovery in november 2005. the demonstration heap was constructed of 17,000 tons of talvivaara ore. similar to the laboratory scale trials, the company varied the key parameters to confirm the optimum conditions. in laboratory tests the temperature remained at the room temperature level. the size of the demonstration plant was large enough to generate heat and the rise of temperature could be observed. the rise was due to the oxidation of the large quantity of pyrrhotite and pyrite in the ore. the temperatures measured inside the heap varied from 30°c to nearly 90°c. according to the measurements there were various temperature gradients inside the heap. the heap was reclaimed during the coldest time in winter 2007 and moved to a new leaching pad. the temperature of the ore was 0 0c, when irrigation of the secondary heap was started at the end of february. the temperature started to rise immediately and was at the level of 80 0c in july and started to decrease gradually after that to the level of 20 – 40 0c, where it remained to the end of july 2008. at that time the pilot had to be stopped in order to start mining in that area. the on-site pilot trial demonstrated that the leach solution temperature and temperatures inside the heaps are practically independent of the surrounding environmental conditions. the oxidative leaching of sulphide minerals is associated with acid production (e.g. pyrite) or acid consumption (monosulphides) (ahonen and tuovinen, 1994). sulphide ores invariably contain accessory non-sulphide minerals some of which may be recalcitrant (e.g. quartz), or they may be susceptible to partial dissolution (e.g. micas, carbonate minerals) and may thereby influence the ph without the involvement of a redox reaction. associated with these reactions are the acid-consuming oxidation of fe2+ and the subsequent acid-producing hydrolysis of fe3+. thus, the net acid consumption or acid production in bioleaching processes is the sum of several concurrent dissolution, precipitation, oxidation, and reduction reactions. the acid 12 riekkola-vanhanen, m. consumption of talvivaara ore was 15 kg/t of ore in the primary leaching and 2 kg/t of ore in the secondary leaching. microbial community dynamics. the microbial inoculum to the pilot heap was obtained from local acidic metal-rich ponds that had developed naturally in areas adjacent to the exposed ore and which contain a wide range of different species of mineral oxidizing acidophiles. the enrichment was originally grown on elemental sulphur, ferrous iron and finely ground talvivaara ore. in the final stage the culture was grown on elemental sulphur and ore dust in an aerated pond on site. the ph value was adjusted to 1.8 with sulphuric acid. the enrichment culture used for inoculation as revealed by pcr-dgge-sequencing contained e.g. acidithiobacillus ferrooxidans, acidithiobacillus caldus and leptospirillum ferrooxidans. depending on the leaching conditions various chemolithotrophs became enriched during the progress of leaching. the moderate thermophiles at. caldus and sulfobacillus thermosulfidooxidans were dominant during some periods of leaching. also extreme thermophile archae were found (riekkola-vanhanen, 2007). these results demonstrate that the mine site waters and the ore harbour a microbial community consisting of several members and that depending on the leaching conditions and especially the leaching temperature the dominant biocatalysts become different. as the actual leaching heaps have gradients of temperatures due to the heat released in the exothermic reactions and the varying boreal conditions, succession of different organisms at different depths of the heap and at different times is obvious. leaching recoveries. the results from the demonstration plant were substantially better than anticipated based on laboratory and other pilot results and confirmed the viability of the bioheapleaching of the talvivaara ore. it is assumed that most of nickel and zinc will be leached in the primary heap within one and one-half years. the leaching rates were calculated from the chemical analyses of the solution taken away for metal recovery. every tenth sample was sent to an accredited laboratory in order to be sure that the results are correct. the recovery rates were higher than anticipated. nickel recovery reached 80 % within 400 days. the corresponding zinc recovery was 80 % in 480 days. the demonstration plant has shown that the assumed recoveries for nickel and zinc can be reached (puhakka et al., 2006). the recovery of cobalt remained low and the leaching rate was progressing slowly over the first 500 days. only 2.5 % of copper were recovered. copper is in chalcopyrite. the main part of cobalt is in pyrite. as sulphide minerals have semiconductor properties, galvanic interactions appear when there is an electrical contact among mineralogical phases. during dissolution of a mineral assembly of different sulphides, those minerals that have the highest rest potentials behave as cathodes which mean that they are galvanically protected and their leaching is hindered until the minerals with lower rest potentials have been leached. the electrochemical potentials of chalcopyrite and pyrite are higher than the ones of pyrrhotite, pentlandite and sphalerite (riekkola-vanhanen and heimala, 1993). the leaching of copper and cobalt proceeded well in the secondary leaching phase of the demonstration plant. nova biotechnologica 10-1 (2010) 13 0 10 20 30 40 50 60 70 80 90 100 5.9.2005 24.3.2006 10.10.2006 28.4.2007 14.11.2007 1.6.2008 18.12.2008 date m et al r ec ov er y % secondary leaching primary leaching ni zn co cu fig. 3. leaching recoveries in talvivaara pilot. 4. conclusions extensive research and pilot trials have proven bioleaching a feasible and environmentally sound technology in treating talvivaara low grade sulphide nickel deposits in subarctic conditions. talvivaara project ltd., which was established to build the mine and plant, progressed in the set timetable and budget. the mine and the plant are in industrial use since the beginning of year 2009. references riekkola-vanhanen, m., heimala, s.: electrochemical control in the biological leaching of sulfidic ores. in: a.e. torma, j.e wey, v.i. lakshmanan (eds.), proceedings of the 10th international biohydrometallurgy symposium, tms warrendale, pennsylvania, 1993, 561-570. ahonen, l., tuovinen, o.h.: solid phase alteration and iron transformation in column bioleaching of a complex sulfide ore in: c.n. alpers and d.w. blowes (eds.), environmental geochemistry of sulfide oxidation. american chemical society, washington, d.c., 1994, 79-89. riekkola-vanhanen, m., heimala, s.: study of the bioleaching of a nickel containing black-schist ore. in: r. amils, a. ballester, (eds.) proceedings of the 13th international biohydrometallurgy symposium part a, elsevier, amsterdam, 1999, 533-542. riekkola-vanhanen, m., sivelä, c., viguera, f., tuovinen, o.h.: effect of ph on the biological leaching of a black schist ore containing multiple sulphide minerals. in: v.s.t., ciminelli, o. garcia (eds.) proceedings of the 14th international biohydrometallurgy symposium part a, elsevier, amsterdam, 2001, 167-174. 14 riekkola-vanhanen, m. riekkola-vanhanen, m.: bioleaching of talvivaara black schist ore. materia, 3, 2005, 38-43. puhakka, j.a., kaksonen, a.h., riekkola-vanhanen, m.: heap leaching of talvivaara black schist ore. in: d.e. rawlings, d.b. johnson (eds.) biomining, springer-verlag, 2007, 139-152. riekkola-vanhanen, m.: talvivaara black schist bioheapleaching demonstration plant. adv. mater. res., 20-21, 2007, 30-33. dopson, m., halinen, a.k., rahunen, n., boström, d., sundqvist, j.e., riekkola-vanhanen, m., kaksonen, a.h, puhakka, j.a.: silicate mineral dissolution during heap bioleaching. biotechnol. bioeng., 99, 2008, 811-820. microsoft word dudkova nb 9-2.doc nova biotechnologica 9-2 (2009) 119 microbial dechlorination of polychlorinated biphenyls vlasta dudková1, kateřina demnerová1, donna l. bedard2 1institute of chemical technology in prague, faculty of food and biochemical technology, department of biochemistry and microbiology, technická 3, 166 28 prague 6; czech republic, (dudkovav@vscht.cz) 2rensselaer polytechnic institute, department of biology, 110 eighth street, troy, ny 12180-3590, u.s.a. abstract: polychlorinated biphenyls (pcbs) are organic xenobiotics contaminating environment for at least 50 years. they could be eventually eliminated by various organisms under different conditions. the degree of chlorine substitution per biphenyl molecule influences biodegradability which decreases with increasing chlorination. our work is focused on the pcbs biodegradation under anaerobic conditions. the suitable high chlorinated biphenyls are converted via reductive dechlorination to the chlorinated biphenyls with lower extent of chlorine, which could be eventually fully mineralized by aerobic bacteria. microbial consortium was isolated from sediment of strážský creek (located near by plant producing pcbs in the past). this consortium was able to dechlorinate polychlorinated biphenyls under anoxic conditions. the effectiveness of this process was tested under different cultivation condition – different energetic sources (aroclor 1248 or aroclor 1260 or delor 103 or delor 106), addition of potential electron donors (pyruvate, lactate or acetate with hydrogen) and further if there is necessary to add yeast extract into fresh low sulphur cultivation media. our microbial consortia so far do not need supplementation by non-contaminated sediment to maintain dechlorination activity. addition of yeast extract is non essential, but needs to be further proved in serial transfers. in all cases (except acetate without yeast extract) dechlorination proceeds at metaand flanked para position. key words: polychlorinated biphenyls, reductive dechlorination, gas chromatography 1. introduction polychlorinated biphenyls (pcbs) are a class of organic compounds with 1 to 10 chlorine atoms attached to biphenyl molecule (it is possible to derive 209 different congeners). pcbs were commercially produced as complex mixtures containing multiple isomers at different degrees of chlorination. their unique character (nonflammable; good heat transfer fluid; electroisolation properties; low vapor pressure; low water solubility and high solubility at organic solvents and fatty acids) caused their robust production and wide usage. their commercial and industrial production started at the end of 20s last century. pcbs were produced by catalytical chloration of biphenyl (at czechoslovakia they were manufactured at chemko strážské until 1985). pcbs production was banned in the 1970s (in most countries of west world) due to the high toxicity of most pcb congeners and mixtures to the organisms. 120 dudková, v. et al. listed properties caused food chain accumulation and difficulties during degradation and removing. pcbs are classified as persistent organic pollutants. they may be destroyed by chemical, thermal, and biochemical processes. it is extremely difficult to achieve full destruction, and there is the risk of creating extremely toxic dibenzodioxins and dibenzofurans through partial oxidation. chemical analogs of pcbs (as chlorophenols; chlorobenzenes or dioxines) are in nature produced during forest fires or volcano eruptions (borja et al., 2005). it was evidenced that pcbs are transformed by microorganisms (faster at laboratory conditions than in nature). it gives us possibilities how to decrease current concentration in the environment. the halftime differs through environmental kind (aerobic, anaerobic; water, soil, atmosphere, sediment), type of organisms participated on degradation (bacteria, fungi, plants, animals) and amount and character of other contaminating compounds. anaerobic bacterial degradation of pcbs is not so well-known as the aerobic degradation. but at short time were serious results achieved and it was demostrated that anaerobic degradation plays an important function through pcbs biological decontamination (maltseva et al., 1999). organisms growing on organohalides get energy for their metabolism and reproduction by reductive dechlorination (mohn and tiedje, 1992) (halogen from the organohalide molecule is used as a terminal electron acceptor). above mentioned mechanism (dehalogenation) transforms the high chlorinated biphenyls to the low chlorinated biphenyls which could be consumed during aerobic degradation. it should be very interesting but technically very difficult to try to combine anaerobic and aerobic degradation. mechanism of anaerobic degradation was first described at the end of 90s last century. it was observed at laboratory conditions that degradation ability should be primed by presence of some congeners or amended by exogenic compounds which should be used as an energy source or as a proton donor (dibromobiphenyls, lactate, malate, pyruvate, acetate, butyrate and others) (bedard et al., 1998; wu et al., 1999). adrian and coworkers (2009) finally describe pure culture (dehalococcoides sp. strain cbdb1) extensively dechlorinating commercial pcb aroclor 1260. 2. materials and methods pcb mixes and aroclors were purchased from accustandard (new haven, the u.s.a.). delor was provided by mr. kočan from the slovak republic. diethylether declared as gc grade was supplied by merck (darmstadt, germany). sediment (fractioned under 1 mm2) was resuspended in special low sulphur purely synthetic, carbonate buffered mineral medium containing ti(iii) citrate as reducing agent and vitamins (adrian et al., 2000). set of samples was amended by 4-4 dibromobiphenyl (final concentration 350 μmol/l), other was amended by 2,6 dibromobiphenyl and others were retained without addition and cultivated at two different temperatures (4 °c and 28 °c). brominated biphenyls were sorbed on silica mesh 250 nm (providing homogenic distribution of pcbs and increasing internal area). microbial activity was measured indirectly by changing concentration of every pcb. growing cultures were sampled (every 3 weeks) under anoxic condition (quensen et al., 1990). nova biotechnologica 9-2 (2009) 121 the taken media were shaked out to the diethylether (volume distribution 1:12.5). proper assesment of concentration of pcb from diethylether was provided on gas chromatograph (hp 6890n) with automatic injector (hp 7683) and micro-electrone capture detector. for separation of congeners capillary column (db-xlb, length 30m, inside diameter 0.25 mm and thickness of stationary phase 0.25 μm) was used. mobile phase was nitrogen and the final flow was 45.1 ml/min. sample (1 μl) was inject on column using splitless technique. measurment was proceded by using isobaric mode (0.993 bar). temperature program was following: the initial temperature was 50 °c and immediately increased to 160 °c (rate 30 °c/min) and then immediately increased to 300 °c (rate 2.5°c/min) and there was terminated. detector temperature was 340 °c and final flow of mobile phase was 60 ml/min (makeup gas + column flow). data were collected by using software gc chemstation. however we are still not able fully quantify the whole process (it is the reason why we show data at not very wellarranged shape – chromatograms). 3. results and discussion our first experiment should manifest presence of dehalogenating organisms and a possible way of accelerating their metabolism. after dechlorination activity was documented and extensive advance (samples cultivated at 28 °c) we transferred our microbial consortia in a fresh media (portion of primary culture was 10 vol. %). commercial mixture pcbs (aroclor 1248, or aroclor 1260, or delor 103, or delor 106 at finally concentration 50 μg/ml) sorbed on silica was added as an energy source. we added different proton sources for microbial consortia – pyruvate, or lactate, or acetate amended by hydrogen. table 1. sum of detected pcbs (%) in different time of cultivation. indicator pcbs: 28, 52, 101, 118, 138, 153, 180 sum of detected pcbs [%] sum of indicator pcbs [%] 0. day 182. day 285. day 473. day 586. day 0. day 182. day 285. day 473. day 586. day acetate 100 100 100 100 100 100 95 104 111 107 acetate with yeast extract 100 100 100 98 97 100 101 103 86 80 lactate 100 95 94 94 94 100 64 59 59 58 lactate with yeast extract 100 97 96 95 95 100 74 67 65 62 pyruvate 100 98 95 95 94 100 79 62 65 63 pyruvate with yeast extract 100 95 94 94 94 100 65 58 60 58 122 dudková, v. et al. more detailed will be discussed the microbial consortia of the 4th transfer containing only 0.04 vol. % of origin sediment cultivated on aroclor 1260 pcb mixture supplemented by pyruvate, lactate or acetate with hydrogen. we study if there is necessary to supplement fresh bacterial media for our dechlorinators by more complex carbon source yeast extract. pcb dechlorination activity was measured as described above. sum of reminder pcbs (%) as well as sum of indicator pcbs during incubation period is documented in table 1. decreasing concentration of pcbs 138, 153 and 180 which are well present at originally used pcb mixture – aroclor 1260 were mainly responsible for so huge non-expecting decreasing concentration of indicator pcbs. on the other hand we observed a bit increasing concentration of remaining indicator congeners. we also analyzed change of chlorine distribution on biphenyl molecule. documentation is at table 2. table 2: distribution of chlorines per biphenyl molecule (%). particular amount of ortho-, meta-, and parachlorines (%) acetate acetate with yeast extract lactate lactate with yeast extract pyruvate pyruvate with yeast extract 0. day 586. day 586. day 586. day 586. day 586. day 586. day ortho 39.5 39.3 41.0 43.1 42.5 42.8 43.2 meta 39.8 39.7 39.1 38.4 38.4 37.8 37.8 para 20.7 21.0 19.9 18.5 19.1 19.4 19.0 at all cases (except acetate) there is examined decreasing amount at metaand parasubstitution. dechlorination pathways were studied and it was set up our microbial communities are removing metaand flanked parachlorines from biphenyl molecule. 4. conclusions our subcultures transformed nona, octa and hepta chlorinated biphenyls through hexa to tri, tetra and penta chlorinated biphenyls. dechlorination proceeds at metaand flanked paraposition. we observed decreasing concentration of indicator pcbs 138, 153 and 180 and on the other hand increasing concentration of indicator pcbs 28, 52, 101 and 118. addition of yeast extract in fresh media seems not to be necessary for most of tested conditions (exception of acetate) – need to be further confirmed at next transfer. our consortia do not need additional supplementation with non-contaminated sediment as many others. incubation time at laboratory condition seems to be too long, but when dechlorination proceeds it is going relatively fast. we presume, that as our consortia nova biotechnologica 9-2 (2009) 123 adapt to our condition (temperature, composition of media, non-presence of sediment) the lag period would be much shorter. acknowledgement: the authors thank for the support of the grants: centrum 1m06011, frvš g4/943/2009, npv ii 2b06156 and vz msm 6046137305. references adrian, l., dudkova, v., demnerova, k., bedard, d.l.: dehalococcoides sp. strain cbdb1 extensively dechlorinates the commercial polychlorinated biphenyl (pcb) mixture aroclor 1260. appl. environ. microbiol., 2009 (in press). adrian, l., szewzyk, u., görisch, h.: bacterial growth based on reductive dechlorination of trichlorobenzenes. biodegradation, 11, 2000, 73-81. bedard, d.l., dort, h., deweerd, k.: brominated biphenyls prime extensive microbial of aroclor 1260 in housatonic river sediment. appl. environ. microbiol., 64, 1998, 1786-1795. borja, j., taleon, d.m., auresenia, j., gallardo, s.: polychlorinated biphenyls and their biodegradation. process biochem., 40, 205, 1999–2013. maltseva, o.v., tsoi, t.v., quensen, j.f., fukuda, m., james, m.: degradation of anaerobic reductive dechlorination products of aroclor 1242 by four aerobic bacteria. biodegradation, 10, 1999, 363-371. mohn, w.w., tiedje, j.m.: microbial reductive dehalogenation. microbiol. rev., 56, 1992, 482-507. quensen, j.f. iii., boyd, s.a., tiedje, j.m.: dechlorination of four commercial polychlorinated biphenyl mixtures (aroclors) by anaerobic microorganisms. appl. environ. microbiol., 56, 1990, 2360-2369. wu, q., bedard, d.l., wiegel, j.: 2,6-dibromobiphenyl primes extensive dechlorination of aroclor 1260 in contaminated sediment at 8-30 ˚c by stimulating growth of pcb-dehalogenating microorganisms. environ. sci. technol., 33, 1999, 595-602. microsoft word ondrejovic2 nb 9-2.doc nova biotechnologica 9-2 (2009) 175 optimization of rosmarinic acid extraction from lemon balm (melissa officinalis) miroslav ondrejovič1,2, hana benkovičová1, stanislav šilhár2 1department of biotechnology, university of ss. cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic (miroslavondrejovic@gmail.com) 2food research institute, dept. biocentre, kostolna 7, sk-900 01, modra, slovak republic abstract: the aim of this study was optimization of rosmarinic acid extraction from lemon balm (melissa officinalis). the optimal conditions for the extraction of rosmarinic acid from lemon balm were determined using response surface methodology (rsm). a center composide design (ccd) was used to investigate the effects of three independent variables, namely solid-liquid radio, solvent composition (%) and extraction temperature (°c). dependent variable was yield of rosmarinic acid. a second-order polynomial model was used for predicting the response. optimized conditions for rosmarinic acid were: peme 1:29 (w/v), temperature 66 °c a % propan-2-ol 34 %. the experimental values agreed with predicted within a 95 % confidence interval. yield of rosmarinic acid extraction by these optimized conditions was achieved 72.6 mg of rosmarinic acid / g of dry extraction matter. keywords: rosmarinic acid, optimization, melissa officinalis, extraction 1. introduction rosmarinic acid is an ester of caffeic acid and 3,4-dihydroxyphenyllactic acid (pereira et al., 2005; petersen, 1996). it has a number of interesting biological activities, e. g. antimicrobial (pal bais et al., 2002), antiallergic (ito et al., 1998; matsuno et al., 2002), antiviral and anti-inflammatory (georgiev et al., 2006; huang et al., 2006; kamatou et al., 2005). rosmarinic acid is commonly found in species of the boraginaceae and lamiaceae. the plants with rosmarinic acid content were used in traditional medicine. today, plant extracts found some application in food and cosmetic industry. the aim of the present study was to evaluate the effect of changing solvent polarity characterisation using dielectric constant, liquid to solid ratio, temperature and time of extraction on the rosmarinic acid yield in extracts. 2. material and methods 2.1 plant material adult leaves of melissa officinalis were harvested with the twigs and dried at 40°c. thereafter, the leaves were separated from the twigs and cut in small squares of 1 – 1.5 cm2. this extraction material was stored in powder flask at laboratory temperature. 176 ondrejovič, m. et al. 2.2 extraction procedures in all experiments, the extractions were done in experimental microtubes and stopped by a rapid decantation of extracts. the impact of solvent composition on the rosmarinic acid content from propanol, ethanol, methanol and their water solution (33 and 66 %; v/v) to water were explored using extraction by solid-liquid ratio 1:30 (w/v), at 40 °c during 1 hour. the influence of the solid-liquid ratios on the extraction was investigated, by considering four ratios (1:10, 1:20, 1:30, 1:40; w/v) with 33 % (v/v) water solution of propan-2-ol as extraction solvent. a kinetic study was performed to select reach an asymptotic region in the extraction. the axial (40 and 80 °c) and central (60 °c) temperatures were used in this kinetic study. the solid-liquid ratio was 1:100 and extraction solvent was again 33 % (v/v) water solution of propan2-ol. 2.3 experimental design for the response surface methodology (rsm) the rsm used a three-factor and central composite design in three blocks consisting of 17 experimental runs with three replicated at the centre point. the design variables were the solid-liquid ratio (0.019 – 0.099 g/ml; x1), the propan-2-ol proportion (propan-2-ol: water, 1 – 95 %, v/v; x2) and the temperature (20 – 80 °c; x3). the variables particle size (< 0.5 mm) and extraction time (1 hour) were kept at constant values. experimental data were fitted to the following second-order polynomial model (eq. 1) and regression coefficients were obtained. ∑∑∑∑ − < = === +++= 1 1 2 2 11 0 k ji i j jiiji k i ii k i ii xxbxbxbby (1) where x1, x2, ..., xk are the independent variables affecting the response y; b0, bi (i = 1, 2,.., k), bii (i = 1, 2, ..., k) and bij (i = 1, 2,...k – 1; j = 2, 3,..., k) are regression coefficients for intercept, linear, quadratic, and interaction terms, respectively; k is the number of variables (silva et al., 2007). the optimum conditions of rosmarinic acid extraction were looked by using statgraphic, 5.1. the verification of the validity and adequacy of the predictive extraction model was carried out in these optimum conditions of solid-liquid ratio, solvent composition and extraction temperature. three experimental replicates were performed at the optimized conditions and the experimental and predicted values were compared. 2.4 determination of rosmarinic acid content the rosmarinic acid content in prepared extracts was determined by hplc analysis using purospher star rp18e, 250 x 4 mm, 5 μm, gradient elution of 0.1 % trifluoracetic acid in water (a) and acetonitrile (b), at flow rate 1 ml/min: 0 min 15 % b, 18 min 30 % b, 25 min 80 % b, 27 min 80 %, with detection at 325 nm. final nova biotechnologica 9-2 (2009) 177 rosmarinic acid content was expressed as mg of rosmarinic acid per g of dry material (dm). 3. results and discussion 3.1 selection of optimized extraction parameters extraction efficiency of natural compounds is impacted by multiple parameters such as temperature, time and solvent polarity, among others, and their effects may be either independent or interactive. at the beginning of this study, the factors extraction solvent, solid-liquid ratio, temperature and time of extraction were investigated to determination the appropriate experimental ranges to be considered during the optimization process. as stated in the literature, for preparation of crude extracts with rosmarinic acid content, authors used methanol, ethanol, acetone and their water solutions (akowuah et al., 2005; almela et al., 2006; al et al., 1994; zelić et al., 2005). the best of rosmarinic acid yields was reached with 50 % (v/v) water solution of methanol or ethanol. yield of extracted compounds is dependent on their solubility in solvent, which dependents on polarity of solvent. for the evaluation of solvent polarity the dielectric constant is used. dependence of rosmarnic acid yields on dielectric constant (fig. 1) was developed on the base evaluation extraction yields using methanol, ethanol, propan-2-ol and their water solutions (33 and 66 %; v/v) as extraction solvents. dielectric constants were calculated according to equation 2: alcoholalcoholwaterwaterionwatersolut vv ** εεε += , (2) where ε is dielectric constant of extraction solvents and v is volume coefficient of resulting solution used as extraction solvent. 15 20 25 30 35 40 45 50 55 60 65 70 75 80 85 0 10 20 30 40 50 60 y ie ld o f r a m g/ g of d ry m at te r theoretical dielectric constant of extraction solvent fig. 1. dependence of rosmarinic acid yield on theoretical dielectric constant of extraction solvent. results indicated that the biggest rosmarinic acid yields were obtained using solvent with dielectric constant in the range from 48 to 59, which represented 33 – 47 % water solution of propan-2-ol. therefore, one of optimized parameter was concentration of propan-2-ol in water solution used as extraction solvent. dependence 178 ondrejovič, m. et al. of isolated compound yields on theoretical dielectric constant of extraction solvent is well-know from literature. similar course of this dependence was observed at various natural compounds such as antibiotics (bora and dutta, 2000) or pigments from paprika (kiss et al., 2000). the impact of the solid-to-liquid ratio on the extraction of rosmarinic acid from m. officinalis was conducted with four ratios (1:10, 1:20, 1:30 and 1:40; w/v) during 1 hour at 80 °c with 33 % (v/v) water solution of propan-2-ol as extraction solvent. the results of the one-way analysis of variance showed that there was a significant difference among the ratios studied. there was no statistically significant difference between the ratios 1:30 and 1:40 (w/v). the solid-liquid ratio optimal for rosmarinic acid extraction is between the ratios 1:20 and 1:30 (w/v). this survey is consonant with literature (akowuah et al., 2005; georgiev et al., 2006; baskan et al., 2007). 10 20 30 40 0 10 20 30 40 50 60 y ie ld o f r a m g/ g of d ry m at te r volume of extraction solvent ml/g of dry matter fig. 2. effect of the solid-liquid ratio on the extraction of rosmarinic acid from m. officinalis leaves over 1 hour with a 33 % (v/v) water solution of propan-2-ol at 80 °c. 0 20 40 60 80 100 120 36 38 40 42 44 46 48 50 52 54 56 58 60 y ie ld o f r os m ar in ic a ci d [m g/ g of d ry m at te r] extraction time [min.] fig. 3. kinetics of rosmarinic acid extraction with a 33 % (v/v) water solution of propan-2-ol at various temperatures (● – 40 °c; ▲ – 60 °c; ▼– 80 °c) by solid-liquid ratio 1:100. from kinetics of rosmarinic acid extraction represented in fig 3, it is evident, that maximum yield of rosmarinic acid was reached after 60 min of extraction for the three temperatures studied. the best bits were achieved using the exponential model, for the three temperatures and the range of time used, as expressed by the coefficients of determination (r2) (tab. 1). nova biotechnologica 9-2 (2009) 179 table 1. exponential models for the kinetic of rosmarinic acid extraction from m. officinalis leaves. y = a + b*exp(-x/c) temperature (°c) a b c r2 40 53.82 ± 0.37 -34.78 ± 3.23 16.76 ± 1.67 0.9752 60 57.34 ± 0.59 -25.75 ± 1.47 18.95 ± 2.46 0.9788 80 58.93 ± 0.54 -34.03 ± 1.06 9.22 ± 1.15 0.9556 3.2 optimization of extraction by rsm the rosmarinic acid extraction from m. officinalis was optimized through the rsm approach. a fixed extraction time (1 hour) and a fixed particle size (< 0.5 mm) were chosen. results of rosmarinic acid yields for all runs are reported in table 2. multiple linear regressions using the second-order polynomial model (eq. 1) were performed in the results of table 2. the response variability was explained by the model, the coefficient of multiple determination (r2) was 0.9253. 3.2.1 analyses of the regression coefficients and the response surface the regression coefficients of the model for rosmarinic acid yield obtained by the multiple linear regression are reported in table 3. variables in their coded form (table 2) permitted a direct interpretability of effects (linear, quadratic and interaction) of independent variables, and the surface plot (fig. 4) facilitated the visualisation of the statistically significant factors (denoted by the superscript letters on the regression coefficients of table 3) derived from the statistical analysis. table 2. experimental results for the response variable (rosmarinic acid yield) and independent variables (x1, x2 and x3) in original and coded form. factor 1 (x1) factor 2 (x2) factor 3 (x3) factor y standard order solid-liquid ratio (g/ml dm) propan-2-ol (%) temperature (°c) ra yield mg/g dm 1 0.035 (-1) 20 (-1) 32 (-1) 38.71 2 0.035 (-1) 20 (-1) 68 (1) 62.54 3 0.083 (1) 20 (-1) 32 (-1) 36.65 4 0.083 (1) 20 (-1) 68 (1) 33.52 5 0.035 (-1) 76 (1) 32 (-1) 21.04 6 0.035 (-1) 76 (1) 68 (1) 55.98 7 0.083 (1) 76 (1) 32 (-1) 17.88 8 0.083 (1) 76 (1) 68 (1) 30.59 9 0.059 (0) 48 (0) 20 (-1.68) 21.68 10 0.059 (0) 48 (0) 80 (1.68) 55.79 11 0.019 (-1.68) 48 (0) 50 (0) 62.62 12 0.099 (1.68) 48 (0) 50 (0) 17.37 13 0.059 (0) 1 (-1.68) 50 (0) 53.73 14 0.059 (0) 95 (1.68) 50 (0) 0.5 15 0.059 (0) 48 (0) 50 (0) 62.62 16 0.059 (0) 48 (0) 50 (0) 63.5 17 0.059 (0) 48 (0) 50 (0) 65.34 180 ondrejovič, m. et al. table 3. regression coefficients of second-order model for dependent variable – rosmarinic acid yield. model parameters ra yield intercept -89.391 temperature 3.52489 solid-liquid ratio 1837.34 linear propan-2-ol 0.78097 temperature x temperature -0.02493 solid-liquid ratio x solid-liquid ratio -13245.3 quadratic propan-2-ol x propan-2-ol -0.01559 temperature x solid-liquid ratio -14.2332 temperature x propan-2-ol 0.00668 interaction solid-liquid ratio x propan-2-ol 0.47061 regression coefficients with a statistically significant at p < 0.05 are printed in bold. as indicated by the p value, regarding the propan-2-ol proportion (x2), negative linear and quadratic effects were verified to be statically significant for rosmarinic acid yield. this result indicated that rosmarinic acid yield increases with decreasing of propan-2-ol proportion but quadratic effect of this variable parameter suggested forming of specific area whit maximal yield of rosmarinic acid. these results supported by results in first part of this study (an appropriate extraction solvent with dielectric constant between 48 and 55) and results of another study (durling et al., 2007). negative linear and quadratic effects of solid-liquid ratio (x1) suggested that the increase of extraction solvent volume to extraction material mass improves the rosmarinic acid yield. positive effect of temperature (x3) was detected, which confirms that the increase in temperature improves the rosmarinic acid yield. indeed, a higher temperature increases the solubility and diffusion coefficient of rosmarinic acid, allowing higher extraction rate. propan-2-ol proportion solid-liquid ratio y ie ld o f r a [m g/ g d m ] 35 45 55 65 75 85 (x 0,001) 20 40 60 80 0 10 20 30 40 fig. 4. response surface plot for yield of rosmarinic acid, in function solid-to-liquid ratio and proportion of propan-2-ol in extraction solvent at 50 °c. 3.3 determination and experimental validation of the optimal conditions in order to verify the predictive capacity of the model, an optimum condition was determined using the simplex method and the maximum desirability for the rosmarinic nova biotechnologica 9-2 (2009) 181 acid yield, and it was used for an extraction test (table 4). the measured values lay within a 95 % mean confidence interval of the predicted value for rosmarinic acid yields. these results confirm the predictability of the model for the extraction of rosmarinic acid from m. officinalis leaves in the experimental condition used. table 4. comparison of predicted and experimental values at optimal conditions of rosmarinic acid extraction. optimized conditions propan-2-ol 39 temperature [°c] 66 solid-liquid ratio 0.035 predicted value of rosmarinic acid yield [mg/g] 74.4 ± 2.59 experimental value of rosmarinic acid yield [mg/g] 72.6 ± 3.12 4. conclusions the response surface methodology was successfully employed to optimize the rosmarinic acid extraction from m. officinalis leaves. the second-order polynomial model gave a satisfactory description of the experimental data. an optimized condition for maximum extraction of rosmarinic acid was determined. the optimal conditions were – propan-2-ol proportion 39 %, extraction temperature 66 °c and solid-liquid ratio 1:29 (w/v). this study can by useful for the development of industrial extraction processes, including further studies concerning the optimal number of sequential steps to enhance the efficiency of a large-scale extraction system. references akowuah, g. a., ismail, z., norhayati, i., sadikun, a.: the effects of different extraction solvents of varying polarities on polyphenols of orthosiphon stamineus and evaluation of the free radical-scavenging activity. food chem., 93, 2005, 311-313. al, ch. b., deng, q. h., song, w. z., li, l. n.: salvianolic acid j, a depside from salvia flava. phytochemistry, 37, 1994, 907-908. almela, l., sanchez-munoz, b., fernandez-lopez, j., roca, m. j., rabe, v.: liquid chromatograpic-mass spectrometric analysis of phenolics and free radical scavenging activity of rosemary extract from different raw material. j. chromatogr. a, 1120, 2006, 221-223 baskan, s., oztekin, n., erim, f. b.: determination of carnosic acid and rosmarinic acid in sage by capillary electrophoresis. food chem., 101, 2007, 17481751 bora, m. m., dutta, n. n.: extraction equilibria of cephalosporin antibiotics with aliquat-33. j. chem. eng. data, 45, 2000, 399403 durling, n. e., catchpole, o. j., grey, j. b., webby, r. f., mitchell, k. a., foo, l. y., perry, n. b.: extraction of phenolics and essential oil from 182 ondrejovič, m. et al. dried sage (salvia officinalis) using ethanol-water mixtures. food chem., 101, 2007, 1417-1424 georgiev, m., kovatcheva, e., marcheva, n., ilieva, m.: purification rosmarinic acid extracts from lavandula vera mm cell biomass. food chem., 94, 2006, 111-114 kiss, g. a. c., forgács, e., cserháti, t., mota, t., morais, h., ramos, a.: optimisation of the microwave-assisted extraction of pigments from paprika (capsicum annuum l.) powders. j. chromatogr. a, 889, 2000, 41-49. silva, e. m., rogez, h., larondelle, y.: optimization of extraction of phenolics from inga edulis leaves using response surface methodology. separ. purif. technol., 55, 2007, 381-387 zelić, b., hadolin, m., bauman, d., vasić-rački, d.: recovery and purification of rosmarinic acid from rosemary using electrodialysis. acta chim. slov., 52, 2005, 126-130 microsoft word ondrejovic nb 9-3.doc nova biotechnologica 9-3 (2009) 313 isolation of antioxidants from alchemilla xanthochlora miroslav ondrejovič1,2, zuzana ondrigová1, janka kubincová2 1department of biotechnology, university of ss. cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic (miroslavondrejovic@gmail.com) 2food research institute, dept. biocentre, kostolna 7, sk-900 01, modra, slovak republic abstract: the aim of this study was to find conditions for isolation of antioxidants from alchemilla xanthochlora. the solid-liquid extraction of plant material with different solvents (n-hexane, chloroform, ethylacetate, methanol, and water) was used for preparation of crude extracts of antioxidants. for additional purification of crude extract, liquid-liquid extraction in different organic solvents (chloroform, ethylacetate, methanol) and water, and column chromatography with silica gel as stationary phase and mixture of chloroform : methanol as mobile phase were used. the content of active compounds was monitored by photometric method and special tlc analysis using dpph as basic reagent. tlc-dpph analysis of herbal extracts showed that antioxidants from alchemilla xanthochlora were separated into two groups with different polarity. finally, for the isolation of antioxidants from alchemilla xanthochlora were successfully used the following procedures: extraction of dried grounded plant material with methanol at 50°c during 1 hour, subsequent liquid-liquid extraction in isopropanol and water and fractionation of isopropanol extract by column chromatography. fraction with isolated antioxidants showed antioxidant activity 535.2 mg to g of fraction residue. keywords: antioxidants, alchemilla xanthochlora, extraction, purification 1. introduction alchemilla xanthochlora belongs to the somniferous herbs from the family rosaceae. it is commonly used for the locally treatment of various skin diseases. the antibacterial activity of this plant was related with its tannin content (djipa et al., 2000). in recent study, alchemilla xanthochlora was presented as herb with enormous antioxidant activity (trouillas et al., 2003; hamad et al., 2007) comparable with commonly used antioxidant sources such as strawberry, blackberry or raspberry (fikselová and ivanišová, 2008). various assays have been used for the analysis of natural antioxidants but the mostly widely used methods are those that involve generation of free radical species which are then neutralised by antioxidant compounds (arnao et al., 2001). the dpph method measures electron-donating activity of other compounds in the mixture and hence provides an evaluation of antioxidant activity due to free radical scavenging. any molecule that can donate an electron or hydrogen to a mixture will react with and bleach dpph. in qualitative analysis of antioxidants, the 2,2-diphenyl1-picrylhydrazyl (dpph) assay on tlc plates was used as a screening test for the radical scavenging ability of the compounds present in the different extracts (naik et al., 2003). 314 ondrejovič, m. et al. the aim of the present study was to evaluate the antioxidant activities of various solvent extracts and fractions acquired by solid-liquid and liquid-liquid extraction and column chromatography from alchemilla xanthochlora, and choose an extraction system suitable for isolation responsible compounds. 2. material and methods 2.1 plant material adult leaves of alchemilla xanthochlora were harvested with the twigs and dried at 40°c. thereafter, the leaves were separated from the twigs and cut in small squares of 1 – 1.5 cm2. this extraction material was stored in powder flask at laboratory temperature. 2.2 preparation of extracts 1 g of plant material was extracted with 20 ml of extraction solvent (hexane, chloroform, ethylacetate, methanol and distilled water) over 1 hour at 50°c. the extraction mixture was centrifuged at 3000 x g for 10 minutes and the supernatant was decanted. the solvent was removed under reduced pressure on the rotary vacuum evaporator at 50°c. the solid residue was solubilized in mixture of chloroform and water and water phase enhanced with saturated water solution of nacl was further extracted with ethylacetate and isopropanol, respectively. the isopropanol fraction (10 ml) was fractionated on a silica gel (20 g) eluted with chloroform: methanol (10:0; 9:1; 7:1; 5:1; 3:1; 1:1; 0:10). totally 21 fractions was analysed by tlc-dpph and photometric dpph analysis. 2.3 tlc-dpph analysis chemical constituents of plant extracts were analysed by thin layer chromatography (tlc) using aluminium-backed tlc plates (silica gel 60 f254). the tlc plates were developed with four following mobile phases as methanol : formic acid (10:1) (developing to ¼ of tlc plate length), chloroform : methanol (9:1) (developing to ½ of tlc plate length), toluene: acetone (7:3) (developing to ¾ of tlc plate length) and hexane: ethylacetate (5:1) (complete developing of tlc plate) respectively. between developing in mobile phases the plates were dried in the fume hood at 50 °c. to detect antioxidant compounds, chromatograms were sprayed with 0.2% 2,2-diphenyl-2-picryl-hydrazyl (dpph) in methanol, as an indicator. the presence of antioxidant compounds was detected by yellow spots against a purple background. 2.4 photometric dpph analysis the dpph assay was performed as described (paulová et al., 2004). in this assay, bht (butylhydroxytoluene) was used as positive control, and reaction mixtures nova biotechnologica 9-3 (2009) 315 contained a methanolic solution of 150 μm dpph (100 μl) and sample (25 μl) placed in a 96 well microplate and incubated at laboratory temperature for 10 minutes. after incubation, the absorbance was read at 517 nm and the radical-scavenging activity was determined by the following equation: dpph activity = [(ac as)/ac x 100] x mdpph/mrs where as is absorbance of reaction mixtures with sample, ac is absorbance of reaction mixtures with methanol instead of sample, mdpph is calculated mass of dpph in reaction mixture and mrs is calculated mass of extract/fraction residue. 3. results and discussion screening of antioxidants from alchemilla xanthochlora was made by preparation of crude extract with extraction solvents such as hexane, chloroform, ethylacetate, methanol and water. selected extraction solvents can extract a wide range of natural compounds from plant material. n-hexane chloroform ethylacetate methanol water 0,0 0,5 1,0 1,5 2,0 2,5 3,0 a nt io xi da nt a ct iv ity [g o f d p p h to g o f c ru de e xt ra ct r es id ue ] extraction solvent fig. 1. antioxidant activity of extracts from alchemilla xanthochlora prepared with various extraction solvents over 1 hour at 50°c. a antioxidant activity measured by photometric method expressed in g of dpph scavening with one g of crude extract residues; b – qualitative composition of antioxidants measured by tlc-dpph method (h – n-hexane, ch – chloroform, e – ethylacetate, m – methanol, v – distilled water). the tlc-dpph screening method (fig. 1) indicated the presence of antioxidant compounds in all tested extracts. the most prominent antioxidant activity was observed particularly in methanolic extract (fig. 1). the presence of two various groups of antioxidants from alchemilla xanthochlora were confirmed. the first group of antioxidants represents compounds with lipofilic character such as β-carotene or lycopene. compounds from this group are extracted in extraction solvents such as hexane, chloroform, ethylacetate and methanol. the second group of antioxidants comprises compounds with properties like flavonoid or coumarin glycoside. compounds from this group are extracted in methanol and water. in the literature, a b 316 ondrejovič, m. et al. phytochemical screening on the genus alchemilla revealed that there are flavonoids (e.g. quercetin-3-arabinopyranoside and quercetin-3-glucuronide) (lamaison et al., 1991; fraisse et al., 2000), tannins, polyphenols and coumarins (esculetin) (schimmer and eschelbach, 1997). these compounds may be founded in the second antioxidant active group. for the separation of these groups of natural antioxidants, the plant material can be extracted with chloroform and water. the crude extract for another analysis was prepared with methanol to obtain present antioxidants in alchemilla xanthochlora. chloroform ethylacetate isopropanol water phase 0 10 20 30 40 50 60 70 80 p ar tit io n of c ru de e xt ra ct [% ] extraction solvent % aa % sr fig. 2. effect of the extraction solvent by extraction liquid-liquid on the extraction of antioxidants from crude extract of alchemilla xanthochlora (%aa – part of crude extract antioxidant activity in the fractions; % sr – part of crude extract residue in the fractions). at first, the crude methanolic extract was purified to eliminate ballast compounds by liquid-liquid extraction. three various solvents (chloroform, ethylacetate, isopropanol) and water were used. the suitability of extraction solvent in the extraction liquid-liquid was studied by the percent evaluation of antioxidant activity and solid residue from crude extracts. these parameters were used to describe the purity and efficiency of separation step – extraction liquid-liquid. the results of these experiments are presented in the fig. 2. successive extraction was shown that more than 80 % of antioxidant activity of crude methanolic extract from alchemilla xanthochlora was cumulated in isopropanol fraction and more than 60% of crude extract residue was eliminated from isopropanol fraction by these methods. therefore, the necessity of liquid-liquid extraction of crude extract with isopropanol and water before separation by column chromatography is evident. purification of antioxidants from extracts of alchemilla xanthochlora was executed by column chromatography on the silica gel with gradient elution of chloroform : methanol mixtures. the separation of antioxidants on the column was studied by measuring of radical-scavening activity in obtained fractions (fig. 3). used separation system is suitable for isolation of antioxidants from alchemilla xanthochlora as for active compounds from first lipofilic group as for active compounds from second hydrophilic group. antioxidative active compounds were nova biotechnologica 9-3 (2009) 317 cumulated in 5 fractions (4-5; 17-19) with high content of antioxidant active compounds. 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 0 100 200 300 400 500 600 a nt io xi da nt a ct iv ity [m g of d p p h /g o f f ra ct io n re si du e] fraction number fig. 3. antioxidant activity of fractions of isopropanol fraction of crude methanolic extract from alchemilla xanthochlora. (1-3 – chloroform; 4-6 – chloroform : methanol (9:1)(v/v); 7-9 – chloroform : methanol (7:1)(v/v); 10-12 – chloroform : methanol (5:1)(v/v); 13-15 – chloroform : methanol (3:1)(v/v); 16-18 – chloroform : methanol (1:1)(v/v); 19-21 – methanol). 4. conclusions for the isolation of antioxidants from alchemilla xanthochlora, extraction of the dried grounded plant material with methanol at 50°c during 1 hour with subsequent extraction liquid-liquid of crude extract residue between phases of water and isopropanol and column chromatography on silica gel with gradient elution of chloroform : methanol mixtures were successfully used. isolated fraction showed specific antioxidant activity 535.2 mg dpph to g of fraction residue. the results of this work may be used for determination of antioxidant active compounds from alchemilla xanthochlora. references arnao, m.b., cano, a., acosta, m.: the hydrophilic and lipophilic contribution to total antioxidant activity. food chem., 73, 2001, 239-244. djipa, c.d., delmee, m., quetin-leclercq, j.: antimicrobial activity of bark extracts of syzygium jambos (l.) alston (myrtaceae). j. ethnopharmacol., 71, 2000, 307-313. fikselová, m., ivanišová, e.: byliny a čaje ako potenciálne zdroje prírodných antioxidačných látok. in: aktuálne problémy riešené v agrokomplexe. spu, nitra, 2008, 334-338. fraisse, d., heitz, a., carnat, a., carnat, a.p., lamaison, j.l.: quercetin 3-arabinopyranoside, a major flavonoid compound form alchemilla xanthochlora. fitoterapia, 71, 2000, 463-464. 318 ondrejovič, m. et al. hamad, i., erol-dayi, o., pekmez, m., onay-ucar, e., arda, a.: free radical scavenging activity and protective effects of alchemilla vulgaris (l.). j. biotechnol., 131, 2007, s40-s41. lamaison, j.l., carnat, a., petitjean-freytet, c., carnat, a.p.: quercetin-3-glucuronide, main flavonoid of alchemilla, alchemilla xanthochlora rothm. (rosaceae). ann. pharm. fr., 49, 1991, 186-189. naik, g.h., priyadarsini, k. i., satav, j.g., banavalikar, m.m., sohoni, d.p., biyani, m.k., mohan, h.: comparative antioxidant activity of individual herbal components used in ayurvedic medicine. phytochemistry, 63, 2003, 97-104. paulová h., bochořáková h., táborská e.: metody stanovení antioxidační aktivity přírodních látek in vitro. chem. listy, 98, 2004, 174-179 schimmer, o., eschelbach, h.: esculetin in alchemilla speciosa: identification and antimutagenic properties. pharmazie, 52, 1997, 476-478. trouillas, p., calliste, c.a., allais, d.p., simon, a., marfak, a., delage, c., duroux, j.l.: antioxidant, anti-inflammatory and antiproliferative properties of sixteen water plant extracts used in the limousin countryside as herbal teas. food chem., 80, 2003, 399-407. microsoft word szabo nb 9-3.doc nova biotechnologica 9-3 (2009) 231 comprehensive investigation of the corrosion state and surface properties of the stainless steel tubes of steam generators andrea szabó nagy1,2, kálmán varga1, bernadett baja1, zoltán németh1, dezső oravetz3, zoltán homonnay4, ernő kuzmann4, jános schunk5, gábor patek5 1institute of radiochemistry and radioecology, university of pannonia, h-8201 veszprém, p. o. box: 158, hungary (vargakl@almos.vein.hu) 2department of physics and chemistry, university of istván széchenyi, h-9026 győr, hungary (nszaboa@sze.hu) 3institute of materials engineering, university of pannonia, h-8201 veszprém, hungary 4institute of chemistry, university of loránd eötvös, h-1117 budapest, hungary 5paks npp ltd., h-7031 paks, p. o. box: 71, hungary abstract: evaluating the water chemistry in the primary circuit and the effect of chemical decontamination of the heat exchanger tubes performed by the ap-citrox (ap: alkaline permanganate; citrox: citric and oxalic acid) procedure at paks npp (hungary), a project dealing with the comprehensive investigation of the general corrosion state of the steam generators (sgs) has been initiated. owing to the fact that there is no investigation method available for the in-situ monitoring of the inner surfaces of heat exchanger tubes, a research program based on sampling as well as on ex-situ electrochemical (voltammetric) and surface analytical measurements (sem-edx, cems, xrd, xps) was developed and elaborated. in the time period of 2000-2008 within the frame of the above project 45 stainless steel specimens, cut out from various locations of the steam generators of the paks npp were investigated. based on the measured corrosion characteristics (corrosion rate, thickness and chemical composition of the protective oxide-layer) it was found that these parameters are strongly dependent on the decontamination history of steam generators. the present work gives a brief overview on the general corrosion state of the heat exchanger tubes of sgs, concerning the long-term effects of the ap-citrox procedure on the chemical composition and structure of the protective oxide-layer. key words: stainless steel, steam generator, corrosion, decontamination 1. introduction some years ago, a systematic study of the primary and secondary circuit water chemistry data, and the corrosion effects of the chemical decontamination procedures performed at paks npp made it clear that an overall estimation of the corrosion state of the steam generators, i.e. the preparation of a so-called ‘corrosion map’ is unavoidable. this ‘corrosion map’ takes a survey of the corrosion features of the heat exchanger tubes made from austenitic stainless steel in the sgs. owing to the fact that there are no investigation methods available for the in-situ monitoring of the inner 232 szabó, n.a. et al. and outer surfaces of heat exchanger tubes, a research project based on sampling as well as on ex-situ electrochemical (voltammetric) and surface analytical measurements (sem-edx, cems, xrd, xps) was launched in the year 2000. within the frame of the above project the inner surfaces of 45 stainless steel samples, which had been in contact with the primary coolant, originating from various locations in the sgs (24 sgs altogether for the 4 reactors) in the time period of 20002008 were investigated. based on the measured corrosion characteristics (corrosion rate, thickness and chemical composition of the protective oxide-layer) it was found that these parameters are strongly dependent on the decontamination history of steam generators. during the time period of 1993-2001 chemical decontamination of 24 sgs in the blocks 1-3 of the paks npp (hungary) were carried out by a non-regenerative version of ap-citrox technology, sometimes in 2 or 3 consecutive cycles. the applied version of the ap-citrox procedure is an eight-step process, including an oxidizing pre-treatment of the surface with alkali potassium permanganate followed by a concentrated mixture of citric and oxalic acids to remove the contaminated surface layer (varga, 2004; rado et al., 2006). our previous studies have revealed that a ”hybrid” structure of the amorphous and crystalline phases is formed in the outermost surface region of the austenitic stainless steel tubes as an undesired consequence of the industrial application of the apcitrox technology (varga et al., 2006; homonnay et al., 2006; szabó et al., 2006; homonnay et al., 2007). the formation of this mobile oxide-layer increased the amount of the corrosion products in the primary circuit significantly, resulting in magnetite deposition on fuel assemblies. the primary aim of this paper is to report some new findings obtained by electrochemical (voltammetric) and sem-edx methods in order to reveal the beneficial changes in the corrosion properties, morphology and chemical composition of the inner surfaces of the decontaminated heat exchanger tubes after 4-7 years under normal operation conditions. in addition, special attention is paid to the comparative mobility studies of the surface oxide layers in boric acid solution by making use of a pilot plant model system and icp-oes method. 2. materials and methods the experiments have been performed on 45 austenitic stainless steel specimens (type: 08x18h10t (gost 5632-61) which corresponds to aisi 321 and din 1.4541; outer diameter: 16 mm, average wall thickness: 1.6 mm) originating from different sgs of the paks npp. the main characteristics of the specimens obtained from the same sgs at various sampling date are given in table 1. the surface decontamination procedure of the heat exchanger tubes was carried out at paks npp according to a nonregenerative version of the ap-citrox technology (varga et al., 2004; rado et al., 2006). the passivity of the tube samples was studied by potentiostatic polarization method. the experiments were carried out by the means of a voltalab 40 (radiometer) type electrochemical measuring system controlled by pc. the measurements were carried out in boric acid solution (c = 12 g·dm-3) in argon gas nova biotechnologica 9-3 (2009) 233 atmosphere (99.999 v/v % ar). the schematic of the measuring system, the detailed experimental procedure and the determination of the corrosion parameters have been described in our earlier papers (varga et al., 2006; szabó et al., 2006). the morphology and chemical composition of the oxide layer developed on the inner surfaces of the 45 stainless steel specimens were studied by scanning electron microscopy (sem), equipped with an energy dispersive x-ray microanalyzer (edx) (type: jeol jsm-50a, controlled with röntec edr 288 software). in addition, the metallographic cross sections of tube specimens were also studied (varga et al., 2006; szabó et al., 2006). the mobility of the surface oxide layers grown on the inner surfaces of the sg tube specimens was studied in boric acid solution, modelling the first 30 hours of reactor restarting period. a pilot plant circulation system elaborated earlier (varga, 2004) was utilized for the boric acid treatment. using icp-oes method, the concentrations of the main alloying components (fe, cr, ni) dissolved into the solutions as a function of the time were determined. additionally, the solutions removed from circulation system were filtered, and the amount of dispersed corrosion product was weighed after 1 week drying. from these findings the average thickness values of the oxide layer removed from the surface were calculated as a function of the year of sampling (baja et al., 2009). table 1. main characteristics of the stainless steel tube specimens originating from the same sgs at various sampling date. number of sg specimens* year of decontamination time period between the last decontamination and the sampling [year] i/1 1996, 1997 4 i/2 1996, 1997, 2001 4 ii/1 1996 1 ii/2 1996 4 ii/3 1996, 2001 4 iii/1 1999, 2001 1 iii/2 1999, 2001 3 iii/3 1999, 2001 5 iv/1 2001 1 iv/2 2001 5 v/1 2001 0 v/2 2001 4 vi/1 1993 7 vi/2 1993, 2001 3 vii/1 2001 1 vii/2 2001 1 vii/3 2001 6 viii/1 2001 2 viii/2 2001 6 * roman numerals refer to the same sgs. 234 szabó, n.a. et al. 3. results and discussion some illustrative polarization curves measured in boric acid solution at the inner surface of the stainless steel specimens cut out from the same sgs of the paks npp at various sampling date are shown in fig. 1. as may be seen in fig. 1, the inner surfaces of the samples have a passive character in a wide potential interval next to the corrosion potential. the average corrosion rates calculated for all samples are not higher than the literature data which were measured for the stainless steels type 08x18h10t and aisi 321 in aqueous solutions having similar composition (0.3 – 4 μm/year) (geraszimov and monahov, 1981; lister, 2003) and references therein). the electrochemical data imply that no unfavourable trend in the passivity of the inner surfaces of the heat exchanger tubes can be detected since the last sg decontaminations performed in 2000 and 2001. -0,4 -0,2 0,0 0,2 0,4 0,6 0,8 e / v [sce] lg i / a c m -2 ii/2 -6 -7 -5 -8 -9 ii/1 ii//3 -0,4 -0,2 0,0 0,2 0,4 0,6 0,8 e / v [sce] lg i / a c m -2 iii/3 -6 -7 -5 -8 -9 iii/1 iii/2 -10 fig. 1. potentiostatic polarization curves measured at the inner surface of the samples no. ii and no iii in boric acid solution (c = 12 g·dm-3). scan rate: 10 mv·min-1. nova biotechnologica 9-3 (2009) 235 the long-term tendencies in the morphology and chemical composition of the protective oxide layers formed on the inner surfaces of the heat exchanger tubes were investigated by sem-edx method. some typical sem micrographs of the inner surface and the metallographic cross-section of steel samples studied are shown in fig. 2. as may be seen in fig. 2, on the surfaces of samples never-decontaminated, which had been in contact with the primary boric acid coolant, a thin film (thickness up to 1-2 μm) of the grown-on oxides with excellent protective character can be detected after various periods of normal operation. this grown-on layer, next to the bulk metal, is a non-stoichiometric mixed oxide of spinel structure (crxniyfe3-x-yo4, where 0≤x+y≤3) (szabó et al., 2006; baja et al., 2009). significant amounts of the crystalline magnetite (fe3o4) and occasionally some hematite (fe2o3) are deposited onto surfaces of the grown-on passive layer. a b c fig. 2. selected sem micrographs and metallographic cross sections (m = 3000 x) detected on the inner surface of a sample has never been decontaminated (a), and samples decontaminated four years before sampling (b (no. (ii/2) and c (no. i/2)). 4-7 years after the chemical decontamination treatment medium thick or thick (up to 11 µm) oxide-layer having amorphous character (“hybrid” structure) can be detected on the inner surfaces of all tube samples studied. however, the surface region is rich in chromium and nickel which refers to the presence of spinel structure (nickelferrite and chromites) in the oxide layers (homonnay et al., 2006). the increased amount of the crand ni-rich spinel constituents improve the chemical stability of the oxide-layers formed on stainless steel in the long run (baja et al., 2009). moreover, it is special importance to emphasize that the protective oxide layer of the sample no. i/2 (see fig. 2) covered with large crystals which are also rich in chromium and nickel. 236 szabó, n.a. et al. the experimental findings of the mobility studies of the surface oxide layers in boric acid solution (see fig. 3), in accordance with the sem-edx results, demonstrate without any doubt that beneficial changes in the phase and chemical compositions are accompanied with a suppressed mobility of oxide films grown on the surface of decontaminated tube specimens, and these oxide films have basically the same mechanical stability for both types of heat exchanger tubes in the time period of 2006-2007. fig. 3. average thickness of the oxide layer removed from the surfaces into the boric acid solution as a function of the sampling year. 4. conclusions in the frame of a project dealing with the comprehensive investigation of the corrosion state of the steam generators of the paks npp, hungary, the long-term tendencies in the corrosion state, chemical composition and structure of protective oxide layer of the heat exchanger tubes decontaminated by ap-citrox procedure have been studied. the ap-citrox chemical decontamination procedure does exert an undesired transformation on the stable constituents of surface layer, leading to the formation of a “hybrid” structure of amorphous and crystalline phases. as a consequence of this detrimental prompt effect, some adverse features (medium thick or thick oxide-layer with great mobility) could be detected after 1-3 years of applying the ap-citrox procedure. however, the electrochemical data imply that no unfavourable trend in the passivity of the inner surfaces of the heat exchanger tubes can be detected since the last sg decontaminations performed in 2000 and 2001. some beneficial changes (dominance of the crand ni-rich inverse spinel) take place in the phase and chemical compositions of the oxide-layers grown on decontaminated tube samples after 4-7 years under normal operation conditions. the increased amount of the crand ni-rich spinel constituents improve the chemical stability of the oxide-layers formed on stainless steel in the long run. the above nova biotechnologica 9-3 (2009) 237 changes are accompanied with a suppressed mobility of the oxide films grown on the surface of decontaminated tube specimens and yield inner surfaces covered with oxide-layers having basically the same mechanical stability for both types of heat exchanger tubes in the time period of 2006-2007. acknowledgements: this work was supported by the paks npp co. ltd (paks, hungary). references baja, b., varga, k., szabó, n.a., németh, z., kádár, p., oravetz, d, homonnay, z., kuzmann, e., schunk, j., patek, g.: long-term trends in the corrosion state and surface properties of the stainless steel tubes of steam generators decontaminated chemically in vver type nuclear reactors. corrosion sci., 2009, (in press). geraszimov, v.v., monahov, sz.: materiali jadernoj techniki. atomizdat, moskva, 1981 (hungarian translation). homonnay, z., kuzmann, e., stichleutner, s., varga, k., németh, z., szabó, a., radó, k., makó, k.é., kövér, l., cserny, i., varga, d., tóth, j., schunk, j., tilky, p., patek, g., oszvald, f.: comprehensive investigation of the corrosion state of the heat exchanger tubes of steam generators, part ii. chemical composition and structure of tube surfaces. j. nucl. mater., 348, 2006, 191-204. homonnay, z., szilágyi, p.á., kuzmann, e., varga, k., németh, z., szabó, a., radó, k., schunk, j., tilky, p., patek, g.: corrosion study of heat exchange tubes in pressurized water cooled nuclear reactors by conversion electron mössbauer spectroscopy. j. radioanal. nucl. chem., 273, 2007, 85-90. lister, d.h.: some aspects of corrosion in cooling water systems and their effects on corrosion product transport. proceedings of the eurocorr 2003, budapest, hungary, 28 september – 2 october, 2003, (on cd-rom). radó, k., németh, z., varga, k., schunk, j., kőrösi f.: fundamental issues of the effective decontamination of the steam generators of paks npp. j. radioanal. nucl. chem., 268, 2006, 313-322. szabó, a., varga, k., németh, z., radó, k., oravetz, d., makó, k.é., homonnay, z., kuzmann, e., tilky, p., schunk, j., patek, g.: effect of a chemical decontamination procedure on the corrosion state of the heat exchanger tubes of steam generators. corrosion sci., 48, 2006, 2727-2749. varga, k.: the role of interfacial phenomena in the contamination and decontamination of nuclear reactors. in: horányi, g. (ed.), radiotracer studies of interfaces, interface science and technology, vol. 3, elsevier b.v., amsterdam, 2004, 313-358. varga, k., németh, z., homonnay, z., szabó, a., radó, k., oravetz, d., schunk, j., tilky, p., oszvald, f.: comprehensive investigation of the corrosion state of the heat exchanger tubes of steam generators, part i. general corrosion state and morphology. j. nucl. mater., 348, 2006, 181-190. microsoft word luptakova nb 9-2.doc nova biotechnologica 9-2 (2009) 147 positive and negative aspects of sulphate-reducing bacteria in environment and industry alena luptakova1, eva macingova1, vlasta harbulakova2 1department of mineral biotechnology, institute of geotechnics of slovak academy of sciences, watsonova 45, kosice, sk-043 53, slovak republic (luptakal@saske.sk), (macingova@saske.sk) 2technical university of košice, civil engineering faculty, institute of building and environmental engineering, vysokoškolská 4, košice, sk-042 00, slovak republic, (vlasta.harbulakova@tuke.sk) abstract: the submitted work is oriented on the study of two aspects of the sulphate-reducing bacteria metabolism: the metals bioprecipitation and the concrete biodeterioration. the bioprecipitation of metals with the bacterially produced hydrogen sulphide by sulphate-reducing bacteria (srb) represents the positive effect of the srb existence in the environment. it allows the industrial exploitation in the area of the removal metals from industrial wastewaters. referred method involves principal stages such as: hydrogen sulphide bacterial production, metals precipitation by biologically produced hydrogen sulphide, metal sulphides separation, setting ph of the filtrate from previous steps by 1m naoh and metal hydroxides separation. the basis of the first stage i.e. the hydrogen sulphide bacterial production is the cultivation of srb. in the laboratory conditions the sodium lactate is the energetic substrate for the growth of bacteria. its price is not economic for the application in the practice and is needed investigate the alternative substitutes. therefore was studied the cultivation of sulphate-reducing bacteria to using the selected energetic substrates such as: calcium lactate, glycerol and whey. experimental studies confirm that all chosen substrates are suitable alternative substrates of sodium lactate for the bacterial sulphate-reduction. in the regard to the efficiency of bacterial sulphate reduction the calcium lactate is the best. the biodeterioration of the concrete presents the negative effect of the srb existence in the environment. the research was oriented on the simulation of the biodeterioration of concrete samples under the simultaneous influence of the sulphur-oxidising bacteria genera acidithiobacillus thiooxidans and sulphatereducing bacteria genera desulfovibrio in the environs of the waste water, the acid mine drainage, the nutrient medium and the distilled water. the observation of the surface structure changes of concrete samples confirms the highest biodeterioration influences in the case of the acid mine drainage application. key words: sulphate-reducing bacteria, sulphur-oxidising bacteria, sulphuretum, bioprecipitation, biodeterioration 1. introduction sulphur is widely distributed on the earth and occurs predominantly bound in the form of sulphides, sulphates or as elemental sulphur. in the nature sulphur circulates permanently because it is continuously oxidized or reduced by chemical or biological processes. in a biogeochemical sulphur cycle (fig. 1) the biological transformations may have either assimilatory or dissimilatory metabolic functions. with the exception of animals and humans, most plants, fungi and bacteria are capable of performing an assimilatory reduction of sulphate to sulphide, which is necessary for the biosynthesis 148 luptakova, a. et al. of sulphur containing cell compounds. on the other hand the energy producing dissimilatory sulphur metabolism is restricted to a few groups of bacteria. these groups include microorganisms such as: anaerobic dissimilatory sulphate reducers (bacteria desulfovibrio, desulfotomaculum, desulfomonas,….), anaerobic dissimilatory sulphur reducers (bacteria such as desulfuromonas,…), anaerobic phototrophic sulphur oxidisers (some cyanobacteria and most anoxygenic phototrophic bacteria), aerobic chemotrophic sulphur oxidisers (bacteria such as acidithiobacillus, sulfolobus, thiospira, thiobacterium, ….), anaerobic chemotrophic sulphur oxidisers (bacteria such as acidithiobacillus denitrificans, thiomicrospira denitrificans,..) (rehm and reed, 1981). fig. 1. the biological sulphur cycle (rehm and reed, 1981; conformed). 1 assimilatory sulphate reduction by plants, fungi and bacteria; 2 death and decomposition by fungi and bacteria; 3 sulphide assimilation by bacteria and some plants; 4 excretion of sulphate by animals; 5 dissimilatory sulphatereducing bacteria; 6 dissimilatory sulphur-reducing bacteria; 7 phototrophic and chemotrophic sulphideoxdizing bacteria; 8 phototrophic and chemotrophic sulphur-oxidizing bacteria. the microbial population of dissimilatory part is called “sulphuretum”. its activity is the fundamental of many processes in the nature and industry (e.g. biocorrosion, bioleaching, bioprecipitation, biodeterioration). the typical species of sulphate-reducing bacteria (srb) is desulfovibrio desulfuricans, which reduce sulphates according the reaction (1): srb 2 ch3chohcoo+ so42————> 2 ch3coo+ 2 hco3+ h2s (1) srb produce considerable amount of hydrogen sulphide (h2s). consequently participation of biologically produced hydrogen sulphide in next processes mentions on the positive or negative influence of the srb metabolism in the environment and industry (table 1). sulphuretum 8 4 so4 2 biologically bound sulphur s0 s2 1 5 2 3 7 6 assimilatory part dissimilatory part nova biotechnologica 9-2 (2009) 149 table 1. some influence of the srb metabolism in the environment and industry. positive influence negative influence attendance in biogenesis of oil hydrocarbons biocorrosion of pumping machinery attendance in biogenesis of sulphur deposits blackening and discoloration of products participation in the biological sulphur cycle biodeterioration of concrete removal of heavy metals from waste waters biodeterioration of building materials removal of so4 2from mine waters production of smell production of sulphur from waste waters devaluation of gasoline removal of sulphur from crude oil, petrol and coal 1.1 positive influence of the srb metabolism in the environment and industry the positive influence of srb is based on the process called bioprecipitation, when the biologically produced hydrogen sulphide precipitates of heavy metals from aqueous solution in the metal sulphides form. along this line the bacterial sulphate reduction (reaction 1) has the major application for the removal of heavy metals from industrial waste waters. it is suitable method for removal heavy metals from acid mine drainage (amd). amd generation is the most serious environmental problem created mainly by the mining industry of the sulphide minerals. the impacts of acid mine water pollution on biological systems are mostly severe. the consequence of acidity and heavy metal contamination of amd in aquatic and terrestrial ecosystems is a reduction in both species diversity and the total biomass composition of systems. nowadays is pay attention to biotreatment of amd by selective sequential precipitation to recover metals as hydroxides and sulphides. it is the process of the heavy metals precipitation by bacterially produced hydrogen sulphide with the combination of the metals precipitation by sodium hydroxide at the various values of ph amd (tabak et al., 2003). in general these methods involve principal stages such as: the biological sulphate reduction i.e. the hydrogen sulphide bacterial production, the metals precipitation by biologically produced hydrogen sulphide, the precipitate filtration, the setting ph of the filtrate by 1m naoh with simultaneously precipitation of metals as hydroxides and metal hydroxides separation. the basis of the first stage the biological sulphate reduction is the cultivation of srb. in the laboratory conditions the sodium lactate is the energetic substrate for the growth of bacteria. its price is not economic for the application in the practice and is needed investigate the alternative substitutes. various types of organic substances have been employed as electron donors and carbon sources including sewage sludge, wood chips, animal manure, vegetal compost, mushroom compost, whey and other agricultural waste (dvorak et al., 1992). in addition, synthetic organic compounds have also been used as electron donors, especially small molecular weight compounds, such as lactate, acetate, propionate, pyruvate and butyrate. ethanol and other alcohols can also be used. nearly all of these compounds are known to be fermentation products of anaerobic bacterial 150 luptakova, a. et al. degradation of carbohydrates, proteins and other constituents of dead biomass. molasses, which contains a high amount of sucrose, has also been used as electron donor. therefore was studied the cultivation of srb to using the selected energetic substrates such as: calcium lactate, glycerol and whey. 1.2 negative influence of the srb metabolism in the environment and industry on the negative influence of the srb to suggest the aspect of the biologically produced hydrogen sulphide oxidation by bacteria acidithiobacillus thiooxidans to the sulphuric acid, which corrode some materials. this process is named the concrete biocorrosion or the concrete biodeterioration. it is the term for the concrete destruction by biogenic acid (e.g. biogenic sulphuric acid) that is generated predominantly by the sulphur-oxidising bacteria genera acidithiobacillus thiooxidans and sulphate-reducing bacteria genera desulfovibrio through diverse mechanisms (okabe et al., 2007). the concrete biodeterioration has a serious economic impact worldwide, especially when the replacement or repair of municipal sewer systems is required. in sewer systems and wastewater treatment facilities where high concentrations of hydrogen sulphide, moisture, and oxygen are present in the atmosphere, the deterioration of concrete is caused mainly by biogenic sulphuric acid. roberts et al. described the general mechanism for the sulphuric acid caused corrosion of sewer systems (robertset et al., 2002). in the first step, hydrogen sulphide is produced by srb under anaerobic conditions in sewer pipes. this one enters the sewer atmosphere by volatilization and dissolves in the condensate on the sewer crown. finally, sulphur-oxidizing bacteria acidithiobacillus thiooxidans oxidize the dissolved hydrogen sulphide and other sulphur compounds to sulphuric acid, which corrodes the concrete. 2. materials and methods 2.1 positive influence of the srb metabolism in the environment and industry microorganisms the cultures of srb (desulfovibrio desulphuricans) were used, which was isolated from the potable mineral water (gajdovka spring, slovakia). bacteria desulfovibrio desulphuricans were selected from the mixed cultures by the modified dilution method (karavajko et al., 1988). cultivation of sulphate-reducing bacteria series of cultivation tests were studied in the hermetically closed glass jar at 30 °c, during 10 days under anaerobic conditions. the anaerobiosis was generated by an inert gas (n2) and chemically with sodium thioglycollate. the total volume of filling solution with ph 7.5 consisted from 50ml of the bacterial cultures and 400 ml the classical selective nutrient medium dsm-63 postgate′s c (the energetic substrate for the growth of srb was sodium lactate (dl -na)) or its the modifications. the basis of this modification was the dlnova biotechnologica 9-2 (2009) 151 na substitution by the adequate amount of chosen substrates: the calcium lactate (dlca), the glycerol (gly) and the whey (srv). sodium lactate, calcium lactate and glycerol were used in the form of chemicals with the analytical grade. whey was bought in the chemist (i.e. non analytical grade). analytical procedures a turbidimetric method was used to measure the sulphate concentration. a glass ph electrode combined with the reference ag/agcl electrode was used to measure ph by digital phmeter gprt 144 agl (germany). 2.2 negative influence of the srb metabolism in the environment and industry microorganisms for the experiments were used two types of bacterial cultures: sulphate-reducing bacteria desulfovibrio desulphuricans and sulphur-oxidising bacteria acidithiobacillus thiooxidans. bacteria desulfovibrio desulphuricans were isolated from the potable mineral water (gajdovka spring, slovakia). the srb were selected from the mixed cultures by the modified dilution method (karavajko et al., 1988). bacteria acidithiobacillus thiooxidans were isolated from the acid mine water (the shaft pech, the deposit smolník, slovakia). the isolation and following cultivation of the acidithiobacillus thiooxidans clean bacterial culture was realised using waksman´s and joffe´s selective nutrient medium by the plate dilution method (karavajko et al., 1988). concrete specimens – concrete samples in the cylinder form (25 mm diameter and 20 mm height) were taken from pipes produced using the normal industrial processes. before experiments samples were sterilized in 70% ethanol and dried in oven at 60ºc to constant weight. concrete biodeterioration – the glass desiccator was used as reactor. concrete samples were put into reactor and inserted into four containers: the first was filled by waste water (ww), the second by acid mine drainage (amd), the third by nutrient medium for acidithiobacillus thiooxidans (nm) and the fourth by distillated water (dv). the reactor was interconnected with the flask filled by bacterial cultures desulfovibrio desulphuricans and the flask filled by cadmium acetate for to capture of h2s. concrete samples were every 7 days inoculated by acidithiobacillus thiooxidans and in the same period the change of nutrient medium for desulfovibrio desulphuricans were realized during 90 days. methods – the disruption and damages of the concrete surface were investigated by stereomicroscopy, atomic force microscopy (afm) and electron microscopy. mineralogical stereomicroscope stm 723 zoom with the combination of digital camera olympus – c-770 ultra zoom was used for upper (not immersed) part concrete samples study because of noticeable changes in structure of concrete. afm (jpk instruments, germany) was used for both (immersed and not immersed) parts of concrete samples investigation. a nanowizardii contant mode afm was used to image the surface of concrete samples. compounds precipitated onto samples surface were investigated by scanning electron microscopy (sem). the qualitative analyses of precipitates from samples surface were investigated by energy dispersive spectrometry (eds) analysis. 152 luptakova, a. et al. 3. results and discussion 3.1 positive influence of the srb metabolism in the environment and industry the growth of srb in all liquid mediums (without abiotic controls) was demonstrated by the sensorial detection of h2s typical odour, the srb presence by the origin of fes according following reaction (2), fe2+ is standard compound of nutrient medium dsm-63 postgate′s c: fe2+ + h2s ⎯→fes + 2h + (2) during experiments were observed the decrease of the sulphates concentration. the formation of black precipitates, the sensorial detection of classical strong h2s smell and the decrease of sulphate concentration were not observed in the abiotic control. it confirms that aforesaid changes were caused by the bacterial metabolism of srb. fig. 2 documents, that all used substrates are suitable alternative substitutes. in the regard to the amount of reduced sulphates the calcium lactate is the best. 0 20 40 60 80 100 dl-na dl-ca gly srv a m on ut o f re du ce d su lp ha te s [% ] fig. 2. comparison of reduced sulphates amount with srb by using substrates: sodium lactate (dl-na), calcium lactate (dl-ca), glycerol (gly), whey (srv). 3.2 negative influence of the srb metabolism in the environment and industry the most considerable biodeterioration of concrete was observed on samples immerged into acid mine drainage. in the first instance the changes of concrete samples structures were observed by stereomicroscopy. fig. 3 illustrates a surface of concrete specimen before experiment. fig. 4 shows the visible surface changes after 90 days sulfuretum simulation of samples taken from amd. for detailed study of concrete samples surface changes afm method was used. in fig. 5 the surface of concrete sample before experiment is shown. the surface is quite smooth, with the low roughness. fig. 6 demonstrates the image of samples taken from amd after 90 days sulfuretum simulation. on figure is visible that the roughness increased and some aggregates were fallen out of concrete surface. nova biotechnologica 9-2 (2009) 153 fig. 3. smooth surface filling among aggregates before experiment. stereomicroscopy. magnification of image 20 x 4.5 fig. 4. considerable biodeterioration of concrete sample surface after 90 days, samples taken from amd. stereomicroscopy. magnification of image 20 x 4.5 fig. 5. surface of concrete sample before experiment. atomic force microscopy. fig. 6. amd immersed part of concrete sample atomic force microscopy. during the experiment the ph values of leachate amd were increasing up 7.03. depends on ph the lath-shaped crystals of ettringit (3cao.al2o3.3caso4.32h2o) were on the surface observed as shown on fig. 7 and 8. the ettringite is secondarily produced under alkaline conditions after exposure to sulphate (mori et al., 1992). fig. 7. image of ettringit crystals precipitated on the concrete sample surface underwater into amd (sem). fig. 8. eds qualitative ettringite analysis. 4. conclusion experimental studies of the part “positive influence of the srb metabolism in the environment and industry” confirm that all chosen substrates calcium lactate, glycerol and whey are suitable alternative substrates of sodium lactate for the bacterial 154 luptakova, a. et al. sulphate-reduction. in the regard to the efficiency of bacterial sulphate reduction the calcium lactate is the best. efficiency of bacterial sulphate reduction in the case of whey was less compared with calcium lactate. but in experiments was used reclaimed and dried whey. consequently next experiments will orient on the application of whey from dairy works. it is the dayiring industry waste with low cost. experimental studies of the part “negative influence of the srb metabolism in the environment and industry” confirmed visible changes of concrete samples surface structure by the bacteria attack. concrete samples were under biogenic sulphuric acid influence corroded. the most considerable biocorrosion was observed on samples immerged into acid mine drainage. experiment simultaneous effect of bacteria acidithiobacillus thiooxidans and desulfovibrio desulphuricans, which were the source of h2s has proven. crystals participated on concrete surface was identified as ettringite. acknowledgment: this work was supported by the slovak research and development agency under the contract no. apvv-51-027705 and grant agency vega for project no. 2/0075/08. i also thank university of duisburg-essen, biofilm centre, aquatic biotechnology, dusburg, germany especially group of prof. wolfgang sand for opportunity to work with afm. references dvorak, d.h et al.: treatment of metal-contaminated water using bacterial sulfate reduction: results from pilot-scale reactors. biotechnol. bioeng., 40, 1992, 609-16. karavajko, g.i., rossi, g., agate, a.d., groudev, s.n. and avakyan, z.a.: biogeotechnology of metals. centre of projects gknt, moscow, 1988, 350 pp. mori, t.: et al.: interactions of nutrients, moisture and ph on microbial corrosion of concrete sewer pipes. water res., 26, 1992, 29-37. okabe, s., odagiri, m., ito, t., and satoh, h.: succession of sulfur-oxidizing bacteria in the microbial community on corroding concrete in sewer systems. appl. environ. microbiol., 73, 2007, 971-980. rehm, h.j., reed, g.: biotechnology, vol. 6b, verlag chemie gmbh, weuheim, 1981, 473-475. roberts, d. j., nica, d., zuo, g., and davis, j.l.: quantifying microbially induced deterioration of concrete: initial studies. int. biodeterior. biodegrad., 49, 2002, 227-234. tabak, h.h., scharp, r., burckle, j., kawaharai, f.k., govind, r., advances in biotreatment of acid mine drainage and biorecovery of metals: 1. metal precipitation for recovery and recycle. biodegradation, 14, 2003, 423-436. microsoft word vrtoch nb 9-2.doc nova biotechnologica 9-2 (2009) 199 linear and non-linear regression analysis for the biosorption kinetics of methylene blue ľuboš vrtoch, jozef augustín department of biotechnology, university of ss cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic (vrtochl@ucm.sk) abstract: the nonviable biomass of rhizopus sp. r-18, penicillium candidum and penicillium chrysogenum was studied for biosorption of methylene blue (mb). the sorption of mb was studied be performing batch kinetic experiments. kinetic measurements showed that sorption of mb reached equilibrium in 4 hours. the batch sorption models, based on a pseudo-first, pseudo-second and pseudo-nth order were applied to predict the rate constant of sorption and the equilibrium capacity. the linear and nonlinear least-square methods were used to obtain the kinetic parameters. the best-fit model was identified using statistic analysis. the results showed that both linear and nonlinear form of pseudosecond order expression could be used to fit the experimental data but nonlinear method may be a better way to obtain the desired parameters. as well the pseudo n-th order kinetic model was successfully applied to the kinetic data. the order (n) of adsorption reaction was found for all employed biosorbents: for rhizopus sp. r-18 it had value 3.1, p. candidum 3.0 and p. chrysogenum 3.8. key words: biosorption, kinetics, methylene blue, regression analysis, fungi 1. introduction environmental pollution due to technological development is one of the most important problems than men have to face. biosorption as a separation process has aroused considerable interest during recent years. in wastewater treatment, biosorption is regarded as one of the most potent techniques for the removal of dyes (aksu, 2005). two important physico-chemical aspects for evaluation of a sorption process as a unit operation are the equilibrium of the sorption and the sorption kinetics (ho et al., 2000). the nature of sorption process will depend on physical or chemical characteristics of the adsorbent systems and also on the system conditions at which sorption processes may include ion exchange, chelation, physical and chemical sorption. predicting the rate at which the pollutants removal takes place in a given solid/solution system is one of the most crucial factors for the effective sorption system design. chemical kinetics explains how fast the rate of chemical reaction occurs and also the factors affecting the reaction rate. several researchers have used different kinetic models to predict the mechanism involved in the sorption process. these models can be divided into two main types: diffusion based models and reaction based models (al-degs et al., 2006; svilović and stipišić, 2009). in the present study, we used reaction based models, namely lagergren pseudo-first order kinetic model, pseudo-second order model and pseudo-nth order kinetic model for prediction of batch sorption kinetics. in the present study, a comparison between linear and non-linear regression method has been made to predict the best sorption kinetics and also to obtain the kinetic parameters. 200 vrtoch, ľ. and augustín, j. 2. materials and methods 2.1 biosorbents and absorbate three different fungi were used as biosorbents, rhizopus sp. r-18, penicillium candidum and penicillium chrysogenum. the rhizopus sp. r-18 and p. candidum were obtained from the collection of microorganisms, ss. cyril and methodius university, trnava, slovakia. p. chrysogenum biomass in paste form was obtained from local antibiotics producing plant. the rhizopus and p. candidum biomass was obtained by cultivation in the czapek-dox broth. after 7 days the biomass was harvested, washed with distilled water and dried at 60°c for 24 h. subsequently, dried biomass was powdered by using mortar and pestle. the powder was sieved to obtain the particle size fraction below 0.31 mm. in a similar manner was utilized p. chrysogenum biomass, too. the absorbate used in all the experiments was methylene blue (basic blue 9), a cationic dye. the stock solution of mb was prepared by dissolving 0.5 g of substance in one liter of distilled water. all working solutions of desired concentrations were prepared by diluting the stock solution with distilled water. 2.2 sorption kinetic experiments kinetic experiments were conducted on the rotary shaker with constant agitation speed of 200 rpm, using 50 ml erlenmeyer flasks containing 10 ml mb solutions 200 mg.l-1, ph 6.0 and 0.03 g of each type of biosorbent for 360 min. samples were drawn from the mixture at pre-determined time intervals for analysis. the dye concentration in supernatants (3 000 rpm) were estimated spectrophotometrically at 665 nm. 2.3 regression analysis, goodness-of-fit measure and model comparison the kinetic parameters were evaluated by linear and/or non-linear regression analysis by using qc.expert® 3.1 and originpro® 7.0. in the present study, several error analysis methods were used in order to confirm the best-fitting kinetic model, namely the coefficient of determination (r2), the sum of the squares of the errors (sse), the sum of the absolute errors (sae) and chi-square analysis (reduced χ2). we used one statistical approach for comparing models: akaike’s information criterion (aic). 3. results and discussion 3.1 linear regression analysis a commonly used model for describing sorption kinetic is the pseudo-second order kinetic model. because this kinetic model is non-linear, fitting this model to measured data requires a “trial and error” approach. alternatively, a linearized version of this model (at least four different version exist -) can be used (table 1). a limitation to nova biotechnologica 9-2 (2009) 201 this approach, however, is that the transformation of data required for linearization can result in modifications of error structure, introduction of error into the independent variable, and alteration of the weight placed on each data point, often leading to difference in fitted parameter values between linear and non-linear version of the pseudo-second order kinetic model (kumar, 2006; bolster and hornberger, 2007). table 2 shows kinetic parameters obtained by using linear equations of the four pseudo-second order kinetic models. table 1. pseudo second-order kinetics and their linear forms, qt, qe-the amount of dye adsorbed at any time t and at equilibrium, respectively; k2-the rate constant of sorption (ho, 2006). kinetic model linear form plot parameters model 1 tqqkq t eet 11 2 2 += )(/ tfqt t = qe = 1/slope k2 = slope2/intercept h = 1/intercept model 2 eet qtqkq 11 ) 1 ( 1 2 2 += )/1(/1 tfqt = qe= 1/intercept k2= intercept2/slope h = 1/slope model 3 t q qk qq t e et ) 1 ( 2 −= )/( tqfq tt = qe = intercept k2 = -1/(slope*intercept) h = intercept/slope model 4 e te e t q qqk qk t q 222 2 −= )(/ tt qftq = qe= intercept/slope k2 = slope2/intercept h = intercept table 2. pseudo-second order kinetic parameters obtained by using the linear methods (qt and qe, mg.g-1; k2, g.mg-1.min-1; t, min). biosorbent model 1 k2* qe r2 model 2 k2 qe r2 model 3 k2 qe r2 model 4 k2 qe r2 rhizopus sp. r-18 -0.07 45.5 0.999 0.05 45.5 0.904 0.05 46.0 0.836 0.04 46.4 0.836 penicillium candidum 0.02 42.6 0.999 0.08 42.0 0.975 0.08 41.9 0.929 0.08 42.0 0.929 penicillium chrysogenum 0.008 40.0 0.999 0.03 37.9 0.953 0.03 38.2 0.896 0.02 38.6 0.896 *statistic non-significant parameters on the significance level α=0.05 for all biosorbents tested, the best fit was achieved by model 1. this model is statistically significant with a coefficient of determination near one for all three biosorbents. but this model gives statistically non-significant regression coefficients (in this case it is the intercepts) at a significance level of α=0.05 (statistics data are not shown). because of this, the model is not appropriate for the description of the experimental data. in the table 2 we can see that model 2 gives the best fits for all three biosorbents. it was observed that the kinetic parameters obtained from the three linear forms of pseudo-second order expressions were (models 2-4) very similar. from the aforementioned we can conclude that for description of kinetics of the sorption of methylene blue by the biomass of the fungi all three linear equations of the pseudosecond order can be used. 202 vrtoch, ľ. and augustín, j. 3.2 non-linear regression analysis in the present study we used reaction based kinetic models, namely lagergren pseudo-first order kinetic model, pseudo-second order model and pseudo-nth order kinetic model (table 3). the kinetic parameters were determined using non-linear regression analysis by using gauss-newton algorithm. table 4 shows obtained the predicted kinetic parameters. from the comparison of aic and r2 it is clear that the pseudo-nth order kinetic model gives the best fit for all biosorbents. table 3. kinetic models employed in this paper and their differential and non-linear equation forms. kinetic model differential equation non-linear equation reference pseudo-first order )(1 te t qqk dt dq −= )1( 1 tk et eqq −−= lagergren, 1898 pseudo-second order 2 2 )( te t qqk dt dq −= e e t tqk tkq q 2 2 2 1+ = ho, mckay, 1998 pseudo-nth order n ten t qqk dt dq )( −= )1/(11 ])1([ nn n eet tknqqq −− −−−= özer, 2007 table 4. kinetic model parameters obtained by using non-linear regression analysis (1-rhizopus sp. r-18; 2p. candidum; 3-p. chrysogenum; k1, k2 and kn are rate constants; n is the order of reaction; qe is the amount of dye adsorbed onto biosorbent at equilibrium (mg.g-1). bio sorbent pseudo-first order kinetic k1 qe r2 aic pseudo-second order kinetic k2 qe r2 aic pseudo-nth order kinetic kn qe n r2 aic 1. 1.7 45.2 0.962 26.1 0.05 46.1 0.984 15.4 0.001 48.0 3.1 0.991 11.0 2. 1.6 41.1 0.998 10.0 0.08 41.9 0.996 -4.9 0.004 43.1 3.0 0.999 -22.0 3. 0.5 37.2 0.927 111 0.02 38.7 0.981 14.3 5.10-7 43.0 3.8 0.997 -2.31 0 50 100 150 200 250 300 350 400 0 10 20 30 40 50 60 rhizopus sp. r-18 ( ) penicillium candidum ( ) penicillium chrysogenum ( ) q t [ m g. g1 ] t [min] a 0 50 100 150 200 250 300 350 400 0 10 20 30 40 50 60 rhizopus sp. r-18 ( ) penicillium candidum ( ) penicillium chrysogenum ( ) q t [ m g. g1 ] t [min] b fig. 1. pseudo-first (a) and pseudo-second (b) order kinetics by non-linear method by using gauss-newton algorithm and experimental kinetics for the sorption of methylene blue onto three different biosorbents. the order of adsorption reaction (n) was found to be between 3.0 and 3.8. from the aforementioned we can conclude that the adsorption of methylene blue by the biomass of the fungi is governed by a reaction order higher than 2. but the model gives nova biotechnologica 9-2 (2009) 203 statistically insignificant coefficients (in the case it is kn) for all three biosorbents (statistics data are not shown). this excludes the use of this model for the description of our experimental data. we can’t forget that this model, contrary to the two others, is a three parameter model. on the one hand the higher number of parameters gives us a better fit, but on the other hand the statistical significance of the regression coefficients is lower. one possible way to increase the statistical significance of the regression coefficients is to increase the number of experimental measurements. because of this, in this work, the pseudo-second order kinetic model seems to be the best fitting for all three biosorbents (fig. 1). 3.3 comparison of linear and non-linear regression analysis to compare model fits between the different linearizations and the nonlinear pseudo-second order kinetic model equation, the best-fit lines for each linearization were transformed back to sorbed concentrations (qt) and error analysis as well as aic were using for comparison goodness-of-fit measure between the different linearizations and the non-linear equation (table 5). table 5. statistic parameters for the nonlinear and linearized pseudo-second order kinetic equations for three different biosorbents. kinetic model biosorbent statistic* parameter model 2 model 3 model 4 nonlinear model sse 32.4 31.8 31.8 30.9 sae 13.6 13.4 13.9 13.8 red χ2 0.086 0.084 0.089 0.084 rhizopus sp. r-18 aic 20.9 20.7 20.7 20.4 sse 5.71 5.49 5.71 5.72 sae 6.1 5.90 6.10 6.23 red χ2 0.016 0.015 0.016 0.016 penicillium candidum aic 0.088 -0.38 0.088 0.115 sse 42.5 42.4 28.4 28.1 sae 18.2 17.6 14.2 14.2 red χ2 0.160 0.165 0.126 0.124 penicillium chrysogenum aic 24.3 24.3 19.9 19.8 * ssethe sum of the squares of the errors; saethe sum of the absolute errors; red χ2reduced chi-square analysis; aicakaike’s information criterion . from the statistical analysis we can conclude, that the linearized models 2, 3 and 4 give us very similar fits to the non-linear models. the best example for this is biosorbent p. candidum with an aic value of -0.38 (model 3). this fact can be described in the following way: the linear regression analysis was done using the leastsquares methods. in order to use this method some conditions known from statistics must be met. if we want to use the linear forms of the kinetic equations of the pseudo204 vrtoch, ľ. and augustín, j. second order the data from the measurement must be transformed. the transformation probably changed the conditions in a positive way, and that caused that the linear models (except model 1) give very similar or better fits than the non-linear models (look at p. candidum in the table 5). as mentioned in the literature this doesn’t always have to be the case the data transformation can also negatively affect the estimate of the regressive model. therefore, the primary drawback to linearization is not the inability to provide similar parameter estimates as the nonlinear equation but rather the inability to provide poor (or good) model fits when the data don’t (or do) conform to the kinetic model. 4. conclusions the sorption of methylene blue by three fungal biosorbents was found to be rapid whereby the equilibrium was reached during one hour. the results confirmed the applicability several kinetic models, namely pseudo-second and pseudo nth order kinetic models. present investigation further showed that the search for best-fit kinetic model using linearization technique is not an appropriate technique to predict biosorption kinetics. the non-linear methods would be more appropriate techniques in predicting the biosorption kinetics. references aksu, z.: application of biosorption for the removal of organic pollutants: a review. process. biochem., 40, 2005, 997-1026. al-degs, y. s., el-barghouthi, m. i., issa, a. a., khraisheh, m. a., walker, g. m.: sorption of zn(ii), pb(ii) and co(ii) using natural sorbents: equilibrium and kinetic studies. water res., 40, 2006, 2645-2658. bolster, h. c., hornberger, m. g.: on the use of linearized langmuir equations. soil sci. soc. am. j., 71, 2007, 796-1806. ho, y. s., mckay, g.: kinetic models for the sorption of dye from aqueous solution by wood. trans. inst. chem. eng., 76, 1998, 183-191. ho, y. s., ng, j. c. y., mckay, g.: kinetics of pollutant sorption by biosorbent: review. sep. pur. methods, 29, 2000, 189-232. kumar, k. v.: linear and non-linear regression analysis for the sorption kinetics of methylene blue onto activated carbon. j. hazard. mater., 137, 2006, 1538-1544. lagergren, s.: about the theory of so-called adsorption of soluble substances. k. sven. vetenskapsakad. handl., 24, 1898, 1-39. özer, a.: removal of pb(ii) ions from aqueous solutions by sulphuric acid-treated wheat bran. j. hazard. mater., 141, 2007, 753-761. svilović, s., stipišić, d. r.: modeling batch kinetics of copper ions sorption using synthetic zeolite nax. j. hazard. mater., 2009 (in press). microsoft word maresova nb 9-3.doc nova biotechnologica 9-3 (2009) 333 influence of anionic surfactants on zn2+ and sr2+ uptake by ivy (hedera helix l.) leaves jana marešová, miroslav horník, martin pipíška, jozef augustín department of biotechnology, university of ss. cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic (jana.maresova@ucm.sk) abstract: surfactants are frequently used as adjuvants for improving the efficiency of foliar applied fertilizers, pesticides and other biologically active substances. in our paper we used detached leaves of ivy (hedera helix l.) for the study of the influence of anionic surfactants sodium dodecylsulfate (sds) and sodium dicyclohexyl sulfosuccinate (dcss) on zinc and strontium uptake by leaf surface and transport by radiotracer technique with 65zncl2 and 85srcl2. accumulated amounts of zn2+ and sr2+ ions by the surface of detached intact ivy leaves were 5.0 and 1.1 μg/g, respectively. ivy leaves pretreated for 24 h in 1 mm sds or dcss solutions accumulated approx. twice more zn and five time more sr than non treated leaves. pretreatment with surfactants increased mobility of zinc and strontium in leaf tissues. separate experiments showed that both sds and dcss were sorbed onto the leaf tissue reaching equilibrium within several hours of immersing leaf blades to surfactant solutions. the process can be described in terms of partition equilibria p = [c]leaf/[c]solution with log p = 1.396 within surfactant concentration studied co ≤ 100 μmol/l. the mechanism of action of surfactants on metal ion uptake is discussed. key words: ivy, h. helix l., foliar uptake, surfactants, zinc, 65zncl2, strontium, 85srcl2 1. introduction the cuticle is the main interface between plants and their environment. it covers the epidermis of all aerial primary parts of plant organs as a continuous extracellular matrix. this hydrophobic natural composite consists mainly of the biopolymers, cutin, and cuticular lipids called waxes. water-repellent cuticle or waxes on a plant surface is the major barrier to the spreading, retention and penetration of solutes (bargel et al., 2006). surfactants are frequently used as surface-acting adjuvants that improve the absorbing, emulsifying, dispersing, spreading, sticking, wetting or penetrating properties of foliar applied fertilizers. on the other hands, surfactants alone are able to accumulate in plants and to change physico-chemical properties of the leaf surface. it has been proposed that there is a requirement for surfactants to be absorbed into plant leaves at rates similar to those for the active ingredient for the best uptake results (stock et al., 1993). however, there have been only a few studies of surfactant uptake (zabkiewicz et al., 1995) compared to the multitude of studies quantifying active ingredient uptake, and all of these are reported on a percentage basis. the finding that active ingredient mass uptake can be related to initial dose applied (forster et al., 2004; nielsen et al., 2005) raises the question of whether the surfactant component of a typical spray formulation will behave in a similar fashion. our paper is a step towards addressing the question of the influence of anionic surfactants sodium dodecylsulfate (sds) and sodium dicyclohexyl sulfosuccinate (dcss) on the uptake of zn and sr as bivalent metals by the leaf surface of ivy (hedera helix l.). 334 marešová, j. et al. ivy (h. helix) is a common, easily available species, which possesses a number of advantages. the ultra-structure of leaves is well described (canet et al., 1996; gilly et al., 1997). ivy leaf cuticle was used as a model to investigate cuticle permeability (chamel, 1986). fine structure and permeability of ivy leaf cuticles in relation to foliar development and after selective chemical treatments and relationship between structure and permeability are well described (gilly et al., 1997). in our previous papers are described some properties and behavior of sulfosuccinate esters in biological systems (vrbanová et al. 1997; cserháti et al. 1997) and leaf uptake and distribution of zn ions by ivy (marešová et al., 2009). 2. materials and methods 2.1 chemicals standardized 65zncl2 solution (0.877 mbq/cm 3, 50 mg/dm3 zncl2 in 3 g/dm 3 hcl) and 85srcl2 (2.665 mbq/cm 3, 20 mg/dm3 zncl2 in 3 g/dm 3 hcl) were obtained from the czech institute for metrology, prague. sodium dodecylsulfate (sds) was obtained from sigma, sodium dicyclohexyl sulfosuccinate (dcss) from cytec corp., u.s.a. solutions were prepared in deionized water, conductivity 0.05 μs/cm, ph was adjusted with naoh. 2.2 plant material ivy branches (h. helix l.) were picked during spring months from freely grown garden vegetation. the upper part of branches were cut from a wild ivy plant, washed repeatedly in deionized water and used for experiments. leaves about 0.2 – 0.3 g of fresh weight and leaf area 11.5 12.5 cm2 were used in experiments. fig. 1. macro photo of ivy leaves in experiments. leaf blades immersed by both sides in nutrient media in petri dishes. characteristic signs: short petioles; shallow sinus; well developed veins; terminal, lateral and basal lobes. 2.3 bioaccumulation experiments pretreatment of leaves by surfactants was made by immersing of detached leaf blades into sds or dcss solution in deionized water. for metal uptake experiments leaf blades were immersed in 10 ml 25% hm medium supplemented with 5 µmol/l 65zncl2 or 85srcl2 in dishes covered with plastic lids (fig. 1.) in cultivation room at 22±2°c illuminated with artificial light (2 000 lx) in 12h/12h light/dark cycle. the following molar concentrations of salts were present in full-strength hm (mm): nova biotechnologica 9-3 (2009) 335 mgso4.7h2o – 1.5; kno3 – 4.0; cacl2 – 4.0; nah2po4.2h2o – 1.87; na2hpo4.12h2o – 0.13; feso4.7h2o – 0.06; nano3 – 4.0; nh4cl – 3.17; nh4no3 – 2.0; h3bo3 – 0.14; na2moo4.2h2o – 0.0025; mnso4.5h2o – 0.21; znso4.7h2o – 0.023; cuso4.5h2o – 0.033. 2.4 radiometric analysis a gamma spectrometric assembly using the well type scintillation detector 54bp54/2-x, nai(tl) (scionix, the netherlands) and data processing software scintivision 32 (ortec, usa) were used for 65zn and 85sr determination in leaf biomass and solutions. counting time 600 s allowed obtaining data with measurement error <2 %, which do not reflect other source of errors. 2.5 surfactant analysis anionic surfactants were determined by the mbas method (arand et. al., 1992). shortly, anionic detergents react with methylene blue to form a blue colored complex that is extracted into chloroform and blue coloration is measured at 651 nm. 3. results and discussions 3.1 uptake of surfactants by ivy (h. helix l.) leaves leaf surface of h. helix is able to accumulate anionic surfactants sds and dcss from water solutions (fig. 2.). concentration equilibrium csolid/cwater is reached at 20 °c within several hours. such slow processes are typical for partition equilibria between solution and solid materials at which the rate limiting step is the diffusion process in existing membrane systems. 0 1 2 3 4 23 24 0,0 0,5 1,0 1,5 2,0 2,5 q s d s [μ m ol /g ] time [h] c sds = 25 μ mol/dm3 c sds = 50 μ mol/dm3 c sds = 100 μ mol/dm3 fig. 2. kinetics of sds uptake (µmol/dm3, w.w.) by detached ivy leaves (h. helix l.) at 20 °c. the initial sds concentrations: 25.0 (■-■-■), 50.0 (●-●-●) and 100.0 (▲-▲-▲) µmol/dm3. leaf biomass: 40.3 ± 0.15 g/dm3 w.w. (±sd), leaf blades area 1 654 ± 58.0 cm2/dm3 (±sd). 336 marešová, j. et al. qsds and qdcss (μmol/g, d.w.) values are proportional with the initial concentration of surfactants in solution within the concentration range studied c0 ≤ 100 μmol/l (fig. 3.). the process of sds and dcss accumulation by h. helix leaf tissues can be described in terms of partition equilibria with partition coefficient log p = 1.349 for both substances. both sds and dcss contain c12 hydrocarbon part and one ionisable anionic group, what explain similar behaviour in the contact with the leaf structures. 0 25 50 75 100 0,0 0,5 1,0 1,5 2,0 2,5 q 24 [μ m ol /g ] c 0 [μmol/l] sds dcss fig. 3. uptake of sds (■) and dcss (●) by the surface of detached ivy leaves (h. helix l.), expressed as q24 (µmol/g) in dependence on the initial concentration c0 in solution. log p = 1.394 3.2 influence of pretreatment of leaves by surfactants on sr and zn uptake and distribution ivy leaves treated with sds or dcss solution accumulated higher amounts of zn2+ and sr2+ ions, comparing with non-treated control leaves. enhancement ratio er for zn and sr is shown in tab. 1. non-treated ivy leaves accumulated 4.55 times more zinc than strontium and sds-treated leaves 3.2 times more zinc than strontium. similar behavior can be expected also in the case of other bivalent metals. the effect of surfactants on metal sorption of inorganic sorbents was studied by ahn et al. (2009). sds and dcss -impregnated activated carbon sorbed cd2+ up to 0.198 mmol/g, which was more than one order of magnitude better than cd2+ sorption by activated carbon without surfactants. treating of ivy leaves with sds or dcss solution caused the increase of zinc and strontium mobility in plant tissues. as can be seen from data presented in fig. 4 both metals are transported with higher efficiency from immersed part of leaf blades to petiols and to other parts of plants. strontium and zinc foliar uptake and transfer in tomato plants (lycopersicum esculentum l.) was studied by brambilla et al. (2002). leaf to fruit transfer coefficient for 65zn was one order magnitude higher than for 85sr. nova biotechnologica 9-3 (2009) 337 tab.1. zinc and strontium uptake (μg/g, d.w.) by non treated and pretreated leaf surface of ivy (h. helix l.) after 24 h in 1.0 mmol.dm-3 sds or dcss. zn and sr uptake from 25% hm spiked with 65zncl2 (5 µmol.dm-3) or 85srcl2 (5 µmol.dm-3). uptake [μg/g] uptake [μg/g] metal non-treated sdspretreated er* non-treated dcsspretreated er* zn2+ 5.0 17.0 3.4 3.9 11.1 2.8 sr2+ 1.1 5.4 4.9 * enhancement ratio er is the ratio of the metal concentration in leaves treated with surfactants to the metal concentration in non-treated leaves. 0 2 0 4 0 6 0 8 0 q z n [n m ol /g ] n o n t r e a t e d s d s p r e t r e a t e d a 0 2 0 4 0 6 0 8 0 q s r [ nm ol /g ] n o n t r e a t e d s d s p r e t r e a t e d b fig. 4. influence of sds pretreatment on zn (a) and sr (b) uptake and distribution in ivy leaves (h. helix l.). leaves were pretreated for 24h with 1.0 mmol/dm3 sds, then immersed in 5.0 µmol/dm3 zncl2 or srcl2 in 25 % hm, spiked with 65zncl2 (114 kbq/dm3) or 85srcl2 (311 kbq/dm3) without sds. uptake via the surface of fully immersed leaves. cultivation at illumination 12h/12h light/darkness (2 000 lx), ph 5.5 and 22±2°c. data as the mean of two replicates. error bars represent standard deviation (sd) of the mean. wet weight of leaves: a. 0.29 ± 0.02 (±sd) g /10 ml, b. 0.24 ± 0.01 (±sd) g/10 ml. leaf area [cm2] – a. 10.82 ± 0.67 (±sd), b. 11.7 ± 0.36 (±sd). data of leaf blades (■■) and non immersed leaf stalks (■■) expressed as zn or sr concentration (nmol/g), d.w. 338 marešová, j. et al. to explain the effect of anionic surfactants on metal uptake by leaf surface and distribution in leaf structures will require a more detailed study. stimulating effect can be caused by the following factors: increase of capacity of polar or water path for ion transport or the decrease of viscosity of cuticular and wax structures on the leaf surface, or metal cation surfactant anion interactions improving metal mobility in the lipophilic leaf structures. riederer and schönherr (1999) showed that treating the outer surfaces of isolated cuticles of seville orange (citrus aurantium l.) and pear (pyrus communis l. cv. bartlett) leaves with a number of nonionic (polyoxyethylene) surfactants increased their permeability to water by factors ranging from 4.1 to 14.7 and from 7.2 to 152.4, respectively. none of the surfactant treatments altered the amounts or composition of waxes in the cuticles used for transport measurements. anionic surfactants can react with cations of bivalent ions. talens-alesson (2007) found that sds micelles are able to bind zn2+ ions and ions of other metals. however in all sorption experiments we used sds and dcss solutions in concentrations ≤ 1 mmol/l, what is approximately 7 times lower concentration than critical concentration of micelle formation cmc = 6.9 mm (nakagarajan, 2003). according to kirkwood (1999) the physico-chemical properties of the cuticle may affect the rate and efficiency of cuticle permeation. the permeation of organic solutes is influenced by their solubility characteristics as indicated by octanol/water partition coefficients (log kow) and cuticle/water partition coefficient (log kcw). penetration of hydrophillic organic compounds (low log kow) may be enhanced by hydration of the cuticle, while transcuticular transport of non-polar organic solutes (high log kow) is increased by factors which reduce the wax viscosity. 4. conclusions anionic surfactants sodium dodecylsulfate c12h25oso3na and sodium dicyclohexyl sulfosuccinate c16h25o4so3na are sorbed by ivy leaves (hedera helix l.) immersed in surfactant water solution. pretreatment of leaves by surfactants increases their capacity to sorb zn2+ and sr2+ ions. obtained data are discussed from the point of view of the effect of surfactants on the leaf structures and metal uptake. references ahn, ch.k., park, d., woo, s.h., park, j.m.: removal of cationic heavy metals from aqueous solution by activated carbon impregnated with anionic surfactants. j. hazard. mater., 164, 2009, 1130-1136. arand, m., friedberg, t., oesch, f.: colorimetric quantitation of trace amounts of sodium lauryl sulfate in the presence of nucleic acids and proteins. anal. biochem., 207, 1992, 73-75. bargel, h., koch, k., cerman, z., neihuis, ch.: structure-function relationships of the plant cuticle and cuticular waxes: a smart material? funct. plant biol., 33, 2006, 893-910. nova biotechnologica 9-3 (2009) 339 brambilla, m., fortunati, p., carini, f.: foliar and root uptake of 134cs, 85sr and 65zn in processing tomato plats (lycopersicon esculentum mill.). j. environ. radioact., 60, 2002, 351-363. canet, d., rohr, r., chamel, a., guillain, f.: atomic force microscopy study of isolated ivy leaf cuticles observed directly and after embeding in epon®. new phytol., 134, 1996, 571-577. cserháti, t., csiktusnádi kiss, g., augustín, j.: the use of principal component analysis for the study of the interaction of anionic surfactants with hydroxypropyl-β-cyclodextrin. j. incl. macro. phenom., 33, 1997, 123-133. chamel, a.: foliar absorption of herbicides: study of the cuticular penetration using isolated cuticles. physiol. veg., 24, 1986, 491–508. forster, w.a., zabkiewicz, j.a., reiderer, m.: mechanisms of cuticular uptake of xenobiotics into living plants: 1. influence of xenobiotic dose on the uptake of three model compounds, applied in the absence and presence of surfactants into chenopodium album, hedera helix and stephanotis floribunda leaves. pest manag. sci., 60, 2004, 1105-1113. gilly, c., rohr, r., chamel, a.: ultrastructure and radiolabelling of leaf cuticles from ivy (hedera helix l.) plants in vitro and during ex vitro acclimatization. ann. bot., 80, 1997, 139-145. kirkwood, r.c.: recent developments in our understanding of the plant cuticle as barrier to the foliar uptake of pesticides. pestic. sci., 55, 1999, 69-77. marešová, j., horník, m., pipíška, m., augustín, j.: zinc uptake and distribution in ivy (hedera helix l.) leaves. nova biotechnol., 9, 2009, 73-82. nakagarajan, r.: theory of micelle formation. quantitative approach to predict micellar properties from surfactant molecular structure. in: esumi, k., minoru, v. (eds.): surfactant science series: structure-performance relationships in surfactants. marcel dekker, ag., basel, 112, 2003, 1-110. nielsen, c.m., stelle, k.d., forster, w.a., zabkiewicz, j.a.: influence of dose and molecular weight on foliar mass uptake of surfactant. new zealand plant protect., 58, 2005, 174-178. riederer, m., schönherr, j.: effects of surfactants on water permeability of isolated plant cuticles and on the composition of their cuticular waxes. pestic. sci., 29, 1999, 85–94. stock, d., holloway, p.j., grayson, b.t., whitehouse, p.: development of a predictive uptake model to rationalize selection of polyoxythylene surfactant adjuvants for foliage-applied agrochemicals. pestic. sci., 37, 1993, 233-245. talens-alesson, f.i.: behaviour of sds micelles bound to mixtures of divalent and trivalent cations during ultrafiltration. colloid. surface. a, 299, 2007, 169-179. vrbanová, a., prokšová, m., augustín, j., ziegler, w.: function and parameters of sorption and primary biodegradation of a series of alkyl sulphosuccinates by comamonas errigena n3h. biologia, 52, 1997, 747-751. zabkiewicz, j.a., forster, w.a., steele, k.d., liu, z.q.: comparison of uptake into field bean (vicia faba) and wheat (triticum aestivum) of organosilicone and non-silicone surfactants. in: gaskin, r.e. (eds.) adjuvants for agrochemicals. rotorua, new zealand, 1995, 219–224. microsoft word guldanova et al_nb 2010.doc nova biotechnologica 10-2 (2010) 95 bioaccumulation and distribution of 137cs in tobacco cultivated under hydroponic conditions jana guldanová, miroslav horník, jana marešová, martin pipíška, jozef augustín department of biotechnology, university of ss. cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic (hornikm@ucm.sk) abstract: potential of plants to uptake metals from soil solution can be successfully applied for removal of long-lived radionuclides such as radiostrontium 90sr or radiocaesium 137cs. this work deals with bioaccumulation of cs in tobacco plants (nicotiana tabacum l.) hydroponically grown in diluted hoagland media (hm) spiked with 137cscl. speciation analysis using a program visual minteq showed, that more than 97% of caesium in hm occurred in the form of cs+ ions. we found that bioaccumulation of cs significantly decreased from the value 100% to the value 20% removing of cs from media after 8 days cultivation of plants with increasing hm concentration. however, the concentration ratio (cr) [cs]shoot : [cs]root increased with increasing hm concentration from the value 0.10 to the value 0.85. bioaccumulation of cs by tobacco plants significantly decreased with increasing cscl concentration in media from the value 95% found at concentration of cscl 10 µmol/dm3 to the value 44% at concentration of cscl 1 000 µmol/dm3. we did not found visual symptoms of cs toxicity on plants after 8 days cultivation or significant differences in growth rate or transpiration activity at cscl concentration up to 0.2 mm. however, at > 0.2 mm cscl concentration the decrease of growth rate and necrosis of young leaves or die-back of leaves (> 2 mm cscl) were observed. the cr ([cs]shoot : [cs]root) increased with increasing concentration of cscl (10 – 1 000 µmol/dm3) in media from the value 0.10 to the value 0.40. the obtained data suggest that fast growing plant species with high biomass production like tobacco might be a suitable in phytoextraction or rhizofiltration technologies used for 137cs removing from environment. key words: 137cs, radiocaesium, bioaccumulation, tobacco, nicotiana tabacum, phytoremediation 1. introduction the presence of radionuclides in soil and water exposes the stability of ecosystem and poses serious risk to human health through the food chain. radionuclides can enter to the environment from natural or artificial sources. the artificial sources of radionuclides in the environment represent: testing of nuclear weapons, nuclear waste disposal, accidents resulting from nuclear power generation as well as manipulation with nuclear fuel (see e.g. hu et al., 2010). contamination caused by long-lived radionuclides, particularly 137cs and 90sr, poses a long-term environmental problem. caesium can exist in at least 39 isotopes forms, mostly within the range of atomic masses 112cs to 151cs. of these, the two cs isotopes are of environmental concern owing to their rapid incorporation into biological systems as physico-chemical analogue of potassium, their relatively long half-lives and emissions of β and γ-radiation during decay, are 134cs (τ = 2.06 y) and 137cs (τ = 30.2 y) (white and broadley, 2000). 96 guldanová, j. et al. from the monograph kabata-pendias and pendias (2001) results that cs contents in world soils are in the range from several tenths to tens of mg/kg. in some canadian soils range from 0.3 to 5 mg/kg, in bulgarian soils from 2 to 17 mg/kg, in ukrainian soils the mean value is 3.2 mg/kg. the background values of cs contents in slovakian soils are 5 mg/kg, similarly to the other world soils (čurlík and šefčík, 1999). as the result of chernobyl accident, in ukraine alone, over 260 000 km2 have received more than 40 gbq/km2 of contamination with 137cs (dushenkov, 2003). median values for the inventory of 137cs in topsoil of belarus, about a decade after the chernobyl accident, ranged from 103 to 1 500 kbq/m2, and the highest concentration was as much as 600-times higher than the pre-accident value (kagan and kadatsky, 1996). these authors estimated that about 90% of the inventory of 137cs is contained in the top 3 to 7 cm soil layer. nowadays, it can be expected that the radionuclide contamination is lower and significantly decrease with time. kashparov et al. (2003) found that in the year 2000 radionuclide contamination within the 30-km chernobyl zone was 2 – 3 times lower than the previous estimates. however, the release of new contamination still persists. also, climate/environmental changes e.g. global warming (dowdall et al., 2008) can play a possible role in distribution of radionuclides in soils as well as in soil-to-plant transfer processes. remediation of areas contaminated with toxic metals or radionuclides represent one of the objects of recent science research. remediation of contaminated areas by traditional physico-chemical methods e.g. precipitation, coagulation, soil leaching, flocculation, ion-exchange, reverse osmosis, adsorption, ultrafiltration, using of disperse and chelating agents, is financially unbearable and in many cases also ecologically unacceptable. bioremediation as a using of biological systems (microorganisms, algae and plants) in remediation processes represent new potential approach to solve the problems with toxic metals and radionuclides contaminations. phytoremediation technologies involve the processes, which use of plants for remediation of contaminated environment. several comprehensive reviews (see over the past five years e.g. gardea-torresdey et al., 2005; ghosh and singh, 2005; prasad et al., 2005; pilon-smits, 2005; leduc and terry, 2005; audet and charest, 2006; leštan et al., 2008; vangronsveld et al., 2009 and wenzel, 2009) and monographs (raskin and ensley, 2000; terry and bañuelos, 2000; mackova et al., 2006; morel et al., 2006, singh and tripathi, 2007; willey, 2007) have been written, summarizing many important aspects of this technology. these reviews also give general guidance and recommendations for applying phytoremediation in practice. plants ideal for phytoremediation of contaminated soils should fulfill some requirements: fast growing and high biomass (more than 8 tons/ha for year), extensive root system, easy to harvest, ability to tolerate and accumulate of high amount of metals in the aboveground parts (more than 1 g/kg). however, plants are able to metal uptake only from soil solution. tobacco was selected as a model of plant mainly for the reason its fast-growth rate and high biomass production over 12 tons/ha (keller et al., 2003). also, tobacco is nova biotechnologica 10-2 (2010) 97 important agricultural plant, which represent important source mainly of cd exposure from smoking cigarettes (who, 1992). in our previous papers we study cobalt 60co (horník et al., 2006; vrtoch et al., 2007) and caesium 137cs (vrtoch et al., 2006) bioaccumulation by tobacco as well as effect of complexing agents on cd, co and zn bioaccumulation and distribution in tissues of tobacco plants (horník et al., 2009a; 2009b; 2009c). in this work we present results from studying of effect of macroand microelements as well as cscl concentration on bioaccumulation and translocation of caesium in tissues of tobacco (nicotiana tabacum l.) cultivated in nutrient media spiked with 137cscl. 2. materials and methods 2.1 plant material seeds of tobacco (nicotiana tabacum l.) were germinated and grown at photoperiod 12h light/12 h dark (illumination 2 000 lx) and 22°c in pots filled with granulated perlite as an inert carrier. plants were watered with diluted solution of hoagland medium (hoagland, 1920). the composition of the full strength (100%) nutrient solution was (mmol/dm3): mgso4.7h2o – 1.5; kno3 – 4.0; cacl2 – 4.0; nah2po4.2h2o – 2.1; na2hpo4.12h2o – 0.13; feso4.7h2o – 6.4.10 -2; nano3 – 4.0; nh4cl – 4.0; nh4no3 – 2.0; h3bo3 – 0.14; na2moo4.2h2o – 2.5.10 -4; mnso4.5h2o – 2.1.10 -2; znso4.7h2o – 2.3.10 -3; cuso4.5h2o – 3.2.10 -3 (ph 6). after 4 weeks pre-cultivation seedlings were gently removed from perlite, roots were washed by deionized water for removing of perlite granules and used in bioaccumulation experiments. 2.2 bioaccumulation experiments uniformed plants (approx. 15 cm height and 7 g wet weight) from pre-cultivation phase were transferred into series of 250 ml erlenmeyer flask with 120 ml of 25% hoagland medium with the known 133cscl concentration and added radioactivity of 137cscl as a tracer. the ph of nutrient solutions was adjusted to 6.0 using 1 m naoh solution. all flasks were covered with black foil to protect plant roots against the lights. plants were hydroponically cultivated during 8 days in triplicate series under the same conditions as was mentioned in pre-cultivation phase without the addition of radionuclides. in time intervals aliquot samples of nutrient solution were taken, 137cs radioactivity was measured by gammaspectrometry and subsequently samples were returned into the cultivation medium. at the same time reduction of nutrient medium volume caused by transpiration of water was recorded and the difference was compensated by glass balls. at the end of the experiments plants were removed from nutrient solutions, roots were carefully washed in deionized water and incorporated 137cs radioactivity in roots, stems and leaves was measured. plant parts were dried at 60°c for 48 hours and dry weights were determined. 98 guldanová, j. et al. growth value (gv) was calculated using the following equation (1): 0 0 m mm gv t − = (1) where mt or m0 are fresh weight of plants at the start or end of experiments, respectively. 2.3 radiometric analysis for determination of 137cs radioactivity in plant parts and nutrient solution gammaspectrometric scintillation detectors 54bp54/2-x and 76bp76/3 with well type crystal nai(tl) (scionix, nl) and data processing software scintivision32 (ortec, usa) were used. a library of radionuclides was built by selecting characteristic γ-ray peaks (88.04 kev for 109cd, 661.66 kev for 137cs, 834.81 kev for 54mn and 1115.52 kev for 65zn) for energy and efficiency calibration. standardized solution of 137cs in the form of 137cscl (5.723 mbq/cm3, 20 mg/dm3 cscl in 3 g/dm 3 hcl) was provided from czech metrological institute (prague, cr). 2.4 speciation modelling the percentage occurrence of individual cs ionic forms in nutrient solution was determine by equilibrium speciation modelling software visual minteq (ver. 2.53) obtained from gustafsson (2010). this speciation modelling program allows the calculation of metals speciation in solutions as a function of total salt concentration, solution ph, ionic strength and temperature. 2.5 statistical analysis all analytical determinations were performed in triplicate. statistical significance of differences in calculated values of cs bioaccumulation in plant tissues were evaluated by kruskal-wallis non-parametric test and analysis of variance, respectively. this was followed by multiple range test to ascertain differences between individual groups. the level of significance was 0.05 in all cases. origin 7.0 (originlab corp., usa) and statgraphics centurion ver. 15 (statpoint, inc., usa) were used for graphing and statistical analyses, respectively. 3. results and discussion necessary assumption for successful remediation of contaminated soils with radiocaesium is ability of plants to accumulate significant amount of radioactivity from soil to aboveground part of plants. however, irreversible incorporation of 137cs onto clay minerals is a limiting factor of these processes. sorption reactions in soil-water boundary line are important phenomena, which determine the behaviour, bioavailability and transport of cs in environment. caesium has very low hydratation nova biotechnologica 10-2 (2010) 99 energy, thus electrostatic attraction between cs+ ions and clay particles is high and therefore cs ions are preferentially bound onto clay particles. however, sesquioxides mainly organically bound aluminium and iron oxides are responsible also for cs sorption in soils (chiang et al., 2010). despite these facts, phytoremediation of soil could be effective method of soil decontamination during the first years after radiocaesium penetration into the soil (willey, 2007; willey and collins, 2007). the results of laboratory experiments with plants can not be direct applied for phytoextraction of cs in real conditions. however, they can be useful for study of three processes take place in phytoextraction independently i.e. solubilization of metals from soil and their transport to root system of plants, uptake of metals by root system of plants and translocation of metals into aboveground biomass. experiments with hydroponics can be useful for study of two last mentioned processes (see e.g. tandy et al., 2006). also, this configuration of experiments allows quantitative study of individual speciation forms of metals under strictly defined conditions. in the case of plant cultivation in soil a complex equilibrium system is formed when the concentration of all substances in soil solution is in equilibrium with concentration of substances bound onto soil particles. also, inorganic nutrients occurred in soil solution or in synthetic solutions formed a very complex equilibrium system defined by dissociation constants, concentration, temperature and ph value. experimental determination of all speciation forms of metals is very difficult. therefore, for description of this system is very useful to use the speciation models. in our work we used the speciation modelling program visual minteq ver. 2.53 for calculation of individual ionic forms of cs in hoagland media (hm). we found that caesium at ph 6.0 and 22°c was occurred practically only in the form of cs+ ions (≥ 97%) in the case of all nutrient media containing different concentration of macro and microelements (8.3% – 100% hm) as well as concentrations of cscl (10 – 50 000 µmol/dm3). 0 1 2 3 4 5 6 7 8 0 20 40 60 80 100 100% hm 50% hm 25% hm 8.3% hm time [day] b io ac cu m ul at io n of c s [% ] 0,00 0,05 0,10 0,15 0,20 0,25 0,30 b io ac cu m ul at io n of c s [μ m ol /g ]; w .w . 100 50 25 8.3 hoagland medium [%] fig. 1. influence of nutrient salts concentration in hm on cs bioaccumulation by roots of tobacco plants (n. tabacum l.) during 8 days hydroponic cultivation in 100%, 50%, 25% or 8.3% hm containing 10 μmol/dm3 cscl (34.0 kbq/dm3 137cscl), ph 6.0, at photoperiod 12h light/12h dark (2 000 lx) and 22°c. bioaccumulation of cs expressed in per cent of the total amount of cscl in medium (a; kinetic) and in µmol/g (wet weight) (b; after 8 days cultivation). error bars represent standard deviation of the mean (n = 3). all values of means of cs bioaccumulation were significantly different at the p < 0.05 level based on multiple range test (fig. 1b). a b 100 guldanová, j. et al. fig. 1 a depicts cs bioaccumulation by tobacco hydroponics during 8 days at different concentration of hm containing 10 μmol/dm3 cscl. we found that at the lowest concentration of 8.3% hm (0.83 mm k+ and nh4 + ions) the bioaccumulation reached 100% already after 5 days of cultivation. in the case of 25% hm (2.5 mm k+ and nh4 + ions) the total removing of cs from medium was reached after 8 days of plants cultivation and in the case of 50% (5 mm k+ and nh4 + ions) or 100% hm (10 mm k+ and nh4 + ions) at this time was observed only 40% or 20% bioaccumulation of cs, respectively. similar effect can be seen on the fig. 1 b, where bioaccumulation of cs in μmol/g (wet weight) decreased with increasing hm concentration after 8 days plants cultivation. a kruskal-wallis test confirmed significant effects (at p < 0.05) of the cultivation conditions on cs bioaccumulation. on the basis of results of authors soudek et al. (2004; 2006) it can be expect that differences in cs bioaccumulation at different concentration of hm will be caused mainly in change of k+ and nh4 + concentration in media as competitive ions for cs uptake by plants. sandeep and manjaiah (2008) in the case of mustard, spinach and wheat plants cultivated in contaminated soil with 134cs observed that cs bioaccumulation decreased with increasing concentration of k in soil. similar result found also singh et al. (2008). 0 1 2 3 4 5 6 7 8 9 0 20 40 60 80 100 b io ac cu m ul at io n of c s [% ] time [day] 10 μmol/dm3 20 μmol/dm3 50 μmol/dm3 100 μmol/dm3 200 μmol/dm3 500 μmol/dm3 1000 μmol/dm3 0 200 400 600 800 1000 0 2 4 6 8 10 12 linear regression: y = a + b * x parameter value error a 0.200 0.009 b 0.012 0.0001 -------------------------------------------- r2 sd n p 0.985 5.97 7 <0.0001 b io ac cu m ul at io n of c s [μ m ol /g ]; w .w . c 0 cscl [μmol/dm3] fig. 2. influence of cscl concentration on cs bioaccumulation by roots of tobacco plants (n. tabacum l.) hydroponically cultivated in 8.3% hm containing 10, 20, 50, 100, 200, 500 or 1 000 μmol/dm3 cscl (33.5 kbq/dm3 137cscl), ph 6.0, at photoperiod 12h light/12h dark (2 000 lx) and 22°c. bioaccumulation of cs expressed in per cent of the total amount of cscl in medium (a; during 8 days cultivation) and in µmol/g (wet weight) (b; after 8 days cultivation). error bars represent standard deviation of the mean (n = 3). it is known that the uptake of cs is operated mainly via two transport pathways on plant root cell membranes, namely k+ transporters or k+ channels (zhu and smolders, 2000). however the role of cs+ in plant nutrition is no known (marschner, 1995; white and broadley, 2000). cs+ is nontoxic to plants at external cs+ concentrations below approx. 200 µmol/dm3, although this limit depends critically on the concentrations of other ions (k+, nh4 +) in the substrate. the toxicity symptoms induced by unnaturally high cs concentrations include necrosis of shoot and root tissues (kordan, 1987; white and broadley, 2000). a b nova biotechnologica 10-2 (2010) 101 in the next experiments we observed influence of cscl concentration in the range 10 – 50 000 μmol/dm3 on plant growth as well as on cs bioaccumulation by tobacco roots. for evaluation of phytotoxic effects on tobacco plants the calculation of growth value (the ratio of fresh weight of plants at the start or end of experiments difference to fresh weight of plants at the start of experiments) and macroscopic observation of phytotoxic symptoms on leaves were used. we did not found visual symptoms of cs toxicity on plants after 8 days cultivation or significant differences in growth rate at cscl concentration up to 0.2 mm. however, at cscl concentration above 0.2 mm cscl the decrease of growth rate and necrosis of young leaves or die-back of leaves (> 2 mm cscl) were observed (data not shown). the results in fig. 2 a show that cs bioaccumulation by tobacco plants significantly decreased with increasing cscl concentration in media from the value 95% found at concentration of cscl 10 µmol/dm3 to the value 44% at concentration of cscl 1 000 µmol/dm3. after conversion to µmol cs per gram (wet weight), we found linear correlation (r2 = 0.985) between cs bioaccumulation by tobacco roots and cscl concentration in nutrient media containing 0.33 mm k+ ions (fig. 2 b). it can be assumed, that this correlation corresponds with correlation between k uptake in plant and k concentration in soil solution. it means, that at higher cs concentration than concentration of k in cells of root system will be this correlation affected not only with specific uptake of k or cs ions by k+ transporters (often ≤ 0.3 mm), but also with low specific uptake via ion channels (for k+ ions). the k+ transporters operating at low k concentrations can transport cs+ efficiently whereas cs+ permeates only slowly in k+ channels operating at k concentrations above 0.5 – 1 mm (zhu and smolders, 2000). however, we did not found saturation of the first mentioned system and beginning the second system, what should be reflect to form a characteristic double phase isotherm relationship between cs+ influx to roots and external cs+ concentrations. 0 20 40 60 80 100 c b aa b b a a c b a 8.3 25 50 100 d is tr ib ut io n of c s [% ] root stem leaves hoagland medium [%] a 0,0 0,2 0,4 0,6 0,8 1,0 c b a 1005025 [c s] sh oo t / [c s] ro ot 8.3 hoagland medium [%] a fig. 3. influence of nutrient salts concentration in hm on cs translocation from roots to shoots of tobacco plants (n. tabacum l.) after 8 days hydroponic cultivation in 100%, 50%, 25% or 8.3% hm containing 10 μmol/dm3 cscl (34.0 kbq/dm3 137cscl), ph 6.0, at photoperiod 12h light/12h dark (2 000 lx) and 22°c. distribution expressed in per cent of the total cs uptake by plant (a) and as concentration ratio [cs]shoot : [cs]root (bq/g; dry weight) (b). error bars represent standard deviation of the mean (n = 3). means with the same letter at columns are not significantly different at the p < 0.05 level based on multiple range test. a b 102 guldanová, j. et al. the reviews of authors zhu and smolders (2000) or white and broadley (2000) describe the studies demonstrated that k+ and cs+ competed for influx to excised roots, suggesting that the influx of these cations to root cells is mediated by the same molecular mechanism. the molecular identity and electrophysiological signature of many k+ transporters expressed in the plasma membrane of root cells have been also described. the inward-rectifying k+ (kir), outward-rectifying k+ (kor) and voltage-insensitive cation (vic) channels are all permeable also to cs+. by modelling cation fluxes through these transporters into a stereotypical root cell, it can be predicted that vic channels mediate most (30 – 90%) of the cs+ influx under physiological conditions and that the kup transporters mediate the bulk of the remainder. cation influx through kir channels is likely to be blocked by extracellular cs+ under typical ionic conditions in the soil. from point of view of phytoremediation technologies it is important that toxic metals and radionuclides have to be accumulated mainly in aboveground parts of plants. for evaluation of caesium mobility in conductive tissues of plants in the term of caesium translocation efficiency we established non-dimensional concentration ratio (cr), which represent the ratio of caesium concentration in aboveground part of plants [cs]shoot to caesium concentration in root system of plants [cs]root. 0 20 40 60 80 100 ee dcdbc a ab e d d c bc a ab e e d cdbc a 1000500200100502010 d is tr ib ut io n of c s [% ] c 0 cscl [μmol/dm3] root stem leaves ab 0 200 400 600 800 1000 0,0 0,1 0,2 0,3 0,4 0,5 [c s] sh oo t / [c s] ro ot c 0 cscl [μmol/dm3] fig. 4. influence of cscl concentration on cs translocation from roots to shoots of tobacco plants (n. tabacum l.) after 8 days hydroponic cultivation in 8.3% hm containing 10, 20, 50, 100, 200, 500 or 1 000 μmol/dm3 cscl (33.5 kbq/dm3 137cscl), ph 6.0, at photoperiod 12h light/12h dark (2 000 lx) and 22°c. distribution expressed: a. in per cent of the total cs uptake by plant; b. as concentration ratio [cs]shoot : [cs]root (bq/g; dry weight). error bars represent standard deviation of the mean (n = 3). means with the same letter at columns are not significantly different at the p < 0.05 level based on multiple range test. our previous results obtained by direct analyzing of radioactivity in individual plant tissues as well as from autoradiography of whole plants showed that caesium was localized mainly in root system and young leaves (vrtoch et al., 2006). in this work we found that percentual content of cs in root, stem and leaves are affected with hm concentration i.e. macroand microelements concentrations (significant differences are shown in fig. 3a at the p < 0.05 level based on multiple range test). the concentration a b nova biotechnologica 10-2 (2010) 103 ratio (cr) [cs]shoot : [cs]root increased with increasing hm concentration from the value 0.10 to the value 0.85, particularly at 50% and 100% hm, when concentration of monovalent cations (k+ and nh4 +; [k+] : [nh4 +] = 2 : 3) were 5 mm and 10 mm, respectively (significant differences are shown in fig. 3b at the p < 0.05 level based on multiple range test). similar effect was observed in our previous work with sunflower hydroponics, when shoot-to-root specific 137cs radioactivity ratio (bq/g : bq/g; wet weight) increased with increasing concentration of hm from the value 0.10 to the value 0.69 (horník et al., 2005). buysse et al. (1996) and smolders et al. (1996) found that shoot-to-root cs concentration ratio decreased with decreasing k supply. it can therefore be assumed that the main influence in this respect will be concentration of k+ ions in media. fig. 4 depicts influence of cscl concentration in nutrient media on cs distribution in tissues of tobacco plants cultivated in 8.3% hm. there is a significant change in cs distribution in root, stem and leaves of tobacco. the percentual content of cs in aboveground part of tobacco increased with increasing cscl concentration in media (significant differences are shown in fig. 4a at the p < 0.05 level based on multiple range test). also, the cr ([cs]shoot : [cs]root) increased with increasing concentration of cscl (10 – 1 000 µmol/dm3) from the value 0.1 to the value 0.4. however, at concentration of cscl in media > 500 µmol/dm3 the cr was not changed (fig. 4b). 4. conclusions the results from hydroponic cultivation of tobacco plants (n. tabacum) indicate that bioaccumulation of cs was significantly affected by concentration of hoagland medium particularly monovalent cations as well as concentration of cscl in media. on the other side, higher concentration of hoagland medium and concentration of cscl in media have a positively effect on translocation of cs into aboveground parts of tobacco plants. it may be concluded that fast growing plant species with high biomass production like tobacco might be a suitable in phytoextraction or rhizofiltration technologies used for 137cs removing from environment. however, it should be proven by field experiments, because hydroponic experiments are only a principal model to study metals uptake but do not give information on soil-plant relations and metals uptake under the real conditions. acknowledgement: this work was supported by the ministry of education, science, research and sport of the slovak republic within the bounds of project conrelmat, decree no. cd-2009-36909/39460-1:11. references audet, p., charest, c.: heavy metal phytoremediation from a meta-analytical perspective. environ. pollut., 147, 2006, 231-237. buysse, j., van de brande, k., merckx r.: genotypic differences in the uptake and distribution of radiocaesium in plants. plant soil, 178, 1996, 265-271. 104 guldanová, j. et al. čurlík, j., šefčík, p.: geochemický atlas slovenskej republiky. časť v: pôdy. mžp sr, bratislava, 1999, 99 pp. dowdall, m., standring, w., shaw, g., strand, p.: will global warming affect soil-to-plant transfer of radionuclides? j. environ. radioact., 99, 2008, 17361745. dushenkov, s.: trends in phytoremediation of radionuclides. plant soil, 249, 2003, 167-175. gardea-torresdey, j.l., peralta-videa, j.r., de la rosa, g., pardone, j.g.: phytoremediation of heavy metals and study of the metal coordination by x-ray absorption spectroscopy. coord. chem. rev., 249, 2005, 1797-1810. ghosh, m., singh, s.p.: a review on phytoremediation of heavy metals and utilization of its byproducts. appl. ecol. environ. res., 3, 2005, 1-18. gustafsson, j.p.: visual minteq. web (april 2010): http://www.lwr.kth.se/english/our software/vminteq/index.htm. horník, m., pipíška, m., vrtoch, ľ., augustín, j., lesný, j.: bioaccumulation of 137cs and 60co by helianthus annuus. nukleonika, 50, 2005, 49-52. horník, m., pipíška, m., vrtoch, ľ., augustín, j., lesný, j.: bioaccumulation and translocation of cobalt in nicotiana tabacum l.. in: szilágyi, m., szentmihályi, k. 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j. exp. bot., 51, 2000, 1635-1645. microsoft word kraic.revision.doc nova biotechnologica 8-1 (2008) 71 influence of nutrients in soil and vine leaves and meteorological factors upon vine crop and must quality filip kraic1, jan mocak1,2, miroslav argay 3 1department of biotechnology, university of ss. cyril and methodius, j. herdu 2, sk-917 01, trnava, (filip.kraic@ucm.sk) 2 institute of analytical chemistry, slovak university of technology, radlinskeho 9, sk-812 37 bratislava 3 research institute of oenology and viticulture, matuskova 25, sk-831 01 bratislava abstract: the aim of this work was to analyze the supply of vine by nutrients by determining the content of nitrogen, phosphorus, potassium, calcium and magnesium in the vineyard soil and the vine leaves. its further goal was to discover mutual relationships among the content of determined nutrients, the vine crop, and the quality of the produced must. must quality was here defined by the contents of sugar and acids. the final goal was to investigate the relations among the nutrients, vine crop and its quality and meteorological factors measured during the whole year cycle, and especially at the time of important vegetation changes. the necessary evaluations were performed using multidimensional data analysis. key words: vine, soil analysis, nutrients, electroultrafiltration, principal component analysis, discriminant analysis 1. introduction the relations among the nutrients content in vine leaves and in the soil extracts are complicated and established by the concentration levels as well as antagonistic/ synergic interrelations of the individual influences. the applicable agrochemical methods of the soil analysis utilize different extraction agents of different concentration and ionic strength (németh, 1979; németh, 1985). the nutrients were extracted by different solvents: water (electroultrafiltration method), calcium lactate solution adjusted to ph 3.7 (phosphorus determination by egner), strong polar solvents like the mixture of acetic acid, ammonium fluoride and ammonium chloride in hydrochloric acid (melich method), and the mixture of ammonium acetate and ammonium oxalate (potassium by schachtschabel). different analytical methods were used also for the nutrients analysis in leaves, where the concentration of the most important elements was determined. all corresponding results together with meteorological factors (expressed mainly by temperature, quantity of rainfall and extent of the sunshine in individual vegetation cycles) represent a large number of factors related to the vine crop, must quality, and consequently, to the quality of the produced wine. the primary goal of this work was to determine the supply of vine by nutrients, which was obtained by analyses of nitrogen, phosphorus, potassium, calcium and magnesium in the vineyard soil and the vine leaves. the second goal was to discover 72 kraic, f. et al. the mutual relationships among the determined content of nutrients and three target variables: vine crop, sugar content and content of acids. the last goal was to uncover the hidden relations among the nutrients, vine crop and its quality (sugar, acids) and the meteorological factors measured during the whole year cycle, mainly in the time of important vegetation changes. 2. material and methods 2.1 analytical determinations the extractions of nutrients present in soil were made in two ways: (a) by water (when using electroultrafiltration method), (b) by 0.21 mol/l ammonium chloride in 0.012 mol/l hydrochloric acid (when melich method was applied). determinations of nutrients in leaves were performed after the leaves had been dried and mineralized. for determining the nutrient elements p, k, ca, and mg in soil two quantitative methods were used: electroultrafiltration (németh, 1982; mengel and kirkby, 2001) and melich method (melich, 1984; jones, 2001). 2.2 exploited data the studied data originated from the research institute of oenology and viticulture in bratislava, slovakia. the number of sampling sites, all localized in southern slovakia, was 24. the total number of the considered variables (factors) was 41, among them 4 target variables (vine crop, sugar content in must, content of acids in must, and year of the vine production), 10 variables concerning vine leaves given by the content of 5 elements (n, p, k, ca, mg) at the beginning (april may, denoted by number 1, e.g. k1) and the end (september october, denoted by 2) of the vegetation cycle, 8 variables concerning the vineyard soil given by the content of 4 elements (p, k, ca, mg) found by two analytical methods (electroultrafiltration and melich), and 19 meteorological factors given by 7 temperature indicators t4, t5, t9, t10, t1t12, t4t9, t4t10 (with the number related to the month or to the time interval between two months), 6 rainfall indicators rain4, rain5, rain9, rain10, rain1t12, rain4t10, and finally 6 sunshine indicators sun4, sun5, sun9, sun10, sun1t12, and sun4t10. 2.3 multidimensional (multivariate) data analysis assessment of the interrelations among the selected target variable and individual soil, leaves and meteorological factors was made using several techniques of multidimensional data analysis, namely principal component analysis, cluster analysis, and discriminant analysis (sharma, 1996; everitt and dunn, 2001). the statistical technique of correlation analysis was also implemented. the calculations were performed using commercial software packages statgraphics (ver. 5.1), spss (ver. 15), and sas jmp (ver. 5.1). nova biotechnologica 8-1 (2008) 73 3. results and discussion 3.1 correlation analysis table 1 brings a summary of the most important pair correlations, which represents an extract from a much larger correlation table. each row of the table shows the pair correlation coefficients between the selected target variable (specified in the left column of the table) and the given variable. some observations follow from the results given in table 1. target variable crop is mostly influenced by the amount of rainfall and sunshine in september as well as by the nitrogen content in the first phenophase (with a negative correlation!). target variable sugar is mostly influenced by the amount of rainfall and sunshine in april, the temperature level from april to september, the temperature during the whole year and the rainfall in september. sugar is also highly correlated with the potassium content in the second phenophase. target variable acids mostly correlates with the content of calcium and phosphorus in the second and magnesium and potassium content in the first phenophase. the highest and negative correlation is between acids and sugar. all mentioned important correlations concern the content of nutrients in vine leaves. the nutrients content in soil (not included into table 1) seems to be less important for the selected three target variables. tab. 1. most important correlations extracted from the correlation table at the significance level α=0.05 %. target variable highest positive correlation coefficient (in parentheses) highest negative correlation coefficient (in parentheses) crop rain9 (0.510) n1 (0.579), sun9 (0.500) sugar rain4 (0.640), t4 (0.625), t4t9 (0.620), k2 (0.545), sumt1t12 (0.545) acids (0.666), rain9 (0.538) acids ca2 (0.563), mg1 (0.534) sugar (0.666), k1(0.534), p2 (0.501) target variable highest absolute values of the pair correlation coefficient (in parentheses) crop n1 (0.579), rain9 (0.510), sun9 (0.500) sugar acids (0.666), rain4 (0.640), t4 (0.625), sumt4t9 (0.620), k2 (0.545), sumt1t12 (0.545), rain9 (0.538) acids sugar (0.666), ca2 (0.563), k1(0.534), mg1 (0.534), p2 (0.501) 3.2 cluster analysis ward method and squared euclidean distance were applied since they were found as the most effective way of cluster analysis in preliminary calculations. obtained 74 kraic, f. et al. results of cluster analysis are in good accordance with the performed correlation analysis (figure 1). target variable crop is clustered first of all with the phosphorus content in vine leaves (p1, p2) and the magnesium content in soil (mgme, mgeuf). target variable sugar is clustered mainly with meteorological variables – temperature in april (t4) and in the period april – september (t4t9) and rainfall in april (rain4). target variable acids is clustered mainly with the magnesium content in vine leaves (mg1, mg2) and the calcium content in soil (came). 3.3 principal component analysis the sampling sites represented the objects and analytical results and meteorological factors in different year period represented the variables in principal component analysis. they are depicted together in the form of a pca biplot in figure 2. it is clearly seen that the objects create three natural clusters, which (according to object numbers in a more detailed analysis) belong to three years of the vine crop: 2000, 2001 and 1999 (from the left to the right). fig. 1. dendrogram of cluster analysis of all variables involved in the vine crop and must quality (defined in the text). ward’s clustering technique. software statgraphics plus 5.1. it was also important to find, which variables are closely related to the three selected target variables, namely crop (in kg per vine shrub), sugar (sugar content in kg/hl in must), and acids (content of acids in g/l in must), which reflect the crop quantity as well as the must quality. the smallest angle between crop and rain9 indicates the importance of the september rainfall. almost 180° angle between crop and n1 as well as crop and sun9 indicates a large negative dependence of crop upon nitrogen content in leaves during the first phenophase as well as amount of sunshine in september. these q d is ta nc e 0 200 400 600 800 1000 n 1 n 2 p 1 p 2 k 1 k 2 c a1 c a2 m g1 m g2 p m e p e u f k m e k e u f c am e c ae u f m gm e m ge u f c ro p s ug ar a ci ds t 4 r ai n4 s un 4 t 5 r ai n5 s un 5 t 9 r ai n9 s un 9 t 10 r ai n1 0 s un 10 t 1t 12 r ai n1 t1 2 s un 1t 12 t 4t 9 t 4t 10 r ai n4 t1 0 s un 4t 10 nova biotechnologica 8-1 (2008) 75 findings are in accordance with the results of correlation analysis, as may be expected. moreover, the crop ray points to the 2001 cluster, which means that this year was most successful with regard to the crop of vine. a close position of sugar and rain4 rays indicates the importance of the april rainfall for the sugar content in must. the importance of the april temperature and the temperature level from april to september is indicated in a similar way. almost opposite position of the sugar and acids rays demonstrates a high content of sugar simultaneously with a low acids content in must and vice versa. finally, from the interposition of the samples corresponding to the years 2000 and 1999, respectively, it is visible a large impact of sunshine on the year 2000 samples as well as rainfall on the year 1999 samples. fig. 2. biplot pca showing 40 variables and 24 sampling sites. three clusters of the sampling sites represent the year of sampling: 2000, 2001 and 1999 – from the left to the right. software statgraphics plus 5.1. 3.4 linear discriminant analysis classification of the objects, which in our case mean the sampling sites, is generally made according to the selected target variable, which has to be categorical. a categorical variable should reflect a known categorization of an object into the chosen category. if it happens, the classification algorithm categorizes the given object into a different category than was the pre-determined category, which is then accompanied by decrease of the classification performance. after calculating the discrimination model, it is possible to use further objects either to validate the performance of the discrimination model by an independent way, or to predict the category where an unknown object should be classified. 76 kraic, f. et al. observed classification performance depended, as expected, on the selected categorical target variable. figure 3 shows the case when year was used as the target variable. here 100.0 % of the originally grouped objects were correctly classified when calculating the discrimination model and 87.5 % of the cross-validated objects were correctly classified using leave-one-out method; altogether 3 objects out of 24 were categorized into a different category then supposed. a 100.0 % performance was observed also in case when crop was the target variable and all 40 independent variables were used. the same performance was achieved with 20 independent variables without using the meteorological factors. performance characteristics were obtained also for other combination of variables: soil and meteorological, leaves and meteorological, etc. fig. 3. plot of discriminant functions (df’s) showing 24 sampling sites clustered by year. a 100 % performance was achieved for the sampling sites classification in discrimination model; 87.5 % performance was achieved for the sampling sites classification using leave-one-out validation. all 40 variables were used in calculations. software spss 15. 4. conclusions crop of vine and quality of the produced must are interrelated to the results of elemental analysis of the vineyard soil and the vine leaves. they are also influenced by the meteorological factors like sunshine, rainfall in different months and various years. nova biotechnologica 8-1 (2008) 77 most important factors influencing the vine crop, the sugar content and the content of acids in must were determined, as well. sampling sites in south-western slovakia were classified according to the target variables crop, sugar and acids by linear discriminant analysis and a very high classification performance was achieved. acknowledgment: the support of this work by the grants vega 1/3584/06 and av-4/2025/08 is highly acknowledged. references everitt, b.s., dunn, g.: applied multivariate data analysis, arnold, london, 2001. jones, j. b.: 1. laboratory guide for conducting soil tests and plant analysis, crc press, boca ranton, 2001. melich m.: melich-3 soil test extractant: a modification of the melich-2 extractant. comm. soil sci plant anal., 15, 1984, 1409-1416. mengel, k., kirkby, e.a.: principles of plant nutrition, kluwer academic publishers, bern 2001. németh, k.: recent advances in euf research (1980-1983). plant soil, 83, 1985, 1-19. németh, k.: application of electro-ultrafiltration in agricultural production, kluwer academic publishers, bern 1982. németh, k.: the availability of nutrients in the soil as determined by electroultrafiltration (euf). adv. agronomy, 31, 1979, 155-188. sharma, s.: applied multivariate techniques, j. wiley, new york, 1996. microsoft word ukropcova nb 9-3.doc nova biotechnologica 9-3 (2009) 255 biotechnology commercialisation in europe dana ukropcova1, ernest sturdik2 1bioscience slovakia limited, kostliveho 10, bratislava, sk-821 03, slovak republic (dana.ukropcova@orangemail.sk) 2institute of biochemistry, nutrition and health protection, faculty of chemical and food technology, slovak university of technology, radlinskeho 9, bratislava, sk-812 37, slovak republic (ernest.sturdik@stuba.sk) abstract: european biotechnology was mapped for research and commercialisation from various information sources. social and economical benefits from technology transfer in biotechnology are clearly visible in those european countries where proper attention is given to bioscience entrepreneurship education alongside with scientific base creation and spin-off development. successful bioscience commercialisation is a result of a coordinated support of research and specific commercialisation programmes leading to spinoff establishment and industry partnership. key words: commercialisation, biotechnology, technology transfer, spin-off 1. introduction europe is considered a continent where education and research are undoubtedly strongly supported. biotechnology has deep roots in extensive european life science research and globally competitive results. however, the phase of commercialisation of biotechnology research and development is a different matter. the usa has accumulated and maintained a large absolute advantage in innovative biotechnology activities compare to the rest of the developed world (allansdottir et al., 2002). europe began investing into life sciences commercialisation later than us and made a great effort to become the principal world competitor in biotechnology business (hodgson, 2006; duchene et al., 2007; beuzekom and arundel, 2009). there are many studies being published whether universities and research institutions should accept the role of active players for commercialisation activities or stay in the traditional role of an educator and fundamental research base (muldur et al., 2003). universities were traditionally funded by public money, ensuring a certain amount of neutrality and independence (downie and herder, 2007). for those universities and research institutions that decided to become entrepreneurial more than a decade ago, the results are evident in financial resources from licensing, royalties and other economic provisions flowing back to research and development (siegel et al., 2007). these make prestigious universities modern institutions and, consequently, have an advantage at the competitive global market. spin-off companies are increasing seen as a favoured route for commercialisation of university intellectual property. thus research spin-offs are companies what have been created in order to commercialise intellectual property arising out of a research where staff are transferred from the research institution to a new firm. intellectual property from the institution is licensed to the founding intellectual property of the firm (thornburn, 2000; 256 ukropcova, d. and sturdik, e. jarrett, 2007). the success of the biotechnology commercialisation depends on an array of interwoven factors, not the least of which is the protection, preservation and promotion of public trust in the science, the scientists and the regulators (chalmers and nicol, 2004; savage, 2006). the idea of entrepreneurial research institutions and new firms creation disseminates and yet further research and development is necessary (rothaermel et al., 2007; mroczkowski, 2009). the european commission can play a major role in fostering innovations in the life sciences sector, through its framework programmes for research and technological development, as well as through other policy initiatives implementing a coherent eu strategy for biotechnology and life sciences (kütt et al., 2003). the european council and the european parliament have recognised the importance of life sciences and biotechnology, and the european commission has put forward an action plan to address the challenges and opportunities involved. this ‘strategy on life sciences and biotechnology’, adopted by the european commission in 2002, proposed a 30 point action plan involving the commission, the other european institutions and other stakeholders and it runs until 2010 (european commission, 2007). in this article, we map biotechnology commercialisation in europe and summarize the papers and reports on this topic in european countries. in the concluding section, we discuss some organizational and societal issues that arise from past experience and gained knowledge in biotechnology commercialisation. 2. history and present status biotechnology commercialisation began in europe at the end of 1980s, more than a decade later than in usa. the first to stir up the market appeared united kingdom followed by germany, france and switzerland. some of the smaller european countries, particularly ireland, denmark, the netherlands and the scandinavians countries, are also focused on biotechnology (allansdottir et al., 2002). united kingdom united kingdom (uk) leads europe in biotechnology, although it is still some way behind the united states (sainsbury, 1999; dectera et al., 2007). almost a quarter of all european biotechnology companies are located in the uk. despite the maturity of uk biotechnology, r&d institutions seeking to license intellectual property or use it as the basis for a new life science venture still face several challenges in finding the relevant expertise and creating a fertile environment to facilitate start-up activity (searle et al., 2003). in 2003, there were 455 firms involved in biotechnology in uk. these spent in public-private partnership $ 2008.4 million on r&d and employed 22405 fulltime equivalent employees, 59% of which were working in the healthcare sector (van beuzekom and arundel, 2006; smith and bagchi-sen, 2006). germany although the european biotechnology industry is large and growing larger, individual countries represent very different stages of biotechnology growth and nova biotechnologica 9-3 (2009) 257 venture capital progress. germany provides a good example of how directed changes in governmental policy and commitment can lead to flourishing biotechnology and venture capital industries. before the 1990s, germany had an extensive research base but little interest in commercialising its results. in 1996, the german minister for science and technology launched the bioregio contest to promote the commercialisation of biotechnology. bioregio was a government initiative that promoted the development of biotechnology 'clusters', with the winning 'model' regions receiving $25 million over five years. at the same time, germany set up a program called "risk capital for small technology companies" investing into new biotechnology enterprises (howell et al., 2003). in 2004, there were 607 firms involved in biotechnology or biotechnology-related businesses and 24134 biotechactive employees, of which 11958 (50%) were employed by core biotech firms and 10995 (46%) by large life science firms (van beuzekom and arundel, 2006). france the financial, fiscal, and research landscape for innovation and biotechnology has dramatically improved in france between 2001 and 2006. france became an attractive country for research, innovation, and the rise up of innovative small and middle enterprise. the "young innovative company" status was conceived in france and already benefits more than 300 of the country's biotechnology companies and their shareholders. proposal ‘excellence valo’ aims at creating a favourable environment for technology transfer and the emergence of start-up projects in research organisation (notably universities) thanks to a france-wide competition designed to spread good technology transfer practices and better funding to technology transfer teams throughout france (carmagnol, 2007). according to the french biotechnology association and the industry representative france biotech, the sector has been buoyed by venture capital investments throughout the first half of 2008, particularly pumppriming rounds, with investment of eur 87mil. (costa and carmagol, 2008). in 2003, 755 firms undertook biotechnology r&d in france, which represented 11% of all firms undertaking r&d, and spent $ 1342.0 million on biotechnology r&d in private-public partnership, which represented 5.6% of total business enterprise r&d spending (van beuzekom and arundel, 2006). switzerland out of a total of 693 european biotechnology products in the development pipelines of listed companies, 97 come from switzerland (alexakis, 2007). this second-place ranking in europe shows the country’s innovative capabilities. with 137 enterprises and 81 suppliers, switzerland boasts the world’s highest per capita biotechnology density. in 2006, the swiss biotechnology industry generated a turnover of more than 6 milliard chf and had a workforce of over 14 300 employees. the basis for this ongoing success is the intensified collaboration and exchange of knowledge within a network of institutes, universities and private businesses. switzerland, with over 40 venture capital firms and private equity funds, as well as various science parks and incubators, is a very inviting environment for innovative start-up companies. 258 ukropcova, d. and sturdik, e. denmark danish biotechnology not only outperforms its european counterparts but is on the rise. in 2006, companies raised unprecedented amounts of venture capital, pried open the window for initial public offerings and tempted investors with follow-up offerings (giovannetti and jaggi, 2007). the danish biotech industry has developed at a rapid pace over the past ten years. in the late 1990s, there were around 30 businesses in denmark, the number rose to 117 in 2004, whereas in 2007 it was 82 active biotech companies. geographically, 77 percent of the companies are located in the danish part of the cluster medicon valley (moran, 2006). a new report from ernst & young shows that denmark ranks third in europe in terms of number of biotech products under development (sorensen et al., 2008). scandinavian states the research council of norway supported biotechnology, biology, biomedicine and functional genomics research in total funding in 2003 close to eur 70 million (johne, 2004). in the business sector, had the highest r&d expenditures on biotechnology (public-private partnership $11.2 million), followed by the chemical sector (public-private partnership $10.2 million). in 2003, 1440 biotechnology researchers worked in the higher education and institute sector; about half of these were women. scandinavia has a strong life science and healthcare industry (brazil, 2008). medcoast scandinavia is a norwegian/swedish network organization with the aim to strength and develops the biomedical sector in the göteborg-oslo region. it includes 400 biomedical companies with 10 000 employees, every year about 20 start-ups are and the biotech venture capital investment about eur 50 million annually (oxford research, 2004). belgium in 2006, there were over 140 biotechnology companies operating in belgium, 7% of all such companies in europe and two are elite companies (tab. 2). belgian biotechnology companies accounted for 16% of european turnover and almost 10% of r&d expenditure (belgian federal government, 2008). ireland irish biotechnology sector is strongly supported by state funding. because commercialising technology is vital to achieve sustainable growth this aim, state agency enterprise ireland has established expert commercialisation teams working across the academic-industry interface in three key technology areas: life sciences and food, informatics and industrial technologies. proof of concept funding is available to individuals or small groups who wish to demonstrate that their ideas have originality and true commercial potential. commercialisation of research and development funding aims to bring a new product idea or business venture from third level educational institutions to market. these funding encourages knowledge based campus companies and academic entrepreneurs and to the year 2004 created 49 spin-off nova biotechnologica 9-3 (2009) 259 companies. the bio-incubators at trinity college dublin and national university of ireland in galway, funded by enterprise ireland in 2004, already house a number of spin-off companies (enterprise ireland, 2008). 3. biotechnology and life sciences clusters there are sixteen biotechnology and life sciences clusters in europe. for a number of years now the area where denmark and sweden meet, copenhagen capacity and region skane, has been branded ‘medicon valley’. this area is a life science cluster of research and development, as well as being home to a number of other institutions important for r&d, including several universities and contract research organisations (brazil, 2008). the trinational biovalley is a unique, global, cross-border life sciences cluster, has one of the world's highest densities of life science activities, is one of the biggest life science clusters in europe, has a strong scientific basis: more than 600 companies including big pharma, medtech and start-up companies, four renowned universities basel, freiburg, mulhouse and strasbourg (daniel et al., 2006). central and eastern europe the two main features of the restructuring are increased autonomy for scientists and the beginnings of competitive research funding. in some countries in central and eastern europe, high proportion of research funding is still allocated as block grants to institutes and/or universities. however, these funds may be allocated to institutes dedicated to a specific area of research, e.g. molecular biology. none of the countries reach the eu-25 average for gross domestic expenditure on r&d as a percentage of gdp, which was 1.86% in 2004; most are significantly below this figure (enzing, 2007). the agencies that fund research are normally separated from those that fund its commercialisation through support to applied research, technology development, industrial research grants, university-industry research collaboration and measures to encourage the creation of small firms. applied research and development was carried out in industrial research institutes under specific ministries and was completely separate from the enterprises and there was little in-house industrial r&d. the czech and slovak republic differ from this general pattern and over half of r&d was performed in the business sector. only four countries have attempted to implement this priority by allocating funds to biotechspecific research programmes – bulgaria, hungary, lithuania and slovak republic. there is limited data on commercialisation in nms and ams and this probably reflects the early stage of development of biotechnology in these countries. for instance, there is no data on venture capital investment in biotechnology firms or on initial public offerings (firms floated on stock markets). growth in publications output over time, particularly the capacity to sustain and increase growth of publications, provides a basis to cluster countries with similar performance into three groups: group 1: the czech republic, estonia, hungary and slovenia are closing the gap with the eu-25. group 2: cyprus, croatia, poland and slovak republic are making progress. 260 ukropcova, d. and sturdik, e. group 3: bulgaria, latvia, lithuania, malta, romania and turkey have weak performance. 4. measuring biotechnology commercialisation the socio-economic impact of biotechnology has become very important for policy makers, industry, and consumers. a broad range of indicators measures commercial orientation of the various countries in biotechnology: patents and scientific publications, number of spin-off companies, distribution of employees and venture capital investment. patents and scientific publications commercialisation begins with science. evidence suggests that public expenditure on biotechnology research has been increasing steeply in recent years. several european countries have declared the fostering of biotechnology to be a key priority in their science and technology policies. for example, ireland dedicated a substantial sum of 635 million euro to promoting excellence in scientific research in strategic areas such as biotechnology and information and communication technologies (muldur et al., 2003). in order to obtain a general impression of the commercial orientation of european countries in biotechnology, authors of the report biopolis related the patent output as a measure for technology generation and commercial interest to the scientific publications output, which could be considered as a measure for scientific activities (enzing, 2007). in 2003 almost similar numbers of patent applications are observed from europe and the united states while in the preceding years a clear lead of the united states could be detected. biotechnology seems to gain more importance in smaller high-performing countries, such as sweden, finland, denmark, iceland or switzerland (muldur, 2003). these countries also perform best according to measure of relative scientific output in biotechnology and show the highest relative growth rates. performance in terms of technology generation as measured by patent applications on a per-capita basis also reveals a broad variety among european countries. top performing countries in the most recent years are iceland, denmark and switzerland (muldur, 2003). biotechnological industry – companies and employees as number of biotechnology companies indicates a quality level of biotechnology commercialisation, report critical i in the year 2006 compares the biotechnology sectors across some eighteen european nations and the united states (hodgson, 2006). the survey for 2006 report critical i gathered data from 4 154 companies, of which 2 163 were in europe and 1 991 in the usa. european companies are younger and tend to be smaller. while the healthcare sector in europe accounts for just over a third of companies, it employs 50 000 people, approximately 52% of the european biotechnology workforce (fig. 1). nova biotechnologica 9-3 (2009) 261 agbio and environmental 11% services 34% human healthcare 37% biodiagnostics 18% fig. 1. distribution of biotechnology companies in europe by sector (hodgson, 2006). venture capital in biotechnology measuring commercialisation of biotechnology in terms of venture capital investment reveals an increasing flow of venture capital into almost all countries considered since the mid 1990s (tab. 1). tab. 1. a snapshot of the eu biotech sector data collected from dedicated biotech companies (hodgson, 2006). interestingly, for most countries where data is available (denmark, austria, united kingdom, sweden and finland), we observe a continuous growth over years 19952004. the past few years marked a recovery period for the european biotechnology sector. looking at 2006, it appears that it is now on the right track of sustained progress (tab. 2). a record year of financing, with 4.7 milliard euros raised with 45 percent increase demonstrates the robustness and growing strength of the european biotechnology sector (duchene, 2007). although venture capital funding did not increase at similar rates, the amount of private equity raised by european companies set an all-time record, passing 1.5 milliard euro for the first time ever. with 722 million euros in proceeds from 32 initial public offerings a stable trend in european public company financing appears to be emerging (ernst & young report, 2008). indicator europe us number of companies 2 330 1 991 number of new companies formed 131 78 number of employees 98 500 190 500 r & d expenditure (in mld €) 7.6 21 revenue (in mld €) 21.5 41.5 venture capital raised (in mld €) 1.02 3.2 equity raised (in mld €) 3.65 11.3 debt raised (in mld €) 0.81 7.4 262 ukropcova, d. and sturdik, e. tab. 2. top venture funding in europe (hodgson, 2006). 5. conclusions there is no doubt that biotechnology is the key technology of modern economies. biotechnology industry is built upon excellent science and market demand. if adequate attention is given to creation of scientific base and consequently commercialisation, economic rewards are beneficial for the academic and business community. the results are clearly visible in old member states of european union where combination of biotechnology specific and generic policy instruments have been adopted since end of 1990s (sainsbury, 1999). the analysis confirmed the trend towards commercialisation even in those countries that fell behind the european overage. the new member states and accession countries of european union suffer from lack of public resources to invest into research in general. fragmented and uncoordinated support of biotechnology research makes it difficult for any commercialisation at all. government science and technology policy, significant factors that can often explain the biotechnology performance, are restructuring to make the support system more effective (enzing, 2007). european biotechnology companies are part of a smaller industry due to lower amounts of capital available, and therefore take longer to raise capital (hodgson 2006). they face slow growth beyond the start-up stage than those in us and remain sub-critical size. a recent study showed that there are close to 1 400 technology transfer offices in europe (european commission, 2009). many started as industry liaison offices and also developed services to encourage commercialisation of research results. over time, many of these have developed specialised staff and services for assessing disclosed inventions, patenting, licensing, and developing and funding spinoffs, but also for actively approaching firms for contract based arrangements. name country round amount raised (in mil eur) movetis belgium first round 49 chroma therapeutics uk third round 44 cerenis therapeutics france second round 43 nabriva therapeutics austria first round 42 ablynx belgium fourth round 40 palau pharma spain first round 40 santaris pharma denmark fourth round 40 nowimmune switzerland second round 37 chiasma israel second round 35 esba tech switzerland third round 32 neuropharma spain second round 32 genextra italy second round 30 nova biotechnologica 9-3 (2009) 263 aknowledgement: the project was supported by european social fund, ministry of labour, social affairs and family of the slovak republic, project code dp 161/05i/32-2. references alexakis, a.: swiss biotech report 2007, druckerei feldegg ag, zollikerberg, 2007. allansdottir, a., bonaccorsi, a., gambardella, a., mariani, m., orsenigo, l., pammolli, f., riccaboni, m.: innovation and competitiveness in european biotechnology, office for official publications of the european communities, brussels, 2002. belgian federal government: biotech in belgium, belgian public services, brussels, 2008. brazil, m.: special report: scandinavian biotech, nature publishing group, 2008. carmagnol, a.f.c.: 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h.l., bagchi-sen, s.: university-industry interactions: the case of the uk biotech industry, industry & innovation, 2006, 371 – 392. sorensen, b.l., almen, l., carlsen, s.: biotech in denmark growing stronger. ernst & young denmark, copenhagen, 2008. thornburn, l.: government policies to encourage creation of spin-off firms from academic institutions. sapporo: apec symposium on intellectual property rights, 2000. van beuzekom, b., arundel, a.: oecd biotechnology statistics 2006, oecd publishing, paris, 2006. van beuzekom, b., arundel, a.: oecd biotechnology statistics 2009, oecd, paris, 2009. microsoft word fecko et al 2010-1.doc nova biotechnologica 10-1 (2010) 71 bio-treatment of soil from international airport in ostrava peter fečko, radmila kučerová, eva pertile, lucie nezvalová, nikolas mucha, iva janáková, vladimír čablík vsb – technical university of ostrava, faculty of mining and geology, 17. listopadu 15, 708 33 ostrava poruba, czech republic (peter.fecko@vsb.cz) abstract: the paper deals with an examination of possible application of biodegradation in the decontamination of soil samples from international airport in ostrava. the laboratory biodegradation tests were carried out with a pure bacterial culture of pseudomonas putida, a pure laboratory culture of rhodococcus sp, their mixture and a mixture prepared combining their media free of bacteria. the results of the paper imply that for biodegradation of airport pollutants is most suitable to apply a mixed bacterial culture of pseudomonas putida and rhodococcus sp. the results show that the biodegradation method is applicable for the pollution. keywords: biodegradation, pseudomonas putida, rhodococcus sp., mixed culture 1. introduction biodegradation (biological decontamination) is grounded in the capacity of certain bacterial strains to use hydrocarbons as a source of carbon and energy for their growth and in this way, decomposition of contaminants occur all the way to harmless products carbon dioxide and water. in short, biodegradation is a special case of degradation during which decomposition of polymers takes place due to the action of biological factors. it makes part of natural processes taking place in water and soil. for example, there is spontaneous degradation of biologically degradable oil substances at contamination of soil by oil substances. however, the process is slow and meanwhile contamination may spread into the surroundings. in the locality some resistant substances remain. in order to speed up the rate of degradation, it was necessary to make the process more intense and to remove resistant substances bacterial mixtures may be utilized. the ability of microorganisms to degrade hydrocarbons has been known since 1895, when miyoshi described growth of yeast on paraffin and shortly after the capacity of bacteria to make use of methane as a source of carbon was discovered. gradually, it was demonstrated that they are able to decompose practically all components of crude oil and many other hydrocarbons. at present, over 200 types of microorganisms have been described that are able to degrade hydrocarbons. some are able to make use of one hydrocarbon only (e.g. methane), but no microbial strain is known to degrade a whole range of hydrocarbons present in crude oil, for example. therefore, these are rather microbial associations that participate in degradation (novotný, 2005). the objective of the paper was to examine the application of bacterial leaching to the decontamination of soil samples from the leos janacek airport in ostrava – these samples were taken from two sampling points. 72 fečko, p. et al. 2. materials and methods 2.1 leos janacek airport in ostrava the first mention of air traffic at the territory of the present airport is from 1939 when german luftwaffe built a field aerodrome to attack poland. the modern history began in 1956 when the current airport began to be constructed. before 1989, the airport was used mainly for the needs of the air force. civil aviation was ensured by csa, namely for domestic flights, rarely for international ones. a significant turning point was the year of 1993 when the military traffic was terminated at the airport. on 13 december 2006 the airport was ceremonially christened after the composer of leos janacek and a new departure hall was put into operation. with regard to its excellent technical parameters, a pronounced development of this traffic junction is expected in the future (see references). several oil leaks have occurred at the airport and figure 1 and figure 2 show an oil interceptor lapol d and lapol 2, which intercepts leaks of hazardous substances. table 1 summarizes leaks of hazardous substances since 2005. at the same time, it gives substances that penetrated into the environment and the materials by used for their elimination. table 1. leaks of oil substances at the airport. date leak locality substance qty of leaked subst. [l ] material used for disposal leak into sewer system 23.6.2005 central passenger terminal jet a – 1 200 vapex, cansorb no 21.6.2006 central passenger terminal jet a – 1 not determ. cansorb no 28.7.2006 central passenger terminal hydraulic oil not determ. cansorb no 12.9.2006 central passenger terminal jet a – 1 not determ. cansorb no 18.9.2006 taxiway jet a – 1 50 vapex, cansorb, wa ter, surfaceactive agent no 27.9.2006 northern stand jet a – 1 30 cansorb no 29.3.2007 central passenger terminal jet a – 1 30 cansorb no 28.3.2008 bunkers of airport propellants oil products – closely unspecified not determ. vapex, sorption layer, absorption heaps, sewer seal yes nova biotechnologica 10-1 (2010) 73 it is apparent from the table that accidents with environmental impact prevail, accompanied by leaks of aviation turbine fuel jet a-1. fig. 1. lapol d – leaks of oil products. fig. 2. lapol 2. 2.2 characteristics of drawn samples the soil samples were taken directly from the airfield of the leos janacek airport in ostrava – mosnov see figure 3. fig. 3. view of the sampling point. the mineralogical analyses were implemented in the laboratories of the institute of geological engineering at mining college technical university of ostrava by means of an x-ray diffraction. the results of the mineralogical analyses of sample 1 (figure 4) imply that the samples contain about 18 % of amorphous phase, majority of quartz about 57 % and followed by calcite, chlorite, muscovite, orthoclase and albite. fig. 4. mineralogical analysis of the sample no.1. 74 fečko, p. et al. the results of the mineralogical analyses of sample 2 (figure 5) imply that the samples contain about 30 % of amorphous phase, majority of quartz about 42 %. . fig. 5. mineralogical analysis of the sample no.2. 2.3 characteristics of bacterial cultures and the method of laboratory tests for biodegradation of the samples, pure bacterial cultures of pseudomonas putida and rhodococcus sp were used. the bacterial cultures are shown in figures 6 a, b (fečko et al., 2004). fig. 6. pseudomonas putida (a) and rhodococcus sp. rha1 (b) (fečko et al., 2004). the culture media were the liquid medium of m1 for pseudomonas putida and medium of m96 for rhodococcus sp. the laboratory experiments were carried out with pure bacterial cultures of psedomonas putida and rhodococcus sp., mixed culture and bacterial medium made of 50 % mi medium and 50 % of m96 medium. the experiments were carried out in the laboratories of the institute of environmental engineering at vsb-tu ostrava, where 28day bacterial degradation took place. each sample was placed into a 2 l glass beaker. aeration was secured by means of aquarium pumps placed into the beakers. the necks of the beakers were sealed with a foil and then the beakers were moved into the chemical hood. in the course of 4-week degradation the volume in the beakers was regularly filled with distilled water as gradual evaporation occurred. having finished the experiment, the samples were filtered, dried and sent to further chemical analyses into the brown coal research institute in most. nova biotechnologica 10-1 (2010) 75 3. results and discussion the results of laboratory biodegradation tests after one-month biodegradation with applied pure bacterial cultures and mixed culture are stated in tables 2, 3. the tables imply that in the course of biodegradation tests, gradual degradation of harmful substances content from the sample occurred. for biodegradation the following pure bacterial cultures were used: pseudomonas putida pp, rhodococcus sp. r, mixed culture rhodococcus sp. and pseudomonas putida r+pp, and a check sample from media mixtures k. table 2. course of degradation the selected contaminants by means of rhodococcus r, pseudomonas putida pp and mixed culture pp+r, check test – k. evaluation of the biodegradation test of sample 1 input r removal degree pp removal degree pp+r removal degree check test k removal degree parameter mg/kg mg/kg % mg/kg % mg/kg % mg/kg % nel*) 196 127 35.2 120 38.78 72 63.27 89 54.59 anthracene 11.4 1.3 88.6 1.03 90.96 2.22 80.53 4.28 62.46 benzo(a) anthracene 65.8 8.2 87.54 5.83 91.14 12.88 80.43 29.09 55.79 benzo(b) fluoranthene 67.2 11.51 82.87 7.74 88.48 14.61 78.26 40.22 40.15 benzo(k) fluoranthene 61.2 54.16 11.5 5.97 90.25 11.81 80.7 27.36 55.29 benzo(a) pyrene 105 102.29 2.58 3.71 96.47 5.78 94.5 17.66 83.18 benzo(ghi) perylene 56.5 49.76 11.93 3.09 94.53 6.13 89.15 14.31 74.67 fenantrene 208.8 32.03 84.66 22.69 89.13 46.36 77.8 114.38 45.22 fluoranthene 264 24.05 90.89 18.88 92.85 36 86.36 96.96 63.27 chrysene 86.9 0.32 99.63 0.72 99.17 16.41 81.12 42.57 51.01 indeno (1,2,3-d)pyrene 18.7 0.1 99.47 11.98 35.94 4.44 76.26 18.67 0.16 naftalene 12.3 1.35 89.02 0.95 92.28 2.14 82.6 3.71 69.84 pyrene 230.9 4.08 98.23 12.45 94.61 25.16 89.1 64.17 72.21 σ pah 1188.7 289.15 75.68 95.04 92 183.94 84.53 473.38 60.18 pcb 28 0.01 0.01 0 0.01 0 0.01 0 0.01 0 pcb 52 0.01 0.01 0 0.01 0 0.01 0 0.01 0 pcb 101 0.01 0.01 0 0.01 0 0.01 0 0.01 0 pcb 118 0.02 0.01 50 0.01 50 0.01 50 0.02 0 pcb 138 0.02 0.02 25 0.02 25 0.01 45 0.02 0 pcb 153 0.06 0.02 57.89 0.04 36.84 0.02 59.65 0.04 24.56 pcb 180 0.02 0.01 50 0.02 15 0.01 50 0.01 50 σ pcb 0.15 0.09 39.46 0.11 26.53 0,08 42.86 0.12 16.33 *) nel – hydrocarbons c10 – c40 76 fečko, p. et al. it is apparent from the results of four-week biodegradation test that the most suitable application for the sample 1 is that of the pure bacterial cultures of pseudomonas putida, where the degradation of contaminants of pah was 92 %. in terms of degradation of pcb the best was the application of mixed culture, i.e. 42.9 %. in this case, the efficiency of the mixed bacterial culture was very positive as is visible from the following removed quantities: 63.3 % of nel, 84.50 % of pah and 42.9 % of pcb. table 3. course of degradation the selected contaminants by means of rhodococcus r, pseudomonas putida pp and mixed culture pp+r, check test – k. evaluation of the biodegradation test of sample 2 input r removal degree pp removal degree pp+r removal degree check test k removal degree parameter mg/kg mg/kg % mg/kg % mg/kg % mg/kg % nel 150 100 33.3 60 60 35 76.6 120 20 antracene 0.7 0.49 30 0.07 90 0.1 85.71 0.12 82.86 benzo(a) antracene 2.36 1.89 19.92 0.33 86.02 0.44 81.36 0.48 79.66 benzo(b) fluoranthene 5.2 4.95 4.81 0.6 88.46 0.69 86.73 0.71 86.35 benzo(k) fluoranthene 3.1 2.99 3.55 0.43 86.13 0.54 82.58 0.59 80.97 benzo(a) pyrene 5.31 4,67 12.05 0.53 90.02 0.59 88.89 0.74 86.06 benzo(ghi) perylene 3.5 1.16 66.86 0.21 94 0.27 92.29 0.28 92 fenantrene 2.65 2.45 7.55 0.86 67.55 0.14 94.72 1.45 45.28 fluoranthene 5.7 0.27 95.26 0.19 96.67 0.41 92.81 0.58 89.82 chrysene 2.7 0.13 95,19 0.25 90.74 0.02 99.26 0.02 99.26 indeno(1,2,3-cd) pyrene 6.99 6.66 4.72 2.39 65.81 0.11 98.43 0.56 91.99 naftalene 0.09 0.07 22.22 0.07 22.22 0.07 22.22 0.07 22.22 pyrene 4.75 2.69 43.37 0.6 87.37 0.17 96.42 1.3 72.63 σ pah 43.05 28.42 33.98 6.53 84.83 3.55 91.75 6.9 83.97 pcb 28 <0.01 <0.01 <0.01 <0.01 <0.01 pcb 52 <0.01 <0.01 <0.01 <0.01 <0.01 pcb 101 <0.01 <0.01 <0.01 <0.01 <0.01 pcb 118 <0.01 <0.01 <0.01 <0.01 <0.01 pcb 138 <0.01 <0.01 <0.01 <0.01 <0.01 pcb 153 <0.01 <0.01 <0.01 <0.01 <0.01 pcb 180 <0.01 <0.01 <0.01 <0.01 <0.01 σ 7 pcb <0.07 <0.07 <0.07 <0.07 <0.07 *) nel – hydrocarbons c10 – c40 nova biotechnologica 10-1 (2010) 77 it is apparent from the results of four-week biodegradation test that the most suitable application for the sample 2 is that of mixed bacterial cultures of pseudomonas putida and rhodococcus, where the degradation of contaminants of pah was 91.75 %. the amount of pcb was lower as detection limit. in this case, the efficiency of the mixed bacterial culture was very positive as is visible from the following removed quantities: 76.6 % of nel, 84.83 % of pah and 0 % of pcb. 4. conclusions the objective of the paper was to examine the application of biodegradation in the decontamination of soil sample from the leos janacek airport in ostrava. for the laboratory biodegradation tests soil samples from the airport of the leos janacek in ostrava – mosnov was used. the laboratory biodegradation tests were implemented with pure bacterial culture of pseudomonas putida, pure bacterial culture of rhodococcus sp, their mixture and mixture made combining their media free of bacteria. the efficiency of the biodegradation of sample 1 after one-month leaching with pure bacterial culture of pseudomonas putida (pp) was 38.8 % for nel, 92% for pah, 26.5 % for pcb, by means of pure bacterial culture of rhodococcus sp. (r) was 35.2 % for nel, 75.7 % for pah, 39.5 % for pcb, by means of mixed bacterial culture it was 63.3 % for nel, 84.5 % for pah, and 42.9 % for pcb. the efficiency of the biodegradation of sample 2 after one-month leaching with pure bacterial culture of pseudomonas putida (pp) was 60 % for nel, 84.5% for pah, 0 % for pcb, by means of pure bacterial culture of rhodococcus sp. (r) was 33.3 % for nel, 28.5 % for pah, <0.07 % for pcb, by means of mixed bacterial culture it was 76.6 % for nel, 91.8 % for pah and 0 % for pcb. the paper results imply that the laboratory sample 1 biodegradation efficiency with the selected contaminants ranged from 35.2 – 63.3 % for nel, 60.2 92 % for pah and 16.3 – 42.9 % for pcb. the paper results imply that the biodegradation efficiency of laboratory sample 2 with the selected contaminants ranged from 33.3 – 76.6 % for nel, 33.98 – 91.75 % for pah. the amount of pcb was lower as detection limit. the best efficiency was obtained in the laboratory biodegradation of pah. intermediate efficiency was reached with biodegradation of nel and pcb. the highest amount of nel and pcb were removed by mixed bacterial culture (pp+r). for soil biodegradation, it is thus the most suitable to apply the mixed bacterial culture of pseudomonas putida and rhodococcus sp. the results demonstrate that for the given type of contamination the method of biodegradation is suitable. acknowledgement: the work was carried out within the vav sp/2f2/98/07 project solution “research in the utilization of waste as substitutes for primary raw material sources” and supported by the ministry of environment (moe) of the cr. 78 fečko, p. et al. references novotný, c.: biodegradace a biotechnologie, ostravska univerzita, ostrava, 2005. 96 pp. basic information on the airport [online]. 2009 [cit. 2009-03-02]. available from www: . history of the airport [online]. 2008 [cit. 2009-03-02]. available from www: . technical data on the airport [online]. 2008 [cit. 2009-03-02]. available from www: . mosnov municipality [online]. 2009 [cit. 2009-03-02]. available from www: . fecko, p. et al.: environmentalní biotechnologie, ostrava, vsbtu ostrava, 2004. 180 pp. nova biotechnol chim (2022) 21(1): e1246 doi: 10.36547/nbc.1246 1 nova biotechnologica et chimica low abundant bovine colostrum proteins in combination with amaranth oil reveal topical analgesic activity nail j. sagdiev1, jamolitdin f. ziyavitdinov1, nodir sh. berdiev1, soyib s. bozorov1, tohir a. khudoyberdiev1, shukhratjon s. olimjonov1, natalya l. vypova1, akmal m. asrorov1, 2,  1institute of bioorganic chemistry of uzbekistan academy of sciences, 100125, 83, m. ulughbek str., tashkent, uzbekistan 2ajou university in tashkent, 100204, 113a, asalobod str., tashkent, uzbekistan  corresponding author: akmal84a@gmail.com article info article history: received: 21st october 2021 accepted: 1st december 2021 keywords: amaranth oil analgesic activity bovine colostrum low-abundant proteins water-alcohol-soluble fraction abstract colostrum is an arsenal of proteins and peptides required at the earliest stage of a newborn development. proteins involved in all biological processes of an infant development have been found in its composition. it is expected as cost-effective source of biologically active proteins and peptides. in this work, we separated wateralcohol-soluble low abundant proteins from bovine colostrum in preparative amounts that were further utilized in combination with amaranth oil for topical cream composition. the ratio of the obtained proteins’ fraction made a thousandth of the colostrum dry mass. the partial sequences of 37 identified proteins were established by mass-spectrometer and using blast search in ncbi database. in our previous work, we established the chemical composition of amaranth seed oil with ~6 % squalene by mass. the physical mixtures of these natural resources were fabricated into cream using hyaluronic acid as moisturizing agent and their analgesic activities were established. the optimal ratio of proteins and oil was determined in terms of their effects as analgesic means by experiments carried out on mice. several proteins could possibly be responsible for the revealed biological efficacy. among them, g-protein coupled receptor and synaptotagmin were previously linked with analgesic activity. establishing an optimum ratio of ingredients proved also the contribution of higher quantity of amaranth oil, a rich source of squalene and unsaturated fatty acids. introduction colostrum is a rich source of proteins, fats, carbohydrates, and other ingredients. as a product secreted after birth, it has a higher content of proteins than milk. immunoglobulins, lactoferrin, lysozyme, and different growth factors compile the main content of colostrum (silva et al. 2019). albumin, heavy chains of immunoglobulins m and g, antitestosterone antibody, lactotransferrin, and polymeric immunoglobulin receptors were demonstrated as the main content of the colostrum whey (zhang et al. 2011). by two-dimensional analysis, ighg1 (immunoglobulin heavy constant gamma 1), c1 with uncharacterized function and vi1a protein were found as low abundant proteins in bovine colostrum whey (golinelli et al. 2011). recent research analysis revealed that exosomes of colostrum are enriched with proteins regulating the immune response and growth. the biological roles mailto:akmal84a@gmail.com nova biotechnol chim (2022) 21(1): e1246 2 of the proteins from exosomes were found to belong to immune regulation, growth and infant development (samuel et al. 2017). a number of colostrum-based products have reached the market as cosmetics, bioadditives, and other means. in combination with other ingredients, colostrum has been patented as a pharmaceutical and cosmetic composition (gobbi 2007). in another document, different ratios of horse colostrum and milk were earlier patented with other ingredients as painrelieving agents against sun burns and fire burns (gobbi 1993). in-depth analysis of bovine colostrum with 2d-lcms/ms analysis identified 403 proteins in the nonfractionated colostrum (nissen et al. 2012). in the fluid phase, 69 additional proteins were found. among all identified proteins, 38 % of them belonged to cellular processes, biological regulations, response to stimulus, and regulations of biological processes. studying the proteomic changes in bovine colostrum and milk revealed that the highest number of proteins belonged to immunity, transport and cell processes both in colostrum and milk (zhang et al. 2015). number of proteins in colostrum involved in cellular process, response to stimulus, metabolic processes, and regulation of biological processes were found as the highest both in bovine colostrum and milk; but all of them made lower number in the composition of milk (nissen et al. 2017). a study on the effects of heat treatment on bovine colostrum protein profile demonstrated that low abundant proteins, involved in cellular processes and immune response, are affected by heat (tacoma et al. 2017). besides, higher number of low abundant proteins was found to belong to metabolic processes, biological regulation, multicellular organismal processes and response to stimulus. recent advances in research allowing find low and very low abundant proteins from colostrum and milk. using so-called combinatorial peptide library technology (cpll) treatments made it possible to detect the signal of proteins masked by major proteins that constitute >95 % of total bovine colostrum protein mass (altomarea et al. 2016). another tandem with lc-ms/ms in this approach used isobaric tag for relative and absolute quantification (itraq) (yang et al. 2017). thus, the method allowed to compare differentially expressed proteins in whey of human and bovine colostrum and milk. in this work, we identified the low-abundant proteins in bovine colostrum after enrichment and by eluting with water-alcohol solution. the enrichment process was carried by trapping the proteins in polytetrafluoroethylene sorbent that was further eluted with water-alcohol solution. the idea came from the isolation of the ones of more hydrophobic nature. the proteins of hydrophobic interaction could have higher membrane positioning and thus cross the membrane more easily (lomize et al. 2017). sequences of the isolated proteins and peptides were established by mass-spectrometric analysis. further analgesic activity of the fraction was studied in combination with amaranth oil and hyaluronic acid; optimum mass ratio of the ingredients were established. in our previous work, we demonstrated high hyperlipidemic efficiency of amaranth oil that could be resulted from high concentration of unsaturated fatty acids and squalene (bozorov et al. 2018). oil samples obtained from local amaranth varieties (olimjonov et al. 2020) can contribute to economic competitiveness. skin surface lipids contain up to 13 % squalene (passi et al. 2002) that can contribute to higher interaction with squalene that ease the penetration of active compounds. experimental separation of proteins from bovine colostrum bovine colostrum samples obtained from cattle (bos taurus) on the 1st, 2nd, and 3rd days of the birth were gathered and the mixture was further used for analysis. to precipitate high-molecular-weight proteins, 60 ml of 54 % (w/v) perchloric acid (hclo4) solution was added to 945 ml of colostrum and kept in the refrigerator for 24 h capped. the precipitate was centrifuged and supernatant was collected, the volume was 600 ml. the excess amount of hclo4 in the obtained supernatant was neutralized with potassium alkali until ph reached 7.5 and kept in refrigerator for 10 h. the resulted mixture was centrifuged to remove excess of kclo4. supernatant volume compiled was 550 ml. it was left in the refrigerator overnight and used for column chromatography. nova biotechnol chim (2022) 21(1): e1246 3 column chromatography hydrophobic chromatography with a sorbent polytetrafluoroethylene (polychrome-1) filled in a 400 ml column connected to lkb bromma pump chromatography system was used to separate the fractions in a 550 ml mixture and desalinate the solution. for that, the obtained solution was first passed through a column. the column was washed out with water; the elution of the trapped proteins from the sorbent was carried out using an aqueous solution of 60 % ethyl alcohol (120 ml solution was used once with a flow rate 60 ml.h-1). the eluents were collected and the excess alcohol was removed using a rotory evaporator (re 2000a). further, the solutions were gathered and lyophilized (the virtis automatic freeze-dryer, 10-010). mass spectroscopy analysis of low-abundant fraction of proteins for mass-spectral analysis, 2 – 5 µl of digested protein samples were subjected to chip (150 µm × 43 mm) zorbax sb c18 column in agilent technologies 1260 cap pump with a flow rate of 4 µl per min, elution rate made 0.6 µl per min. b solution was managed as following: 5 %, 3 min; 80 %, 25 – 30 min. the solution was degassed in agilent technologies 1260 µ-degasser. mass detection was performed in chip-q-tof lc-ms agilent technologies 6520в series mass spectrometer. mass data was recorded in positive ionization mode (ionization source – chip interface, gas flow rate – 4 l.min-1 at 350 oc, skimmer current power – 65 v, ms/ms – 50 – 2400 m/z, mobile phase: a – 0.1 % formic acid, b – acetonitrile + 0.1 % formic acid) and partial sequences were identified with spectrum mill database. for functional annotations, obtained fragments were further searched by blast analysis in the ncbi database (https://blast.ncbi.nlm.nih.gov/blast.cgi): taxid: 9903 (belonging to bos taurus) identity was chosen as organism. for functional annotations and reliability, ncbi search results of the identified peptides with percentage identity higher than 85 % were checked with higher identities in the proteome of other mammals. establishment of amaranth oil composition the chemical composition of amaranth oil was established as described in our previous work (bozorov et al. 2019). the seeds of helios variety were ground in a porcelain mortar using quartz sand. the oil was extracted from the resulting powder with acetone by stirring for 30 min. the squalene content in the oil sample was 5.7 %. fabrication of the cream the basic components of the cream included 5 g of t-1 emulsifier and 0.2 g of sorbic acid as antibacterial means in a total mass of 100 g cream. in order to establish optimum ratio of putative biologically active ingredients, we suggested 10 compositions using various ratios of bovine colostrum proteins, amaranth oil (lacatusu et al. 2018) and hyaluronic acid (juncan et al. 2021) (table 1). the composition variants were added to the cream basis respectively, and filled up with water to a final mass of 100 g and further emulsified using a mixer. the obtained cream was of a dairy colour that is stable for more than a year when stored at 4 oc. analgesic activity the efficiencies of the compositions were determined by the analgesic activity during contactthermal irritation in the hot plate test following a commonly used method as described by deuis et al. (2017). the thermal irritation model reveals a central component in the mechanism of the analgesic action of a substance. the analgesic activity was established by the change in the threshold of pain sensitivity in animals during contact-thermal stimulation under the influence of the cream. the initial reaction of the white outbred mice (the time to start licking the hind limbs) was determined when they were placed on a standard plate with a temperature of 55 °c. ethical norms of evaluating pain behaviors, described by deuis et al. (2017), were followed when analgesic activity of cream samples was determined. then the rate of the same reaction was taken into account after certain time of applying the cream compositions to the animals on the hind and fore paws (15, 30 and https://blast.ncbi.nlm.nih.gov/blast.cgi nova biotechnol chim (2022) 21(1): e1246 2 45 min before the study), and its measurements were expressed as a percentage relative to the initial value. animal experiments were carried out according to requirements used for scientific purposes (european directive 2010/63/eu). table 1. establishment of optimum ratio of ingredients to fabricate analgesic means. compositions amaranth oil [g] bovine colostrum proteins [mg] hyaluronic acid [g] 1 5 0 0 2 0 10 0 3 0 0 2 4 6 8 1 5 5 10 2 6 4 7 3 7 3 10 1 8 2 10 2 9 5 8 3 10 1 9 4 samples that revealed highest analgesic activity are indicated in bold. general and acute toxicity the study of the acute toxicity and general action of the investigated cream was carried out on white outbred mice weighing 20 ± 1.5 g. five mice were included in each group. the tested substance was orally administered at doses up to 5,000 mg.kg-1; cream samples were dermally used at doses up to 2500 mg.kg-1. the observation was carried out 3 times a day for 2 – 3 days in a laboratory condition and further for 10 days in a vivarium. results proteins were isolated from bovine colostrum as above described. obtained fraction of the wateralcohol-soluble fraction of low-abundant proteins made by dry mass approximately a thousandth of the colostrum dry mass. proteins, highly abundant in colostrum such as casein, immunoglobulins, and lactoglobulins, are mainly transport proteins and/or ones involved in immune processes (nissen et al. 2017). our hypothesis originated from isolating the ones that interact with hydrophobic sorbent polytetrafluoroethylene – polychrome (despite fluorine is electronegative, the polymerized sorbent is of hydrophobic nature). in total, ~1.4 g of protein fraction of low abundant ones were obtained and subjected to sequence analysis. in table 2, were provided the sequence of the identified proteins, ncbi annotation as well as accession number, query cover, and percentage identity. query cover only higher than 90 % were selected. our results by analgesic activity showed the initial reaction of mice in the control group occurred after 9.3 ± 0.7 seconds. some of the cream samples that did not contain either amaranth oil alone or amaranth oil and bovine colostrum fractions (samples 2 and 3) revealed lowest effect that could be attributed to their presence. they enhanced analgesic activity in 45 min by 175.3 and 207.5 %, respectively. the effect of hyaluronic acid in pain relief can be noticed in samples 6 and 10 that contain 3 and 4 g of hyaluronic acid, respectively. samples 7, 8, and 10 turned out to be moderately active despite the highest quantity of protein fraction included. when these samples were applied, analgesic activity in 45 min increased by 296.8 % (36.9 ± 3.6 s), 267.7 % (34.2 ± 3.2 s) and 284.9 % (35.8 ± 4.3 s), respectively, compared to the initial latent period. the most active ones were samples 5 and 9, the analgesic activity of which enhanced almost 3.84 % (45.0 ± 3.8 s) and 3.6 times (42.6 ± 4.1 s), respectively (table 3). the observed time lag in pain relief can be concluded with highest quantity of amaranth oil, bovine colostrum protein fraction, and hyaluronic acid. based on the obtained results of the studied samples, the most optimal choice in terms of the ratio of components was sample 5 that contained 5 g of amaranth oil, 10 mg of bovine colostrum protein fraction and 2 g of hyaluronic acid (table 1). in relation to the initial indicators, this composition increased the analgesic activity by 131.2 %, 230.1 % and 383.9 % after 15, 30, 45 min of topical application, respectively (table 3). based on the data obtained, we developed cosmetic cream that was named "zumara". the cream consists of t1 emulsifier, hyaluronic acid, bovine colostrum proteins, amaranth oil, ethyl alcohol, sorbic acid and purified water. the highest biological activity among samples belonged to samples 5 and 9 that could be attributed to higher content of bovine colostrum protein fraction, amaranth oil that contains 4 nova biotechnol chim (2022) 21(1): e1246 3 table 2. identified sequences of low-abundant proteins in bovine colostrum and their accession numbers, query covers and percentage identities in ncbi database. sequences identified by mass analysis accession number query cover per. identity proteins name/ncbi annotation 1. rlvrfypradrvmsvclrvelygclwkaglxstqtg xp_019841431.1 100 % 100 % discoidin domain receptor family, member 1 2. vllgwgsllimlknegfyssmcpaenstnstqdeqrr xp_027418094.1 91 % 85.29 % neutral amino acids transporter small subunit 3 3. nisyggcmaqmfflswsvaaevllftamaydryva xp_027385372.1 100 % 77.14 % olfactory receptor 13a1-like 4. aiyhcreqpasdwpeavclligrqdlskqa xp_005891645.1 100 % 100 % anaphase-promoting complex subunit 1 isoform x1 5. vlsvelpgllaqlarsfalllpvyalgylglsfswvllalallaw xp_027394252.1 97 % 88.64 % extended synaptotagmin-2 6. siggtpirgalqi xp_027405056.1 100 % 100 % tyrosine phosphatase, receptor type, δ isoform 1 precursor 7. siphlllpla np_001192519.1 90 % 87.50 % integrin alpha-10 8. qllsqwsahamevyswklvhptd elr61599.1 100 % 95.95 % cytoplasmic fmr-1 interacting protein 9. vlvvasfdelqrraseargkiivynqp elr52717.1 100 % 77.78 % plasma glutamate carboxypeptidase 10. qlekswsqylacpedisgllhs xp_005892933.1 100 % 95.45 % huntingtin interacting protein 1 11. ssgpyltsvmgkaageref abg67017.1 94 % 77.78 % transcobalamin ii precursor 12. gllcvcwspdgkyivtggeddlvtv xp_024837551.1 100 % 96 % wd repeat containing protein 20 13. pketpflvsfiiaqivttcsgilsypf aic38345.1 100 % 92.59 % adp/atp translocase 4 14. gepgktgppglpgaggsgaistatyttvprvafyaglknph elr50847.1 100 % 100 % crf, c1q-related factor 15. npvacelkafv daa15478.1 90 % 80 % dna-directed rna polymerase iii 16. sfqtgswlldhcqesyceptvcq np_001074209.1 100 % 86.96 % keratin associated protein 11-1 17. lyrwqgifvpfedlsie xp_005907599.1 100 % 100 % very large g protein-coupled receptor 18. slpppplqp xp_027384342.1 100 % 100 % the peroxisome proliferator-activated receptor γ coactivator-1 5 https://www.ncbi.nlm.nih.gov/protein/xp_019841431.1?report=genbank&log$=prottop&blast_rank=1&rid=nbnvkgtz016 https://www.ncbi.nlm.nih.gov/protein/xp_027418094.1?report=genbank&log$=prottop&blast_rank=1&rid=nes9vpm3014 https://www.ncbi.nlm.nih.gov/protein/xp_027385372.1?report=genbank&log$=prottop&blast_rank=1&rid=nm3gv1bn014 https://www.ncbi.nlm.nih.gov/protein/xp_005891645.1?report=genbank&log$=prottop&blast_rank=1&rid=net27gzv014 https://www.ncbi.nlm.nih.gov/protein/xp_027394252.1?report=genbank&log$=prottop&blast_rank=1&rid=net63xyt014 https://www.ncbi.nlm.nih.gov/protein/xp_027405056.1?report=genbank&log$=prottop&blast_rank=2&rid=netatm43014 https://www.ncbi.nlm.nih.gov/protein/np_001192519.1?report=genbank&log$=prottop&blast_rank=3&rid=netsud3a014 https://www.ncbi.nlm.nih.gov/protein/elr61599.1?report=genbank&log$=prottop&blast_rank=4&rid=nkyjywhf016 https://www.ncbi.nlm.nih.gov/protein/elr52717.1?report=genbank&log$=prottop&blast_rank=1&rid=neuftm8f01r https://www.ncbi.nlm.nih.gov/protein/xp_005892933.1?report=genbank&log$=prottop&blast_rank=2&rid=neummzs101r https://www.ncbi.nlm.nih.gov/protein/abg67017.1?report=genbank&log$=prottop&blast_rank=2&rid=nhstf1sc016 https://www.ncbi.nlm.nih.gov/protein/xp_024837551.1?report=genbank&log$=prottop&blast_rank=2&rid=nevarxdd014 https://www.ncbi.nlm.nih.gov/protein/aic38345.1?report=genbank&log$=prottop&blast_rank=3&rid=nevfvbbj016 https://www.ncbi.nlm.nih.gov/protein/elr50847.1?report=genbank&log$=prottop&blast_rank=1&rid=new1hfgb016 https://www.ncbi.nlm.nih.gov/protein/daa15478.1?report=genbank&log$=prottop&blast_rank=1&rid=nex9ncnc016 https://www.ncbi.nlm.nih.gov/protein/np_001074209.1?report=genbank&log$=prottop&blast_rank=3&rid=ney2yc5z016 https://www.ncbi.nlm.nih.gov/protein/xp_005907599.1?report=genbank&log$=prottop&blast_rank=3&rid=neycvsnd016 https://www.ncbi.nlm.nih.gov/protein/xp_027384342.1?report=genbank&log$=prottop&blast_rank=1&rid=neytt5v9014 nova biotechnol chim (2022) 21(1): e1246 2 table 2. identified sequences of low-abundant proteins in bovine colostrum and their accession numbers, query covers and percentage identities in ncbi database – continued. sequences identified by mass analysis accession number query cover per. identity proteins name/ncbi annotation 19. mlenysnlvflglavskpqlvtfleqr elr60893.1 96 % 80.77% zink finger protein znf720 20. iqvtdddineiiqidgtgdnssaeeg xp_027411025.1 100 % 72 % transcription factor iia α/β 21. tssihskeifhslt xp_027422939.1 100 % 92.7% dna polymerase epsilon (ε) catalytic subunit a 22. iqgayyprrgsseiafhtipliqr xp_027411356.1 96 % 86.4 % retinol saturase 23. efrrrdqfpltrgraiqecrspvpppa xp_027369964.1 96 % 95.8 % striated muscle preferentially expressed protein kinase (speg) 24. qgveyakavplgtpiqs np_991380.2 100 % 94.45 % γ-protocadherin-c3 isoform 25. tillgpmstlvhtdqistpetp np_991380.2 100 % 95.45 % hepatocyte nuclear factor 4 γ 26. misqlvleqfllighckd xp_024835263.1 94 % 64.7 % zinc finger and scan domain containing protein 4d 27. qkleqqlkvvprfqpisehqt xp_024846738.1 100 % 95.24 % a kinase anchor protein 9 28. dstfaniskddsdliystygedpdlpsdfsih xp_005218672.1 100 % 100 % bromodomain containing protein 7 29. hiviyssieekttlkdknalhlfsingkylgsqi xp_027420629.1 100 % 85.3 % neurobeachin-like protein 1 30. prgpkghmgdsvigqkger np_001160001.2 100 % 84.21 % collagen 4 alpha 3 31. vhgeplgygv xp_027413406.1 100 % 80 % serine/threonine-protein kinase lats2 32. nlldlllnhqvlvpgcldpfpllsayv daa13671.1 100 % 100 % glutathione s-transferase p 33. siqsqssltitvsstp np_776434.1 93 % 73.33 % hematopoietic progenitor cell antigen cd34 34. apnvqsrelnyd np_001179782.1 100 % 83.33 % parathyroid hormone b1 35. ghrntvlltwkppd xp_027370093.1 100 % 100 % obscurin-like 1 36. sdkihfps e1bpq3.1 100 % 87.5 % g-protein coupled receptor family c gr. 6 member a 37. svnsevlgatrvkrhknllaerweahiya xp_005209316.1 96 % 75 % mitotic interactor and substrate of plk1 6 https://www.ncbi.nlm.nih.gov/protein/elr60893.1?report=genbank&log$=prottop&blast_rank=1&rid=neyueea2014 https://www.ncbi.nlm.nih.gov/protein/xp_027411025.1?report=genbank&log$=prottop&blast_rank=1&rid=nm2u02vz014 https://www.ncbi.nlm.nih.gov/protein/xp_027422939.1?report=genbank&log$=prottop&blast_rank=2&rid=nez4s03n016 https://www.ncbi.nlm.nih.gov/protein/xp_027411356.1?report=genbank&log$=prottop&blast_rank=3&rid=nezabedj016 https://www.ncbi.nlm.nih.gov/protein/xp_027369964.1?report=genbank&log$=prottop&blast_rank=1&rid=nezhayer014 https://www.ncbi.nlm.nih.gov/protein/np_991380.2?report=genbank&log$=prottop&blast_rank=1&rid=nezs3bh2016 https://www.researchgate.net/publication/306270257_the_g-protocadherin-c3_isoform_inhibits_canonical_wnt_signalling_by_binding_to_and_stabilizing_axin1_at_the_membrane https://www.ncbi.nlm.nih.gov/protein/np_991380.2?report=genbank&log$=prottop&blast_rank=1&rid=nm3ve0tz014 https://www.ncbi.nlm.nih.gov/protein/xp_024835263.1?report=genbank&log$=prottop&blast_rank=3&rid=nf012vj5014 https://www.ncbi.nlm.nih.gov/protein/xp_024846738.1?report=genbank&log$=prottop&blast_rank=3&rid=nf01wswa016 https://www.ncbi.nlm.nih.gov/protein/xp_005218672.1?report=genbank&log$=prottop&blast_rank=3&rid=nf063a2k016 https://www.ncbi.nlm.nih.gov/protein/xp_027420629.1?report=genbank&log$=prottop&blast_rank=2&rid=nf0bmu5y016 https://www.ncbi.nlm.nih.gov/protein/np_001160001.2?report=genbank&log$=prottop&blast_rank=2&rid=nf0f024b016 https://www.ncbi.nlm.nih.gov/protein/xp_027413406.1?report=genbank&log$=prottop&blast_rank=1&rid=nf0jtnu3016 https://www.ncbi.nlm.nih.gov/protein/daa13671.1?report=genbank&log$=prottop&blast_rank=3&rid=nf0kac5c016 https://www.ncbi.nlm.nih.gov/protein/np_776434.1?report=genbank&log$=prottop&blast_rank=2&rid=nf0rhtp3014 https://www.ncbi.nlm.nih.gov/protein/np_001179782.1?report=genbank&log$=prottop&blast_rank=2&rid=nhrzzrwg014 https://www.ncbi.nlm.nih.gov/protein/xp_027370093.1?report=genbank&log$=prottop&blast_rank=1&rid=nhs6d0fr016 https://www.ncbi.nlm.nih.gov/protein/e1bpq3.1?report=genbank&log$=prottop&blast_rank=1&rid=nhs5tw7u016 https://www.ncbi.nlm.nih.gov/protein/xp_005209316.1?report=genbank&log$=prottop&blast_rank=1&rid=nhsd5y33016 nova biotechnol chim (2022) 21(1): e1246 3 table 3. effects of the fabricated creams on the latency period and analgesic activity in the thermal nociceptive hot plate test (m  m; n = 6). fabricated cream compositions time with the moment of cream application [min] 15 30 45 latent period (seconds) analgesic activity (percentage increased by) latent period (seconds) analgesic activity (percentage increased by) latent period (seconds) analgesic activity (percentage increased by) control (initial) 9.3 ± 0.7 9.3 ± 0.7 9.3 ± 0.7 1 18.2 ± 1.8 95.7 20.0 ± 2.0 115.1 22.5 ± 3.4 141.9 2 10.5 ± 2 12.9 12.2 ± 0.7 31.2 25.6 ± 2.8 175.3 3 15.3 ± 1.5 64.5 17.5 ± 1.8 88.2 28.6 ± 3.2 207.5 4 20.3 ± 1.5 118.3 25.6 ± 1.5 175.3 40.2 ± 3.5 332.3 5 21.5 ± 1.8 131.2 30.7 ± 2.2 230.1 45.0 ± 3.8 383.9 6 20.3 ± 2.0 118.3 25.7 ± 0.7 176.3 38.7 ± 2.8 316.1 7 19.6 ± 1.8 110.8 24.5 ± 2.0 163.4 36.9 ± 3.6 296.8 8 18.4 ± 1.5 97.8 23.6 ± 1.5 153.8 34.2 ± 3.2 267.7 9 22.5 ± 1.8 141.9 31.2 ± 2.2 235.5 42.6 ± 4.1 358.1 10 19.6 ± 2.0 110.8 24.6 ± 0.7 164.5 35.8 ± 4.3 284.9 р < 0.01 – reliability in relation to the mean value of initial control. samples revealing highest activity and their effects, respectively, are shown in bold letters. ± bars indicate standard deviation value of a data set. squalene up to 5.7 % in the composition and hyaluronic acid. further analysis will prove our hypothesis. discussion previous researchers demonstrated different mechanisms of analgesic activities of peptides. dooley et al. (1994) reported rfwink peptide that do not resemble to any known opioid peptide. reported six amino acid-long peptide was demonstrated to induce long-lasting analgesia in mice. the peptide was suggested to cross blood brain barrier. in another work, gycaekgircddihcctglkckcnasgyncv crkk peptide, isolated from alopecosa marikovskyi spider venom, was found to possess analgesic activity by influencing purinergic p2x3 receptors. the maximum bioactivity of the peptide, studied by thermal hypersensitivity test, was 0.5 mg.kg-1when administered intravenously (palikova et al. 2019). zrccnggcssrwcrdhsrcc peptide (siiia) and similar structures are expected to be potent blocking agents of ttx-r and ttx-s sodium channels (bulaj et al. 2005; green et al. 2007). μ-conotoxins were established to block voltagegated sodium channels (vgsc) and more than twenty sequences belonging to conotoxins were already identified that interact with vgsc subtypes (green et al. 2014). another mechanism of analgesic effect of peptides was shown to be connected to a linkage with clathrin heavy chain. synthetic peptide, obtained by modifying salmon calcitonin sct16-21 fragment retained the activity of a full molecule (kotin et al. 2019). some peptides, identified in this work, were reported to be associated with analgesic mechanisms. very large g-protein coupled receptor 1 (vlgr1) is one of these peptides included in these analgesic processes. the large ectodomain of vlgrl contains calcium exchanger repeats that possess resemblance to sodium-calcium exchanger proteins. very large g protein-coupled receptor 1 (vlgr1), having a large ectodomain, contains multiple calcium exchanger repeats resembling regulatory domains of sodium-calcium exchanger proteins. (mcmillan et al. 2002). g proteincoupled receptors mediate (gpcr) human sense of vision, smell, taste and pain, and are involved in 7 nova biotechnol chim (2022) 21(1): e1246 2 cell recognition processes. they structurally are classified as gpcr possessing short n-terminal ectodomain (50 – 80 residues) and long ectodomain (80 – 600 residues). the long n-terminus can be involved in ligand recognition; the bound ligand can possibly move to the transmembrane region to activate g protein (vaidehi et al. 2002). vlgr1 is a core component for the development of ear inner cells. mutations in vlgr1 genes were defined to cause usher syndrome with symptoms congenital hearing loss and progressive retinitis pigmentosa (hu et al. 2014). we suggested synaptotagmin-2 (syt-2) protein as the next one involved in analgesic processes. syt-2 was reported to be involved in neuronal processes (bouhours et al. 2017). extended synaptotagminlike proteins, are a family of proteins that are involved in ca2+-regulated secretion and characterized by an n-terminal transmembrane sequence and two c-terminal c2 domains (c2a and c2b) (rizo and rosenmund 2008). e-syts consist of a short, nonconserved n-terminal transmembrane region and c2 domains. their c2 domains generally act as ca2+and phospholipidbinding domains and/or as protein–protein interaction domain (min et al. 2007). the e-syt2 c2a domain binds up to four ca2+ ions, whereas the c2b domain does not bind ca2+ (xu et al. 2014). other proteins that could be involved in analgesic activity among the ones, identified in this work, are receptor protein tyrosine phosphatase (rptp) delta isoform, corticotropin releasing factor, and γprotocadherin c3. since analgesic effects of these proteins were not conducted separately, our suggestions are speculative only. however, obtained fraction of water-alcohol soluble proteins, possibly of more hydrophobic nature, has been demonstrated as proper natural resources that can be obtained in preparative amounts. further researches will clarify deeper fundamental basis of the work. amaranth oil is another factor contributing to the efficiency of the cream. beneficial effects of squalene in the composition of creams and other means of cosmetic dermatology provide advantages to amaranth oil over other sources (huang et al. 2009). up to 13 % concentration among the components of the skin surface lipids (passi et al. 2002) causes higher interaction of the cream composition with a high ratio of squalene that contributes to the penetration of active compounds. the study of the general and acute toxicity of the substances and the cosmetic cream showed that they belong to practically harmless substances. ld50 level of the product reached more than 25,000 mg.kg-1 with cutaneous and oral administration in mice and rats. the study of the specific toxicology of the substance and the cream showed that they do not have a local irritating effect on the skin of rats and the conjunctiva of the eyes of rabbits and do not have an allergenic effect. the study of the chronic toxicity of the substance and the developed cream showed that the cream revealed prolonged action and did not lead to any changes in the biochemical parameters of the peripheral blood and internal organs of the experimental animals (results are not shown). the study of specific activity showed that the cream smoothes the skin by retaining moisture resulted from hyaluronic acid (sundaram et al. 2018; lubart et al. 2019). hyaluronic acid, another significant component in the composition of the product, is found in many connective tissues (gupta et al. 2019; chang et al. 2021). it is mostly used moisturizing agent used in cosmetology. hyaluronic acid is responsible for the regeneration process of the skin: it helps the synthesis of collagen (silva et al. 2017) and elastin (joddar and ramamurthi 2006), thus contributing to their correct positioning. thanks to this, the turgor and elasticity of the skin are improved. in addition, the unique ability of hyaluronic acid to retain water provides stability to the product. in the upper layers of the skin, it works as a conductor of nutrients and facilitates their diffusion (dovedytis et al. 2020). conclusion in this work, we identified 37 low abundant proteins in bovine colostrum that are soluble in 60 % ethanol. the identified peptides contribute to the extension of proteomic data of bovine colostrum. the used method can serve to identify lowabundant proteins from the colostrum and milk of other mammals. the sum of these peptides was found likely to possess analgesic effects when used as topical cream. we hypothesized the observed 8 nova biotechnol chim (2022) 21(1): e1246 3 analgesic activity might be attributed to at least two proteins: vlgr1 and synaptotagmin-2. amaranth oil containing high amount of squalene was concluded as efficient additive that likely contributes to biological efficiency. acknowledgement the work was supported with 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itraq-coupled lc-ms/ms. int. j. food sci. nutr. 6: 971-681. zhang l, boeren s, hageman ja, van hooijdonk t, vervoort j, hettinga k (2015) bovine milk proteome in the first 9 days: protein interactions in maturation of the immune and digestive system of the newborn. plos one 10: e0116710. zhang l, wang j, yang y, bu d, li s, zhou l (2011) comparative proteomic analysis of changes in the bovine whey proteome during the transition from colostrum to milk. asian-aust. j. anim. sci. 2: 272-278. 10 microsoft word ivanova et al 2010-1.doc nova biotechnologica 10-1 (2010) 45 stability of immobilized biosorbents and its influence on biosorption of copper dana ivánová1, hedviga horváthová2, jana kaduková2, jana kavuličová1 1technical university of košice, faculty of metallurgy, department of chemistry, letná 9, košice, sk-040 13, slovak republic (dana.ivanova@tuke.sk) 2technical university of košice, faculty of metallurgy, department of non-ferrous metals and waste treatment, letná 9, košice, sk-040 13, slovak republic (hedviga.horvathova@tuke.sk) abstract: biomass immobilization in a polymeric matrix may improve biosorption capacity and facilitate the separation of biomass from metal-bearing solutions. many polymers are studied as immobilizing agents for biosorption including biopolymers such as sodium alginate. in the article swelling behaviour of gel and dry beads has been studied in aqueous solutions with different acid-base character. swelling of gel or dry calcium alginate beads was found in all acidic and basic solutions except of the gel beads in strong acidic solutions, which exhibited the tendency to shrink. dry beads in diluted acidic solutions had the greatest stability because they exhibited minimum swelling. dry and gel beads were completely dissolved in concentrated solutions of sodium and potassium hydroxides. the potential use of immobilized algal biomass in ca-alginate beads for removal of copper ions from aqueous solution was also investigated. the results of the kinetic studies showed that the sorption of copper ions on gel immobilized beads are the most suitable. key words: calcium alginate beads, ph, stability, dissolution, swelling, biosorption, chlorella kessleri 1. introduction heavy metal pollution is one of the most important environmental problems today. one of the processes used for heavy metal removal from waste water and even their recovery can be biosorption that utilizes various natural materials of biologic origin (volesky, 2003; kaduková et al., 2008; wang and chen, 2009). biosorption can be defined as the passive sequestering of metal ions by metabolically inactive biomass via various physicochemical mechanisms. metal uptake may take place by different metal-binding mechanisms such as physical adsorption, chemisorption, ion exchange, microprecipitation, complexation, coordination, chelation (volesky, 2003; kaduková and štofko, 2006; wang and chen, 2009). for industrial application of biosorption, it is important to utilize an appropriate immobilization technique to prepare commercial biosorbents. disadvantage of the free microbial cells used in laboratory conditions is that they are basically small particles, with low density, poor mechanical strength and little rigidity. in real application they may come up with the solid-liquid separation problems, possible biomass swelling, inability to regenerate/reuse and development of high pressure drop in the column mode. high pressures can cause disintegration of free biomass. the immobilization of the biomass in solid structures would create a biosorbent material with the right size, mechanical strength, rigidity and porosity 46 ivánová, d . et al. necessary for use in practical processes. various methods are available for biomass immobilization. these include entrapment in polymers, adsorption, cross-linking and covalent linkage (volesky, 1990). the polymeric matrix determines the mechanical strength and chemical resistance of the final biosorbent particle to be utilized for successive sorption-desorption cycles (wang and chen, 2009). important immobilization matrices used in biosorbent immobilization include sodium or calcium alginate. alginate is a linear polysaccharide isolated from many strains of marine brown algae. alginates constitute a family of unbranched binary copolymers of 1-4 linked β-d-mannuronic acid (m) and α-l-guluronic acid (g) residues (vijaya et al., 2008; vreeker et al., 2008). the aim of this work was to study the stability of the different calcium alginate beads in acidobasic conditions with respect to application in biosorption and desorption experiments. the technical feasibility of using immobilized algal biomass for the removal of copper ions from aqueous solutions and the effect of beads preparation on kinetics of biosorption were investigated. 2. materials and methods 2.1 preparation of calcium alginate beads sodium alginate was dissolved in distilled water at a concentration of 3wt. %. after sodium alginate was completely dissolved, the solution was left undisturbly for 30 minutes to eliminate the air bubbles. the solution was then dropped from a height of 20 cm into gelling medium of 0.2m calcium chloride solution using a syringe with a needle. on the principle of simple ion exchange water soluble sodium alginate was converted to water insoluble and stable calcium alginate salt. the formed beads were cured in the gelling medium for 30 min. calcium alginate beads were divided to three groups: gel beads: fresh prepared calcium alginate beads were washed with distilled water and used for experiments. the average size of the bead was found to be 3.03 mm. dry beads a: prepared calcium alginate beads were rinsed with distilled water, dried and dipped in distilled water for 5 days. the average size of the bead was found to be 1.02 mm. dry beads b: prepared calcium alginate beads were rinsed with distilled water and dried, resulting in particles with a diameter of 0.89 mm. 2.2 study of the prepared beads stability the concentrated and diluted solutions of hydrochloric, nitric and sulphuric acids and sodium and potassium hydroxides were prepared. ph values were measured for each solution. approximately 8-16 beads from each fraction were immersed in the tubs with 10 ml of acidic and basic solutions and stored at laboratory temperature and changes in the form of beads were observed. nova biotechnologica 10-1 (2010) 47 during the whole experiment average diameter of beads were measured by using the micrometer screw gauge and these data were used for % volume change calculation according to the formula: 100. i if c v vv v − = (1) where cv volume change [%] fv final volume [mm 3] iv initial volume [mm 3] 2.3 preparation of immobilized algae in calcium alginate beads powder prepared from dried alga chlorella kessleri was mixed with 3% sodium alginate solution in the ration 1:9. immobilized beads were prepared with the same technique like calcium alginate beads (in section 2.1). prepared beads were consequently divided into three groups. a gel immobilized beads (stored in distilled water) b dry immobilized beads before using dipped in distilled water for 12 hours c dry immobilized beads 2.4 copper biosorption experiments immobilized algae were used for biosorption of cu2+ ions from solution with initial concentration 140 mg l-1. ph value of used solutions was 5.00. each fraction (a, b, c) of beads at concentration 2 g l-1 of beads were added into the solutions. these solutions were mixed during 24 hours. at selected time intervals, solution samples were withdrawn for metal analysis. the concentration of cu2+ ions was measured by atomic absorption spectroscopy (varian aa20+). the metal uptake q was calculated from the mass balance equation as follows: m ccv q e )( 0 −= (2) where q the quantity of metal uptake by biomass [mg g-1] c0 the initial metal concentration [mg l -1] ce final (after sorption at equilibrium) metal concentration [mg l -1] v the volume of solution [l] m dry weight of the biomass added [g] 3. results and discussion 3.1 calcium alginate beads stability obtained characteristics of the behaviour in acidic conditions are shown for gel beads (table 1) and dry beads (table 2-3). the changes of the gel beads and dry beads in the basic solutions are listed in table 4 6. 48 ivánová, d . et al. table 1. ph values of the acidic solutions, average diameter of the beads, their volume with % volume change before and at the end of experiment with gel beads. initial diameter and initial volume of beads were 3.03 mm and 14.57 mm3, respectively. ph of the solution hcl hno3 h2so4 hcl hno3 h2so4 initial 1.13 1.14 1.29 2.64 2.78 2.79 with gel beads 1.13 1.14 1.3 3.23 3.34 3.32 diameter of beads [mm] 2.82 2.38 2.25 3.6 3.5 3.9 volume [mm3] 11.74 7.06 5.96 24.43 22.45 31.06 volume change [%] -19.4 -51.5 -59.1 67.7 54.1 113.2 table 2. ph values of the acidic solutions, average diameter of the beads, their volume with % volume change before and at the end of experiment with dry beads a. initial diameter and initial volume of beads were 1.02 mm and 0.56 mm3, respectively. ph of the solution hcl hno3 h2so4 hcl hno3 h2so4 initial 1.13 1.14 1.29 2.64 2.78 2.79 with dry beads a 1.15 1.15 1.31 3.77 3.68 3.99 diameter of beads [mm] 1.30 1.23 1.30 1.07 1.07 1.03 volume [mm3] 1.15 0.97 1.15 0.64 0.64 0.57 volume change [%] 107 75.4 107 15.4 15.4 3 table 3. ph values of the acidic solutions, average diameter of the beads, their volume with % volume change before and at the end of experiment with dry beads b. initial diameter and initial volume of beads were 0.89 mm and 0.37 mm3, respectively. ph of the solution hcl hno3 h2so4 hcl hno3 h2so4 initial 1.13 1.14 1.29 2.64 2.78 2.79 with dry beads b 1.14 1.14 1.3 3.66 3.54 3.62 diameter of beads [mm] 1.23 1.3 1.34 1.17 1.05 1.04 volume [mm3] 0.97 1.15 1.26 0.84 0.61 0.59 deviation [%] 164.0 211.6 241.3 127.2 64.2 59. 6 table 4. ph values of the basic solutions, average diameter of the beads, their volume with % volume change before and at the end of experiment with gel beads. initial diameter and initial volume of beads were 3.03 mm and 14.57 mm3, respectively. ph of the solution koh naoh naoh koh initial 10.73 11.12 12.73 12.98 with gel beads 8.07 8.33 12.04 12.36 diameter of beads [mm] 3.6 4.1 dissolved by 3 days volume [mm3] 24.43 36.09 volume change [%] 67.7 147.8 from the presented results it is obvious that diameter and volume of the gel and dry beads of all groups in diluted acidic solutions of hcl, hno3, h2so4 and in concentrated and diluted acidic solutions of naoh, koh have increased in comparison with initial state and exhibited the tendency to swell. the dry beads b in nova biotechnologica 10-1 (2010) 49 concentrated solutions of the acids reached the highest swelling. from table 2 it is visible that the dry beads a in diluted acidic solutions with ph values 2.64-2.79 have showed out minimal volume changes from 3-15.4%. the dry beads for both groups were more swelled in concentrated acidic solutions than in diluted acidic solutions. in according to hoffman (2002) swelling of hydrogels is mainly attributed to the hydration of the hydrophilic groups of alginate. also in this study is assumed that diluted acidic solution penetrates inside the beads in order to fill the inert pores among the polymer chains. after obtaining of maximum swelling degree dry and gel beads began indicate dissolution or degradation. table 5. ph values of the basic solutions, average diameter of the beads, their volume with % volume change before and at the end of experiment with dry beads a. initial diameter and initial volume of beads were 1.02 mm and 0.56 mm3, respectively. ph of the solution koh naoh naoh koh initial 10.73 11.12 12.73 12.98 with dry beads a 8.02 8.43 12.24 11.5 diameter of beads [mm] 1.13 1.25 dissolved by 3 days volume [mm3] 0.76 1.02 volume change [%] 36 84.1 table 6. ph values of the basic solutions, average diameter of the beads, their volume with % volume change before and at the end of experiment with dry beads b. initial diameter and initial volume of beads were 0.89 mm and 0.37 mm3, respectively. ph of the solution koh naoh naoh koh initial 10.73 11.12 12.73 12.98 with dry beads b 7.96 8 12 11.53 diameter of beads [mm] 1.1 1.1 dissolved by 4 days volume [mm3] 0.70 0.70 deviation [%] 88.8 88.8 the changes of ph values were observed in the all solutions, excepting the concentrated acidic solutions. ph values in acidic solutions were higher and in alkaline solutions were lower after the swelling of calcium alginate beads. whether with gel or with dry beads, ph values in concentrated acidic solutions remained without changes. the gel and dry beads were dissolved by 3 days in concentrated solutions of sodium and potassium hydroxides. observed degradability of alginate beads is caused by the presence of high concentrations of non-gelling ions, such as na+ and k+ (bajpai and sharma, 2004). the swelling mechanism and subsequent degradation of the beads in presence of the solution of naoh/koh is related with the ca2+ and na+/ k+ exchange. the gel beads tended to shrink when exposed to the concentrated acidic solutions of hcl, hno3 and h2so4 (table 1). at low ph values the carboxylic groups of alginate are protonized and hence the electrostatic repulsion among these groups lessens and shrinkage is favoured (hoffman, 2002; pasparakis and bouropoulos, 2006). 50 ivánová, d . et al. 3.2 application of immobilized algae for the removal of cu2+ heavy metal ions from aqueous solutions the results obtained from kinetic studies on cu2+ sorption by immobilized algal beads of group a, b and c are shown in fig. 1. 0 5 10 15 20 25 30 35 40 45 0 120 240 360 480 600 720 840 960 1080 1200 1320 1440 time [min] s pe ci fic a ds or pt io n [m g g -1 ] group a group b group c fig. 1. specific adsorption of copper solutions by immobilized algal beads of groups a, b, c. it can be seen that biosorption capacity expressed as specific adsorption (q) has reached 33.8 mg g-1 of cu2+ ions (50%) in first hour during the experiment when gel beads a were used. when beads from group b and c were used specific adsorption capacity 35 mg g-1 of cu2+ ions from model solutions took 2 and 4 hours for beads from group b and c, respectively. group a and b reached equilibrium after 6 hours of biosorption. group c reached equilibrium within 8 hours. after 24 hours all group a, b and c removed 63% cu2+ ions from solutions and it corresponds with specific adsorption capacity 43 mg g-1 of cu2+ ions. from these results seems to be the fastest biosorption by gel beads from group a. on the other site dry beads from group b and c had higher mechanical stability. kinetics of biosorption of cu2+ ions by immobilized algae was compared with free powdered algae chlorella kessleri (horváthová et al., 2008). in the case of using free powdered algae equilibrium was reached within 10 minutes and the biosorption capacity was 46.6 mg g-1 of cu2+ ions. 4. conclusions this study shows that the stability of calcium alginate beads depends on ph values of the aqueous solutions and the initial physical state of the beads. behaviour of gel or dry beads is interesting because of the influence of individual metal ions in solutions. calcium alginate beads are sensitive to the solutions nova biotechnologica 10-1 (2010) 51 containing sodium and/or potassium ions. in these solutions they are swelled and subsequently dissolved by ion-exchange process taking place between na+/k+ ions in solution and ca2+ ions in the beads. their presence is the limiting factor for utilization of calcium alginate in metal biosorption. dry beads a treated with diluted acidic solutions exhibited minimum swelling and they are the most preferable in bioreactors because of their high mechanical stability. in contrast to the dry beads with the minimal swelling, the beads with tendency to increase are suitable when swelling and dissolution of the gels is required – an important factor in all applications where recovery of the cells is essential. this study proved the practical feasibility of using immobilized algal beads for the removal of copper from aqueous solution. from studied groups of immobilized algal beads are gel immobilized beads the most suitable because of the fastest copper removal from model solutions. acknowledgement: this work was supported by vega 1/0134/09. references bajpai, s.k., sharma, s.: investigation of swelling/degradation behaviour of alginate beads crosslinked with ca2+ and ba2+ ions. react. funct. polym., 59, 2004, 129-140. hoffman, a.s.: hydrogels for biomedical applications. adv. drug deliv. rev., 43, 2002, 3-12. horváthová h., kaduková j., mražíková a., slafkovská, g., štofko m.: effect of nickel on copper and zinc biosorption. in: acta metallurgica slovaca, 14, special issue, 1/2008, 5th. international conference (kammel’s quo vadis hydrometallurgy 5) košice, 19.-22.may, 2008, 78-82. kaduková, j., štofko, m.: environmentálne biotechnológie pre hutníkov, knkaso hf tu v kosiciach, košice, 2006, 141 pp. kaduková, j., horváthová, h., mražíková, a., štofko, m.: biosorption of cu, ni and zn from single metal solutions and their mixture by alga chlorella kessleri, e-proceedings from 4th european bioremediation conference, chania, greece, september 3-6, 2008, id188. pasparakis, g., bouropoulos, n.: swelling studies and in vitro reklease of verapamil from calcium alginate and calcium alginate-chitosan beads. int. j. pharm., 323, 2006, 34-42. vijaya, y., popuri, s.r., boddu, v.m., krishnaiah, a.: modified chitosan and calcium alginate biopolymer sorbents for removal of nickel (ii) through adsorption. carbohydr. polymer., 72, 2008, 261-271. volesky, b.: biosorption of heavy metals i. crc press, inc., boston, 1990, 381 pp. volesky, b.: sorption and biosorption, bv sorbex, inc., montreal, 2003, 316 pp. vreeker r., li l., fang y., appelqvist i., mendes e.: drying and rehydration of calcium alginate gels. food biophys., 3, 2008, 361-369. wang, j., chen, c.: biosorbents for heavy metals removal and their future. biotechnol. adv., 27, 2009, 195-226. microsoft word urickova et al nbc 12-2.doc nova biotechnologica et chimica 12-2 (2013) 83 doi 10.2478/nbec-2013-0010 © university of ss. cyril and methodius in trnava right-angle fluorescence spectroscopy for differentiation of distilled alcoholic beverages veronika uríčková, jana sádecká*, pavel májek institute of analytical chemistry, faculty of chemical and food technology, slovak university of technology, radlinského 9, sk-812 37 bratislava, slovak republic (jana.sadecka@stuba.sk) abstract: total luminescence and synchronous scanning fluorescence spectroscopic techniques were investigated for differentiating brandies from mixed wine spirits. the studies were performed on 16 brandies from 3 different producers and 30 mixed wine spirits from 5 different producers. differentiation between samples was accomplished by multivariate data analysis methods (principal component analysis, hierarchical cluster analysis, and linear discriminant analysis). correct classification was obtained using emission spectra (400–650 nm) recorded at excitation wavelength 390 nm, excitation spectra (225–460 nm) obtained at emission wavelength 470 nm and synchronous fluorescence spectra (200–700 nm) collected at wavelength interval 80 nm. these results indicate that right-angle fluorescence spectroscopy offers a promising approach for the authentication of brandies as neither sample preparation nor special qualification of the personnel are required, and data acquisition and analysis are relatively simple when compared to front-face technique. keywords: brandy, mixed wine spirit, fluorescence, chemometric, authentication 1. introduction brandy is a general term for distilled wine, usually 40–60% ethanol by volume. types of brandies, originally at least, tended to be location-specific. brandy has to be aged for a certain period in oak casks. toasting wood to be used in oak casks for aging brandy produces a great number of volatile and odoriferous substances. in addition, aging involves various processes producing significant changes in the composition of ageing spirit and being very important for the quality of the final products (taste, flavor and color) (mosedale and puech, 1998). mixed wine spirits are legally produced using wine distillates diluted with ethanol from other sources. they are frequently blended with sugar, brandy aroma and caramel. some mixed wine spirits contain honey or colorants. owing to the low price of this mixed wine spirit, it is sometimes used for a counterfeiting brandy. this usually occurs in restaurants and therefore affects the consumer and places honest traders at a financial disadvantage. for this reason, there is a need for a rapid method for drink authentication to reassure consumers, protect regional designations and ensure fair competition. several analytical methods have been published for classification of brandies. gas chromatography-mass spectrometry is a powerful tool in the analysis of volatile components of brandies (caldeira et al., 2004; watts et al., 2003). highperformance liquid chromatography has been widely used for the analysis of phenolic compounds and furanic derivatives of brandies. the direct injection allows classification of the brandies according to the botanical species of the wood barrel (canas et al., 2003). capillary zone electrophoresis has been applied successfully in the analysis of phenolic compounds. counterfeit brandy is easy to recognize by the bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:05 utc 84 uríčková, v. et al. absence of sinapaldehyde, syringaldehyde, and coniferaldehyde (panossian et al., 2001). analytical method used to verify the quality and authenticity of alcoholic beverages should to perform an analysis without sample pre-treatment. in addition, it should to accomplish a fast data acquisition and carry out the data treatment accurately with relatively low costs. the combination of chemometric and spectroscopic methods is a good way to reach these premises. the aim of this paper is to show that right-angle fluorescence spectroscopy and multivariate statistical methods (pca, hca, linear discriminant analysis (lda)) can be used for distinguishing between commercial samples of brandies and mixed wine spirits as an alternative method to front-face fluorescence technique (sádecká et al., 2009), exigent of special front surface accessory. 2. materials and methods 2.1. samples and chemicals the studies were performed on 16 brandies (b) from 3 different producers (b1, n=8; b2, n=4; b3, n=4) and 30 mixed wine spirits (d) from 5 different producers (d1, n=12; d2, n=10; d4, n=4; d5, n=2; d6, n=2). samples were purchased from the local supermarkets besides four brandies which were obtained directly from the manufacturers. brandy b1, a traditional slovak product from the small carpathian viticulture region, is made of the grape using a classic method of aging wine spirit in small 300 l oak barrels for a minimum five years. the wine spirit then goes to 20,000 l barrels for next 3 years. brandy b2 is made of the pure high quality foreign wine spirit matured by natural way in oak barrels. b3 is made of the wine spirit from the east slovak viticulture region matured by natural way in oak barrels. mixed wine spirits are produced using wine spirits diluted with ethanol from other sources. they are frequently blended with sugar, brandy aroma and caramel (e 150a). mixed wine spirits d1 contain honey and colorants (e 102, e 110, e 120, e 122, e 132 and e 151). samples were stored in the dark at room temperature until the day of analysis. the plain caramel (e 150a, color no. 525) was a commercial caramel produced by d.d.williamson (uk). the physicochemical characteristics of this product are: color intensity (absorbance of 0.1% w/v solution at 610 nm through a 1 cm square cell) 0.030−0.035, specific gravity (15.56°c) 1.340−1.360 kg l-1, baume (15.56°c) 36.8−38.4, ph, as is 3.0−4.0. a stock solution, 1.000 g l-1, of caramel product was prepared in ethanol:water (40:60, v/v). the stock solution of caramel was diluted with ethanol:water (40:60, v/v) in order to have system with absorbance values similar to those of mixed wine spirit. ethanol, acs spectrophotometric grade, 95.0%, from sigma-aldrich and water (milli-q system) were used. 2.2. fluorescence spectroscopy fluorescence spectra were recorded using a perkin-elmer ls 50 luminescence spectrometer equipped with a xenon lamp. excitation and emission slits were both set at 5 nm. scan speed was 200 nm/min. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:05 utc nova biotechnologica et chimica 12-2 (2013) 85 fluorescence excitation spectra were recorded between 200 and 500 nm (increment 0.5 nm), repeatedly, at emission wavelengths from 300 to 600 nm, spaced by 10 nm interval in the emission domain. fluorescence emission spectra were recorded from 250 to 700 nm (increment 0.5 nm), repeatedly, at excitation wavelengths from 200 to 500 nm, spaced by 10 nm interval in the excitation domain. synchronous fluorescence spectra were collected by simultaneously scanning the excitation and emission monochromator in the excitation wavelength range 200– 700 nm, with constant wavelength differences δλ between them. spectra were recorded for δλ interval from 10 to 100 nm, in steps of 5 nm. fluorescence intensities were plotted as a function of the excitation wavelength. the right-angle geometry was used for samples in 10 mm × 10 mm × 45 mm quartz cell. fluorescence measurements were done in triplicate for each sample. the spectrometer was connected to a computer supplied with fl data manager software (perkin-elmer) for spectral acquisition and data processing. contour maps of total luminescence and synchronous scan fluorescence spectra were plotted using windows-based software originpro 7.5 (originlab, usa, 2002). 2.3. uv-visible absorption spectroscopy absorption spectra were obtained with a spectronic 20 genesys spectrophotometer (thermo fisher scientific) using 10 mm square cuvette and 8 nm slit width. the measurements were made between 325 nm and 700 nm. 2.4. mathematical analysis of data to investigate the differences between fluorescence spectra of the samples pca and hca were applied. pca is an unsupervised (we have no prior knowledge of the groups to be expected) pattern recognition method that reduces the dimensionality of the original data matrix while retaining the maximum amount of variability as well as recognizing the data structure (geladi, 2003). hca is an unsupervised pattern recognition method detecting natural grouping in data. objects are grouped in clusters in terms of their similarity. we used hierarchical (agglomerative) cluster analysis, where similarity extent was measured by manhattan (city-block) distances and cluster aggregation was based on ward’s method. finally, a supervised pattern recognition method, lda, was used to classify samples according to their origin. lda method is an excellent tool to obtain vectors showing the maximal resolution among categories, maximal separation and compactness of the categories. microsoft excel 2000 and statistica software version 6.0 (statsoft, usa, 2001) were used for statistical analysis. 3. results and discussion 3.1. total luminescence spectra figure 1 shows total luminescence spectra of the brandy and mixed wine spirit as contour maps, constructed in such a way that x-axis represents the emission and y-axis bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:05 utc 86 uríčková, v. et al. the excitation wavelengths, while the contours are plotted by linking the points of equal fluorescence intensity. brandy total luminescence contour map spreads in the excitation wavelength range 380–500 nm, in contrast to mixed wine spirit that spreads in the excitation wavelength range 200–240 nm and 300–500 nm, respectively. the contours for brandy are concentrated in the emission wavelength region 510–570 nm and excitation wavelength region 430–480 nm, while the contours for mixed wine spirit are concentrated in the emission wavelength region 460–530 nm and the excitation wavelength region 380–420 nm. in general, spectral features and fluorescence intensity values of all brandies are typical of brandies of similar origin and nature. the fluorescence spectra of brandies b1 are characterized by the main fluorophores centered at an excitation/emission wavelength pair of 460/540 nm. the other brandies have the following excitation/emission maxima: b2 450/523 nm, b3 450/524 nm. however, the excitation/emission wavelength values of the major peaks of the brandies are generally longer than those usually measured for mixed wine spirits, e.g., d1 396/494 nm, d2 390/476 nm. as mentioned, the mixed wine spirits are frequently colored with caramel (e 150a) to imitate the effect of long aging in wooden casks. therefore we assumed that the major peak originates from this colorant. to support this assumption, the stock solution of caramel was diluted with ethanol:water (40:60, v/v) in order to have system with ethanol volume and absorbance values similar to those of mixed wine spirit, and total luminescence spectra of caramel were recorded. emission spectra recorded after excitation at 395 nm showed a maximum located around 494 nm (fig. 1c). the light observed at 450–550 nm under excitation at 200–240 nm is probably scatter originating from caramel colloidal aggregates. a comparison of fluorescence spectra, particularly of those recorded at excitation/emission maxima of caramel supports an earlier assumption. we should note, however, that exact position of maxima of caramel fluorescence vary from one mixed wine spirit to another, which may results from difference in the respective caramel composition and/or from the technological process used. as it is clearly shown in fig. 1 the shape and the fluorescence intensities are different between the two classes of beverages. it appears that total luminescence spectroscopy can be used to characterize brandy and mixed wine spirit samples using suitable wavelength regions. 300 400 500 600 700 200 250 300 350 400 450 500 e xc ita tio n w av el en gt h (n m ) emission wavelength (nm) a 300 400 500 600 700 200 250 300 350 400 450 500 e xc ita tio n w av el en gt h (n m ) emission wavelength (nm) b 300 400 500 600 700 200 250 300 350 400 450 500 e xc ita tio n w av el en gt h (n m ) emission wavelength (nm) c fig. 1. contour plots of total luminescence spectra of brandy (a), mixed wine spirit (b), and caramel (0.750 g l-1 in ethanol:water, 40:60, v/v) (c). contours join the points of equal fluorescence intensity. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:05 utc nova biotechnologica et chimica 12-2 (2013) 87 besides the fluorescence band, fig. 1 shows the presence of the first and the second order rayleigh scatter bands. the first order rayleigh scatter line is centered at the emission wavelength equals excitation wavelength, the second order rayleigh scatter at the emission equals twice the excitation. scattering is much more intense and/or heterogenous for mixed wine spirits than for brandies. this phenomenon may result from the higher heterogeneity of mixed wine spirit, e.g., presence of colloids, with respect to brandy. the light observed at 450–550 nm under excitation at 200– 240 nm is probably scatter, partially originated from caramel colloids in mixed wine spirit. hence, the differences between brandy and mixed wine spirit are also due to scatter bands. because these bands have no information about the fluorophores in the samples the wavelength range where they are located will be discarded from the subsequent data analysis. 3.2. total synchronous fluorescence spectra the contour plots of total synchronous fluorescence (tsf) spectra were obtained by plotting the fluorescence intensity (z-axis) as a function of excitation wavelength (x-axis) and wavelength interval δλ (y-axis). the tsf spectra of a brandy sample are given in fig. 2a. it shows that the tsf contour map spreads in the excitation wavelength 380–550 nm and δλ 10–100 nm. the contours are concentrated in the excitation wavelength region 440–480 nm and δλ 60–100 nm. the plot shows only one fluorescence maximum blue-shifted from 500 to 450 nm with increasing δλ. the maximum fluorescence intensity was recorded at excitation wavelength 460 nm (δλ = 80 nm), 450 nm (δλ = 75 nm) and 450 nm (δλ = 75 nm) for brandy b1, b2 and b3, respectively. the tsf spectra of a mixed wine spirit sample are given in fig. 2b. the contour map spreads in the excitation wavelength 320–550 nm and δλ 10–100 nm. two overlapping bands with maxima at 420 and 479 nm are apparent for δλ = 10 nm. for δλ = 30 nm, the fluorescence intensity of bands increased, changes in their relative intensities were noted, and maxima were blue-shifted to 407 and 460 nm, respectively. at increased δλ, the first band was shifted to 405 and 399 nm and the second one to 452 and 435 nm for δλ = 40 and 60 nm, respectively. the further increase of intensity and band broadening was apparent for δλ = 70 nm, resulting in only one band with maxima at 400 nm. the banding intensity increases at higher δλ values. the shape and intensity of the fluorescence maxima varied from one mixed wine spirit to another. for example, the maximum fluorescence intensity for sample d1 and d2 was observed at excitation wavelength 396 nm (δλ = 95 nm) and 391 nm (δλ = 85 nm), respectively. generally, the fluorescence maxima shift to shorter wavelengths with increasing δλ for both brandy and mixed wine spirit. brandies give a longer wavelength less intensive fluorescence band, while mixed wine spirits give a shorter high intensive band. the shape and intensity of the synchronous fluorescence spectra of caramel depend on the difference between excitation and emission wavelengths δλ (fig. 2c). for δλ = 10 nm, two bands with maxima at 420 and 478 nm are observed. at increased δλ, the first band was shifted to 407, 404 and 400 nm and the second one to 460, 453 bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:05 utc 88 uríčková, v. et al. and 435 nm for δλ 30, 40 and 60 nm, respectively. for δλ = 70 nm, only one band with maxima at 399 nm was recorded. comparison shows that the maxima observed for caramel at different δλ-values are consistent with the respective maxima in mixed wine spirits. 200 300 400 500 600 700 20 40 60 80 100 w av el en gt h in te rv al ( nm ) excitation wavelength (nm) a 200 300 400 500 600 700 20 40 60 80 100 w av el en gt h in te rv al ( nm ) excitation wavelength (nm) b 200 300 400 500 600 700 20 40 60 80 100 w av el en gt h in te rv al ( nm ) excitation wavelength (nm) c fig. 2. contour plots of total synchronous fluorescence spectra of brandy (a), mixed wine spirit (b), and caramel (0.750 g l-1 in ethanol:water, 40:60, v/v) (c). contours join the points of equal fluorescence intensity. 3.3. multivariate analysis of excitation and emission spectra the pca was carried out separately on the excitation and emission spectra to investigate differences between samples. the best classification was achieved using excitation spectra (225–460 nm) recorded at emission wavelength 470 nm or emission spectra (400-650 nm) recorded at excitation wavelength 390 nm. the fluorescence spectra showed different shapes. the width of excitation spectra was larger for mixed wine spirits than those for brandies. mixed wine spirits had higher fluorescence intensity regardless of wavelength but they were also more heterogeneous in this respect. excitation and emission spectra obtained for the mixed wine spirit at the excitation/emission wavelength pair 390/470 nm are similar to those of caramel. moreover, the absorption spectrum is in good agreement with that of caramel in the wavelength range 325−600 nm. the pca output indicates that the first pc (pc1) has the largest eigenvalue at 38.0 and accounts for 82.6% of the total variance in the collected data. the second pc (pc2) has next largest eigenvalue at 7.8 and accounts for 17.0% of the data variation. the remaining pcs account for 0.4% of the variation. according to the eigenvalue results displayed in the scree plot (eigenvalue vs number of eigenvalues), only the first two pcs were used for the purpose of pca illustration. the variances of the subsequent components are similar and correspond to experimental noise, scatter band residuals and baseline fluctuations. the general guideline in pca applications is to select those pcs which account, cumulatively, for at least 80% to 90% of the data variation. cumulatively, the first two pcs from the collected data account for 99.6% of the total variance indicating that two pcs appear sufficient to explain the structures in the data. the similarity map defined by the pc1 and pc2 of the pca performed on excitation spectra allowed a good discrimination of beverages (fig. 3a). spectral pattern associated with the pcs provide the characteristic wavelengths that may be used to discriminate between spectra. the spectral pattern associated with the pc1 bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:05 utc nova biotechnologica et chimica 12-2 (2013) 89 exhibited a positive peak around 280 nm and a broad positive peak between 350– 450 nm corresponding to caramel. the spectral pattern associated with the pc2 exhibited positive peaks at 250 and 300 nm (results are not presented). while a discrimination of the brandy and mixed wine spirit samples was achieved with excitation data collection, a different trend was observed with emission spectra. the pc1 has an eigenvalue at 40.2 and accounts for 87.4% of the total variance in the collected data. the pc2 has an eigenvalue at 5.7 and accounts for 12.4% of the data variation. cumulatively, the first two pcs from the collected data account for 99.8% of the total variance indicating that two pcs appear sufficient to explain the structures in the data. although the pca similarity map defined by the pc1 and pc2 did not lead to a clear discrimination of beverages, a general trend pointing out the brandies and mixed wine spirits was observed on the map (fig. 3b). brandies b1 constitute one subgroup, while brandies b2 and b3 constitute another subgroup. finally, there is a group of mixed wine spirits. 0.0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1.0 0.0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1.0 p c 2 pc1 a 0.4 0.5 0.6 0.7 0.8 0.9 1.0 0.4 0.5 0.6 0.7 0.8 0.9 1.0 p c 2 pc1 b b1 b2,b3 fig. 3. principal component analysis similarity map (score plot) determined by principal component 1 (pc1) and principal component 2 (pc2) for excitation fluorescence spectra recorded at emission wavelength 470 nm (a) and emission spectra recorded after excitation at 390 nm (b) on brandy (□) and mixed wine spirit (o) samples. in a second step, hca was carried out separately on the excitation and emission spectra in order to evaluate the number of subsets of similar samples appearing in the complete data set. for the sake of simplicity, a reduced number of samples were included in the figures, but from them we can clearly recognize the clustering common to all the samples. the evaluation of the above mentioned excitation spectral region provided two main clusters (fig. 4a). all mixed wine spirits are linked together in the first main cluster. this main cluster is heterogeneous enough but consists of various small groups of very similar products. for instance most of the mixed wine spirits from producer 1 (d1) is found as such in one subgroup with 97% of similarity among them. all brandies are linked together in the second main cluster. one subcluster is constituted of b1 (brandy from producer 2) with 98% of similarity. another subcluster is constituted of b2 and b3 with 95% of similarity among them and 90% in relation to b1. fig. 4b shows the results from hca concerning the emission spectra. the dendrogram shows that the brandies are well separated from the mixed wine spirits. the first main cluster contains mixed wine spirit samples, while the second one contains brandy samples. mixed wine spirits form three smaller groups. one small group is constituted of samples d2 with 98% of similarity among them and by sample bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:05 utc 90 uríčková, v. et al. d5 with 92% of similarity with the samples d2 of this group. another group is constituted of d2, d4 and d6 with 96% of similarity among them and 88% in relation to the group of d1. samples d1 show a similarity of 94% to each other. brandy samples form three small subclusters of the second main cluster corresponding to three different producers. one subcluster is constituted of b1 with 95% of similarity. another subcluster is constituted of b2 and b3 with 96 % of similarity among them and 73% in relation to b1. d23 d22 d24 d51 d15 d25 d41 d42 d21 d61 d13 d12 d16 d14 d11 b14 b13 b12 b11 b22 b21 b32 b31 0 20 40 60 80 100 120 (d lin k/ d m ax )* 10 0 d24d23d22d51d25d42d61d21d41d15d13d12d16d14d11b14b13b12b11b22b21b32b31 0 20 40 60 80 100 120 (d lin k/ d m ax )* 10 0 fig. 4. hierarchical cluster analysis dendrogram using manhattan distance for excitation fluorescence spectra recorded at emission wavelength 470 nm (a) and emission spectra recorded after excitation at 390 nm (b) on brandies (b) and mixed wine spirits (d). 3.4. multivariate analysis of synchronous fluorescence spectra pca was applied separately on synchronous spectra measured at δλ 10–100 nm. the best classification was achieved using fluorescence spectra recorded at δλ = 80 nm. the synchronous fluorescence spectra showed different shapes. the width of synchronous spectra was larger for mixed wine spirits than those for brandies. mixed wine spirits had higher fluorescence intensity regardless of wavelength but they were also more heterogeneous in this respect. synchronous fluorescence spectra of brandy, mixed wine spirit and caramel (e 150a) obtained at δλ = 80 nm confirmed an earlier assignment of the band. figure 5a shows that the plot of the first two pcs lead to a good discrimination of beverages according to origin. the pc1 has an eigenvalue at 38.6 and accounts for 84.0% of the total variance. the pc2 has an eigenvalue at 7.2 and accounts for 15.6% of the data variation. cumulatively, the first two pcs from the collected data account for 99.6% of the total variance. the spectral pattern (fig. 5b) associated with the pc1 presented a positive peak at 280 nm, a broad positive peak between 320−460 nm and a negative peak at 550 nm. the spectral pattern associated with the pc2 exhibited a negative peak at 250 nm and a positive peak around 500 nm. applying hca to fluorescence spectra recorded at δλ = 80 nm, the dendrogram shows that the mixed wine spirits are well separated from brandies (fig. 6). the first main cluster contains mixed wine spirit samples only, while the second one contains brandy samples. mixed wine spirits cluster consists of various small groups of very similar products. one small group is constituted of samples d2 with 99% of similarity among them and by sample d5 with 95% of similarity with the samples d2 of this a b bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:05 utc nova biotechnologica et chimica 12-2 (2013) 91 group. another group consists of d1 with 96% of similarity among them and 80% in relation to the previous group (d2, d4, d5, and d6). brandy samples form three small subclusters of the second main cluster corresponding to three different producers. one subcluster is constituted of b1 with 97% of similarity. another subcluster is constituted of b2 and b3 with 95 % of similarity among them and 86% in relation to b1. 0,0 0,2 0,4 0,6 0,8 1,0 0,0 0,2 0,4 0,6 0,8 1,0 p c 2 pc1 a 200 300 400 500 600 700 -0,6 -0,4 -0,2 0,0 0,2 0,4 0,6 0,8 1,0 wavelength (nm) p c b pc1 pc2 fig. 5. principal component analysis similarity map (score plot) determined by principal components 1 (pc1) and principal component 2 (pc2) (a) and spectral pattern (loading) corresponding to pc1 and pc2 (b) for synchronous fluorescence spectra recorded at δλ = 80 nm on brandy (□) and mixed wine spirit (o) samples. d23 d24 d22 d51 d42 d25 d61 d21 d41 d15 d13 d12 d16 d14 d11 b14 b12 b13 b11 b22 b21 b32 b31 0 20 40 60 80 100 120 (d lin k/ d m ax )* 10 0 fig. 6. hierarchical cluster analysis dendrogram using manhattan distance for synchronous fluorescence spectra recorded at δλ = 80 nm on brandy (b) and mixed wine spirit (d) samples. finally, a supervised pattern recognition method, lda, was applied to fluorescence spectra recorded at δλ = 80 nm to classify samples according to their origin. lda starts with number of objects whose group membership is known. a basic problem in lda is deciding which variables (excitation wavelengths) should be included in the analysis. in stepwise discriminant function analysis, a model of discrimination is built step-by-step (forward or backward). specifically, at each step all variables are reviewed and evaluated (fischer’s statistics—f to enter and f to remove values) to determine which one will contribute most to the discrimination between groups. this variable will then be included in the model, and the process bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:05 utc 92 uríčková, v. et al. starts again. after performing backward lda, a classification function was obtained for individual analyzed beverages containing five variables (excitation wavelengths): 280, 388, 396, 402, and 498 nm, which provide 99.6% correct predictions for brandies and wine distillates samples these results show that complete synchronous spectra are not required to discriminate between beverages. instead of them, fluorescence intensity could be measured at selected wavelengths. 4. conclusions this study shows that brandies and mixed wine spirits can be discriminated using differences in their fluorescence spectra. differentiation between samples was accomplished by multivariate data analysis methods (pca, hca, and lda). comparison of the results obtained from multivariate data analysis indicated that better classification was obtained from synchronous fluorescence spectra than from the excitation/emission fluorescence spectra. right-angle fluorescence spectroscopy offers a promising approach for the authentication of brandies as neither sample preparation nor special qualification of the personnel are required, and data acquisition and analysis are more simple when compared to front-face technique. acknowledgments: this work was supported by the slovak research and development agency under the contract no. apvv-0797-11. references caldeira, i., pereira, r., climaco, m. c., belchior, a. p., bruno de sousa, v.: improved method for extraction of aroma compounds in aged brandies and aqueous alcoholic wood extracts using ultrasound. anal. chim. acta, 513, 2004, 125–134. canas, s., belchior, a. p., spranger, m. i., bruno-de-sousa, r.: highperformance liquid chromatography method for analysis of phenolic acids, phenolic aldehydes, and furanic derivatives in brandies. development and validation. j. sep. sci., 26, 2003, 496–50. geladi, p.: chemometrics in spectroscopy. part i. classical chemometrics. spectrochim. acta b, 58, 2003, 767–782. mosedale, j. r., puech, j.-l.: wood maturation of distilled beverages. trends food sci. tech., 9, 1998, 95–101. panossian, a., mamikonyan, g., torosyan, m., gabrielyan, e., mkhitaryan, s.: analysis of aromatic aldehydes in brandy and wine by highperformance capillary electrophoresis. anal. chem., 73, 2001, 4379–4383. sádecká, j., tóthová, j., májek, p.: classification of brandies and wine distillates using front face fluorescence spectroscopy. food chem. 117, 2009, 491– 498. watts, v. a., butzke, c. e., boulton, r. b.: study of aged cognac using solid-phase microextraction and partial least-squares regression. j. agr. food chem., 51, 2003, 7738–7742. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:05 utc microsoft word durcekova 9-1 2009.doc nova biotechnologica 9-1 (2009) 83 relationship between administration of statins and blood serum levels of selected biochemical parameters tatiana ďurčeková1, ján mocák1, ján balla2, gabriela gromanová2, katarína boronová1 1department of chemistry, university of ss. cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic (tatiana.durcekova@ucm.sk) 2analytical-diagnostic laboratory, kováčska 15, prešov, sk-080 01, slovak republic (jan.balla@mail.t-com.sk) abstract: results of biochemical tests of 172 patient data (among them 84 men data and 88 women data, resp.) before and after administration of statins were studied. all monitored patients are characterized by lipoprotein metabolism failure or other kind of lipidaemia. the calculations were performed using several chemometrical methods pursuing visualization of most important biochemical parameters and classification of the patient blood samples by means of up-to-date software packages. the dependences of the content of most common biochemical parameters upon the treatment of patients by statins were elucidated in detail. key words: coronary artery diseases, statins, biochemical parameters, multivariate data analysis. 1. introduction coronary heart disease remains the leading cause of mortality in the civilized countries. in medicine it is now an accepted principle that cholesterol lowering is of major importance in diminishing the risk of a developing coronary artery disease. most patients with coronary artery disease require intensive drug therapy to achieve target lipid levels (kastelein, 1999; shimokata et al., 2004). the introduction of inhibitors of 3-hydroxy-3-methylglutaryl coenzyme a reductase (statins) in 1987 was a major advance in prevention and treatment of cardiovascular diseases. several clinical trials have demonstrated the benefit of lipid lowering caused by statins for the primary and secondary prevention of coronary heart disease (liao, 2002; istvan and deisenhofer, 2001). the clinical practise of cardiovascular medicine has been innovated by the advent of the statins. the statins have a wide range of beneficial biologic effects in addition to lipid lowering, a phenomenon commonly termed a pleiotropic effect (fujita et al., 2008; gounari et al., 2009). statins act by inhibiting 3-hydroxy-3-methyl-glutaryl coenzyme a (hmg-coa) reductase and thereby reducing cholesterol synthesis (garcia et al., 2008). 2. material and methods 2.1 description of data data from the out-patient department in prešov were obtained in cooperation with the specialist internal (gromanova, 2008). in this study, biochemical data steming 84 ďurčeková, t. et al. from 172 probands were analyzed by several chemometrical methods in order to reveal relationships between administration of statins and the level of biochemical parameters. the investigated patients were characterized by lipoprotein metabolism failure and other kind of lipidaemia. two data tables (for men 84 samples, and for women – 88 samples) containing the sample origin (patients) in rows and investigated variables in columns (10 biochemical parameters plus 1 combined parameter and age of the patient) were assembled. the following biochemical variables (often called as parameters) were selected: total cholesterol (tchol), high density lipoprotein cholesterol (hdlc), low density lipoprotein cholesterol (ldlc), triacylglycerols (tg), aterogenic index (ai) the combined parameter, creatinine (crea), aspartate aminotransferase (ast), alanine aminotransferase (alt), alkaline phosphatase (alp), creatinine kinase (ck), and gamma-glutamyl transferase (ggt). the parameter values were measured before administration of statins and one year after the statin treatment. the patient samples objects were therefore divided into two groups: class 1 – parameter values before the treatment by statins and class 2 – parameter values one year after the treatment. 2.2 multidimensional data analysis the results of biochemical tests were subjected to multidimensional data analysis using four software packages. statgraphics plus 5.1 was utilized to perform cluster analysis (vandeginste et al., 1997) as well as principal component analysis (massart et al., 1997); spss 15 and sas packages enabled to accomplish discriminant analysis and logistic regression (otto, 1999; sharma, 1996). correlation analysis (meloun and militky, 2002) was also made in addition to the mentioned more sophisticated statistical techniques using software jmp 6.0. 3. results and discussion 3.1 correlation analysis correlation analysis was performed in common for the patients’ results obtained before and after the statins administration. it is represented by the correlation table containing the calculated pair (pearson) correlation coefficients, which indicate the strength of correlation between all pairs of variables biochemical parameters for men and women, distinctively. in order to see the measure of their importance, the correlation coefficient values were compared to the critical value of the sample correlation coefficient, r = 0.215 for men dta set and 0.210 for women data set, which depends on the number of degrees of freedom (the sample number minus two) and the selected probability (usually 0.05). consequently, all values in the correlation tables (table 1, table 2) indicating significant correlations are marked in bold. it can be seen from the observed values that many of the observed significant correlations (marked bold) are very well understandable, as e.g. between tchol a ldlc (strongest correlation for men and women), tchol and its component parts (ldlc and hdlc), nova biotechnologica 9-1 (2009) 85 tchol and tg (for men only), as well as the negative correlation between index of aterogenity ai and so called “good” cholesterol hdlc (high values of hdlc correspond to low values of ai). similarly, significant correlations between the pairs ast – alt and gmt – alt are expectable. what is also interesting are the negative correlations for men between age and any of the variables tg, and ai, which is pronounced after the statins intake. strong positive correlations of tg with tchol and with ai as well as strong negative correlation of tg with hdlc, all observed only after the statins, may also be remarkable. table 1. summary of correlation coefficients expressing mutual correlation between the pairs of investigated biochemical parameters for men data set. variable age crea ast alt gmt alp age 1.000 crea 0.170 1.000 ast -0.081 -0.128 1.000 alt -0.287 -0.090 0.889 1.000 gmt -0.170 0.137 0.168 0.358 1.000 alp 0.290 -0.042 -0.039 -0.048 0.021 1.000 ck 0.021 0.048 0.110 0.039 0.036 -0.298 tchol -0.111 0.040 -0.033 0.054 -0.035 0.001 hdlc 0.171 -0.128 0.094 0.135 0.022 -0.130 ldlc -0.020 0.002 -0.034 0.025 -0.102 0.098 tg -0.352 0.181 -0.073 0.006 0.122 -0.143 ai -0.281 0.156 -0.092 -0.053 -0.072 0.129 continuation ck tchol hdlc ldlc tg ai ck 1.000 tchol -0.084 1.000 hdlc 0.123 0.346 1.000 ldlc -0.094 0.927 0.240 1.000 tg -0.099 0.403 -0.205 0.099 1.000 ai -0.176 0.588 -0.526 0.608 0.528 1.000 3.2 cluster analysis cluster analysis was performed distinctively for the men data set and the women data set. the cluster analysis results are most frequently represented by a dendrogram. figure 1 depicts the dendrogram, which was calculated using squared euclidean distance, commonly used in practice. it shows three significant clusters. the first significant cluster is created by tchol, ldlc, tg and ai, all representing high cardiovascular risk. the second significant cluster is formed by ast, alt (characterizing liver enzymes) and third cluster is created by hdlc with ck, crea with gmt, to which alp and age variables are added at larger distance value (figure 1), which means that these variables are less similar compared to the four ones mentioned. the results for women data set (figure 2) are similar except the observed clustering of age, this time with crea instead of alp. however, with regard to the most important variables indicating lipidaemia, the situation among men and women is similar. 86 ďurčeková, t. et al. table 2. summary of correlation coefficients expressing mutual correlation between the pairs of investigated biochemical parameters for women data set. variable age crea ast alt gmt alp age 1.000 crea 0.389 1.000 ast 0.079 0.105 1.000 alt -0.257 -0.113 0.680 1.000 gmt -0.103 0.163 0.188 0.279 1.000 alp 0.207 -0.017 0.055 -0.003 0.028 1.000 ck 0.085 0.036 0.455 0.253 -0.039 0.105 tchol 0.120 0.082 0.130 0.095 0.172 0.156 hdlc 0.329 0.124 0.418 0.133 0.004 -0.186 ldlc 0.037 -0.016 -0.031 -0.003 0.100 0.164 tg -0.090 0.065 -0.210 0.040 0.253 0.341 ai -0.197 0.023 -0.375 -0.119 0.101 0.328 continuation ck tchol hdlc ldlc tg ai ck 1.000 tchol -0.110 1.000 hdlc 0.007 0.368 1.000 ldlc -0.143 0.859 0.122 1.000 tg -0.068 0.168 -0.477 0.074 1.000 ai -0.084 0.320 -0.670 0.458 0.642 1.000 d is ta nc e 0 200 400 600 800 1000 a ge c r e a a s t a lt g m t a lp c k tc h o l h d lc ld lc t g a i fig. 1. dendrogram of cluster analysis of 12 variables for 84 objects (men). ward`s clustering method, squared euclidean distance. software statgraphics plus 5.1. 3.3 principal component analysis the obtained principal component analysis results are visualized in the biplot form (figure 3). biplot simultaneously represents the samples together with twelve selected nova biotechnologica 9-1 (2009) 87 variables, depicted by the rays, which start from the origin and end at the point determining the variable position in the plane of principal components. 0 200 400 600 800 1000 d is ta nc e ag e c r e a a s t a lt g m t a lpc k tc h o l h d lc ld lct g a i fig. 2. dendrogram of cluster analysis of 12 variables for 88 objects (women). ward`s clustering method, squared euclidean distance. software statgraphics plus 5.1. a close position of tchol, ai, ldlc and tgt at the shown pca biplot confirms their mutual dependence found also by correlation analysis and it helps to understanding the pc1 axis as that expressing the cardiovascular risk. almost opposite position of hdlc is in correspondence with the previous statement. the variables ast, alt and gmt as well as their opponents alp and age are in the perpendicular position (located along the pc2 axis) to the cholesterol variables, which mean their independence with respect to them. this is also in accordance with the results of correlation analysis. 3.4 discriminant analysis discriminant analysis makes a linear combination of the originally selected variables in the way that the discrimination between the classes is mostly pronounced. table 3 shows a summary of the results of linear discriminant analysis (lda), quadratic discriminant analysis (qda) and logistic regression (lr) for the men data set. all these methods are used for classification of the patient samples into two classes – before (class 1) and after (class 2) treatment by statins. the results for training set (used for calculating the classification model) and leave-one-out method validation (one object is left out from the training set in a stepwise mode until all objects are interchanged) are represented in per cents. success in validation step, where the samples independent of the calculations performed in the training process, is more important for overall assessment of the classification method. it is obvious that the predictive ability is better for lda than the qda. however, the most promising are the results achieved by logistic regression. 88 ďurčeková, t. et al. fig. 3. biplot pc1 vs. pc2 (men), 12 variables (with the symbols specified in part 2), 84 patient samples. software statgraphics plus 5.1. table 3. results of discriminant analysis (lda, qda) and lr for two software packages (spss, sas) – classification of the men samples into two categories: before and after statin treatment. spss sas method results training set leave-one-out training set leave-one-out true/all 73/84 67/84 73/84 67/84 lda % true 86.9 79.8 86.9 79.8 true/all 73/84 n.a. 70/84 55/84 qda % true 86.9 n.a. 83.3 65.5 true/all 75/84 n.a. 75/84 72/84 lr % true 89.3 n.a. 89.3 85.7 n.a. – not accessed. tabable 4.: results of discriminant analysis (lda, qda) and lr for two software packages (spss, sas) – classification of the women samples into two categories: before and after statin treatment. spss sas method results training set leave-one-out training set leave-one-out true/all 81/88 74/88 81/88 74/88 lda % true 92.0 84.1 92.0 84.1 true/all 81/88 n.a. 76/88 61/88 qda % true 92.0 n.a. 86.4 69.3 true/all 79/88 n.a. 79/88 77/88 lr % true 89.8 n.a. 89.8 87.5 n.a. – not accessed. nova biotechnologica 9-1 (2009) 89 df1 n o class 1 2 -2,7 -1,7 -0,7 0,3 1,3 2,3 3,3 4,3 -10 10 30 50 70 90 fig. 4. lda scatterplot of 84 patient samples (men) marked by number (no) calculated from 12 variables. df1 is the only discriminant function. class 1before, class 2 – after treatment by statins. software statgraphics plus 5.1. a good separation between the investigated two categories of the patient samples is confirmed also in figure 4, calculated also for the men data set. the results for women data set are collected in table 4. all results referring to the training set are close to or over 90% of the correct results, the best outcome in validation by leave-one-out method was obtained for lr. 4. conclusions treatment of patients with the risk of a developing coronary artery disease can be successfully monitored using the visualization and classification methods of multidimensional statistical analysis. the interrelation of eleven biochemical laboratory parameters as well as the patient’s age and gender was investigated in detail. achieved results enable to evaluate the treatment by statins in each individual case. they may also help in estimation of the pertaining cardiovascular risk after the statin drug administration and in monitoring the dynamic progression of the disease. acknowledgement: the support of this work by the grants vega 1/1005/09 and vvce-000407 is acknowledged. references fujita, m., yamazakib, t., hayashic, d., kohroc, t., okadac, y., nagai, r.: pleiotropic effects on cardiovascular events in the japanese coronary artery disease study. int. j. cardiol., 129, 2008, 294-296. garcia, i., munteanu, c.r., fall, y., gómez, g., uriarte, e., gonzález-díaz, h.: qsar and complex network study of the chiral hmgr inhibitor structural diversity. bioorg. med. chem., 17, 2009, 165-175. 90 ďurčeková, t. et al. gounari, p., tousoulis, d., antoniades, c., kampoli, a.m., stougiannos, p., papageorgiou, n., roulia, g., stefanadi, e., siasos, g., tsioufis, c., stefanadis, c.: rosuvastatin but not ezetimibe improves endothelial function in patients with heart failure, by mechanisms independent of lipid lowering. int. j. cardiol., 2009, (in press) . gromanová, g.: influence of hypolipidaemic treatment by statins on levels of selected biochemical parameters (in slovak). diploma thesis, tu trnava, 2008. istvan, e., deisenhofer, j.: statin inhibition of hmg-coa reductase: a 3dimensional view. atherosclerosis suppl., 4, 2003, 3-8. kastelein, j.j.p.: the future of best practise. atherosclerosis 143, 1999, s17-s21. liao, j.k.: beyond lipid lowering: the role of statins in vascular protection. int. j. cardiol., 86, 2002, 5-18. massart, d.l., vandeginste, b., buydens, l., de jong, s., lewi, p., smeyers-verbeke, j.: handbook of chemometrics and qualimetrics, part a, elsevier, amsterdam, 1997, 886 pp. meloun, m., militký j.: compendium of statistical data processing (in czech), academia, praha, 2002, 764 pp. otto, m.: chemometrics: statistics and computer application in analytical chemistry, wiley, weinheim, 1999, 314 pp. sharma, s.: applied multivariate techniques, j. wiley, new york, 1996, 588 pp. shimokata, k., yamadac, y., kondo, t., ichihara, s., izawa, h., nagata, k., murohara, t., ohnod, m., yokota, m.: association of gene polymorphisms with coronary artery disease in individuals with or without nonfamilial hypercholesterolemia. atherosclerosis, 172, 2004, 167-173. vandeginste, b., massart, d.l., buydens, l., de jong, s., lewi p., smeyers-verbeke, j.: handbook of chemometrics and qualimetrics, part a, amsterdam, elsevier, 1997, 876 pp. microsoft word moravcik nbc 12-2.doc nova biotechnologica et chimica 12-2 (2013) 108 doi 10.2478/nbec-2013-0013 © university of ss. cyril and methodius in trnava high – performance liquid chromatographic method for enantioseparation of underivatized α-amino acids using cyclofructan – based chiral stationary phases jakub moravčík, katarína hroboňová institute of analytical chemistry, faculty of chemical and food technology, slovak university of technology, radlinského 9, bratislava, sk-812 37, slovak republic (jakub.moravcik@stuba.sk) abstract: chromatographic columns with chiral stationary phases based on chemically – bonded derivatized cyclofructans were evaluated for hplc enantioresolution of underivatized α-amino acids. the analytical study of chiral separation of these analytes was focused on the selection of suitable chiral stationary phase and mobile phase. using isopropyl carbamate cyclofructan 6 as a chiral stationary phase, αamino acid optical isomers were separated. the retention and enantioseparation of chiral amino acids were also influenced by a mobile phase composition. the mixture methanol/acetonitrile/acetic acid/triethylamine (75/25/0.3/0.2 v/v/v/v) was found to be the most effective mobile phase for hplc separation of studied compounds. hplc enantioresolution of chiral amino acids was thermodynamically studied. based on the enthalpy and entropy contribution values calculated from the van´t hoff equation, hplc enantioseparation under chosen chromatographic conditions was found to be an enthalpically driven. key words: amino acids, cyclofructan – based chiral selectors, hplc, thermodynamic study 1. introduction chirality was discovered in 1848 by louis pasteur (flack, 2009). since most biologically important compounds exist in two enantiomeric forms that can possess differences in their physiological activity, the impetus for the separation of optical isomers and the preparation of enantiomerically pure compounds in the field of biotechnology, chemistry and pharmacology is still increasing (ilisz et al., 2012). chromatographic methods, i.e. capillary electrophoresis (ce), gas chromatography (gc), high – performance liquid chromatography (hplc), supercritical fluid chromatography (sfc), thin layer chromatography (tlc), have been frequently used for the enantioresolution of chiral analytes. among them, enantioselective hplc method is one of the most powerful and widely used separation techniques at both analytical and preparative scales (ding et al., 2004). amino acids play an important role in living organisms. they serve as the basic structural units of peptides and proteins. most proteinogenic α-amino acids contain an asymmetric carbon atom. their stereoisomers can differ markedly in physiological effects. chiral separation of these substances is a great analytical challenge in several research areas, such as asymmetric syntheses in organic chemistry, biochemistry of amino acids, pharmaceutics, the dating of archaeological materials and the study of bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:14 utc nova biotechnologica et chimica 12-2 (2013) 109 food processes in human body (shpigun et al., 2002). the recent direct hplc separations of amino acid stereoisomers and related compounds are summarized in table 1. table 1. summary of chiral stationary phases for direct hplc separations of amino acid stereoisomers. separated stereoisomers chiral selectors mobile phases references cyclodextrins 20 unusual amino acids α-cd, β-cd, acetylated β-cd, 3,5dimethylphenylcarbamoylated β-cd 0.1% aqueous tfaa (ph 4-5) remsburg et al., 2008 crown-ether β-amino acids, proteinogenic d,l-amino acids, aliphatic and aromatic β3-amino acids (+)-(18-crown-6)2,3,11,12-tetracarboxylic acid h2o/meoh + 10 mmo.l -1 acoh, h2o/meoh (80/20-20/80 v/v) + 5-10 mmol.l-1 acoh, h2o/meoh (50/50 v/v) + 0.02 mol.l-1 h2so4 chen et al., 2006; wang et al., 2010; berkecz et al., 2006 β-amino acids (3,3´-diphenyl-1,1´binaphtyl)-20-crown-6 h2o/mecn (80/20 v/v) + 0.01 mol.l-1 h2so4 + 1.0 mmol.l-1 ch3co2nh4 choi et al., 2008 proteinogenic amino acids pseudo-18-crown-6 having 1-phenyl-1,2cyclohexanediol unit hexane/etoh/tfaa/h2o (75/25/0.5/0.2 v/v/v/v) hirose et al., 2005 macrocyclic glycopeptide n-methyloxycarbonyl-α-amino acids ristocetin a, teicoplanin, vancomycin 15 mmol.l-1 nh4oac (ph 4.1)/meoh (80/20 v/v), meoh/mecn/acoh/tea (25/75/0.25/ 0.25 v/v/v/v) boesten et al., 2006 tryptophan, phenylalanin, leucin teicoplanin, teicoplanin aglycone, methylated teicoplanin aglycone 1% tfaa/meoh (60/40 v/v) meoh/mecn/acoh/tea (55/45/0.3/0.2 v/v/v/v) xiao et al., 2006 acoh – acetic acid, nh4oac – ammonium acetate, cd – cyclodextrin, csp – chiral stationary phase, etoh – ethanol, mecn – acetonitrile, meoh – methanol, tea – triethylamine, tfaa – trifluoroacetic acid cyclofructans (cfs) belong to a relatively small group of macrocyclic oligosaccharides. they consist of six or more β-(2→1) linked d-fructofuranose units. native cyclofructans have limited capabilities as chiral selectors (sun et al., 2009). recently, it was found that aliphatic and aromatic functionalized cfs could be highly selective for chiral molecules containing a primary amine functional group (jiang et al., 2009). in the present work derivatized cyclofructans were tested as chiral selectors for the direct hplc enantioseparation of underivatized α-amino acids. isopropyl carbamate bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:14 utc 110 moravčík, j. and hroboňová, k. cyclofructan 6 (ip-cf6), (r)-naphtylethyl carbamate cyclofructan 6 (rn-cf6) and dimethylphenyl carbamate cyclofructan 7 (dmp-cf7) (fig. 1) chiral stationary phases (csp) were selected. the influence of the mobile phase composition on the values of chromatographic parameters (retention factor, resolution) was investigated. the enantioseparation process was thermodynamically characterized by the values of enthalpy and entropy contributions calculated from the van´t hoff equation. or o ro o or n r = derivatization group n = 6 (cyclofructan 6, cf6), 7 (cyclofructan 7, cf7) derivatization groups o nh2 o h3c h n h c3 ch 3 h n o isopropyl carbamate (ip) (r)-naphtylethyl carbamate (rn) dimethylphenyl carbamate (dmp) fig. 1. scheme of stationary phases based on chemically bonded derivatized cyclofructan and chemical structures of used derivatizing groups. coohh2 n cooh nh 2 cooh nh 2 alanine (ala) valine (val) leucine (leu) cooh nh 2 coohnh 2 cooh nh 2 s norleucine (nle) γ-aminobutyric acid (gaba) methionine (met) cooh nh 2 cooh nh 2 n h phenylalanine (phe) tryptophan (trp) fig. 2. chemical structures of separated proteinogenic α-amino acids and γ-aminobutyric acid. covalent linker silica gel bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:14 utc nova biotechnologica et chimica 12-2 (2013) 111 2. materials and methods 2.1 chemicals and samples racemic mixtures of certain proteinogenic amino acids (alanine, leucine, methionine, norleucine, phenylalanine, tryptophan, valine) and γ-aminobutyric acid (fig. 2) were purchased from sigma aldrich. acetonitrile, methanol, acetic acid and triethylamine were purchased from merck. the solutions of racemic mixtures of each amino acid were prepared by dissolving in methanol (concentration 10 mg.ml-1). the homogenization of prepared solutions was performed by an ultrasonic bath (bandelin sonorex rk 100h). 2.2 hplc analysis the hplc separation of chiral α-amino acids were carried out on a agilent (series 1100) hplc system equipped with a binary pump, an injection valve (rheodyne) with a 20 μl injection loop, column thermostat, spectrophotometric detector and a chromatographic datasystem. direct separation of α-amino acid enantiomers were performed on chromatographic columns with chiral stationary phases based on chemically – bonded derivatized cyclofructans ip-cf6, rn-cf6 and dmp-cf7 (4×250 mm i.d, 5 μm). the temperature range of 0 – 35 °c was chosen for the thermodynamic study of the hplc enantioseparation of selected analytes. the mobile phases that were tested consisted of methanol and acetonitrile as organic solvents and acetic acid and triethylamine as ionic modifiers. the different concentration of methanol (50, 65, 75 and 85 vol. %) was used to investigate the influence of the mobile phase composition on the retention and enantioresolution of αamino acid racemic mixtures. the ratio of ionic modifiers was constant (0.3/0.2 v/v). the flow rate was 0.8 ml.min-1. the chromatograms of eluted optical isomers were sxcanned at the wavelength of 210 nm. 3. results and discussion 3.1 the influence of the chiral stationary phase composition on the retention and enantioseparation of chiral amino acids chiral columns based on chemically – bonded cyclofructans with aliphatic (ip-cf6) and aromatic moieties (rn-cf6, dmp-cf7) were tested in order to select the appropriate csp for hplc separation of studied chiral amino acids. the mobile phase methanol/acetonitrile/acetic acid/triethylamine (75/25/0.3/0.2 v/v/v/v) was used for all chromatographic separations. results given in table 2 show that the rn-cf6 chiral selector exhibits no enantioselectivity for the amino acid enantiomers used in this study. all chiral amino acids eluted with retention factors from 0.09 to 0.25. the highest retention factor values were obtained for aromatic amino acids (phenylalanine and tryptophan). the bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:14 utc 112 moravčík, j. and hroboňová, k. lower retention factor value was obtained for aliphatic amino acids. the enantioseparation of amino acid enantiomers was not achieved. the dmp-cf7 chiral column was also evaluated. this chromatographic column is based on a chemically – bonded cf7 with an aromatic substituent which allows different types of interactions between separated enantiomers and the chiral selector. among them, π-π interactions, dipole-dipole interactions and hydrogen bonds generally occur. using this csp, the hplc enantioresolution of amino acid optical isomers was not achieved. compared to the rn-cf6 chiral column, the retention factor values were higher (table 2). based on the relationship between a structure of analytes and their retention behavior the amino acids with more polar functional groups were retained in the dmp-cf7 csp for a longer period of time. table 2. chromatographic results for separation of studied chiral amino acids by cyclofructan – based chiral stationary phases. csp rn-cf6 dmpcf7 ipcf6 amino acid k k k1 k2 rs leu 0.22 ± 0.01 0.25 ± 0.01 0.31 ± 0.01 val 0.28 ± 0.01 0.26 ± 0.01 trp 0.23 ± 0.01 0.30 ± 0.01 0.27 ± 0.01 0.32 ± 0.01 0.33 ± 0.01 phe 0.25 ± 0.00 0.30 ± 0.01 0.29 ± 0.01 0.35 ± 0.01 0.36 ± 0.02 nle 0.37 ± 0.02 0.40 ± 0.01 0.40 ± 0.02 met 0.09 ± 0.00 0.36 ± 0.02 0.46 ± 0.02 0.50 ± 0.02 0.25 ± 0.01 gaba 0.10 ± 0.00 0.37 ± 0.02 0.47 ± 0.02 0.52 ± 0.02 0.44 ± 0.02 ala 0.19 ± 0.01 0.39 ± 0.02 0.69 ± 0.03 0.76 ± 0.03 0.51 ± 0.02 t m [min] 5.04 4.14 4.88 the hplc enantioseparation of proteinogenic amino acids was achieved by the ipcf6 chiral column. resolution values given in table 2 show that enantiomers of some analytes were partially separated (rs = 0.25 – 0.51). the highest enantioresolution was obtained for amino acids with aliphatic substituents. amino acids with aromatic moieties were separated with lower resolution values. based on these results, steric effects can be predicted to have a dominant role during the enantioseparation process under the mentioned conditions (ip-cf6 csp, polar – organic separation mode). 3.2 the influence of the mobile phase composition on the retention and enantioseparation of chiral amino acids the influence of mobile phase composition on the retention and enantioresolution of selected amino acids was observed. all chromatographic separations were performed in the polar – organic separation mode (methanol/acetonitrile/acetic acid/triethylamine). the values of methanol concentration in tested mobile phases were 50, 65, 75 and 85 vol. %. small amounts of ionic modifiers (0.3 vol. % of acetic acid, 0.2 vol. % of triethylamine) were added to prepared mobile phases. the resolution values of chiral amino acids (table 3) were calculated for tested mobile phases. results show that the hplc enantioseparation of studied analytes is markedly bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:14 utc nova biotechnologica et chimica 12-2 (2013) 113 influenced by the mobile phase composition. with an increasing value of methanol volume percent concentration the resolution values were decreasing. based on these results, the mixture methanol/acetonitrile/acetic acid/triethylamine (75/25/0.3/0.2, v/v/v/v) was found to be the most effective mobile phase for the hplc separation of all set of chiral α-amino acids. the resolution values obtained for this mobile phase composition were from the interval 0.25-0.51. table 3. the influence of methanol concentration in used mobile phases on the resolution values of chiral amino acids. methanol/acetonitrile/acetic acid/triethylamine (v/v/v/v) 50/50/0.3/0.2 65/35/0.3/0.2 75/25/0.3/0.2 85/15/0.3/0.2 amino acid rs gaba 0.76 ± 0.03 0.67 ± 0.03 0.44 ± 0.02 0.35 ± 0.01 ala 0.65 ± 0.03 0.59 ± 0.02 0.51 ± 0.02 0.40 ± 0.01 leu 0.81 ± 0.03 0.44 ± 0.02 0.31 ± 0.01 0.26 ± 0.01 met 0.58 ± 0.02 0.34 ± 0.01 0.25 ± 0.01 0.21 ± 0.01 nle 0.55 ± 0.02 0.46 ± 0.02 0.40 ± 0.01 0.35 ± 0.01 phe 0.54 ± 0.02 0.42 ± 0.02 0.36 ± 0.01 0.31 ± 0.01 trp 0.56 ± 0.02 0.42 ± 0.02 0.33 ± 0.01 0.28 ± 0.01 t m [min] 4.09 4.06 4.27 4.50 fig. 3. the dependence of retention factors (k1, k2) of methionine (■,●) and phenylalanine (♦,▲) on the concentration of methanol in a mobile phase. the retention factor values of eluted amino acid enantiomers exhibited an observable dependence on the change of methanol volume percent concentration. this dependence for selected analytes (methionine, phenylalanine) is graphically k1, k2 concentration of methanol in a mobile phase (vol. %) bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:14 utc 114 moravčík, j. and hroboňová, k. represented in fig. 3. the increase in methanol content in a mobile phase has the same effect on the retention of studied compounds as on the resolution. 3.3 the influence of the column temperature on the retention and enantioseparation of chiral amino acids the column temperature is one of the factors that can affect elution parameters. moreover, increasing the temperature usually causes the enantioresolution values to get lower. thermodynamic study of chiral separation provides useful information about enantioseparation mechanism and the nature of the interactions between optically active analytes and chiral stationary phases. based on the values of enthalpy and entropy contribution calculated from the van´t hoff equation, separation of optical isomers can be characterized as an enthalpically or an entropically driven process. thermodynamics is the effective tool for evaluating both enantioselective separation and chiral selectors (weng et al., 2004). [min.] time 2 4 6 8 [mv] v ol ta ge 15 20 25 30 t = 273 k t = 283 k t = 296 k fig. 4. hplc chromatograms of methionine racemic mixture in the temperature interval 273 – 296 k. chromatographic conditions: stationary phase: isopropyl carbamate cyclofructan 6, mobile phase: methanol/acetonitrile/acetic acid/ triethylamine (75/25/0.3/0.2 v/v/v/v), flow rate: 0.8 ml.min-1, detection: spectrophotometric (λ = 210 nm), injected volume: 20 μl. the effect of the column temperature on the retention and resolution of chiral amino acids was investigated. the hplc enantioseparation of selected analytes was carried out at eight different temperature values (0 °c, 5 °c, 10 °c, 15 °c, 20 °c, 23 °c, 30 °c and 35 °c). when the column temperature was increasing, the retention factor values of eluted amino acid racemic mixtures were decreasing. the hplc chromatograms of methionine enantioseparation in the temperature interval 273 – 296 are shown in fig. 4. the resolution values (table 4) were also markedly influenced by the temperature at which enantiomeric separations were realized. the influence of the column temperature on the enantioseparation of selected amino acids exhibited the same trend as the temperature dependence of the retention of bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:14 utc nova biotechnologica et chimica 12-2 (2013) 115 separated amino acid enantiomers. the resolution of chosen chiral amino acids reached its maximum value at 0 ºc. with the increasing column temperature, the hplc enantioseparation of studied compounds was getting worse (lower values of rs). for the thermodynamic characterization of the chromatographic enantioseparation of studied compounds, the van´t hoff equation was used. this equation represents the dependence of the natural logarithm of the retention factor value (ln k) on reciprocal value of the column temperature (1/t). the van´t hoff analysis is suitable for the determination of the fundamental thermodynamic parameters, i.e. the standard partial molar enthalpy of transfer (δhi) and the standard partial molar entropy of transfer (δsi). the values of these parameters were calculated according to the equation: ln ki = -δhi/rt + δsi/r + ln φ where ki is the retention factor, δhi [jmol -1] is the standard partial molar enthalpy of transfer, δsi [jk -1mol-1] is the standard partial molar entropy of transfer, r is the gas constant (8.314 jk-1mol-1), t [k] is the column temperature and φ is the phase ratio defined as the volume of the stationary phase (vs) divided by the volume of the mobile phase (vm). the value of the standard partial molar enthalpy of transfer (δhi) was calculated from a slope of -δhi/r and the value of the standard partial molar entropy of transfer (δsi) was calculated from an intercept of δsi/r. the determination of these thermodynamic characteristics requires the knowledge of the phase ratio. it is usually difficult to calculate the phase ratio because the value of the stationary phase volume (vs) is approximate in many cases. its value is relatively easy to calculate only for liquid – liquid chromatography (chester et al., 2003). the values of the standard partial molar enthalpy δ(δhi) and entropy change δ(δsi*) of chosen amino acid racemic mixtures are given in table 5. the values of the entropic contribution δ(δsi*) also included the value of the phase ratio. the values of the standard partial molar gibbs energy (δgi) of both amino acid enantiomers (table 5) were calculated for two different temperatures (273 k and 308 k) according to the gibbs – hemholtz equation: δgi = δhi tδsi* the standard partial molar gibbs energy change δ(δgi) of chosen amino acid racemic mixtures (table 5) was also determined for temperatures of 273 k and 308 k. the standard partial molar enthalpy of the enantiomer with a higher value of retention time (δh 2 ) reached higher values than the standard partial molar enthalpy of the first eluted enantiomer (δh 1 ). this fact was observed for all separated amino acid racemic mixtures. enantioselective interactions between a chiral selector and the second eluted enantiomer are more preferred than enantioselective interactions between a chiral selector and the first eluted optical isomer. higher values of the standard partial molar enthalpy change δ(δhi) were obtained for racemic mixtures of α-amino acids with an aliphatic substitution (leucine, methionine, norleucine). the standard partial molar enthalpy change δ(δhi) exhibited lower values for alanine, γ-aminobutyric acid and phenylalanine. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:14 utc 116 moravčík, j. and hroboňová, k. table 4. the resolution values of the chosen chiral amino acids in the temperature interval 273 – 308 k. t [k] 273 278 283 288 293 296 303 308 amino acid rs trp 0.47 ± 0.02 0.44 ± 0.02 0.41 ± 0.01 0.38 ± 0.01 0.35 ± 0.01 0.33 ± 0.01 0.30 ± 0.01 0.28 ± 0.01 leu 0.66 ± 0.02 0.60 ± 0.02 0.48 ± 0.02 0.44 ± 0.02 0.36 ± 0.01 0.31 ± 0.01 0.29 ± 0.01 0 phe 0.53 ± 0.02 0.50 ± 0.02 0.47 ± 0.02 0.42 ± 0.01 0.38 ± 0.01 0.35 ± 0.01 0.32 ± 0.01 0.29 ± 0.01 nle 0.72 ± 0.03 0.62 ± 0.02 0.56 ± 0.02 0.49 ± 0.02 0.43 ± 0.02 0.40 ± 0.01 0.37 ± 0.01 0 met 0.71 ± 0.03 0.68 ± 0.03 0.62 ± 0.02 0.54 ± 0.02 0.37 ± 0.01 0.25 ± 0.01 0.21 ± 0.01 0.19 ± 0.00 gaba 0.63 ± 0.02 0.61 ± 0.02 0.57 ± 0.02 0.52 ± 0.02 0.48 ± 0.02 0.44 ± 0.02 0.38 ± 0.01 0.35 ± 0.01 ala 0.70 ± 0.03 0.67 ± 0.03 0.61 ± 0.02 0.55 ± 0.02 0.53 ± 0.02 0.51 ± 0.02 0.49 ± 0.02 0.46 ± 0.02 table 5. the values of thermodynamic parameters of chosen chiral amino acids calculated from the van't hoff equation. amino acid δ (δh°) [jmol-1] δ (δs°*) [jk-1mol-1] (δg1°)273 k [jmol-1] (δg2°)273 k [jmol-1] δ (δg°)273 k [jmol -1] (δg1°) 308 k [jmol-1] (δg2°) 308 k [jmol-1] δ (δg°)308 k [jmol -1] phe -286 ± 15 0.35 ± 0.05 1953 ± 179 1528 ± 140 -425 ± 22 3544 ± 324 3151 ± 288 -393 ± 20 met -993 ± 91 -2.69 ± 0.32 871 ± 80 613 ± 57 -258 ± 14 2407 ± 220 2243 ± 205 -164 ± 15 trp -985 ± 90 -2.06 ± 0.25 2281 ± 209 1858 ± 170 -423 ± 22 3688 ± 337 3337 ± 305 -351 ± 18 gaba -616 ± 57 -1.37 ± 0.17 838 ± 77 597 ± 56 -241 ± 13 2360 ± 216 2167 ± 198 -193 ± 10 ala -290 ± 15 -0.31 ± 0.04 -108 ± 10 -313 ± 16 -205 ± 11 1400 ± 128 1206 ± 110 -194 ± 10 leu -2130 ± 195 -6.10 ± 0.80 2069 ± 190 1605 ± 147 -464 ± 24 4663 ± 426 4413 ± 403 -250 ± 13 nle -1007 ± 92 -2.63 ± 0.31 1487 ± 136 1198 ± 110 -289 ± 15 2997 ± 274 2800 ± 256 -197 ± 10 b ereitgestellt von s lovenská poľnohospodárska knižnica | h eruntergeladen 16.01.20 15:14 u tc nova biotechnologica et chimica 12-2 (2013) 117 the chromatographic enantioseparation is also influenced by steric effects. the diffusion of separated optical isomers into interaction parts of a chiral selector is dependent on the size of analyte molecules. the standard partial molar entropy of enantiomers (δs 1 *, δs 2 *) is connected with steric interactions and can be also used for the enantioselectivity evaluation. the entropic contribution of the second eluted enantiomer (δs 2 *) exhibited higher values than the entropic contribution of the enantiomer with a lower value of retention time (δs 1 *). this means that molecules of the second eluted enantiomer were retained in more interaction parts of a chiral selector than molecules of the first eluted enantiomer. based on the values of the enthalpic and entropic contribution to the change of gibbs energy, the hplc enantioseparation of chosen amino acids under selected chromatographic conditions (ip-cf6 column, polar – organic separation mode) was found to be an enthapically driven process. it means that the second eluted enantiomer and a chiral selector form a diastereomeric complex with a higher stability constant value than the enantiomer with a shorter elution time. the van't hoff plots of chosen chiral amino acids are graphically represented in fig. 5. the coefficient of determination values (r2~0.99) indicate the linear dependence of retention of studied compounds on the column temperature. the retention mechanism did not change with the temperature change. fig. 5. the van't hoff plots of chosen chiral amino acids. (■,▲) phenylalanine, (●,♦) methionine 4. conclusions different types of cyclofructan – based chiral selectors were tested for hplc separation of chiral amino acids. among them, isopropyl carbamate cyclofructan 6 showed the ability to separate optical isomers in the polar – organic separation mode ln k1, ln k2 1/t [k-1] bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:14 utc 118 moravčík, j. and hroboňová, k. (mobile phase: methanol/acetonitrile/acetic acid/triethylamine, 75/25/0.3/0.2 v/v/v/v). based on the results of thermodynamic study in the temperature interval 0 ºc – 35 ºc, the hplc enantioseparation of studied racemic mixtures can be characterized as an enthapically driven process. acknowledgements: this study was financially supported by the scientific grant agency of the ministry of education, science, research and sport of the slovak republic and of the slovak academy of sciences (grant vega no. 1/0164/11). the authors thanks to d. w. armstrong for the donation of chiral column. references berkecz, r., sztojkov-ivanov, a., ilisz, i., forró, e., fülöp, f., hyun, m. h., péter, a.: high-performance liquid chromatographic enantioseparation of β-amino acid stereoisomers on a (+)-(18-crown-6)-2,3,11,12tetracarboxylic acid-based chiral stationary phase. j. chromatogr. a, 1125, 2006, 138-143. boesten, j.m.m., berkheij, m., schoemaker, h.e., hiemstra, h., duchateau, a.l.l.: enantioselective high-performance liquid hromatographic separation of n-methyloxycarbonyl unsaturated amino acids on macrocyclic glycopeptide stationary phases. j. chromatogr. a, 1108, 2008, 26-30. chen, j.j., zhang, d.t., shen, b.c., zhang, x.j., xu, b.j., xu, x.z.: enantioseparation of d,l-α-amino acids on crown ether chiral stationary phases. j. anal. chem., 34, 2006, 1535-1540. chester, t.l., coym, j.w.: effect of phase ratio on van´t hoff analysis in reversed-phase liquid chromatography, and phase-ratio-independent estimation of transfer enthalpy. j. chromatogr. a, 1003, 2003, 101-111. choi, h. j., ha, h. j., han, s. c., hyun, m. h.: liquid chromatographic resolution of β-amino acids on csps based on optically active (3,3´-diphenyl-1,1´binaphtyl)-20-crown-6. anal. chim. acta, 619, 2008, 122-128. ding, g.-s., ying, l., cong, r.-z., wang, j.-d.: chiral separation of enantiomers of amino acid derivatives by high-performance liquid chromatography on a norvancomycin-bonded chiral stationary phase. talanta, 62, 2004, 997-1003. flack, a.: louis pasteur´s discovery of molecular chirality and spontaneous resolution in 1848, together with a complete review of his crystallographic and chemical work. acta cryst., 65, 2009, 371-389. hirose, k., jin, i.z., nakamura, t., nishioka, r., ueshige, t., tobe, y.: preparation and evaluation of a chiral stationary phase covalently bound with chiral pseudo-18-crown-6-ether having 1-phenyl-1,2-cyclohexanediol as a chiral unit. j. chromatogr. a, 1078, 2005, 35-41. ilisz, i., aranyi, a., pataj, z., péter, a.: recent advances in the direct and indirect liquid chromatographic enantioseparation of amino acids and related compounds: a review. j. pharm. biomed. anal., 69, 2012, 28-41. jiang, ch., tong, m.-y., breitbach, z.s., armstrong, d.w.: synthesis and examination of sulphated cyclofructans as a novel class of chiral selectors for ce. electrophoresis, 30, 2009, 3897-3909. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:14 utc nova biotechnologica et chimica 12-2 (2013) 119 remsburg, j.w., armstrong, d.w., péter, a., tóth, g.: lc enantiomeric separation of unusual amino acids using cyclodextrin-based stationary phases. j. liq. chromatogr. rel. technol., 31, 2008, 219-230. shpigun, o.a., shapovalova, e.n., ananieva, i.a., pirogov, a.v.: separation and enantioseparation of derivatized amino acids and biogenic amines by high-performance liquid chromatography with reversed and chiral stationary phases. j. chromatogr. a, 979, 2002, 191-199. sun, p., wang, ch., breitbach, z.s., zhang, y., armstrong, d.w.: development of new hplc chiral stationary phases based on native and derivatized cyclofructans. anal. chem., 81, 2009, 10215-10226. wang, y., young, d.j., tan, t.t. y., ng, s.c.: click preparation of hindered cyclodextrin chiral stationary phases and their efficient resolution in high performance liquid chromatography. j. chromatogr. a, 1217, 2010, 7878-7883. weng, w., yao, b., chen, x., lin, w., zeng, q.: thermodynamic studies on mechanism of chiral resolution by liquid chromatography. progress in chemistry, 18, 2006, 1056-1064. xiao, t.l., tesařová, e., anderson, j.l., egger, m., armstrong, d.w.: evaluation and comparison of a methylated teicoplanin aglycone to teicoplanin aglycon and natural teicoplanin chiral stationary phases. j. sep. sci., 29, 2006, 429-445. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:14 utc nova biotechnol chim (2022) 21(2): e1155 doi: 10.36547/nbc.1155 1 nova biotechnologica et chimica characterization of functional effects of different lab isolated from sourdoughs in turkey zuhal alkay, ezgi metin sagir, muhammed ozgolet, muhammed zeki durak department of food engineering, faculty of chemical and metallurgical engineering, yildiz technical university, istanbul, turkey  corresponding author: zuhalakay21@hotmail.com article info article history: received: 7th september 2021 accepted: 22nd november 2021 keywords: antifungal antimicrobial lactic acid bacteria phytase activity proteolytic sourdough abstract in this study, the technological properties of five different lactic acid bacteria (lab) isolated from sourdough collected from three cities of turkey (gümüşhane, manisa, ankara) and cyprus were investigated. for this purpose, antimicrobial, antifungal, phytase, and proteolytic activities of these bacteria and their effect on ph were examined. the ph of the prepared solutions decreased to 3.8 and 4.4 from 6.3 by lab addition following 24 h incubation. lactiplantibacillus plantarum o6f-25 strain showed the best inhibitory effect against four gram-positive and four gramnegative bacteria. in terms of proteolytic activity, lactiplantibacillus plantarum 45mk-32 was the most effective strain. the antifungal effects of lab were tested against aspergillus flavus, aspergillus niger, and penicillium carneum. levilactobacillus brevis kco-48 was the most effective lab strain. phytase activities (710.40 – 840.37 u.ml-1) of lab studied except limosilactobacillus fermentum (29gt-19), which has the lowest phytase activity, were not significantly different (p < 0.05). this study revealed that sourdough labs have the potential to be used as biopreservative and produce functional food products. introduction sourdough technology is one of the earliest fields of biotechnological applications, mainly originated from the fermentation of grain matrices by natural lactic acid bacteria (lab) (gobbetti et al. 2014). however, the trend bringing about the consumption of health-promoting foods has increased the production of functional and nutritional products (teleky et al. 2020). sourdough bread meets this demand of conscious consumers because it offers several important health benefits such as lowering glycemic index, increasing mineral bioavailability, antimicrobial agent, and bioactive peptide formation, thus promoting clean label bread production (rizzello et al. 2017; tsafrakidou et al. 2020). internal and external factors influence sourdough production. flour type and quality, fermentation temperature and time, water activity, relative humidity, dough yield, ph and acidification, oxygen tension, and backslopping dynamics determine sourdough characteristics (de vuyst et al. 2017). since traditional spontaneous sourdough is time-consuming and trying, it needs skilled labour, and causes differences in quality of final bread, liquid or dried starter cultures are chosen for industrial processes (siepmann et al. 2018). the demand for the stable composition of starter cultures in the modern sourdough-making industry encouraged various studies on the selection of starter cultures with superior functionality (gänzle and ripari 2016). the sourdough microbiota is the primary influencer of the technological and mailto:zuhalakay21@hotmail.com nova biotechnol chim (2022) 21(2): e1155 2 nutritional value of the sourdough bread (sakandar et al. 2019). sourdough microbiota consists mainly of lab and yeast of various genera and species. most lab species isolated from sourdoughs belong to the genus lactobacillus with more than 60 species (de vuyst et al. 2017). lb. brevis, lb. fermentum, lb. paralimentarius, and lb. plantarum are among the most prevalent lab present in sourdough (minervini et al. 2014). many of the studies have focused on specific technological and nourishing effects of sourdough lab such as proteolytic activity (ozturkoglubudak et al. 2016; melini and melini 2018), phytase activity (cizeikiene et al. 2015; karaman et al. 2018), antibacterial activity (cizeikiene et al. 2013; petkova et al. 2021), antifungal activity (demirbaş et al. 2017; quattrini et al. 2019). in addition, low ph resulting from lab’s acid production increases the activities of amylases and proteases present in the flour, thus contributing to bread rheology and flavor via influencing gluten structure (yildirim-mavis et al. 2019). furthermore, antimicrobial and antifungal activities sourced from lab metabolites improve the shelf life and safety of the final sourdough bread (demirbaş et al. 2017). therefore, antifungal starter cultures have been successfully applied in bread (axel et al. 2016). another essential feature of sourdough fermentation is the stimulating impact on phytic acid degrading enzymes. phytic acid degradation leads to increased mineral, free amino acid, and protein bioavailability (gobbetti et al. 2014). many studies revealed strain dependency of lab characteristics (cizeikiene et al. 2013; melini and melini 2018; cizeikiene et al. 2015; ozturkoglubudak et al. 2016; demirbaş et al. 2017). in this study, five lab species among 17 isolates of sourdoughs were selected via 16s rdna gene sequencing and ft-ir spectroscopy. the study aims were to assess the technological and nutritional characteristics of selected lab. for this purpose, antibacterial, antifungal, proteolytic, phytase activities and effects of these labs were analysed. experimental bacterial strains and growth conditions lab strains used within the scope of this study were isolated from sourdoughs collected from four different regions of turkey. the type of flour, dough yield and depository used in the collected sourdoughs were given in table 1. each strain was grown in de man rogosa sharpe (mrs, merck kgaa, darmstadt, germany) medium for 24 h at 37 °c and under anaerobic conditions. five lab were chosen among 17 isolated bacteria based on 16s rdna gene sequencing and ft-ir spectroscopy for further analysis. table 1. the type of flour, dough yield and depository used in the collected sourdoughs. sourdough code flour type depository efficiency of sourdough 29gt-19 wheat and rye bakery 250 06b-2 wheat bakery 250 o6f-25 wheat bakery 250 kco-48 wheat home made 150 45mk-32 wheat bakery 250 ft-ir measurements the isolated sourdough lab strains were anaerobically cultivated on all purpose tween agar (apt) at 34 °c for 24 h. 25 μl of cell suspension of grown cells suspended and homogenized in 100 μl distilled water was placed on znse table and then dried at 40 °c. the spectral measurements were practiced by a tensor 27 spectrophotometer (bruker optic gmbh & co. kg, ettlingen, germany) equipped with an htsxt unit in the range of 600 – 4,000 cm-1 wavenumbers. the spectra of the isolates were processed using opus software (karaman et al. 2018). proteolytic activity of lactic acid bacteria milk agar plates, which include 28 g.l-1 skim milk powder, 5 g.l-1 casein peptone, 2.5 g.l-1 yeast extract, 1 g.l-1 glucose, and 15 g.l-1 agar were prepared to evaluate the proteolytic activity of lab strains. then, four 20 μl cell spots of lab strains were placed on the prepared agar, and plates were incubated anaerobically for 16 h at 37 °c. following 48 h incubation, proteolytic activity was indicated as clear zone surrounding lab cell spots (axel et al. 2016). nova biotechnol chim (2022) 21(2): e1155 2 quantitative determination of extracellular phytase activity of lab strains the phytase activities of lab isolated from sourdough samples were determined by adding 0.1 ml of the broth, including lab strains previously grown in fresh mrs medium into 4.9 ml modified mrs medium with 0.1 % naphytate and 0.2 % glucose. following incubation at 30 °c for 24 h, the lab cells were separated from the medium by centrifugation at 9,000 rpm at 4 °c. then, 250 μl cell-free supernatant and 250 μl substrate prepared by solving 2 mmol.l-1 naphytate in 0.1 mol.l-1 sodium acetate-acetic acid were mixed. the mixture was allowed for the reaction at 50 °c for 15 min. in order to cease the reaction, 500 μl of a 10 % (w/v) trichloroacetic acid (tca) solution was used. a mixture of 2.5 % (w/v) ammonium molybdate solved in a 5.5 % (v/v) sulfuric acid solution and 2.5 % (w/v) ferrous sulfate solution in the ratio of 4 : 1 was used to obtain the color reagent. kh2po4 at diverse concentrations were used as phosphorous source to form calibration curve. the absorbance values of samples were measured at 700 nm (yildirim and arici 2019). determination of the antibacterial activity of sourdough lab strains the antimicrobial activities of lab sourdough strains were determined by the method adapted from demirbaş et al. (2017). the inhibitory effects of lab were tested against four gram-negative pathogens; salmonella typhimurium atcc 0402, escherichia coli atcc 25922, pseudomonas aeruginosa atcc 27853, klebsiella pneumoniae atcc 06023 and four gram-positive pathogens; staphylococcus aureus atcc 25923, listeria monocytogenes atcc 13932, bacillus cereus atcc 11778, and bacillus subtilis atcc 6633. the isolated sourdough strains were grown overnight with 1 % inoculation in 10 ml of mrs broth to determine antibacterial activity. the grown cells in the culture were separated at 14,000 × g for 5 min, 4 °c by centrifugation. after the centrifuge, with a sterile 0.22 μm syringe filter, the supernatant was filtered to remove all bacteria cells that had remained in the supernatant. cell-free supernatant (cfs) was adjusted to ph 6.0 with naoh then treated with catalase (merck kgaa, darmstadt, germany) at 25 °c for 30 min. thus, possible inhibition effects of organic acids with h2o2 were eliminated. 20 μl supernatant was poured into the wells punched in tryptic soy agar plates where pathogen strains previously spread and allowed to incubate at 37 °c for 24 h. clear zones were measured as mm around the wells. determination of antifungal activities of sourdough isolates the lactic acid bacteria isolated from sourdough were grown at 37 °c for 24 h with 1 % inoculation in 10 ml of mrs broth. the suspensions were arranged at concentration 107 cfu.ml-1, and following the overnight growth, two 5 μl cell spots of lab strains were placed on the mrs agar plates, and plates were incubated anaerobically for 48 h at 37 °c. afterward, 10 ml of soft malt extract agar (2 % glucose, 0.8 % agar) at suitable temperature comprising 104 cfu.ml-1 penicillium carneum, aspergillus flavus, aspergillus niger were inoculated on lactic acid bacteria in plates and incubated for 2 – 3 d at 25 °c. after that, the antifungal activity was classified as no inhibitory (-), delayed spore formation with no clear zone of inhibition (+), delayed spore formation with the small clear zone of inhibition (++), delayed spore formation with the good clear zone of inhibition (+++), and broad inhibition on spore formation and mycelial growth with remarkable zones around a colony (++++) (demirbaş et al. 2017). ph decrease by lactic acid bacteria metabolites to determine the effect of metabolites produced by lab strains and ph decrease, cultures were grown with 1 % inoculation in 10 ml of mrs broth. the ph measurement was fulfilled after 3, 6, 9, and 24 h by ph meter (hanna instruments deutschland gmbh, vöhringen, germany). statistical analysis one-way analysis of variance (anova) followed by tukey’s test (p < 0.05) was used to determine the difference between strains depending on the measured characteristics. minitab version 17.3.1 (minitab, llc, state college, usa) and jmp 9 version was used for this purpose. each calculation 3 nova biotechnol chim (2022) 21(2): e1155 2 was given as mean ± standard deviation of three replicates. results ft-ir spectra of lab isolates ft-ir microspectroscopy was exploited to identify the microorganisms. this technique is particularly utilized to characterize lab in the microbiological field. this study provided a quick description of lab biodiversity in sourdough samples. lab identification was accomplished thanks to both 16s rdna gene sequencing and ft-ir spectroscopy at hts-xt module. as demonstrated in fig. 1, 16 lab isolates were clustered and obtained dendrogram gave five different groups. the groups have included 6 lactiplantibacillus plantarum, 5 levilactobacillus. brevis, 2 limosilactobacillus fermentum, 2 bacillus haynesii, 1 lactiplantibacillus pentosus, respectively. 16s-rdna based phylogenetic tree was formed as shown in fig. 2 attributed to the dendrogram. therefore, 5 different lactobacillus species, which are levilactobacillus brevis kco-48, lactiplantibacillus plantarum 06f-25, companilactobacillus paralimentarus 06b-2 and limosilactobacillus fermentum 29gt-19 and lactiplantibacillus plantarum 45mk-32 were selected. then, these species were tested for their technological characteristics. fig 1. dendrogram obtained based on ftir spectra of the isolated lab. spectral ranges: 600 – 3,996 and 3,032 – 2,829 cm-1. ward’s algorithm and correlation with standard (euclidean distance). 4 nova biotechnol chim (2022) 21(2): e1155 2 fig 2. phylogenetic tree for 17 isolates based on 16s rdna gene sequencing. phylogenetic reconstruction was generated via neighbor-joining method with a length of 406 nucleotides, 16s rdna fragments. the count of bootstrap replicates is 2,000. bootstrap values higher than 70 % are displayed. the bar shows the length corresponding to 0.1 nucleotide substitution. determination of proteolytic activity five lab were screened for their protease activity on casein-containing plates. the proteolytic activities of lab isolates were determined by measuring clear zone diameter derived from protease enzymes produced by lab on skim milk agar. lab isolates studied except levl. brevis kco-48 demonstrated proteolytic activity. clear zone diameters ranged from 9.97 to 12.60 mm as stated in table 2. table 2. proteolytic activity diameters of clear zones. microorganisms clear zone diameter [mm] levl. brevis kco-48 liml. fermentum 29gt-19 10.0 ± 0.00b lpb. plantarum 06f-25 10.0 ± 0.00b coml. paralimenterius 06b-2 10.0 ± 0.00b lpb. plantarum 45mk-32 12.6 ± 0.29a a-bdifferent letters indicates the significant differences between the selected strains (p < 0.05). the highest proteolytic activity was produced by lpb. plantarum 45mk-32. differences in proteolytic activities of liml. fermentum 29gt-19, lpb. plantarum 06f-25, coml. paralimenterius 06b-2 were negligible (p ˃0.05). extracellular phytase activity extracellular phytase activity of lab isolated from sourdough were determined exploiting the addition of sodium phytate as substrate to mrs broth and release of phosphorous compound by phytase activity produced by lab. as shown in fig. 3, the phytase activities were found between 710 u.ml-1 and 841 u.ml-1. the lab strain with the highest phytase activity is levl. brevis kco-48 with the value of 840.6 u.ml-1 whereas the lowest phytase activity occurred by liml. fermentum 29gt-19 with the value of 710.4 u.ml-1. the phytase activities of lpb. plantarum 45mk-32 and lpb. plantarum 06f-25 were found 825.2 and 821.67 u.ml-1, respectively. the phytase activity of coml. paralimentarius was detected similarly to the lpb. plantarum species. no significant difference was found among phytase activities of lab studied in the study, excluding liml. fermentum 29gt-19. 5 nova biotechnol chim (2022) 21(2): e1155 2 fig. 3. extracellular phytase activities of lab isolates (u.ml-1). a-nwithin the column, the letters indicate that there is significant difference between the strains (p < 0.05). antimicrobial activity of lab against pathogens in this study, the antimicrobial capacity of neutralized and catalase-treated cell-free supernatants (cfs) of lab growth media was tested against 8 pathogenic bacteria to determine the inhibitory action of bacteriocin-like inhibitory substances (blis). in agar well diffusion method, clear zone diameter has been studied to determine the antimicrobial activity. the zone diameters of the inhibition area were given in table 3 and the figure of the lpb. plantarum strain that creates the best antimicrobial zone is given in fig. 4. table 3. antimicrobial activity of cfs of lab strains against pathogenic bacteria. pathogens zone of inhibition [mm] liml. fermentum 29gt-19 lpb. plantarum 06f-25 coml. paralimenterius 06b-2 levl. brevis kco-48 lpb. plantarum 45mk-32 k. pneumoniae atcc 06023 10.0 ± 0.00 a 10.0 ± 0.00 a 10.0 ± 0.00 a 10.0±0.00 a 10.0±0.00 a p. aeruginosa atcc 27853 nd 10.0 ± 0.00 a nd nd nd b. subtilis atcc 6633 10.2 ± 0.03 a 10.0 ± 0.00 a 10.0 ± 0.00 a 10.0 ± 0.00 a 10.0 ± 0.00 a l. monocytogenes atcc 13932 12.0 ± 0.00 a 11.6 ± 0.03 b 10.0 ± 0.00 e 10.2 ± 0.03 d 11.0 ± 0.00 c b. cereus atcc 11788 12.0 ± 0.00 d 13.2 ± 0.03 a 12.8 ± 0.03 b 10.8 ± 0.03 e 12.6 ± 0.03 c s. typhimurium atcc 0402 12.0 ± 0.00 a 12.0 ± 0.00 a 11.8 ± 0.03 b 11.0 ± 0.00 d 11.6 ± 0.03 c e. coli atcc 25922 10.0 ± 0.00 a 10.0 ± 0.00 a 10.0 ± 0.00 a 10.0 ± 0.00 a 10.0 ± 0.00 a s. aureus atcc 25923 12.2 ± 0.03 a 12.2 ± 0.03 a 11.8 ± 0.03 b 11.8 ± 0.03 b 10.0 ± 0.00 c a-b different letters indicates the significant differences between the selected (p < 0.05). nd – no inhibition zone was detected. 6 nova biotechnol chim (2022) 21(2): e1155 2 all bacteria displayed mild or moderate inhibition of pathogens. the highest antimicrobial activity of the supernatants was detected against b. cereus atcc 11778. lpb. plantarum 06f-25 was only strain that inhibits all pathogens. p. aeruginosa inhibited only by lpb. plantarum 06f-25 metabolites has become the most resistant bacteria. the highest zone diameters were observed against b. cereus atcc 11778 by lpb. plantarum 06f-25, coml. paralimentarius 06b-2, lpb. plantarum 45mk-32. even though lpb. plantarum 06f-25 and lpb. plantarum 45mk-32 are the same species, they have differed in antibacterial effect against 6 out of 8 pathogens. lab were found more efficient on gram-positive pathogens than gramnegative pathogens. s. typhimurium atcc 0402 was the least resistant gram-negative pathogen with an average 11.7 mm zone diameter. however, the zone diameters resulted from cfs on other gramnegative bacteria ≤ 10 mm. the lowest inhibition on gram-positive pathogens was observed on b. subtilis atcc 6633 with an average 10.0 mm zone diameter. fig. 4. figure of best zone measurement. antifungal activities of lactic acid bacteria the influence of lab grown in mrs broth on several mould species such as penicillium carneum, a. flavus, and a. niger was analyzed to test antifungal activity. their effects on the moulds were given in table 4. p. carneum was not inhibited by lab. even though any lab did not have any antifungal effect on p. carneum, all tested lab inhibited a. flavus. all lab excluding coml. paralimentarius 06b-2 also showed inhibitory impact on aspergillus niger. the highest inhibitory impact was demonstrated against a. flavus and a. niger by coml. paralimentarius 06b-2 and liml. fermentum 29gt-19. lpb. plantarum species 45mk-32 and 06f-25 demonstrated lower inhibitory action with a small clear zone with delayed spore formation than liml. fermentum and levl. brevis against a. niger. 7 nova biotechnol chim (2022) 21(2): e1155 2 table 4. inhibition of several moulds by lab isolates. microorganisms inhibitory spectrum of lab supernatants penicillium carneum aspergillus flavus aspergillus niger liml. fermentum 29gt-19 ++ ++++ lpb. plantarum 06f-25 ++ + coml. paralimenterius 06b-2 ++++ levl. brevis kco-48 +++ +++ lpb. plantarum 45mk-32 ++ + the mould inhibition of lab was classified as; (-) no inhibition, (+) spore formation delayed but no clear zone, (++), spore formation delayed with a small clear zone around the colony, (+++) spore formation delayed with good clear zone around the colony, (++++) extensive inhibition of spore formation and mycelial growth with definite clear zones around colonies. ph decrease due to the metabolites produced by lab the ph values of mrs broths including lab isolates were measured every 3 h in the first 9 h and 24th h. the measurement results were given in table 5. all lab have a strong impact on the ph value of the mrs broth medium. whereas initial ph values of broths ranged between 6.51 and 6.56, the last ph of broths varied from 3.83 to 4.41. the highest decrease in ph value by 3.83 was observed in lpb. plantarum 45mk-32 containing broth. liml. fermentum 29-gt-19 was found the least effective strain on ph. table 5. ph decreasing effect of lab. microorganisms time [h] 3 h 6 h 9 h 24 h lpb. plantarum 06-f25 6.38 ± 0.02aba 6.18 ± 0.02bb 5.14 ± 0.02dc 4.04 ± 0.01cd levl. brevis k-co48 6.40 ± 0.03aba 6.36 ± 0.02aa 6.09 ± 0.02ab 3.92 ± 0.03dc coml. paralimenterius 06-b2 6.27 ± 0.03ca 6.00 ± 0.03cb 5.31 ± 0.02cc 4.33 ± 0.03bd liml. fermentum 29-gt19 6.29 ± 0.03bca 6.04 ± 0.02cb 5.39 ± 0.03cc 4.41 ± 0.02ad lpb. plantarum 45-mk32 6.41 ± 0.03aa 6.37 ± 0.02aa 5.70 ± 0.02bb 3.83 ± 0.01ec * capital letters – differences in uppercase letters indicate significant difference (p < 0.05) in a row. * small letters – differences in lowercase letters indicate significant difference (p < 0.05) in a column. discussion ft-ir analysis is a thought reliable method to identify bacteria and yeast with chemometric techniques (wenning and scherer 2013). ft-ir analysis was conducted on 17 sourdough lab isolates brought from 7 different regions of turkey. first derivatives of the obtained spectra included in 1,500 – 1,200 cm-1, 1,200 – 900 cm-1, 900 – 700 cm-1 spectral regions were utilized to differentiate spectra of lactobacillus species that had been studied before (akman et al. 2021). in this study, lab isolated from sourdough samples was chosen exploiting ft-ir cluster analysis, which gives faster results than rapd-pcr. according to the cluster analysis, 16 lab isolates were genotypically identified. based on 16s rdna sequencing, among 17 lab, 9 lpb. plantarum, 2 levl. brevis, 1 liml. fermentum, 1 coml. paralimentarius, and 4 bacillus haynesii were determined. in addition, 16s rdna-based phylogenetic tree of lab isolates using the neighbor-joining method presented the conformable phylogenetic cluster. whereas 45mk32 and 06f-25 isolates were clustered on the same branch, 29gt-19, kco-48, and 06b-2 isolates were clustered on distinct branches. the similarity of lpb. plantarum isolates were specified by phylogenetic clustering. it was concluded that cluster analysis of 17 lab isolates was consistent with grouping attributed to 16s rdna and separated these isolates into different groups phylogenetically. proteolytic activity has an important role in the quality of bread. proteolysis derived from lab increases amino acid amount in sourdough; hence, it affects flavor development by reaction between amino acids and reducing sugar during baking (gilcardoso et al. 2021), and atanasova et al. (2014) found that the antimicrobial-active peptides were 8 nova biotechnol chim (2022) 21(2): e1155 2 formed by lab grown in goat milk. lab isolated from yogurt samples and described by biochemical and morphological analysis for their proteolytic activities were studied, and it was found that all lab isolates have proteolytic activities (phyu et al. 2015). moreover, axel et al. (2016) investigated lab isolated from sourdough samples and the lowest proteolytic activity were detected in levl. brevis incompatible with the finding in our research. two different lpb. plantarum strains 45mk-32 and 06f-25 have different clear zone diameters displaying that proteolytic activity of lab is strain-specific. microbial acidification provides favorable environment (ph 3.5 – 4.0) for aspartic proteinases (gänzle et al. 2008). hence, extracellular proteinases of lab are influenced by medium ph. lpb. plantarum 45mk-32, which has the highest proteolytic activity in our study, was the most efficient to alter the ph of mrs medium leading to the formation of favourable conditions for proteinase activity. whole meal bread consumption has remarkably increased since awareness of its nutritionally valuable components, such as dietary fibers, vitamins, minerals, complex carbohydrates, and proteins (mohammadi‐kouchesfahani et al. 2019). however, phytic acid, the major phosphorus form in cereal grains including wheat, impedes the absorption of fe+2, zn+2, ca+2, mg+2, cu+2, and mn+2; thus, mineral deficiencies are promoted (ficco et al. 2009; liu et al. 2019). lab does not degrade phytate directly; however, it presents favourable conditions by decreasing ph for extracellular phytase activity (reale et al. 2007). nevertheless, some studies have been conducted which indicate intracellular phytase activity of lab (nuobariene et al. 2015; yildirim and arici 2019). in the study conducted by karaman et al. (2018) the extracellular phytase activities of lab strains obtained from sourdough were found to range from 703.1 u-ml-1 to 1153.8 u-ml-1. yildirim and arici (2019) also examined 64 lab isolates from sourdough in terms of extracellular phytase activity. the results varied between 725.58 u-ml-1 and 803.95 u-ml-1 in accordance with the results in our study. sourdough bread consumption offers health-promoting effect since lab can degrade phytate in whole wheat flour which contains high amount of phytate. therefore, the decrease in mineral uptake can be prevented (lopez et al. 2003; rizzello et al. 2017). furthermore, lab's phytase activity benefits the small intestine via decomposing the remaining phytate (haros et al. 2009). moreover, the usage of phytase-active lab enables to minimize antinutritional characteristics of animal feeding (humer et al. 2015). it is a fact that lab's antimicrobial characteristics can be exploited to prevent spoilage of foods and kill pathogenic bacteria and the benefits in the large intestine as probiotic. lab produces organic acids, hydrogen peroxide, diacetyl, and bacteriocin-like inhibitory substances which inhibit bacterial growth. bacteriocins can promote invasion of beneficial strains in the gastrointestinal tract via inhibiting competing or pathogen strains; hence, the microbiota and host immune system are regulated (arqués et al. 2015). in our study, almost all lab showed an inhibitory effect on common pathogens following neutralization and catalase treatment. bacteriocin-producing ability of 437 lab isolated from 70 sourdough samples were tested (petkova et al. 2021). whereas 85 of these strains are effective on indicator organisms without removing acids and other antimicrobial agents in cell-free supernatant (cfs), only five lab strains inhibited indicator organisms after neutralization, catalase treatment and sterilization by filtration. venkadesan et al. (2015) investigated the antimicrobial effect of 9 lab isolated from milk products on different pathogens. liml. fermentum strains led to moderate inhibition on e. coli, s. aureus and s. typhi and l. monocytogenes atcc 13932 while lpb. plantarum showed weak inhibition. cizeikiene et al. (cizeikiene et al. 2013) analyzed five lab isolated from rye sourdough to specify their antimicrobial effect against 23 pathogenic bacteria, including b. cereus, b. subtilis, various pseudomonas spp., staphylococcus aureus, listeria monocytogenes, e. coli, and salmonella spp. strains, the results showed that the blis of all lab studied inhibited b. subtilis strains whereas no inhibitory effect was detected on other studied pathogens moreover, our study is consistent with the studies maintaining mild, low, or no inhibitory impact of lab metabolites on well-recognized pathogens. consequently, the antimicrobial capacity of lab supernatants without acid and h2o2 removal is considerable; however, catalase treated and neutralized cfs influence on pathogenic bacteria is limited. 9 nova biotechnol chim (2022) 21(2): e1155 2 mould growth is a major spoilage reason for bakery products. the most prevalent mould species are aspergillus, fusarium, and penicillium. biopreservation techniques have been considered one of the main strategies to prevent spoilage owing to the chemical-free food demand of society (melini and melini 2018). lab produces various antifungal compounds such as organic and carboxylic acids, reuterin, fatty acids, and cyclic dipeptides (crowley et al. 2013). sevgi and tsveteslava (2015) reported that six different lpb. plantarum strains retarded a. niger growth. in our study, lpb. plantarum strains showed mild inhibitory effect by delaying spore formation on a. niger growth and their antifungal impacts were expressed as clear zone diameter around the lab colonies. moreover, demirbaş et al. (2017) found that lpb. plantarum has a moderate impact on a. niger with a small clear zone. kivanc et al. (2011) analyzed 45 different lab against 7 mould species by means of dual agar overlay and well method, levl. brevis strains studied have clear inhibition zone around the colonies against a. flavus in accordance with levl. brevis kco-48 inhibitory impact on a. flavus. antifungal action of lab depends on mould species. although coml. paralimenterius showed the highest antifungal effect on a. flavus, it did not demonstrate any inhibiting impact on penicillium carneum and aspergillus niger. it was suggested that the metabolites produced by lab inhibited mould growth and extended shelf life, thus demonstrating that lab could be exploited as biopreservative (muhialdin et al. 2011). similarly, liml. fermentum 29gt-19 showed extensive inhibition on a. niger with a good clear zone and delayed spore formation and moderate inhibition on a. flavus. the results showed that lab inhibits a. niger and a. flavus differently depending on mould and lab species. penicillium carneum is the most resistant mould against all studied lab. antifungal metabolites producing lab could be utilized as biopreservative in bakery products. conclusion in summary, lab isolates isolated from sourdough samples were tested for some technological and nutritional properties. these strains had antagonistic effects against pathogenic bacteria. they tend to degrade and multiply phytic acid that binds minerals. therefore, they have the potential to improve human health and product quality. it can be said that bioactive peptides and aroma compounds inhibit mould growth and lower the ph as much as preventing the survival of pathogens and spoilage microorganisms. the superior properties of lab differentiate from each other. levl. brevis kco-48 demonstrated the highest phytase activity, lpb. plantarum 06f-25 was only lab that inhibits all tested pathogens. lpb. plantarum 45mk-32 have the highest proteolytic activity and highest ph decreasing effect. liml. fermentum 29gt-19 and levl. brevis kco-48 were most effective to hinder mould growth and spore formation considering total effects on studied moulds. the studied lab can be exploited to promote human health and develop/preserve food quality when taking all their characteristics into account. moreover, the utilization of these lab as combination have promised functional products since they may meet different requirements in terms of product quality. acknowledgments this study was partly funded by the scientific research projects of yildiz technical university with the grant number fdk-2020-3885. we thank hakan dogan and danedolu team for their assistance in providing the sourdough samples. 12 conflict of interest the authors declare that they have no conflict of interest. references akman pk, ozulku g, tornuk f, yetim h (2021) potential probiotic lactic acid bacteria isolated from fermented gilaburu and shalgam beverages. lwt. 149: 111705. arqués jl, rodríguez e, langa s, landete jm, medina m (2015) antimicrobial activity of lactic acid 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m, scherer s (2013) identification of microorganisms by ftir spectroscopy: perspectives and limitations of the method. applied microbiol. biotechnol. 97: 7111-7120 yildirim rm, arici m (2019) effect of the fermentation temperature on the degradation of phytic acid in wholewheat sourdough bread. lwt 112: 108224. yildirim-mavis c, yilmaz mt, dertli e, arici m, ozmen d (2019) non-linear rheological (laos) behavior of sourdough-based dough. food hydrocoll. 96: 481-492. 12 1 microsoft word luptakova nb.doc nova biotechnologica vii-i (2007) 17 importance of sulphate-reducing bacteria in environment alena luptakova department of mineral biotechnologies, institute of geotechnics of slovak academy of sciences, watsonova 45, sk-043 53 kosice, slovak republic (luptakal@saske.sk) abstract: the sulphate-reducing bacteria represent the part of the biosphere, the active component in the cycle of elements in the biosphere and as shown by the existing knowledge they are becoming also the part of the environmental industrial technologies. the objective of this work was to give principal information concerning characteristics, the occurrence and the importance of sulphate-reducing bacteria in environment. key words: sulphate-reducing bacteria, sulphuretum, heavy metals 1. introduction sulphate-reducing bacteria (srb) are a ubiquitous group of anaerobic prokaryotes. they are unified by a shared ability to carry out sulphate reduction as a principal component of their bioenergetic processes. they are found in diverse environments and are of great utilitarian and academic interest. their practical importance arises from both economic and environmental concerns. srb are of significant economic interest in many industrial sectors. their academic importance arises from the unique ecological and evolutionary roles they play. sulphate reducers are important organisms in many anaerobic environments in nature, and their physiological activities are of profound importance for many ecological communities. furthermore, there is increasing biochemical and genetic evidence suggesting that these organisms began evolutionary divergence at an early time. this long evolutionary history has led to development in these organisms of a variety of unique proteins and biochemical processes with profound academic importance and fundamental insights. 1.1 characteristics of sulphate-reducing bacteria the srb represents a group of chemoorganotrophic and strictly anaerobic bacteria that may be divided into four groups based on rrna sequence analysis (castro et al., 1999): gram-negative mesophilic srb, gram-positive spore forming srb, thermophilic bacterial srband thermophilic archaeal srb. they include genera such as desulfovibrio, desulfomicrobium, desulfobacter, desulfosarcina, desulfotomacullum, thermodesulfobacterium, archaeoglobus, etc. the basic metabolic process of srb is the anaerobic reduction of sulphates in which organic substrate (lactate, malate, etc.) or gaseous hydrogen is the electron donor and sulphate is the electron acceptor. considering the inorganic or organic 18 luptakova, a. character of energy source of srb there are two types of anaerobic respiration of sulphates (odom and rivers singleton, 1993): 1. authotrophic reduction of sulphates – the energy source is a gaseous hydrogen, the reaction proceeds in several stages and the whole process can be summarily expressed by equation (1): srb 4 h2 + so4 2 ⎯⎯⎯→ s2+ 4 h2o (1) 2. heterotrophic reduction of sulphates – the energy sources are simple organic substances (lactate, fumarate, pyruvate, some alcohols and the like). depending on the final product of organic substrate oxidation we know: incomplete heterotrophic oxidation of organic substrate in which the final product is acetate (equation 2): srb 2 ch3chohcoo + so4 2 ⎯⎯⎯→ 2 ch3coo+ 2 hco3+ h2s (2) complete heterotrophic oxidation of organic substrate in which the final products are co2 and h2o (equation 3): srb 4 ch3cocoona + 5 mgso4 → 5 mgco3 + 2 na2co3 + 5 h2s + 5 co2 + h2o (3) in the process of anaerobic respiration of sulphates srb produce a considerable quantity of gaseous hydrogen sulphide (h2s) which reacts easily in the water medium with heavy metal cations forming not easily dissoluble sulphides of the given metals (equation 4): me2+ + h2s ⎯⎯⎯→ mes + 2h+ (me2+ metal cation) (4) the typical species of srb is desulfovibrio desulfuricans (fig. 1). fig. 1. scanning electron micrograph of desulfovibrio desulfuricans (luptáková, 2002) 1.2 occurrence of sulphate-reducing bacteria srb are a unique and ubiquitous group of prokaryotic mo, found in a variety of anaerobic environmental niches such as: soil (ronald, 1995), nova biotechnologica vii-i (2007) 19 mud and sediments of freshwaters (rivers, lakes, …), thermal or no-thermal sulphur springs (karavajko et al., 1988, ho-yong j. et al., 1996), mining waters from sulphide deposits (groudeva and groudev, 1997), waters from deposits of mineral oil and natural gas (armstrong et al., 1995), industrial waste waters (metallurgical industry (luptáková, 2002), sea and ocean (postgate, 1982), gastrointestinal tract of man and animals (sneath et al., 1996). 1.3 importance of sulphate-reducing bacteria the metabolic actions of srb described by equations 1-4 are the fundamental of srb importance in environment. they are generator of many processes both positive and negative. despite the odoriferous physiology of these organisms, they are important to study for both practical and academic reasons. their practical importance stems from the significant economic impact they have in many industrial and ecological areas. their academic importance is related to their unique environmental and evolutionary roles in nature. because srb are ubiquitous to oil-bearing shale and strata they play an important economic role in many aspects of oil technology (dockins et al., 1980). they are responsible for extensive corrosion of drilling and pumping machinery and storage tanks. furthermore, because they contaminate resulting crude oil the organisms cause release of hydrogen sulphide into petroleum products, thereby increasing the sulphur level of fuels. they are also important in secondary oil recovery processes, where bacterial growth in injection waters can plug machinery used in these processes. it has also been suggested that these organisms may play a role in biogenesis of oil hydrocarbons. for all of these reasons srb are of vital importance in petroleumproducing and processing-industries (postgate, 1982). a major economic consequence resulting from the metabolic action of srb is anaerobic corrosion of underground buried ferrous metals such as tanks and pipelines. srb play a vital role in a variety of other important economic areas. in many industrial processes they produced iron sulphides, thereby causing blackening and discoloration of products. for example, in the paper industries srb can contaminate processing water, leading to sulphide production, which causes blackening of paper (odom and rivers singleton, 1993). 1.4 environmental importance of srb these organisms are also of great ecological importance, which is in part related to their economic importance. pivotal ecological roles of srb result from their participation in the sulphur cycle, which is a major biogeological cycle in nature. sulphur is widely distributed on earth and occurs predominantly bound as sulphides in the form of sulphates or even as elemental sulphur. in nature sulphur circulates permanently because it is continuously oxidized or reduced by chemical or biological processes. in such a biogeochemical sulphur cycle (fig. 2) the biological transformations may have either assimilatory or dissimilatory metabolic functions. 20 luptakova, a. with the exception of animals and humans, most plants, fungi and bacteria are capable of performing an assimilatory reduction of sulphate to sulphide which is necessary for the biosynthesis of sulphur containing cell compounds. on the other hand the energy producing dissimilatory sulphur metabolism is restricted to a few groups of bacteria. these groups include mo such as: anaerobic dissimilatory sulphate reducers (desulfovibrio, desulfotomaculum, desulfomonas,….), anaerobic dissimilatory sulphur reducers (desulfuromonas, beggiatoa,….), anaerobic phototrophic sulphur oxidisers (some cyanobacteria and most anoxygenic phototrophic bacteria), aerobic chemotrophic sulphur oxidisers (thiobacillus, sulfolobus, thiospira, thiobacterium,….), anaerobic chemotrophic sulphur oxidisers (thibacillus denitrificans, thiomicrospira denitrificans,..) (rehm and reed, 1981). fig. 2. the biological sulphur cycle (rehm and reed, 1981). 1 assimilatory sulphate reduction by plants, fungi and bacteria; 2 death and decomposition by fungi and bacteria; 3 sulphide assimilation by bacteria and some plants; 4 excretion of sulphate by animals; 5 dissimilatory sulphate-reducing bacteria; 6 dissimilatory sulphur-reducing bacteria; 7 phototrophic and chemotrophic sulphide-oxdizing bacteria; 8 phototrophic and chemotrophic sulphur-oxidizing bacteria. fig. 3. schematic diagram illustrating the chemical processes of a sulphuretum (odom and rivers singleton, 1993) as can be seen from fig. 2 the srb miss the assimilatory part of the cycle and produce sulphides. the microbial population of this dissimilatory part is called 8 4 so4 2 biologically bound sulphur s0 s2 1 5 2 3 7 6 assimilatory dissimilatory part accumulates 0 aerobic sulphur-oxidisers (at top) so42 feeds in hs srb hs anaerobic sulphate-reducers (at bottom) diffusion so42so42nova biotechnologica vii-i (2007) 21 “sulphuretum” and its activity from the chemical processes point of view is shown in fig. 3. sulphate ion from the surrounding land mass is leached into and diffuses to the bottom of these small aquatic systems, where it is reduced to s2by anaerobic sulphate-reducing bacteria. sulphite ion then diffuses upward through the water column to the surface layers, where it is oxidized by aerobic organisms to either elemental sulphur (s0) or so4 2-. the latter diffuses to the bottom, anaerobic region where the cycle continues. because of its low solubility in water, however, s0 precipitates from solution and forms a yellow crust on the water surface and near the edges of these systems. the activity of sulphuretum is a basis of many processes in nature and it finds its application in industry, for example: the removal of heavy metals from industrial waste waters (e.g. acid mine drainage) (kontopoulos, 1998; boonstra et al., 1999), the removal of so42from mine waters (kontopoulos, 1998; glombitza, 2001) , the production of sulphur from waste waters (postgate, 1982), the removal of sulphur from crude oil, petrol and coal (desulphurization) (armstrong, 1997). 1.5 evolutionary importance of srb there appears to be clear geochemical evidence that process of biological sulphate reduction is evolutionarily ancient. this conclusion grows from the observation that bacterial reduction of sulphate shows a kinetic isotope effect in which 32so4 2is used more rapidly than the heavier isotope 34so4 2-. consequently, geological sulphur deposits that are enriched in the lighter isotope, relative to the heavier isotope are believed to be biological in origin. evidence of this nature suggests that many of the world´s sulphur reserves were biologically formed and that this action occurred prior to significant accumulation of atmospheric oxygen. this line of reasoning clearly suggests that the process of sulphate reduction was of bioenergetic significance before the process of oxygen reduction. present arguments suggest that development of dissimilatory sulphate reduction occurred between 2.8 and 2.5 x 109 years ago and was simultaneous with oxygenic photosynthesis by ancestral cyanobacteria but prior to aerobic respiration (widdel, 1988). 2. conclusion this paper attempts to give the notion that srb were unified by shared ability to utilize sulphate reduction as an important component of their bioenergetics processes. srb represent the part of the biosphere, the active component in the cycle of elements in the biosphere and as shown by the existing knowledge they are becoming also the part of the environmental industrial technologies. these bacteria are extremely diverse from metabolic, morphological, antigenic as well as ecological perspectives. this diversity will have profound implications for our understanding of the environmental and economic role that these bacteria play in the natural world. 22 luptakova, a. acknowledgment: this work was supported by the slovak research and development agency under the contract no. apvv-51-027705 and grant agency vega for project no. 2/5148/27. references armstrong, s.m., sankey, b.m., voordouw, g.: converzion of dibenzothiophene to biphenyl by sulfate-reducing bacteria isolated from oil field production facilities. biotechnol. lett., 17, 1995, 1133-1136. armstrong, s.m., sankey, b.m., voordouw, g.: evaluation of sulfatereducing bacteria for desulfurizing bitumen or its fractions. fuel, 76,1997, 223227. boonstra, j., van lier, r., janssen, g., dijkman, h., buisman, c. j. n.: biological treatment of acid mine drainage. in: r. amils, a. ballester (eds.) biohydrometallurgy and the environment toward the mining of the 21st century, (eds.). elsevier, amsterdam, 1999, 559-566. castro, h. f., williams, n. h., ogram, a.: phylogeny of sulphate-reducing bacteria. fems microbiol. ecol., 31, 1999, 1-9. dockins, w. s., olson, g.j., mcfeters, g. a., turbak, s. c.: dissimilatory bascterial sulphate reduction in montana ground water. geomicrobiol. j., 2, 1980, 83-98. glombitza, f.: treatment of acid lignite mine flooding water by means of microbial sulfate reduction. waste manag., 21, 2001, 197-203. groudeva, v.i., groudev, s.n.: bioremediation of acide drainage waters. proceedings of international biohydrometallurgy symposium. sydney, australia, 1997, 4-7. jin, h. y., lee, d. h., zo, y. g., kang, c. s., kim, s. j.: distribution and activity of sulfate-reducing bacteria in lake soyang sediments. j. microbiol., 34, 1996, 131-136. karavajko, g. i., rossi, g., agate, a. d., groudev, s. n., avakyan, z. n.: biotechnology of metals, centre of projects gknt, moscow, 1988, 59 pp. kontopoulos, a.: acid mine drainage control. in: effluent treatment in the mining industry, univesity of concepcion, chile, 1998, 57 pp. luptáková, a., kušnierová, m., fečko, p.: minerálne biotechnológie ii., sulfuretum v prírode a v priemysle. es všb – technická univerzita ostrava, 2002. odom, j. m., rivers singleton, j. r.: the sulfate-reducing bacteria: contemporary perspectives, springer-verlag, new york, 1993. postgate, j.: mikróby a my, praha, pyramída, 1982. rehm, h.j., reed, g.: biotechnology, vol. 6b, verlag chemie gmbh, weuheim, 1981, 473-475. ronald, m. a.: principles of microbiology, mosbi -year book, 1995. sneath, p.h., mair, n.s., sharpe, m.e., holt, j.g.: bergey´s manual of systematic bacteriology, vol. 2, vol. 8, sydney, 1200-1202, 1996, 663-679. widdel, f.: microbiology and ecology of sulphateand sulphurreducing bacteria. in: a.j.b zehner (ed.) biology of anaerobic organisms, john wile, new york, 1988, 469-585. nova biotechnol chim (2022) 21(2): e1226 doi: 10.36547/nbc.1226 1 nova biotechnologica et chimica optimization of procedural factors for advanced xylanase synthesis by lysinibacillus fusiformis using kolanut husk as substrate suliat olatidayo omisore, daniel juwon arotupin, michael tosin bayode department of microbiology, federal university of technology, p.m.b. 704, akure, nigeria  corresponding author: omisore34@gmail.com article info article history: received: 13th october 2021 accepted: 1st december 2022 keywords: kolanut husk lysinibacillus fusiformis optimization substrate xylan xylanase abstract xylan is a complex hetero-polysaccharide consisting of different monosaccharides held together by glycosidic and ester bonds. extracellular xylanase fashioned by numerous microbes principally from bacterial species such as bacillus species are responsible for cleaving the glycosidic linkages. microbial xylanases exhibit different substrate specificities and biochemical peculiarities. this study was carried out for optimization of cultivation conditions for xylanase production using the bacterium lysinibacillus fusiformis and kolanut husk as a component of cultivation medium. the bacterium was isolated from kolanut plantation waste soil and screened for the production of xylanase qualitatively on xylan nutrient agar and quantitatively under submerged fermentation. the different conditions optimized included substrate concentration, additional sugars, incubation period, temperature, initial ph, nitrogen supplementation and inoculum mass through one factor at a time approach. maximum xylanase production was obtained at substrate concentration of (1 % xylan and 1.5 % kolanut husk), nitrogen source (yeast extract plus peptone), carbon source (sucrose), incubation period (24 h), ph (5.0), temperature (35 oc) and inoculum size (1 %). lysinibacillus fusiformis has been proven to be a promising bacterium for xylanase production using kolanut husk as substrate. the use of kolanut husk as foremost carbon source is predominantly precious as being an agricultural waste, affordable, and locally available compared to expensive commercially sold xylan. introduction hemicellulose serves as the second most ample source of polysaccharides in nature, exhibiting 25 % 30 % of the dry weight of lignocellulose biomass (coman et al. 2011; walia et al. 2015). it is the major amount of lignocellulose, comprising of varied 5and 6-carbon sugars such as arabinose, galactose, glucose, mannose, and xylose (girisha 2018). xylan is a polymer of xylose molecules which plays the pivotal role in holding the plant cell walls together (irfan et al. 2016; girisha 2018). considerable xylanolytic enzymes comprising α-arabino-furanosidase, act collectively for total disintegration of xylan. the most important endo β1, 4-xylanase plays an imperative part to catalyze the breakdown of xylan into diminutive oligosaccharides (irfan et al. 2012; khusro et al. 2016). udey et al. (2016) reported the latent applications of xylanase in numerous fields such as saccharification of lignocellulosic biomass for ethanol and xylo-oligosaccharides generation in the biofuel industry. its use as a fading agent and mailto:omisore34@gmail.com nova biotechnol chim (2022) 21(2): e1226 2 lighting up of pulp to reduce chlorine in paper and pulp production operations was also reported (raghukumar et al. 2004; sridevi et al. 2016; patel and dudhagara 2020a). it helps in the smooth relocation of the water core in bread dough ensuring a softer dough formation (beg et al. 2001; garg et al. 2010). furthermore, xylanolytic enzymes have been reported by garg et al. (2010) for its application in the animal industry for the conversion of lignocellulose into feedstocks and fuels. xylanases are produced by a diverse number of microbes such as bacteria, fungi and actinomycetes (battan et al. 2006; chakdar et al. 2016; ramanjaneyulu et al. 2017). however, xylanases from bacteria are the most-preferred for industrial applications due to thermo-stability and ability to withstand alkali-substrates (nagar et al. 2013; aarti et al. 2015; mandal et al. 2015). xylanolytic bacteria are the generally striking producers of high-level extracellular xylanase as compared to fungi and actinomycetes, which have timeconsuming generation time alongside the production of extremely glutinous polymers and deprived oxygen transport. there is limited exploitation of xylanase commercially due to its high cost of production. in this view, the search for cost-effective means of production, such as the use of low-cost agro agricultural residues has captivated the attention of scientists (patel and dudhagara 2020b). gautério et al. (2020) and ratnadewi et al. (2020) also buttressed the utility of agriculture waste derivatives like wheat bran, corn cobs, rice straw for exploitation as a lowgrade substrate for xylanase production. kolanut husk alongside its testa has been proven as a budding substrate to produce the microbial enzyme particularly xylanase (fabunmi et al. 2018). therefore, the study was carried out to determine the optimal process parameters needed to improve the yield of xylanase produced from simple inexpensive kolanut husk using lysinibacillus fusiformis. in biotechnological process, the best results are achieved when the individual and combined effects of parameters involved are considered (tandon et al. 2016). the current study aims at optimizing the cultural conditions such as carbon source, nitrogen supplementation, temperature, incubation time and inoculum sizes for xylanase production by lysinibacillus fusiformis, an isolate of kolanut plantation waste soil using a medium with kolanut husk as substrate in other to know the best conditions for highest xylanase. experimental kolanut plantation soil and kolanut husk collection kolanut husks and kolanut plantation soil from the kolanut husk dumpsite were obtained from a kolanut farm at ile ife city, osun state, nigeria (7.4905° n, 4.5521° e). sample transported to the laboratory of microbiology department, federal university of technology akure, ondo state in a ziploc bag. the soil samples were preserved at -20 ºc before use. isolation and identification of bacteria isolates one gram of the soil sample was suspended in 100 ml of distilled water then incubated in a control incubator shaker (gallenkamp, cambridge, uk) at 200 rpm for 30 min. mixtures were allowed to settle, and serial dilutions of up to 104 diluents were prepared using sterile distilled water. bacterial isolation was conducted by aseptically plating 100 µl from the diluent on xylan nutrient agar (nutrient agar supplemented with 1 % xylan) and incubated aerobically for 37 ºc for 24 h. purification of bacteria was done by repeated streaking and sub-culturing for purity and preserved at 4 ºc until use (kartik et al. 2016). authentication of the xylanolytic ability of isolates by well plate diffusion assay the organism was however authenticated qualitatively for positive xylanase production by growing isolates on nutrient agar medium containing 1 % birchwood xylan. the media was sterilized, poured, and allowed to solidify. upon solidification, wells were made with the aid of sterile cork-borer of 10 mm diameter. to each well bored in the solidified media, 100 µl of the overnight pure bacterial culture was poured and incubated for 24 – 36 h. the plate was flooded with nova biotechnol chim (2022) 21(2): e1226 3 0.25 % congo red solution for 15 min after which it was decolorized with 0.5 % acetic acid for 15 min and finally washed twice by 1 m nacl for de-staining as described (chan et al. 2016). clear zones around the well further authenticated xylanolytic activity. submerged fermentation for xylanase production submerged fermentation was conducted using kolanut husk as the substrate in addition to minimal salt medium containing (g.l-1): xylan 10.0, k2hpo4 0.1, cacl2 0.5, mgso4.7 h2o 0.5, peptone 2.0, feso4·7 h2o in trace amount, ph 6.8, sterilized at 121 ºc for 15 min. 50 ml of the sterile minimal salt medium in 250 ml flasks were inoculated with 1 ml of bacterial culture in broth and incubated at 37 oc for 24 h in a rotary shaker (hunterlab digital colorimeter, reston, usa) with agitation speed of 150 rpm. after the incubation period, the enzyme production medium was subjected to cold centrifugation at 10,000 rpm for 10 min to eliminate the bacterial cells and superfluous elements. the supernatant considered as source of the crude enzyme was gently decanted into sterile vials (sari et al. 2016). xylanase assay xylanase activity in the supernatant was assayed by determining the concentration of reducing sugar released by the activity of the crude enzyme on its substrate xylan by 3,5-dinitrosalicylic acid (dnsa) reagent (miller 1959). reaction mixture containing 0.5 ml of culture enzyme with 0.5 ml 1 % of birchwood xylan solution primed in phosphate buffer ph 6.8 was incubated for 20 min at 45 oc. the control experiment was set up to authenticate the results from the actual testing; with the control tube comprising a similar volume of a substrate with enzyme solution being replaced with sterile distilled water. after incubation, the reaction was terminated by adding 1 ml of dnsa reagent as described by miller (1959). the tubes enclosing the resultant blend were excited in the boiling water bath for 10 min, observed for brick red colour development and cooled swiftly in a water bath at room temperature. the optical density of the cooled mixture was measured with a spectrophotometer (lab-tech digital colorimeter) at 540 nm against a blank and articulated as xylose equivalent. one unit of endo-1,4-β-xylanase was defined as the amount of enzyme requisite to discharge 1 µmol of xylose per minute in model assay conditions as depicted by sharma and bhajaj (2005); bhalla et al. (2015). protein estimation the amount of protein released in the supernatant was estimated as described bradford (1976) using bovine serum albumin (bsa) (sigma-aldrich, darmstadt, germany) as standard. 1ml of the enzyme extract was taken in a glass tube and added to it 3 ml of bradford’s reagent, the mixture was incubated at room temperature for 7 – 10 min. the absorbance was measured at 595 nm with a spectrophotometer (hunterlab digital colorimeter, virginia, usa) and compared with the bovine serum albumin standard curve. optimization of cultural and nutritional conditions the optimization of xylanase production by lysinibacillus fusiformis was carried out using “one factor at a time technique” (varying one factor while keeping the rest constant) in order to estimate xylanase activity for each varied parameter. parameters such as the effect of kolanut husk as carbon source at concentration (0.5 – 2.5 %), kolanut husk induction with xylan (0.5 – 1.5 %), additional carbon source at 0.5 % (glucose, fructose, sucrose, galactose and lactose), nitrogen supplementation at 0.25 % (yeast extract, urea, gelatin, tryptone, casein, ammonium chloride, ammonium nitrate, ammonium sulfate, potassium nitrate), incubation period (0 – 42 h), ph (2 – 10), temperature (25 – 45 oc) and inoculum size (0.5 – 2.5 %) were optimized for enhanced xylanase production by lysinibacillus fusiformis. the fermentation broth was separated from the bacterial cells by centrifugation, the supernatant served as a source of a crude enzyme tested for xylanase activity. the entire experimentations were done in triplicates with each mean shown in the result section. each experiment had its control with the control tube not having the tested process parameters. nova biotechnol chim (2022) 21(2): e1226 2 statistical analysis the data obtained after the optimization studies were statistically evaluated using the one-way analysis of variance (anova) at significance level of p < 0.05 using the statistical package ibm spss statistics v. 23.0 (chicago, usa). results screening and authentication of obtained xylanolytic bacteria isolate appeared cream-coloured, regularly shaped, round edges with 1 – 2 mm diameter on nutrient agar plate. it was gram-positive and rod-shaped and conforms to its earlier identification by fabunmi et al. (2018) as l. fusiformis. organisms showed zones of hydrolysis on xylan agar plates after incubation, indicating its ability to degrade xylan in the media alongside its growth during the incubation period with an average of 29 mm diameter zone of hydrolysis on xylan agar medium. optimization of culture and nutritional conditions the effect of different substrate (kolanut husk) concentration (0.5 – 2.5 %) as sole source of xylan in submerged fermentation by l. fusiformis is in table 1. result indicated that the highest enzyme activity was at kolanut husk concentration of 2.0 % with value of 419.28 µmol.ml-1.min-1 while the least at 0.5 % with a value of 201.52 µmol.ml-1.min-1. table 1. upshot of substrate concentration (kolanut husk) on xylanase production by l. fusiformis under smf. values are obtainable as mean ± s.e (n = 3). values with different superscripts are statistically significantly different (p < 0.05). smf – submerged fermentation. effect of xylan supplementation with kolanut husk on xylan production by l. fusiformis the effect of different concentrations of a husk (0.5, 1.0, 1.5, 2.0, and 2.5 %) in combination with a commercial birchwood xylan was supplemented to the fermentation medium for enhanced production of xylanase as shown in table 2. xylan supplementation as inducer showed maximum activity at 1.5 % kolanut husk supplemented with 1 % commercial xylan with xylanase activity of 422.63 µmol.ml-1.min-1 and lowest at 1 % kolanut husk with 0.5 % xylan with activity of 303.06 µmol.ml-1.min-1. effect of carbon source on xylanase production by lysinibacillus fusiformis effect of sugar optimization revealed sucrose to having the highest activity effect amongst others with enzyme activity of 549.75 µmol.ml-1.min-1 exceeding other sugars as shown in table 3. the monosaccharide galactose gave the least activity of 494.5 µmol.ml-1.min-1, the remaining sugars gave moderate improvement on enzyme production but not comparable to sucrose. kolanut husk [%] substrate optimization absorbance enzyme activity [µmol.min-1.ml-1] protein concentration specific enzyme activity [µmol.min-1.mg-1] 0.5 0.54 ± 0.00a 206.52 ± 2.02a 1.96 ± 0.06a 100.18 ± 0.16b 1.0 0.70 ± 0.00b 266.83 ± 2.04b 2.17 ± 0.01b 124.28 ± 0.11e 1.5 0.92 ± 0.00c 341.43 ± 0.29c 3.89 ± 0.02d 88.34 ± 0.08a 2.0 1.11 ± 0.00e 419.28 ± 0.36e 3.91 ± 0.01d 106.83 ± 0.12c 2.5 1.01 ± 0.00d 381.36 ± 0.31d 3.11 ± 0.06c 121.65 ± 0.03d 4 nova biotechnol chim (2022) 21(2): e1226 3 table 2. effect of xylan (x) supplementation as inducer with varied kolanut husk concentration on xylanase production by l. fusiformis under smf. values are obtainable as mean ± s.e (n = 3). values with different superscript are statistically significantly different (p < 0.05). smf – submerged fermentation. table 3. effect of sugar supplementation (carbon source) on xylanase production by lysinibacillus fusiformis under smf. carbon sources [%] carbon sources optimization absorbance enzyme activity [µmol.min-1.ml-1] protein concentration specific enzyme activity [µmol.min-1.mg-1] control (peptone water) 0.86± 0.02a 320.66 ± 0.88a 1.79 ± 0.05d 177.61 ± 0.87a glucose 1.39 ± 0.01d 521.74 ± 0.80e 2.06 ± 0.02e 250.47 ± 0.86b fructose 1.38 ± 0.01d 518.02 ± 1.13d 1.21 ± 0.04c 452.10 ± 0.58d sucrose 1.45 ± 0.02e 550.58 ± 0.71f 1.08 ± 0.02b 500.57 ± 0.86e galactose 1.32 ± 0.01c 495.16 ± 0.44c 0.88 ± 0.01a 566.38 ± 2.34f lactose 1.25 ± 0.02b 476.16 ± 1.48b 1.76 ± 0.02d 264.52 ± 0.86c values are obtainable as mean ± s.e (n = 3). values with different superscript are statistically significantly different (p < 0.05). smf – submerged fermentation. effect of organic nitrogen on xylanase production by lysinibacillus fusiformis nitrogen sources revealed yeast extract giving the highest xylanase titre (437.75 µmol.ml-1.min-1) and gelatin (339.38 µmol.ml-1.min-1) displayed the lowest enzyme titre (table 4). table 4. effect of organic nitrogen source on xylanase production by lysinibacillus fusiformis under smf. inoculum [%] organic sources optimization absorbance enzyme activity [µmol.min-1.ml-1] protein concentration specific enzyme [µmol.min-1.mg-1] control (peptone water) 1.05 ± 0.00b 401.06 ± 0.23b 2.76 ± 0.07b 149.06 ± 0.38b gelatin 0.86 ± 0.01a 340.12 ± 0.47a 2.79 ± 0.06b 116.61 ± 0.45a casein 1.12 ± 0.00c 426.90 ± 0.31c 2.72 ± 0.01b 155.44 ± 0.29c urea 1.13 ± 0.00c 430.72 ± 0.14d 2.39 ± 0.01a 181.06 ± 0.52e tryptone 1.15 ± 0.00d 437.98 ± 0.89e 2.36 ± 0.01a 184.73 ± 0.63f yeast extract 1.15 ± 0.00d 438.55 ± 0.47e 2.70 ± 0.01b 162.89 ± 0.58d values are obtainable as mean ± s.e (n = 3). values with different superscript are statistically significantly different (p < 0.05). smf – submerged fermentation. effect of inorganic nitrogen on xylanase production by lysinibacillus fusiformis table 5 showed the effect of inorganic nitrogen with kno3 resulting in the highest xylanase activity (464.25 µmol.ml-1.min-1) and nh4co3 with the least (325.70 µmol.ml-1.min-1). kolanut husk + xylan [%] substrate optimization absorbance enzyme activity [µmol.min-1.ml-1] protein concentration specific enzyme activity [µmol.min-1.mg-1] k1.0 + x0.5 0.80 ± 0.00a 303.06 ± 0.54a 1.87 ± 0.01a 162.84 ± 0.07d ki.0+ x1.0 1.01 ± 0.00d 384.13 ± 0.59e 2.09 ± 0.05b 190.69 ± 0.85f k0.5+x1.0 0.97 ± 0.01c 367.12 ± 1.16c 2.38 ± 0.01c 153.37 ± 0.49b k1.5+x0.5 0.79 ± 0.00a 374.65 ± 0.87d 2.38 ± 0.07c 166.72 ± 0.43d k1.5+x1.0 1.12 ± 0.00e 422.54 ± 1.44f 2.39 ± 0.01c 178.55 ± 0.23e 2.0k.h 0.92 ± 0.00b 348.36 ± 0.31b 2.36 ± 0.02c 147.21 ± 1.17a 5 nova biotechnol chim (2022) 21(2): e1226 2 table 5. outcome of inorganic nitrogen source on xylanase production by lysinibacillus fusiformis under smf. inoculum [%] inorganic sources optimization absorbance enzyme activity [µmol.min-1.ml-1] protein concentration specific enzyme [µmol.min-1.mg-1] control (peptone water) 1.05 ± 0.00b 400.56 ± 0.86b 2.68 ± 0.02a 148.96 ± 1.15e kno3 1.22 ± 0.01d 463.74 ± 0.90d 3.83 ± 0.01c 121.27 ± 0.36d (nh4)2so4 1.05 ± 0.00c 398.01 ± 0.57b 3.52 ± 0.02b 113.49 ± 0.86c nano3 1.07 ± 0.01c 405.86 ± 0.59c 4.30 ± 0.05d 96.44 ± 0.28b nh4co3 0.85 ± 0.00 325.70 ± 1.19a 4.50 ± 0.01e 92.45 ± 0.27a values are obtainable as mean ± s.e (n = 3). values with different superscript are statistically significantly different (p < 0.05). smf – submerged fermentation. effect of ph on xylanase synthesis by lysinibacillus fusiformis media ph is an extra significant dynamic considered in table 6, enzyme activity was highest value of 537.79 µmol.ml-1.min-1 at ph of 5.0 and the lowest enzyme activity at ph of 2.0 (368.20 µmol.ml-1.min-1). a supplementary boost in ph above 5.0 resulted in a significant drop-off in the activity recorded. table 6. upshot of ph on xylanase synthesis by lysinibacillus fusiformis under smf. ph ph optimization absorbance enzyme activity [µmol.min-1.ml-1] protein concentration specific enzyme [µmol.min-1.mg-1] 2 0.88 ± 0.08a 368.20 ± 0.90a 3.55 ± 0.02d 102.69 ± 0.11a 3 1.11 ± 0.01bc 424.08 ± 0.46b 3.52 ± 0.03cd 121.53 ± 0.03b 4 1.20 ± 0.00cd 456.88 ± 1.55c 3.05 ± 0.02b 148.83 ± 0.06d 5 1.41 ± 0.00g 537.79 ± 1.10h 3.73 ± 0.12e 141.29 ± 0.12c 6 1.39 ± 0.00fg 528.31 ± 0.84g 3.35 ± 0.07c 161.22 ± 0.14g 7 1.31 ± 0.00ef 497.30 ± 0.84f 3.14 ± 0.03b 159.14 ± 0.13f 8 1.28 ± 0.00de 486.26 ± 1.86d 3.10 ± 0.05b 161.25 ± 0.14g 9 1.20 ± 0.00cd 458.18 ± 0.92cc 2.99 ± 0.05b 152.71 ± 0.11e 10 1.09 ± 0.00b 490.56 ± 0.72e 2.75 ± 0.02a 141.44 ± 0.02c values are obtainable as mean ± s.e (n = 3). values with different superscript are statistically significantly different (p < 0.05). smf – submerged fermentation. effect of temperature on xylanase production by lysinibacillus fusiformis xylanase production was at its peak at 35 oc (572.83 µmol.ml-1.min-1) and least at 45 oc (347.33 µmol.ml-1.min-1) (table 7). table 7. effect of temperature on xylanase synthesis by lysinibacillus fusiformis under smf. temp [ºc] temperature optimization absorbance enzyme activity [µmol.min-1.ml-1] protein concentration specific enzyme [µmol.min-1.mg-1] 25 1.20 ± 0.00c 457.64 ± 1.30c 3.07 ± 0.06a 151.82 ± 0.03c 30 1.39 ± 0.00d 531.41 ± 0.33d 3.11 ± 0.11a 169.65 ± 0.17d 35 1.51 ± 0.00e 572.77 ± 1.29e 3.50 ± 0.05b 167.62 ± 1.44d 40 1.10 ± 0.00b 419.86 ± 0.32b 3.39 ± 0.05b 124.51 ± 0.86b 45 0.91 ± 0.00a 346.11 ± 0.67a 2.94 ± 0.02a 119.35 ± 0.87a data are presented as mean ± s.e (n = 3). values with different superscript are statistically significantly different (p < 0.05). smf – submerged fermentation. 6 nova biotechnol chim (2022) 21(2): e1226 3 effect of incubation time on xylanase production by lysinibacillus fusiformis incubation period optimization results showed that 24-h cultivation (624.29 µmol.ml-1.min-1) gave the best production as seen in fig. 1 and further increase revealed a corresponding reduction in enzyme activity. fig.1. effect of time on xylanase production by lysinibacillus fusiformis under submerged fermentation. effect of inoculum size on xylanase production by lysinibacillus fusiformis inoculum size is a vital dynamic in enzyme synthesis and maximum enzyme activity was recorded at 1.5 % with a value of 647.63 µmol.ml1.min-1 and the least observed at 2.5 % with 616.07 µmol.ml-1.min-1 (table 8). table 8. effect of inoculum size on xylanase production by lysinibacillus fusiformis under smf. inoculum [%] inoculum optimization absorbance enzyme activity [µmol.min-1.ml-1] protein concentration specific enzyme [µmol.min-1.mg-1] 0.5 1.62 ± 0.00a 615.27 ± 0.36a 0.89 ± 0.01b 697.68 ± 0.71d 1.0 1.67 ± 0.00b 624.07 ± 0.51b 0.96 ± 0.01c 653.53 ± 0.74b 1.5 1.70 ± 0.00d 647.63 ± 0.32d 1.25 ± 0.01d 518.78 ± 0.32a 2.0 1.69 ± 0.00c 643.35 ± 0.86c 0.97 ± 0.01c 671.07 ± 0.52c 2.5 1.62 ± 0.00a 616.07 ± 0.51a 0.84 ± 0.00a 732.31 ± 0.56e data are presented as mean ± s.e (n = 3). values with different superscript are statistically significantly different (p < 0.05). smf – submerged fermentation. 7 nova biotechnol chim (2022) 21(2): e1226 2 discussion kolanut husk in nature is composed of hemicellulose (40.41 %), lignin (21.29 %), cellulose (38.72 %) as reported by adeyi (2010) and patel and dudhagara (2020a), making it an appropriate substrate for xylanase production. they are mostly disposed of as agricultural waste at production site of kolanut forming a landfill and environmental problems. nevertheless, as a substrate for enzyme production could help to solve environmental pollution problems as well as reduction in production cost of xylanase. kolanut husk as an enzyme source was optimized as a component of the microbial fermentation medium. among the concentration of kolanut husk tested 2.0 % gave the maximum xylanase production. concentration above 2.0 % demonstrated a declined xylanase production but not as low as when lower concentrations of 0.5 % and 1.0 % was used (table 1). this indicated that adding further substrate does not show any noteworthy change in xylanase synthesis. a general boost in substrate absorption could lead to swell in enzyme output velocity at certain point till it reaches substrate saturation where no enzyme activity could be recorded (heskia et al. 2018). furthermore, the fermentation medium was induced with commercial birchwood xylan alongside kolanut husk. this was intended to boost xylanase production in the medium. optimum xylanase production was attained at a lesser substrate concentration in contrast to medium with solely kolanut husk. different xylan concentrations have also been reported to give maximum xylanase activity of 0.5 % (annamalai et al. 2009; heskia et al. 2018). thus, indicating that xylanase stimulation is an intricate trend in which the intensity of reaction varies with altered concentration combinations. decreases in enzyme activity at higher substrate concentration might be owed to the formation of thick suspension in the presence of higher substrate concentration which could have resulted in improper mixing of the substrate or non-uniform circulation of a nutrient under agitation condition (karim et al. 2015). karim et al. (2015) has revealed that substrate concentration used is a decisive element for utmost xylanase optimization and that there are different concentrations for various ligno-cellulose substrates. supplementation of medium with additional carbon sources involving both monosaccharide and disaccharide improved the enzyme activity produced. sucrose had the highest enzyme activity and closely followed by other sugars (table 2 and table 3). the results obtained agree with singh et al. (2011) who stated that amylase synthesis is favored by galactose, linking to the fact growth and enzyme productions of any organism are greatly influenced by both environmental conditions as well as the nutrient present in the growth medium. however, these findings contradict reports that wholesome sugars only have good growth but poor xylanase synthesis (shah and madamwar 2005) and that of seyis and aksoz (2005) that sucrose and glucose gave inhibitory effect on enzyme activity. their reports were attributed to catabolite repression of xylanase genetic material which is guarded at two levels as reported by de graaff et al. (1994), repressed gene transcription and ultimately by repressed transcriptional activator. in addition to carbon sources, nitrogen sources have a significant end product on the synthesis of xylanolytic enzymes produced by bacteria. overall, crude sources gave a higher xylanase production than inorganic sources (table 4 and table 5). this agrees with the report of bajaj et al. (2010), who stated that peptone combined with yeast extract as the largely reasonable and accustomed nitrogen sources in terms of elevated output of xylanase from diverse bacteria. nagar et al. (2010) reported maximum xylanase production by b. pumilus sv85s using peptone followed by yeast extract as nitrogen source. however, it is contrary with the report of sepahy et al. (2011) where tryptone in combination with yeast extract gave the maximum xylanase titre. peptone and yeast extract are multifaceted nitrogen sources rich in diverse growth factors such as minerals and vitamins and hence improve the growth of bacteria and enzyme synthesis (bibi et al. 2014) as few among the inorganic kno3 resulted in higher titre among others. sepahy et al. (2011) stated the ph of the medium has a strong influence on enzymatic processes as it affects the growth and metabolic activities of 8 nova biotechnol chim (2022) 21(2): e1226 3 individual microorganisms. influences of ph ranging from acidic to alkaline were tested for xylanase production as b. megaterium had the highest production at ph 5.0, indicating that acidic favours this particular organism when acting on kolanut husk as substrate. the alkalinity or acidity of the medium affect bacteria growth coupled with other enzymatic reactions through transport of ions, metabolites, and enzyme structure (liang et al. 2010). our results revealed that as the ph of the medium increases from extremely acidic (ph 2.0) to slightly acidic (ph 5.0), so does the enzyme activity increased but tending towards neutral ph, there was a drop in the value and the least value recorded at alkaline ph (table 6). this report is in contrary with the observations of sepahy et al. (2011); irfan et al. (2016) who reported the highest xylanase synthesis at ph 8.0 using b. mojanvensis and b. subtilis under submerged fermentation. this could possibly be attributed to the alkaline medium possessing an inhibitory influence on lysinibacillus fusiformis and moreover each microorganism has its ph for optimum growth and enzyme production. temperature is another key dynamic that influences the success of optimization system. the best medium temperature was 35 oc which is close to the optimal temperature for utmost xylanase titre in submerged fermentation (smf) (table 7) from other bacillus species reported as 37 °c (qureshi et al. 2002; battan et al. 2007; geetha and gunasekaran 2010; nagar et al. 2012) but contradicts the report of 50 °c temperature (sapereira et al. 2002; azeri et al. 2010; sepahy et al. 2011), 50 – 55 °c (anuradha et al. 2007; sharma et al. 2011) and 55 °c (annamalai et al. 2009). this indicates that productions of xylanase are favored at ambient temperature as compared to extremophilic temperature. this could be due to the fact that mesophilic temperature favors the growth of organisms and hence their ability to produce the desired end product. though, thermophilic temperature is best preferred as it diminishes the risk of mesophilic microbial defects (yeoman et al. 2010). generally, bacillus sp. shows ability to grow and produce enzymes at 37 oc under suitable fermentation conditions (sanghi et al. 2008; nagar et al. 2010). the finest temperature for microbial enzyme synthesis may fluctuate as it is linked to their proliferation. the organism used in this study showed relatively high xylanase production within a short period of incubation which could be attractive for large-scale xylanase production. xylanase activity was found to decrease with prolonged incubation which could be linked to depletion in the available nutrient as time progresses and accumulation of end-products (fig. 1). production of toxic metabolites inhibits enzyme synthesis also (irfan et al. 2016). apparently, the increased incubation period affected any xylanase yield but reduced enzyme activity. this appears to be similar to simphiwe et al. (2011) who reported 24-h as an utmost incubation period using digested bran as substrate. in another report (anuradha et al. 2007), xylanase synthesis by bacillus species was growth-related with highest production at 24-h incubation period. however, prakash et al. 2011 reported contrarily with maximum production after 48-h of fermentation with b. habdurans. the decline in xylanase production during the later stage of fermentation could be attributed to the liberation of a limited volume of protease from the mature cells penetrating into autolysis or shortage of impenetrable xylan particles in the medium. limited fermentation time presented better and gainful production which is a favourable condition in large-scale industrial production. optimal inoculum size is crucial for preserving balance between growth sizes and obtainable nutrients in order to obtain the utmost yield. the outcome of this study as illustrated in table 8 is parallel to irfan et al. (2012) where 1.5 % inoculum size as peak of yield using b. megaterium on corn cob but in variance with that of nagar et al. (2010) who tested higher inoculum size (1.0 – 5.0 %) for xylanase production. the reduction might be related to the depletion of available nutrients from the fermentation medium as inoculum level increases which could have resulted to decline in enzyme synthesis. conclusion the search for agricultural waste such as kolanut husk as potential source of enzyme production rather than environmental nuisance is desirable as it reduces cost of production and increases bioconversion of waste to value-added compounds 9 nova biotechnol chim (2022) 21(2): e1226 2 by economically feasible techniques. the results obtained therein showed that l. fusiformis can produce xylanase via kolanut husk as a substrate under submerged fermentation. results indicated that cultural and nutritional parameters are paramount to enzyme production. the optimization process is an important pre-requisite to be considered for a cost-effective production and since kolanut husk is an agro-waste, it could be an alternative to the expensive commercial xylan as substrate especially at large scale. acknowledgements authors cherish the efforts of the technical staff of the department of microbiology, federal university of technology, akure, (futa) nigeria for their technical support in this study. conflict of interest the authors declare that there is no conflict of interest. references aarti c, arasu mv, agastian p (2015) lignin degradation: a microbial approach. south indian j. biol. sci. 1: 119-127. adeyi o (2010) proximate composition of some agricultural wastes in nigeria and their potential use in activated carbon. j. appl.sci. environ. manag. 14: 1. annamalai n, thavasi, r, jayalakshmi s, balasubramanian t (2009) thermostable and alkaline tolerant xylanase production by bacillus subtilis isolated from marine environment. indian j. biotechnol. 8: 291-297. anuradha p, vijayalaxmi k, prasanna nd, sridevi k (2007) production and properties of alkaline xylanases from bacillus sp. isolated from sugarcane field. curr. sci. 90: 1283-1286. azeri c, tamer au, oskay m. 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invitski et al., 1999). the recent well published million-dollar food recalls due to food poisoning bacteria such as listeria monocytogenes (lin et al., 2005; donnelly, 2001; schlech, 2000) has increased the need for more rapid, sensitive and specific methods of detecting these microbial contaminants. the aim of this overview is to summarize the rapid and sensitive detection methods of pathogens in foods. here reviewed methods are focused particularly on detection of antigens (immunological methods), and on detection of species-specific dna sequences (molecular genetic methods). the highlights of these methods lie on their high specificity, rapidity and sensitivity purposes. 2. conventional detection methods traditionally, the detection and identification of bacteria mainly rely on specific microbiological and biochemical identification. although these methods can be sensitive, inexpensive and give both qualitative and quantitative information on the number and the nature of the microorganisms tested, they are greatly restricted by 6 vidová, b. et al. assay time, with initial enrichment needed to detect pathogens, which typically occur in low numbers in food and water (leonard et al., 2003). culture is the term used to describe the biological amplification of cultivatable bacteria using artificial growth media. these media may be liquid (broth), solid (due to the addition of agar, and used for their growth-supporting surface), enriched (with growth-promoting substrates) and selective (with inhibitors to reduce growth of unwanted species) or contain specific indicators to reveal growth of species of particular interest. bacterial growth also requires the right temperature and other physiochemical and chemical conditions. the bacteria have first to be recovered in pure culture. this requires growth of each, individual species in single colonies. the first identification tests performed include observation of bacterial colony morphology, alteration of the surrounding agar medium, the gram stain, termed benchtop tests such as coagulase, catalase and oxidase reactions and specific antibody agglutination reactions (chow et al., 2006). 3. immunological methods detection with antibodies is perhaps the only technique that has been successfully employed for the detection of cells, spores, viruses and toxins alike (iqbal et al., 2000). polyclonal antibodies can be raised quickly and cheaply and do not require the time or expertise associated with the production of monoclonal antibodies (cahill et al., 1995). however, polyclonal antibodies are limited both in terms of their specificity and abundance. since the development of hybridoma techniques (köhler and milstein, 1975) and the emergence of recombinant antibody phage display technology, developed during the past decade (petty et al., 2007), immunological detection of microbial contamination has become more sensitive, specific, reproducible and reliable with many commercial immunoassays available for the detection of a wide variety of microbes and their products (leonard et al., 2003). some of these methods are briefly listed below. 3.1 serotyping serotyping is most widely applied to gram-negative enteric bacterial pathogens such as salmonella and escherichia. among gram-positives, serotyping is important for the genus listeria. the gist of a typical serotyping scheme is the use of specific antibodies (antiserum) to identify homologous antigens (fig. 1). in many foodborne pathogens, the antigens are particulate, and agglutination methods are employed (jo et al., 2004; lukinmaa et al., 2004; bailey et al., 2002; gorman and adley, 2004). 3.2 fluorescent antibody (fa) this technique has had extensive use in both clinical and food microbiology since its development in 1942. an antibody to a given antigen is made fluorescent by coupling it to a fluorescent compound and when the antibody reacts with its antigen, nova biotechnologica 8-1 (2008) 7 the antigen-antibody complex emits fluorescence and can be detected by the use of fluorescent microscope (fig. 2). a b c fig. 1. group b streptococcus [gbs] serotyping test fy essum ab. (a) placing of reagent onto the agglutination site of the test plate. (b) picking some fresh colonies from the plate where the bacteria have been isolated and their transfer adjacent to the test plate. (c) gentle agitating the test plate and reading the agglutination pattern while agitating (processed according to persson et al., 2004) the fluorescent markers used are rhodamine b, fluorescein isocyanate, and fluorescein isothiocyanate, with the last being the most widely used. the fa technique obviates the necessity of pure culture isolations of salmonellae oh globulin labeled with fluorescein isothiocyanate with somatic groups a to z represented (hilker and solberg, 1973; thomason, 1971; insalata et al., 1973). because of the cross-reactivity of salmonellae antisera with other closely related organisms (e.g., arizona, citrobacter, e. coli), false positive results are to be expected when naturally 8 vidová, b. et al. contaminated foods are examined (cherry and moody, 1965). an indirect fluorescent antibody technique based on highly specific monoclonal antibody for streptococcus inae was developed and was found to be suitable for the detection and identification of s. inae from experimentally and naturally infected tilapia (klesius et al. 2006). fig. 2. fluorescent antibody identification of yersinia pestis. (photo: abdul ghaffar) 3.3 radioimmunoassay (ria) this technique consist of adding a radioactive label to an antigen, allowing the labeled antigen to react with its specific antibody, and measuring the amount of antigen that combined with the antibody by a counter to measure radioactivity. the label used by many workers is 125i. the ria technique lends itself to the examination of foods for other biological hazards such as endotoxins, paralytic shellfish toxins, etc. the detection and identification of bacterial cells within 8-10 minutes have been achieved (strange et al. 1971) by the use of 125i-labeled homologous antibody filtered and washed on a millipore membrane. because of its requirement for an isotope and its lack of portability, the ria method is rarely used now for food microbiology. 3.4 enzyme-linked immunosorbent assay (elisa) the elisa (enzyme immunoassay or eia) is an immunological method similar to ria but employing an enzyme coupled to antigen or an antibody rather than a nova biotechnologica 8-1 (2008) 9 radioactive isotope. a typical elisa is performed with a solid-phase (polystyrene) coated with antigen and incubated with antiserum. following incubation and washing, an enzyme-labeled reparation of anti-immunoglobulin is added (fig. 3a). after gentle washing, the enzyme remaining in the tube or microtiter well is assayed to determine the amount of specific antibodies in the initial serum. the amount of enzyme present is ascertained by the colorimetric determination of enzyme substrate. variation of this basic elisa consists of a “sandwich” elisa that allows detection and quantification of pathogen related antigen (fig. 3b) (valdivieso-garcia et al., 2001; gilroya and smith, 2003). in this case, the antibody specific for the antigen is coated to the surface of microtiter wells to which the antigen containing test sample is added. after unbound antigens are washed away, the antibody antigen complexes are than detected by an enzyme-linked antibody, which is specific for a different epitope on the antigen. next, unbound reporter antibodies are washed away, the substrate is added and the coloured reaction product is measured. the “double sandwich” elisa is a variation of the latter method, and it employs a third antibody. the elisa technique is used widely to detect and quantitate organisms and/or their products in foods (bennett, 2005). a b fig. 3 elisa assay (a) typical elisa assay (b) sandwich elisa. 3.5 immunomagnetic separation this method employs paramagnetic beads (about 2-3 μm in size, about 106108/ml) (fig. 4) that are surface activated and can be coated with antibody by incubating in the refrigerator for varying periods of time up to 24 hours. the unabsorbed antibody is removed by washing. when properly treated, the coated beads are added to food slurry that contains the homologous antigen (toxin or whole cells in gram-negative bacteria), thoroughly mixed, and allowed to incubate from a few minutes to several hours to allow for reaction of antigen with antibody-coated beads. the concentrated antigen is assayed by other methods. in one study, immunomagnetic 10 vidová, b. et al. separation was combined with flow cytometry for the detection of e. coli o157:h7. the antigens were labeled with fluorescent antibody, which was measured by flow cytometry, and the combined method could detect <103 cfu/g of pure culture or 103104 cfu/g in ground beef (fu et al., 2005; drysdale et al., 2004; tsai et al., 2006). this method was also used for measuring the number of l. monocytogenes cells (hibi et al., 2006). fig. 4 the aureon biosystems salmonella a-beads™: polydisperse 1.5 um cluster type paramagnetic particles with affinity-purified antibodies against salmonella spp. covalently bound to the surface. the salmonella a-beads™ will bind specifically to salmonella in a mixed flora sample and is designed for the rapid and specific isolation of salmonella from food and environmental samples (edited according photo by charles j. dicomo). 4. molecular genetic methods the progress made in nucleic acids techniques for diagnostics is enormous in relation to the period during which it has been applied to the development of assay systems as compared to that during which phenotypic in vitro analysis has developed. indeed, nucleic acid technology has now assumed an essential role in various areas of in vitro diagnosis. basically, this approach employs genetic materials (dna and rna) as diagnostic targets for identifying suspected pathogens. the rapid advancement of nucleic acid diagnostic is a consequent of two essential advantages: (1) nucleic acids can be rapidly and sensitively measured, and (2) the sequence of nucleotides in a given gene is highly specific and it can be used to distinguish closely related serotypes nova biotechnologica 8-1 (2008) 11 (kwang, 2006). the 16s rrna species-specific sequences are reliable tool for bacterial diagnosis. the importance of 16s rrna was shown at proposing the establishment of three kingdoms of life forms, namely eukaryotes, archaebacteria, and prokaryotes. the 70s bacterial ribosome contains three definable rrna fractions, 5s, 16s and 23s. the 5s contains ca. 120 nucleotides while 16s and 23s contain ca. 1.500 and ca. 3.000, respectively. the 16s rrna has been shown to be an excellent chronometer of life forms, especially bacteria. it was by the use of 16s rrna sequence and hybridization data that the class proteobacteria was established. by use of these sequences, new bacterial genera can be defined on a genotypic rather than a phenotypic basis. from this and other molecular genetic information, the genus pseudomonas has been reduced by the transfer of over 50 species to 10 new genera. the existence of many of gene banks for many other bacterial taxa of importance in foods suggests that generic and species realignments will continue (jay et al. 2005). besides, nucleic acids detection offers many advantages over immunological assays. nucleic acids are more stable than proteins to high temperatures, high ph, organic solvents, and other chemicals; hence samples can be treated in a relatively harsh manner without destroying the nucleic acid for detection. tools used for application of nucleic acid detection like dna primers and probes are more defined entities than antibodies and antigens, and their composition can be accurately checked by sequence analysis, and produced in dna synthesizers whenever necessary. the more commonly applied nucleic acid assay technologies in diagnostic include nucleic acid probes and polymerase chain reaction (kwang, 2006). 4.1 nucleic acid probes the fundament of the specific association of nucleic acid sequences by complementary base pairing through hydrogen bonding, which centralizes based on adenine complementarities to thymine and uridine, while guanine complementary to cytosine, has allowed the development of several nucleic acid diagnostic methods for detection. nucleic acid probes are short fragments of nucleic acid sequences that detect specific sequences associated with pathogen by nucleic acid hybridization with highly conserved sequences. if pathogen contains sequences complementary to the probe, the two sequences can hybridize to form a double-stranded molecule. the probe can be chemically synthesized according to the target gene sequence, which can be derived if a short amino acid sequence of the protein encoded by the target gene is known. during synthesis of the probe, labeled nucleotides are incorporated, to enable detection of the probe after hybridization. the types of labeled probes include radioactive (which gives a radioactive signal), biotin (which generate a color) and chemiluminescent (which is enzyme-linked). nucleic acid hybridization is often performed in the form of southern blotting that detects for dna and northern blotting that detects for rna. in both southern and western blotting, denatured dna and rna samples are separated by electrophoresis and immobilized onto a solid support system, usually nitrocellulose or nylon membrane, respectively, before detection with radioisotope-labeled or enzyme-labeled sequence-specific probe(s). hybridization is allowed to occur at an optimized 12 vidová, b. et al. temperature in which considerable sequence homology between the target sequence and the probe is necessary to form a stable duplex. following washing to remove unhybridized probe, the hybridization is detect according to how the probe was labeled (dooley, 1994). nucleic acid probes can be designed for identifying all serotypes or some interesting serotypes of a pathogen. however, when used alone probes may not be very sensitive. although, nucleic acid hybridization procedures can be combined with pcr due to provide a powerful tool, which exhibits remarkable specificity and sensitivity. it is especially useful when the target pathogen cannot be cultivated, or is difficult to cultivate. on the other hand, nucleic acid probes in diagnostics is designed for use in the food industry, such as for the detection of salmonella and staphylococcus employ probe dipsticks, which remove hybridized dna from liquid solution. for this method, a two-component probe is used, in which one serves to bind to the specific sequence of the pathogen, and the other serves to bind to the dipstick. following hybridization of the two-component probe to target sequence, the dipstick is inserted into the hybridization solution to remove the hybridized dna for measurement (jay et al., 2005). 4.2 polymerase chain reaction (pcr) this method is fast becoming the most widely used of all molecular genetic methods for detecting and identifying bacteria in foods. its increasing use is due to its high sensitivity, specificity, its availability in many formats, and the commercial availability of pcr-based methods in kit-like formats. the polymerase chain reaction diagnostic methods detect for specific nucleic acid sequence found in the genome of pathogens (chotár et al., 2006, fig. 5). fig. 5. determinations of specificity of primers in pcr assay; amplification products of the different primer combinations were analyzed by electrophoresis in 0.9 % agarose gel. lanes: 1–3 – dna s. agalactiae with primers saga1 and saga2 and sip3(f) and sip4(r) (1), ecoli1 and ecoli2 (2), sau1 and sau2 (3); 4–6 – dna e. coli with primers saga1 and saga2 (4), ecoli1 and ecoli2 (5), sau1 and sau2 (6); 7–9 – dna s. aureus with primers saga1 and saga2 (7), ecoli1 and ecoli2 (8), sau1 and sau2 (9); 10 – multiplex pcr with all 8 primers; m – 100-bp dna ladder (biolabs) (chotár et al., 2006, photo: barbora vidová). nova biotechnologica 8-1 (2008) 13 fig. 6. polymerase chain reaction procedure (drawn by michael gaines). it is based on dna replication in vitro to produce large quantities of a target sequence of pathogen isolated from a complex mixture of heterogeneous dna 14 vidová, b. et al. molecules (e.g. host genome, nucleic acid from other microbes present). the reaction is set up using the following reagents reaction buffer, dna template, deoxynucleotides (dntps), primers and thermo stable dna polymerase. a pair of primers is used for the reaction. the primers are single-stranded dna molecules of about 20-30 nucleotides long (oligonucleotides) designed from the sequence flanking the two ends of the target genome. these primers are specific to the pathogen to maximize the specificity of the assay. the amplification of dna by pcr is accomplished through cycling a succession of incubation steps of different temperatures optimized for dna replication (fig. 6). briefly, a sample containing mixture of dna molecules is heat-denatured to separate complementary strands of dna into single-stranded molecules for reaction. next, the reaction is brought down to a lower temperature to allow pathogen-specific primers to search and anneal to the complementary sequence on opposite strands of the target dna. this step is followed by dna extension at a higher temperature, with dna polymerase adding on dntps using the annealed dna sequence as a template to produce copies of the targeted sequence. the three steps make up one cycling reaction, with each cycle producing duplicates of the dna targets. the cycle of steps is then repeated, in which the newly synthesized dna strands can also serve as templates for primer extension. these steps are repeated 20-40 times, yielding exponential amplification of the target dna sequences. the amplified products can then be visualized on agarose gel, or further assayed by nucleic acid probing for increased sensitivity and specificity (snustad and simmons, 2000). pcr offers a major advantage of detecting pathogens in a single cell particle. this saves the hassle of isolating the pathogens in culture. pcr has distinct advantages over culture and other standard methods for the detection of microbial pathogens and offers the advantages of specificity, sensitivity, rapidity, accuracy and capacity to detect small amounts of target nucleic acid in a sample (toze, 1999). pcr have been used extensively for several years for identification and characterization of bacteria in food samples, including meat and dairy products (hill, 1996; wang et al., 1997; aslam et al., 2003; ercolini et al., 2004; alarcón et al., 2006; jensen et al., 1993; fach and popoff, 1997; tsen et al., 1998), viruses (schwab et al., 1996; dubois et al., 1997; traore et al., 1998), protozoa (rochelle et al., 1997; stinear et al., 1996) and helminths (geary, 1996; mathis et al., 1996) and multiple primers can be used to detect different pathogens in one multiplex reaction. alternatively, diagnostic methods like nucleic acid probes, restriction fragment length polymorphism, or sequence analysis can also be used to confirm the identity of the pcr product and to further characterize the genome (vogel et al., 2004). 4.3 real-time polymerase chain reaction real-time pcr, also known as kinetic pcr or quantitative real time pcr, has been increasingly employed in diagnostic microbiology, virology and parasitology. in the biotechnology, real-time pcr has been used to genotype identification of genetically modified organisms, monitor gene expression in bioprocesses and for evaluating the nova biotechnologica 8-1 (2008) 15 safety of biologicals. the importance and wide use of real-time pcr as a quantitative tool in the life sciences is due to the inherent wide dynamic range of quantification (107-109 fold), high assay sensitivity (detection of less than 10 copies), and high precision with no post-pcr manipulations, thus minimizing the risk of crosscontaminations. thus, in view of the high accuracy of measurement and reliability of real-time pcr, this technology will continue to be an essential tool for the quantification of gene expressions and genotyping. taqman real-time pcr pathogen detection assays amplify target nucleic acid sequences from select microbes present in samples collected from complex biological environments. specific amplification of target sequences is directed by custom designed primers and probes. the first degree of specificity is achieved by the combination of amplification primer sequences. an additional degree of specificity results from a probe that hybridizes to a region of nucleic acid sequence that identifies the microbe of interest. as pcr amplification proceeds, fluorescence is excited by laser or halogen light and is detected by a charge-coupled device (ccd) camera. because the probe does not inhibit the pcr reaction, these systems give a linear response to template concentration over at least five orders of magnitude. target sequences that confer specificity to pathogenic microorganisms are found within the portion of the microbe’s genome that encodes their virulent agents. the genes or a portion of the genes that contribute to the disease phenotype of the pathogen distinguish a target microbe from its nearest neighbors (johnson et al., 2005; oberst et al., 1998). fig. 7. ribotyping (drawn by michael gaines) 16 vidová, b. et al. 4.4 ribotyping dna is extracted from cells and digested with a restriction endonuclease such as ecori, and the fragments are separated by agarose gel electrophoresis. separated fragments are transferred to a nylon membrane and hybridized with an appropriately labeled copy dna (cdna) probe derived from ribosomal rna (rrna) by reverse transcriptase. the pattern radioactive / chemiluminescent) that is created is recorded. the automated device creates riboprints that are matched or compared to those of known strains stored on computer software (jay et al., 2005; grif et al., 2006) (fig. 7). in a study of salmonella serotype enteritidis, ribotyping was the most discriminating and accurate of the genetic methods used to distinguish among food, water, and pathogenic strains (landers et al., 1998). fig. 8. microarray assay. microarray is produced by selecting (1) and printing (2) probes in an array on s glass plate (microscope slide). the sample (target) is prepared, labelled (3) and then let to react with the microarray in a process called hybridization (4). after hybridization, the slides are washe with a weak salt solution (4) that removes unspecific binding of the target molecules (stringent washing). the target molecules that have bound to the probes on the array are detected (5) using fluorescent scanning or other scanning techniques. finally, quantified values of the “spots” are analysed to give a genotype. 4.5 microarrays a very simple microarray may consist of a solid surface (such as a nylon membrane, glass slide, or silicon chips) onto that are attached small quantities of a nova biotechnologica 8-1 (2008) 17 single-stranded dna (ssdna) from different known bacterial species (fig. 8). when ssdna from as many unknown species is exposed to these array (dna chip), complementary strains will bind to their respective sites on the chip. if a reporter molecule is used, the identity of the unknown species can be confirmed. a dna microarray is, in essence, a dot blot set-up with the capacity to obtain and process large amounts of data. a dna microarray for microorganisms begins with the construction of oligonucleotides (primers), probes, hybridization, and data analysis. the overall process has been presented and reviewed by ye et al. (2001). as currently used, several hundred to several thousand specimens or probes may be applied to a solid surface. in a study of xanthomonas pathovars, a 47-probe microarray was employed to fingerprint 14 closely related strains, and the fingerprints showed clear differences between the test strains (kingsley et al., 2002). a dna microarray has been developed for the detection of bacteria in the microbial consortium of ready-to-eat vegetable salads, with as few as 100 cfu being detectable in < 1 hour (rudi et al., 2002). 5. conclusion in the field of food protection, it is extremely important to be able to identify and to type pathogenic and spoilage microorganisms at an early stage. here reviewed methods based on immunochemical and nucleic acid technologies provide a very useful alternative against conventional microbiological laboratory methods, because conventional methods involve enriching the food sample and performing various media-based metabolic tests (agar plates or slants), which typically require 3–7 days to obtain a result. on the other hand rapid-screening tests based on immunological or nucleic acid technologies developed for food testing can provide results within hours. an important area for further investigation will lie in the expansion of whole genome sequence comparisons to related pathogens to identify those genes that confer detrimental properties, and to other microorganisms including closely related nonpathogenic species to ascertain evolutionary relationships and to identify novel virulence factors. the use of dna microarrays will facilitate whole genome comparisons among diverse strains and the identification of strainand lineagespecific sequences. specific (serotype) markers could be used to develop accurate identification and subtyping methods for use in both health institutions and the food industry. the combination of such pathogen specific markers with detection on dna microarrays might provide a more sensitive, rapid and informative detection of pathogens in food and food production sites than do classical culture methods. more rigorous and systematic assessment and development procedures are needed to realize the full potential of microarrays for use in industrial and clinical settings, however, because currently this technique is prohibitively expensive and requires highly specialized knowledge. efficient cooperation between academia and industry is required so that dna microarray technology and other novel detection methods can be tailored to the practical needs of the food industry and health institutions. there is also a need to understand better the ways in which pathogens can protect themselves against the 18 vidová, b. et al. conditions that are used in food preservation, because this might lead to the optimization of current foodprocessing strategies. complete genome sequences have already provided us with an unprecedented insight into the evolution and lifestyles of food-borne pathogens, including species that previously have not been studied so well. the availability of several microbial genome sequences has catalyzed a burst of genomics-driven fundamental research in the ecology, physiology and virulence of foodborne pathogens. the coming years will bring the first practical benefits to the field of microbial food safety, including strategies and tools for the detection, identification and control of these pathogens. acknowledgements: the work was supported by projects of the ministry of agriculture of slovak republic (2003 sp 27/028, oe 02/028, oe 02-01-03). we are very grateful to dr. abdul ghaffar (department of microbiology and immunology, university of south carolina, school of medicine, columbia 29208, usa) for permission to publish his photo in this paper as figure 2. also we are very grateful to dr. charles j. dicomo (aureon laboratories, inc., 28 wells ave. yonkers, ny 10701, usa) for permission to edit and publish his photo of salmonella a-beads™ assay as the figure 4. our gratitude belongs also to professor michael s. gaines (department of biology, university of miami, florida 33124-042, usa) for giving us permission to show his two pictures of pcr procedure (figure 6) and ribotyping (figure 7) in this paper. references alarcón, b., vicedo, b., aznar, r.:. pcr-based procedures for detection and quantification of staphylococcus aureus and their application in food. j. appl. microbiol., 100, 2006, 352-364. aslam, m., hogan, j., smith, k.l.: development of a pcr-based assay to detect shiga toxin-producing escherichia coli, listeria monocytogenes, and salmonella in milk. food microbiol., 20, 2003, 345-350. bailey, j.s., fedorka-cray, p.j., stern, n.j., craven, s.e., cox, n.a., cosby, d.e.: serotyping and ribotyping of salmonella using restriction enzyme pvuii. j food prot., 65, 2002, 1005-1007. bennett, r.w.: staphylococcal enterotoxin and its rapid identification in foods by enzyme-linked immunosorbent assay-based methodology. j food 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fragment length polymorphism analysis compared to pulsed-field gel electrophoresis, random amplified polymorphic dna analysis, ribotyping, and pcr-restriction fragment length polymorphism analysis. j. food prot., 67, 2004, 1656-1665. wang, r.f., cao, w.w., cerniglia, c.e.: a universal protocol for pcr detection of 13 species of foodborne pathogens in foods. j. appl. microbiol., 83, 1997, 727-736. ye, r.w., wang, t., bedzyk, l., croker, k.m.: applications of dna microarrays in microbial systems. j. microbiol. meth., 47, 2001, 257-272. nova biotechnol chim (2022) 21(2): e1264 doi: 10.36547/nbc.1264 1 nova biotechnologica et chimica antibacterial activity of medicinal plants against streptococcus agalactiae marina gisel novosak1,, daniana lilian winnik1, margarita ester laczeski1,2, marina inés quiroga1 1department of microbiology, faculty of exact chemical and natural sciences, national university of misiones, conicet, misiones, argentina 2molecular biotechnology laboratory, misiones institute of biotechnology, faculty of exact chemical and natural sciences, national university of misiones, conicet, "dra. maría ebe reca", misiones, argentina  corresponding author: marinanovosak2008@gmail.com article info article history: received: 15th november 2021 accepted: 1st april 2022 keywords: aqueous extract bacterial drug resistance ethanolic extract plants, medicinal streptococcus agalactiae abstract streptococcus agalactiae, group b streptococcus (gbs), infects and causes severe diseases in humans and numerous animal species, including fish, given its ability to cross the host-specific barrier. the emergence of antibiotic resistant gbs strains makes it necessary to look for alternatives to treat and prevent infections that it produces. the aim of the present study was to determine the antibacterial activity of ethanolic and aqueous extracts of medicinal plants from misiones province, northeast argentina, against gbs from humans and fish. we used human streptococcus agalactiae atcc® baa-611™ and tilapia streptococcus agalactiae atcc® 51487™ strains. minimum inhibitory dose (mid) was determined by the disc diffusion method. minimum inhibitory concentration (mic), minimum bactericidal concentration (mbc), mbc/mic ratio, drug synergism with commercial antibiotics, and resistance assays were determined with extracts that showed antibacterial activity. medium lethal dose 50 (ld50) was determined by the artemia salina assay. for ethanolic and aqueous eugenia uniflora l. extracts, we obtained a mid = 0.5 mg.disc-1. for both extracts of eugenia uniflora l., the mic and mbc values were 1 mg.ml-1 and 5 mg.ml-1, respectively. the mici (mbc/mic ratio) = 5 qualified the action of these extracts as bacteriostatic. the drug synergism assay with ampicillin, erythromycin, and clindamycin combination and extracts showed indifference. the ld50 of the aqueous extract was 0.82 mg.ml-1 indicating moderate toxicity. this work is a first step to identify chemical compounds in native medicinal plants of misiones, argentina, that could mean an alternative for the treatment of streptococcus agalactiae infections. introduction streptococcus agalactiae, group b streptococcus (gbs), is a commensal bacterium of human gastrointestinal and genitourinary tracts (tan et al. 2017). it is the primary cause of life-threatening infections in newborns and infants, such as sepsis, meningitis, and pneumonia. its transmission by gbs-colonized pregnant women is the main route of neonatal infestation (raabe 2019). infections by gbs in newborns decreased with the detection of this microorganism in pregnant women between 35 – 37 gestation weeks and the implementation of intrapartum antimicrobial prophylaxis. however, the rate of invasive disease in older adults and people with underlying chronic disease is increasing (sendi et al. 2016). mailto:marinanovosak2008@gmail.com nova biotechnol chim (2022) 21(2): e1264 2 streptococcus agalactiae infects a wide variety of animal species due to its ability to cross the hostspecific barrier. authors have shown that some human gbs strains come from fish and other aquatic animals (skov sorensen et al. 2019). since gbs is the leading cause of septicemia and meningoencephalitis outbreaks in freshwater fish, it is problematic in aquaculture with a significant economic impact on the fish industry (mian et al. 2009; tavares et al. 2019). streptococcus agalactiae is the most important pathogen of nile tilapia (niloticus oreochromis). the tilapia farming industry has recently been hampered by streptococcosis outbreaks associated with high fish densities. in brazil, it causes up to 90 % of deaths in tilapia farms (banrie 2012). similar problems are expected to manifest themselves in misiones province, argentina, where there are more than 4,000 aquaculture producers recorded through provincial development programs (ministry of agriculture, livestock, and fisheries 2020). several authors have identified virulence genes from human gbs strains in fish gbs strains (delannoy et al. 2013; liu et al. 2013) and suggested that colonization with gbs serotypes ia and ib in humans is associated with the consumption of infected fish (foxman et al. 2007). this shows that human and fish gbs strains are closely related. penicillin, a beta-lactam family antibiotic, is recommended as first-line therapy against gbs infections. macrolides (erythromycin) and lincosamides (clindamycin) are second-line antibiotics. these are usually prescribed for betalactams allergy patients (le doare et al. 2017). also, penicillin is commonly used in animal farming and aquaculture for prophylactic or treatment purposes (ibrahim et al. 2020). the number of human clinical gbs isolates with reduced penicillin susceptibility, and a multidrug resistance tendency increased between 2005 – 2006 and 2012 – 2013 in japan (seki et al. 2015). furthermore, a study in china described the appearance of gbs strains resistant to penicillin in human lesions and tilapia (nagano et al. 2019). the appearance of multidrug resistance and gbs not susceptible to penicillin inside and outside health centers is a concern (nagano et al. 2019). also, resistances to erythromycin (14.5 to 70 %) and clindamycin (8.2 to 70 %) have been reported worldwide (nagano et al. 2012). in misiones, 6 % resistance to erythromycin and 5 % resistance to clindamycin were reported in human gbs strains, respectively (novosak et al. 2020). to date, in argentina and brazil, isolates show susceptibility to ceftriaxone, penicillin, and vancomycin. however, researchers reported strains with reduced susceptibility to these antimicrobial agents in japan, the usa, the uk, and canada (bonofiglio et al. 2018; li et al. 2020). the streptococcosis treatment is performed with fish food administration supplemented with antibiotics. however, the intensive antibiotic use in fish farms could lead to resistant strains emergence (amal et al. 2011). in this context, it is necessary to search for alternatives for streptococcosis treatment. medicinal plants have been used to treat several human diseases worldwide for thousands of years. the world health organization (who) has recorded more than 20,000 species of medicinal plants with a variety of potential uses (silva et al. 2021). also, their products are used as alternatives to antibiotics and chemotherapy to prevent and control diseases in aquaculture (cheesman et al. 2017). medicinal plants are sources of nutrients and can be used in whole, in part or as an extract, alone or in combination, by aquatic route or food supplement, or even mixed with other bioactive compounds (doan et al. 2019). moreover, medicinal plants usually have stimulating and immunostimulating properties of fish growth (awad et al. 2017). these have a wide range of bioactive compounds that are generally cheaper, safer, and more accessible than their synthetic equivalents (cheesman et al. 2017), such as phenolic, polyphenolic, alkaloid, quinone, terpenoid, lectin, and polypeptide compounds (abuajah et al. 2015). at least 93 species of native medicinal plants belonging to 21 families have been described in misiones, including apocynaceae, asteraceae, lythraceae, and myrtaceae. previous studies (guida et al. 2003; jerke et al. 2008; bargardi et al. 2021) suggest that these possess metabolites able to inhibit the growth of human and animal pathogenic bacteria. however, the effect of many of these plants against gbs isolates has not been described so far. the aim of the present study was to determine the antibacterial activity of the ethanolic nova biotechnol chim (2022) 21(2): e1264 3 and aqueous extracts of medicinal plants from misiones province, northeast argentina, against gbs from humans and fish. experimental plants collection and identification the leaves of psidium guajava l., eugenia uniflora l., tabernaemontana catharinensis a.dc., baccharis crispa spreng., cecropia pachystachya trécul., and acanthospermum australe (loefl.) kuntze were collected in different misiones province locations. the taxonomic identification was carried out in the chair of pharmacobotany of the faculty of exact, chemical and natural sciences (fceqyn). extraction leaves were dried at room temperature for ten days, stirring periodically. then, dry leaves were crushed in a numak f 100 460 w blade mill (instrumentación científica s. a., buenos aires, argentina). the powder was sieved through a nominal mesh aperture of 1.4 mm with w.s. tyler™ o-tap sieve shaker rx-29 (wstyler, ohio, usa). extracts were obtained by digestion (argentine pharmacopoeia 2013) with water and 96 % hydroalcoholic solution (commercial alcohol) and concentrated with a rotary evaporator laborota 4000-efficient (heidolph instruments gmbh & co. kg, schwabach, germany). powder was stored in a dark and dry place. bacterial strains the bacterial strains used in the assays were streptococcus agalactiae lehmann and neumann (atcc® baa-611™, aatc, manassas, usa) (clinical specimen–human) and streptococcus agalactiae (atcc® 51487™, aatc, manassas, usa) (tilapia sp. brain, israel). minimum inhibitory dose (mid) assay minimum inhibitory dose (mid) was determined by the agar diffusion assay according to seyyednejad et al. (2014) with modifications. extracts effective doses were 0.5, 1, 5, 10, and 15 mg. extract solutions were prepared using dimethyl sulfoxide (dmso) as a solvent for ethanolic extracts and sterile distilled water for aqueous extracts. thirty microliters of these solutions were impregnated on filter paper discs. ampicillin discs (10 μg) (laboratorios britania s.a., buenos aires, argentina) were used as positive controls. discs impregnated with dmso were used as negative control for the ethanolic extracts, whereas discs impregnated with sterile distilled water were used as negative control for aqueous extracts. the bacterial suspension equivalent to mcfarland 0.5 was inoculated on müeller-hinton agar (mha) plates (laboratorios britania s.a., buenos aires, argentina) supplemented with 5 % sheep blood using a sterile swab. discs were placed on the surface of inoculated plates. plates were incubated at 35 – 37 °c for 24 h for the subsequent measurement of inhibition diameters (id). mid was considered the minimum quantity of the extract included in a paper disc able to show a visual inhibition of microbial growth. only extracts with antibacterial activity were used in assays that follow. the percentage of inhibitory effect was obtained by the following expression (eq. 1; martinez et al. 1996): minimum inhibitory concentration (mic) and minimum bactericidal concentration (mbc) assays, and mbc / mic ratio mic and mbc assays were carried out following clinical and laboratory standards institute (clsi) recommendations (clsi 2015). the concentration range tested for each selected extract was from 20 to 0.0625 mg.ml-1. mic was defined as the lowest concentration without visible development. to determine mbc, mic cultures that did not show visible growth were seeded in mha with 5 % sheep blood and incubated for 24 h at 35 – 37 °c in a 10 % co2 atmosphere. mbc was defined as the lowest concentration of the extract capable of totally inhibiting microbial growth (procedures in clinical microbiology 2000). mic and mbc assays were performed in triplicate. when (1) nova biotechnol chim (2022) 21(2): e1264 2 mbc/mic ratio was ≤2 the effect of the active fraction was considered bactericidal, >2 and <16 bacteriostatic, and ≥16 ineffective (shanmughapriya et al. 2008). induction of resistance assay gbs strains were sub-cultured in sub-mic concentration for ten consecutive days to investigate their ability to develop drug resistance (su et al. 2015). tubes with mh broth and 0.5 mg.ml-1 of extract were prepared and stored in tubes at -20 ºc. a tube was used each day. on the first day of an assay, a tube was inoculated with 0.5 mcfarland of streptococcus agalactiae atcc® baa-611™ and incubated in an oven at 35 – 37 °c for 24 h. the next day, 50 µl from the first tube was inoculated into a second tube with the extract. in addition, each day the broth was plated on a nutritive agar plate supplemented with 5 % of sheep blood and incubated at 35 – 37 ºc for 24 h to evaluate possible contamination. the assay was repeated until the tenth day. mic was determined on test day 11. the same assay as in the streptococcus agalactiae atcc® baa-611™ was carried out with streptococcus agalactiae atcc® 51487™. assays were carried out in triplicate. drug synergism assay between extracts and commercial antibiotics it was performed on streptococcus agalactiae atcc® baa-611™ and streptococcus agalactiae atcc® 51487™ by the double-disc assay described by sachdeva et al. (2017) with modifications. commercial antibiotics used for the treatment of gbs were used: ampicillin (10 μg), erythromycin (15 μg), and clindamycin (2 μg) discs (laboratorios britania s.a., argentina). bacterial suspensions equivalent to mcfarland 0.5 were inoculated with a sterile swab on mha supplemented with 5 % sheep blood. a disc with 1 mg of eugenia uniflora l. extract was placed in the center of the plate. commercial antibiotic discs were placed on the sides 2 cm from center to center. the plates were incubated at 35 – 37 ºc for 24 h. the increased inhibition halo in the proximity of discs was interpreted as drug synergism. assays were carried out in triplicate. toxicity assay the artemia salina larvae assay was used to determine the extract toxicity (meyer et al. 1982). approximately 0.1 g of artemia salina cysts (aquagreen®, argentina) was added to one liter of a saline solution (containing 10 g of nacl per liter of distilled water). the container was kept at room temperature (28 – 30 °c), with air supply through a pump submersible pump bl-200 (baojie, zhejiang, china) and constant illumination. after 24 – 48 h the cysts hatched, and the larvae were taken in groups of ten to submit them to different extract concentrations in a 96-well plastic microplate. each well was filled with 200 μl of saline solution (containing 10 artemia salina larvae), 12.5 µl of eugenia uniflora l. aqueous extract dissolved in dmso and the final volume of 250 µl was completed with the same saline solution. concentrations tested were 0.0625, 0.125, 0.25, 0.5, 0.75, 1, 2 mg.ml-1. the microplate was incubated under illumination in a previously saturated glass container (humid atmosphere) at 28 – 30 °c and for 24 h. then, the number of surviving larvae in each well is counted with a stereoscopic magnifying glass nikon smz 445 (nikon corp. tokyo, japan). two controls were carried out: a growth control containing only the larvae in saline solution and a dmso control, which contained larvae, saline solution, and 12.5 µl of dmso without extract. the larvae death was established by the total lack of movement during 10 seconds of observation (vanhaecke et al. 1984). the lethality percentage in each well was calculated by the following equation (eq. 2): the lethal concentration 50 (lc50) was determined by graphic estimation, representing the lethality percentage of the larvae depending on the extract concentration. the lc50 value was obtained by the linear regression method using the software statgraphics centurion xvii (statgraphics technologies, inc., the plains, usa). (2) 4 nova biotechnol chim (2022) 21(2): e1264 3 results minimum inhibitory dose (mid) assay ethanolic and aqueous extracts of eugenia uniflora l. presented antibacterial activity against streptococcus agalactiae atcc® baa-611™ and streptococcus agalactiae atcc® 51487™ at the concentrations tested the mid was 0.5 mg.disc-1 for both extracts (table 1 and fig. 1). while psidium guajava l., tabernaemontana catharinensis a.dc., baccharis crispa spreng., cecropia pachystachya trécul. and acanthospermum australe (loefl.) kuntze did not show antibacterial activity. thus, following assays were conducted only with aqueous and ethanolic extracts of eugenia uniflora l. table 1. inhibition zone diameters and relative inhibitory effect percentages for ethanolic and aqueous eugenia uniflora l. extracts by agar diffusion assay against streptococcus agalactiae atcc® baa-611™ and streptococcus agalactiae atcc® 51487™. ee – ethanolic extract; ae – aqueous extract. fig. 1. minimal inhibitory dose (mid) – agar diffusion assay of aqueous and ethanolic extract of eugenia uniflora l. ae – aqueous extract; ee – ethanolic extract; c (+)– positive control; c (-) ae – negative control for the aqueous extract; c (-) ee – negative control for the ethanolic extract; mm – millimeter. eugenia uniflora l. extract concentra tions [mg] streptococcus agalactiae atcc® baa-611™ streptococcus agalactiae atcc® 514871™ ee ae ee ae inhibition zone diameters [mm] relative inhibitory effect [%] inhibition zone diameters [mm] relative inhibitor y effect [%] inhibition zone diameters [mm] relative inhibitor y effect [%] inhibition zone diameters [mm] relative inhibitory effect [%] 0.5 9.0 ± 0.0 28.12 9.0 ± 0.0 28.12 9.0 ± 0.0 28.12 9.0 ± 0.0 28.90 1 10.66 ± 0.57 33.33 11.0 ± 0.0 34.37 10.66 ± 0.57 33.33 11.33 ± 0.57 35.41 5 12.0 ± 0.0 37.5 11.66 ± 0.57 36.45 12.33 ± 0.57 38.54 12.33 ± 0.57 38.54 10 13.33 ± 0.57 41.66 13.33 ± 0.57 41.66 14.0 ± 0.0 43.75 13.66 ± 0.57 42.70 15 14.66 ± 0.57 45.83 14.0 ± 0.0 43.75 15.33 ± 0.57 47.91 15.0 ± 0.0 46.87 5 nova biotechnol chim (2022) 21(2): e1264 3 mic and mbc assays, and mbc / mic ratio mic and mbc obtained for ethanolic and aqueous eugenia uniflora l. extracts were 1 mg.ml-1 and 5 mg.ml-1, respectively. the mbc/mic ratio was 5 for both extracts. the action of extracts was bacteriostatic according to shanmughapriya et al. (2008) criteria. induction of resistance assay the mic value was 1 mg.ml-1 after gbs exposure to sub mic extract concentrations, suggesting that the microorganism would not develop resistance to the active principles of eugenia uniflora l. drug synergism assay between extracts and commercial antibiotics drug synergism trial showed indifference by the double-disc method. toxicity assay ld50 obtained for the aqueous extract was 0.82 mg.ml1, indicating moderate toxicity. the larval control group maintained 100 % viability and showed no behavioral changes during the test. discussion the results of current research revealed the antibacterial activity of eugenia uniflora l. against streptococcus agalactiae atcc® baa-611™ and streptococcus agalactiae atcc® 51487™. psidium guajava l., tabernaemontana catharinensis a.dc., baccharis crispa spreng., cecropia pachystachya trécul., and acanthospermum australe (loefl.) kuntze did not show any antibacterial activity at the different concentrations assayed. psidium guajava l. is used in the treatment of diarrhea, dysentery, menstrual disorders, vertigo, anorexia, digestive problems, gastric insufficiency, inflamed mucous membrane, laryngitis, skin problems, ulcers, vaginal discharge, and cough (díaz de cerio et al. 2017). silva et al. (2016) informed a low activity of aqueous and ethanolic extracts of psidium guajava l. against gbs but high on other bacterial species. sivananthan et al. (2013) mentioned that psidium guajava l. leaves extract showed antibacterial activity against staphylococcus aureus and streptococcus agalactiae. but the solvent used for the extraction procedure was chloroform. other authors informed the activity of ethanolic and aqueous psidium guajava l. extract against escherichia coli, pseudomonas aeruginosa, saphylococcus aureus, klebsiella pneumoniae y streptococcus pneumoniae (ifeanyichukwu et al. 2015; kenneth et al. 2017). the genus tabernaemontana has an important biological activity for the treatment and prevention of diseases, such as sore throat, hypertension, abdominal pain, and pulmonary disease (naidoo et al. 2021). richard et al. (2021) suggested that the crude latex of tabernaemontana catharinensis a. dc. displays an antimicrobial effect against alicyclobacillus, with potential for application in the food industry. goncalves et al. (2011) informed the in vitro antimicrobial activity of the tabernaemontana catharinensis a. dc. extract against staphyloccocus aureus and pseudomonas aeruginosa. however, no similar studies were found with gbs. baccharis crispa spreng. is used in infusion or decoction, as hepatic, diuretic, as a drying agent of ulcers and antiseptic in external use (rodriguez et al. 2008). palacios et al. (1983) informed antibacterial activity of bacharis crispa spreng. against bacillus subtilis and micrococcus luteus but no activity against staphylococcus aureus. no similar studies against gbs were reported. cecropia pachystachya trécul. is used in traditional medicine to treat respiratory disorders, renal diseases, and for its anti-inflammatory, diuretic, anti-hypertensive, and anti-diabetic properties, antidepressant-like, cardiotonic, sedative, and antimalarial effects (machado et al. 2021). de andrade et al. (2021) informed antibacterial activity of ethanolic extract of cecropia pachystachya trécul. against staphylococcus aureus atcc 29213, staphylococcus aureus atcc 25925, streptococcus pyogenes 1033b with halos that ranged from 12 mm to 18 mm. acanthospermum australe (loefl.) kuntze is used in folk medicine for the treatment of various 6 nova biotechnol chim (2022) 21(2): e1264 2 conditions such as diarrhea, skin diseases, blennorrhagia, dyspepsia, parasitic worms, and malaria. mallman et al. (2018) studied the efficacy of aqueous and hydroalcoholic extracts of acanthospermum australe (loefl.) kuntze against diarrhea-inducing bacteria. the hydroalcoholic root extract was unique in presenting a bactericidal effect against shigella dysenteriae. none of the extracts showed bacteriostatic or bactericidal activities against yersinia enterocolitica and enterococcus faecalis. similar works with extracts of cecropia pachystachya trécul. and acanthospermum australe (loefl.) kuntze against gbs strains were not reported. eugenia uniflora l. is often used in folk medicine as antidiarrheal, antihypertensive, antirheumatic, anti-inflammatory, respiratory disorders, digestive disorders, and numerous infections (de souza et al. 2018). several authors reported the activity of this plant against gram-positive and gram-negative bacteria. falcão et al. (2018) demonstrated activity against staphylococcus aureus atcc 25923, staphylococcus epidermidis incqs 00016, enterococcus faecalis atcc 29212, salmonella enteritidis incqs 00258, and pseudomonas aeruginosa atcc. however, the extract did not show activity against methicillin-resistant staphylococcus aureus and escherichia coli atcc 25922. also, victoria et al. (2012) obtained good activity of the essential oil of the leaves of eugenia uniflora l. against staphylococcus aureus and listeria monocytogenes. oliveira et al. (2008) worked with the lectin from eugenia uniflora l., obtaining antibacterial activity against staphylococcus aureus, pseudomonas aeruginosa, and klebsiella sp. although antibacterial activity has been reported for this plant, there are no published data against gbs so far. the antibacterial action of a plant extract is considered high when its percentage of relative inhibition is > 70 %, intermediate between 50 and 70 %, and low when it is 50 % (cruz-carrillo et al. 2010). for eugenia uniflora l. extracts, it was observed a relative inhibition percentage of less than 50 %, indicating low antibacterial activity. however, secondary metabolites with antibacterial activity are often found at low concentrations proportionally in the weight of dry extracts (compean et al. 2005). so, the extract may contain significant antimicrobial activity but in concentrations that are not high enough to inhibit bacterial growth considerably. according to the criteria of avellaneda et al. (2005) a bacterial strain has a high susceptibility when the tested substance has a mic less than 12.5 mg.ml-1, moderate susceptibility, between 12.5 and 50 mg.ml-1, and low susceptibility when the mic is between 50 and 100 mg.ml-1. during mic evaluation, the growth inhibition was obtained with both eugenia uniflora l. extracts to a lower concentration than 12.5 mg.ml-1. these results indicate high activity of eugenia uniflora l. extracts against the gbs strains studied. mic is considered the fundamental parameter for comparing the bacterium susceptibility against an antibacterial (struthers et al. 2005). it is the most reliable technique to determine substance antimicrobial properties. in brazil, lazzarottofigueiró et al. (2021) reported a mic value of 0.87 mg.ml-1 for the ethanolic extract of eugenia uniflora l. leaves when testing against staphylococcus aureus strains. they obtained higher mic values when testing with gramnegative bacilli (5 mg.ml-1 for escherichia coli, 20 mg.ml-1 for pseudomonas aeruginosa, and 10 mg.ml-1 for salmonella typhymurium). borges monteiro et al. (2019) obtained a mic value of 0.128 mg.ml-1, but they worked with methanolic extracts of eugenia uniflora l. leaves and h. pylori strains. in this study, mbc values were lower than 20 mg.ml-1 with both extracts, which indicates a high activity against gbs, according to the criteria of avellaneda et al. (2005). the mbc/mic ratio was 5 for both extracts, indicating the bacteriostatic extract capacity according to the criteria of shanmughapriya et al. (2008). medicinal plant extracts with intrinsic antimicrobial properties effectively prevent or reduce antimicrobial resistance. however, a combined approach that allows for a drug synergism between plant extracts and conventional antibiotics is possibly the most effective method of combating antibacterial resistance (inui et al. 2007; cheesman et al. 2017). in addition, the drug synergy between the bioactive plant product and antibiotics can prevent problems of toxicity or overdose, as two lower concentrations of agents that are combined in the treatment are required. in 7 nova biotechnol chim (2022) 21(2): e1264 3 this study, we did not observe drug synergy or inhibition effects between eugenia uniflora l. ethanolic and aqueous extracts and commercial antibiotics tested against gbs strains. coutinho et al. (2010) demonstrated a pharmacological synergism between the eugenia uniflora l. ethanolic extract and amikacin, gentamicin, kanamycin, neomycin, and tobramycin when testing against clinical isolates of staphylococcus aureus. however, the clinical isolates of escherichia coli did not show pharmacological synergism with this extract and antibiotics. the exposure of a bacterial population to the antimicrobial action usually produces a deleterious effect, either by inhibiting its growth or producing its death. this effect is not always observed due to the emergence of resistance mechanisms or the selection of resistant mutants (meyer et al. 1982). when determining mic after exposing gbs to submic concentrations of aqueous and ethanolic eugenia uniflora l. extracts for ten consecutive days, results revealed no change in value. therefore, gbs would not be expected to develop resistance to the active substance in the extract during treatment. it is also necessary to evaluate the toxicity of a product which can limit its benefit (santos et al. 2013). the toxicity criteria used were established by leos-rivas et al. (2016), where ld50> 1 mg.ml-1 represents low toxicity, ≥ 0.5 and ≤ 1 mg.ml-1 moderately toxic, and < 0.2 mg.ml-1 high toxicity. ld50 is defined as the substance concentration that causes 50 % of individuals to die in a study population. for ld50 determination, there are different methods using cell lines, laboratory animals, or artemia salina larvae. the latter is fast, economical, and simple. it does not require any special equipment or training and uses a relatively small test sample (leos-rivas et al. 2016). our research group have had previously determined that the toxicity of the ethanolic extract of eugenia uniflora l. is moderate [ld50 0.61 (0.51 – 0.74) mg.ml-1] (bobadilla et al. 2018). in this work, the ld50 value of the aqueous extract of eugenia uniflora l. was 0.82 mg.ml-1 (0.76 – 0.90 mg.ml-1), indicating also moderate toxicity. arcanjo et al. (2012) obtained an ld50 value of 288.46 µg.ml-1 (194.24 – 433.67 µg.ml-1) for the ethanolic extract of eugenia uniflora l. in their tests with artemia salina. however, toxicity studies carried out with this plant present wide methodological variations, making it difficult to compare the observed biological effects. the emergence of a gbs clone with zoonotic potential produced a sepsis outbreak in humans through raw fish consumption in singapore (kalimuddin et al. 2017). the application of antibiotics and chemotherapeutics to control infectious diseases in aquaculture eradicates microflora and emerges the resistant bacteria and accumulates residues in the human body (who 2006). challenges in treating infectious diseases in humans and fish have increased due to the resistance emergence. so, it is necessary to search for alternatives for antibacterial therapy development. natural products are a good option as they are less toxic and have fewer adverse effects than synthetic products. so, the present study expands the knowledge of natural antibacterial options existing in the region. conclusion aqueous and ethanolic extracts of eugenia uniflora l. have antibacterial activity against gbs of human and fish origin. these do not exhibit drug synergism with commercial antibiotics, the intratreatment resistance would not develop, and have moderate toxicity. aqueous and ethanolic extracts from psidium guajava l., tabernaemontana catharinensis a.dc., baccharis crispa spreng., cecropia pachystachya trécul. and acanthospermum australe (loefl.) kuntze did not show antibacterial activity against gbs. more studies are required with other solvents for secondary metabolite extraction from these plant species. this work is a first step to identify chemical compounds in native medicinal plants of misiones, argentina, that could mean an alternative for the treatment of streptococcus agalactiae infections. acknowledgments we thank marta yajía for identifying the plant species studied. this research was funded by pio conicet–unam nº. 237-201601-00007. 8 nova biotechnol chim (2022) 21(2): e1264 2 conflict of interest the authors declare that they have no conflict of interest. references abuajah ci, ogbonna ac, osuji cm (2015) functional components and medicinal properties of food: a review. j. food sci. technol. 52: 2522-2529. amal mna, zamri-saad m (2011) streptococcosis in tilapia (oreochromis niloticus): a review. pertanika j. trop. agric. sci., 34: 195-206. arcanjo ddr, albuquerque acm, melo-neto b, santana lclr, medeiros mgf, citó amgl (2012) bioactivity evaluation against artemia salina leach of medicinal plants used in brazilian northeastern folk medicine. braz. j. biol. 72: 505-509. argentine pharmacopoeia (2013) ministry of health of the nation. 7th eds., vol. iv, buenos aires, argentina. avellaneda ss, rojas hn, cuéllar ca, fonseca juárez m (2005) antibacterial activity of diphysa minutifolia rose. rev. cubana plant med. 10: 1-10. awad e, awaad a (2012) role of medicinal plants on growth performance and immune status in fish. fish shellfish immunol. 67: 40-54. banrie (2012) impact of streptococcosis on tilapia in brazil, aquavac strep sa for management. https://thefishsite.com/articles/impact-of-streptococcosison-tilapia-in-brazil-aquavac-strep-sa-for-management. bargardi s, kramer l, medvedeff m, jordá g, guida a (2001) antibacterial activity of peschiera australis (müell) miers against staphylococcus aureus and bacillus subtilis. rev. cienc. tecnol. 4. bobadilla fj, novosak mg, winnik dl, kachuk av, laczeski me, quiroga mi (2018) antibacterial activity, and toxicity of the ethanolic extract of eugenia uniflora l. leaves on pseudomonas aeruginosa. j. microbiol. biotechnol. food sci. 8: 842-846. bonofiglio l, gagetti p, garcía gabarrot g, kaufman s, mollerach m (2018) susceptibility to β-lactams in βhemolytic streptococci. rev. argent. microbiol. 50: 431435. cheesman mj., ilanko a, blonk b, cock ie (2017) developing new antimicrobial therapies: are synergistic combinations of plant extracts/compounds with conventional antibiotics the solution? 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jacob rg, alves d (2012) essential oil of the leaves of eugenia uniflora l.: antioxidant and antimicrobial properties. food chem. toxicol. 50: 2668-2674. who (2006) report of a joint fao/oie/who expert consultation on antimicrobial use in aquaculture and antimicrobial resistance, seoul, republic of korea. https://apps.who.int/iris/handle/10665/133869. 11 https://apps.who.int/iris/handle/10665/133869 microsoft word janos, lesny nb.doc nova biotechnologica vii-i (2007) 85 czech and slovak young brown coals in environmental applications pavel janoš1, juraj lesný2, lucia závodská3, sylvie kříženecká1, lucie herzogová1 1faculty of the environment, university of jan evangelista purkyně, králova výšina 3132/7, ústí nad labem, cz-400 60, czech republic (pavel.janos@ujep.cz) 2faculty of natural sciences, university of ss. cyril and methodius, nám. j. herdu 2, trnava, sk-917 01, slovak republic (lesnyj@ucm.sk) 2department of projecting&nuclear safety, ekosur, jaslovské bohumice, sk-919 31 slovak republic (zavodska@ekosur.sk) abstract: in recent time, various kinds of young brown (low-rank) coals are utilized increasingly not only as fuels, but also as valuable materials in advanced environmental applications. it should be noted in this context that significant deposits of the young brown coals can be found both in the czech republic as well as in slovakia. for their effective applications e.g. in wastewater treatment or in soil remediation, the properties of the coals should be studied in more details and numerous physico-chemical characteristics should be measured. as a part of a common czech-slovak project, a series of various kinds of coals was collected, including north-bohemian oxihumolites, lignite from south moravia and several lignites from slovakia (baňa zahorie). basic properties were measured, such as acid-base titration curves, contents of main functional groups and sorption capability towards heavy metal cations (cu2+, zn2+, co2+) and some organic pollutants. the contents of humic substances – main active constituents of the young coals – were also determined. selected environmental applications of the brown coals will be mentioned further, e.g. for the removal of metal cations from waters or in phytoremediation of contaminated soils. key words: lignite, oxihumolite, humic acids, metal, sorption 1. introduction young brown coals have been frequently used to improve the soil quality for a long time. large deposits of various kinds of young brown coals can be found in the czech republic (north bohemia, south moravia) as well as in slovakia. young brown coals contain large amounts of humic substances and may serve as an exogenous source of organic soil-constituents. due to their complex-forming ability, humic acids play a crucial role in the mobility of nutrients, essential elements and heavy metals in the environment and in the bioavailability of these elements to plants. a special kind of weathered and oxidatively altered lignite from the north-bohemian coal basin is called “oxihumolite” (veselá et al., 2005). it occurs at the surfaces of lignite deposits and is characterized by a high content of humic substances, unique sorption properties and high biological activity. similar kinds of low-rank coals from other locations are called leonardites. because of their sorption ability towards various kinds of chemical species, they are increasingly used also in other environmental applications, such as in wastewater treatment for the removal of metal cations (lao et al., 2005; janoš et al., 2007b; mizera et al., 2007), hexavalent chromium (lakatoš et al., 2002), ionogenic organic substances, such as synthetic dyes 86 janoš, p. et al. (janoš et al., 2005; janoš et al., 2007a), or low-polarity organic compound, e.g. phenanthrene (kalaitzidis et al., 2006). to exploit successfully the unique properties of various kinds of young brown coals, numerous physico-chemical characteristics should be measured and examined in more details. the following properties of the young brown coals are measured as a part of the common czech-slovak project: • contents and elemental composition of the organic part of coals, which is important for the plant nutrition as well as for the interaction of coals with some organic pollutants (kalaitzidis et al., 2006). • contents, elemental and phase composition of the inorganic part of coals – identification of the clay minerals, determination of the contents of heavy and toxic metals often present in coals, which may limit some environmental applications. • contents of total and extractable humic substances, as these compounds play a crucial role in soil fertility, biological activity as well as in the mobility of pollutants. • acid-base properties and contents of acidic functional groups, as these groups govern the mobility and bioavailability of various species in soils, metal cations in the first place. • radiochemical properties of coals also important for some environmental applications. • surface properties (surface area, pore-size distribution, etc.) that are significant for those applications where the sorption ability of the coals is exploited. some preliminary results of the mentioned project are presented in this contribution. 2. materials and methods various kinds of brown coals were collected from the selected deposits in the czech republic and slovakia. for the sake of comparison, also leonardite from gascoyne (usa) was involved in the study; it is recommended as a standard/reference material by the international humic substances society. the samples were air-dried in laboratory and then used for the measurements without an additional pre-treatment except of grinding and a size classification by sieving, if not specified otherwise in the respective measurement procedure. typically, the fraction with grain sizes less than 2 mm was used for laboratory experiments. the coals used in this study are listed in table 1. the total contents of humic acids and the contents of extractable (free) humic acids in coals were determined according to the standard procedure stn iso 5073. for the investigations of the acid-base properties of the coals and measurements of titration curves, the classical batch method of topp and pepper (topp and pepper, 1949) was adopted. the original method was modified as follows (janoš et al., in press): constants amounts (typically 0.25 g) of the coal were weighted into the series of 100 nova biotechnologica vii-i (2007) 87 ml pe bottles. different amounts the naoh solution were added to each of the bottles and mixed with different amounts of the nacl solution to keep a desired constant ionic strength after adjusting to the constant volume of 50 ml. the solutions were purged with nitrogen for several minutes, the pe bottles containing the samples under a nitrogen atmosphere were closed and equilibrated for 72 hours with intermittent shaking. then the equilibrium ph values were measured using a combined glass electrode. table 1. young-brown coals used in the present study name of the sample kind of coal deposit/sampling site ox-vršany oxihumolite – naturally weathered young brown coal mining site vršany, north-bohemian coal basin, czech republic ox-jiří oxihumolite – naturally weathered young brown coal mining site jiří near sokolov, northbohemian coal basin, czech republic ox-václav oxihumolite – naturally weathered young brown coal mining site václav near duchcov, north-bohemian coal basin, czech republic li-mikulčice lignite mining site mikulčice, south moravia, czech republic leonardit leonardite naturally weathered young brown coal gascoyne, usa li-zahorie i lignite mining site zahorie, slovakia li-zahorie ii lignite mining site zahorie, slovakia li-zahorie iii lignite mining site zahorie, slovakia li-zahorie iv lignite mining site zahorie, slovakia equilibrium sorption experiments (sorption of metal cations) were carried out by shaking a known amount of the coal (typically 0.4 g) with 50 ml of solution of the respective metal with desired concentration (typically ranging from 0.1 to 4 mmol dm3) in pe bottles. the metal solution together with the sorbent was agitated in the closed pe bottle for 72 hours using a horizontal shaker with an intensity of agitation 2 rps. then the solid phase was separated by sedimentation/centrifugation, the concentration of the metal in the solution was determined immediately by ion chromatography or icp-oes, and the sorbed amounts were calculated. 3. results and discussion as mentioned above, humic acids (ha) represent the main active constituents of young brown coals and the content of ha is a decisive factor in potential environmental applications of the coals. various kinds of brown coals may differ 88 janoš, p. et al. significantly in the contents of ha, as can be seen from fig. 1, where the total contents of ha as well as the contents of free ha are compared. as can be seen, all the examined coals contain significant amounts of ha and extremely high contents of ha was found in oxihumolite václav. functional groups in ha, mainly carboxylic and phenolic groups, govern the acid-base properties of coals. acid-base titration curves of selected coals were measured using a discontinuous batch method. according to ritchie and perdue (ritchie and perdue, 2003), the content of carboxylic groups was calculated from the base consumption for titration up to ph 8, whereas the phenolic group content was calculated from the two-fold consumption for the titration between ph 8 and 10. examples of the determinations are listed in table 2. it seems that the contents of functional groups may be related to the contents of ha (see a high content of carboxylic groups in oxihumolite václav), but preliminary results do not allow to make definite conclusions. table 2. contents of acidic functional groups in chosen samples of young brown coals (mmol g-1) name of the sample carboxylic groups phenolic groups ox-jiří 1.20 1.20 ox-václav 3.90 2.20 li-mikulčice 1.45 2.00 li-zahorie i 1.50 3.00 li-zahorie ii 1.55 2.30 0 20 40 60 80 100 ox -v rša ny ox -ji ří ox -v ác lav limi ku lči ce le on ar dit liza ho rie i liza ho rie ii liza ho rie iii liza ho rie iv c on te nt o f h a (% ) total ha free ha fig. 1. contents of humic acids in coals nova biotechnologica vii-i (2007) 89 the sorption capabilities of the czech and slovak brown coals were studied extensively, focusing on their ability to retain heavy metal cations, in the first place. the sorption isotherms were measured for several metal cations and evaluated using various models (langmuir, langmuir-freundlich) – details and model parameters can be found elsewhere (janoš et al., 2007 b). for direct comparison of an ability of different coals to retain metal cations from aqueous solutions, a parameter called “nominal removal efficiency” was introduced in this work. it is defined as an efficiency of the metal removal (in %) under given conditions. these conditions are specified as follows: weight of the sorbent (coal) 1g, volume of the metal solution 50 ml, initial metal concentration 1 mmol dm-3, contact time 72 hours. the removal efficiency was measured for all the above listed coals and selected metal cations cu2+, zn2+, co2+. as can be seen from fig. 2, most of the examined coals exhibited a very high ability to retain metal cations and could be potentially used for the removal of heavy metals from wastewaters or other industrial effluents. 0 50 100 ox -v rša ny ox -ji ří (s ok olo v) ox -v ác lav (d uc hc ov ) limi ku lči ce le on ar dit g as co yn e liza ho rie i liza ho rie ii liza ho rie iii liza ho rie iv r em ov al e ff ic ie nc y (% ) cu zn co fig. 2. nominal removal efficiency for cu2+, zn2+, co2+ ions. (conditions: weight of coal 1g, volume of metal solution 50 ml, initial metal concentration 1 mmol dm-3, contact time 72 hours) however, the sorption ability also affects the mobility of metals and the metal bioavailability, when the coals are used in soil amendments. further experiments consisted in an addition of coals and other ha-containing materials to soils contaminated with heavy metals. consequently, the mobility of heavy metal in the soils was examined using a standardized extraction test (a sequential bcr test) 90 janoš, p. et al. (janoš et al., 2004). preliminary results showed that an addition of ha affected significantly a fractionation of heavy metals in soils. 4. conclusions the total – end free humic acid contents, the content of carboxylic – and phenolic groups as well as by the authors newly introduced parameter, the “nominal removal efficiency” towards cu2+, zn2+ and co2+ have been determined for selected oxihumolite and lignite samples from sampling sites/deposits in czech republic (north bohemia, south moravia) and slovakia (mining site zahorie). a comparison of relevant characteristics for the mentioned samples and for a well known leonardit sample (mining site gascoyne, usa) has been done. the results confirm the correlation between the functional group concentration and the relevant concentration of humic acids. results of the “nominal removal efficiency” towards cu2+, zn2+ and co2+ show a generally high ability to retain metal cations for all the examined samples with exception of the naturally weathered young brown coal from mining site jiří (near sokolov). references janoš, p., herzogová, l., rejnek, j., hodslavská, j.: assessment of heavy metals leachability from metallo-organic sorbent-iron humate-with the aid of sequential extraction test. talanta, 62, 2004, 497-501. janoš, p., kříženecká, s, madronová, l.: acid-base titration curves of solid humic acids. react. funct. polymers, (in press). janoš, p., michálek, p., turek, l.: sorption of ionic dyes onto untreated lowrank coal – oxihumolite: a kinetic study. dyes pigm., 74, 2007a, 363-370. janoš, p., sypecká, j., mlčkovská, p., kuráň, p., pilařová, v.: removal of metal ions from aqueous solutions by sorption onto untreated low-rank coal (oxihumolite). separ. purif. technol., 53, 2007b, 322-329. janoš, p., šedivý, p., rýznarová, m., grötschelová, s. : sorption of basic and acid dyes from aqueous solutions onto oxihumolite. chemosphere, 59, 2005, 881-886. kalaitzidis, s., karapanagioti, h.k., christianis, k., bouzinos, a., iliopoulou, e.: evaluation of peat and lignite phenanthrene sorption properties in relation to coal petrography: the impact of inertinite. inter. j. coal geol., 68, 2006, 30-38. lakatos, j., brown, s.d., snape, c.e.: coals as sorbents for the removal and reduction of hexavalent chromium from aqueous waste streams. fuel, 81, 2002, 691-698. lao, c., zoldán, z., gamisans, x., solé, m. : sorption of cd(ii) and pb(ii) from aqueous solutions by a low-rank coal (leonardite). separ. purif. technol., 45, 2005, 79-85. mizera, j., mizerová, g., machovič, v., borecká, l.: sorption of cesium, cobalt and europium on low-rank coal and chitosan. water res., 41, 2007, 620626. nova biotechnologica vii-i (2007) 91 ritchie, j.d., perdue, e.m.: proton-binding study of standard and reference fulvic acids, humic acids, and natural organic matter. geochim, cosmochim. acta, 67, 2003, 85-96. topp, n.e., pepper, k.w.: properties of ion exchange resins in relation to their structure. i. titration curves. j. chem. soc., 1949, 3299-3303. veselá, l., kubal, m., kozler, j., innemanová, p.: struktura a vlastnosti přírodních huminových látek typu oxihumolitu. chem. listy, 99, 2005, 711-717. nova biotechnol chim (2022) 21(1): e1175 doi: 10.36547/nbc.1175 1 nova biotechnologica et chimica effects of ultrasonic-assisted alkaline pretreatment on xylose production from pineapple peel waste choosit hongkulsup, panchalee pathanibul department of food science and technology, faculty of science and technology, suan sunandha rajabhat university, bangkok, thailand  corresponding author: choosit.ho@ssru.ac.th article info article history: received: 16th september 2021 accepted: 1st december 2021 keywords: aeromonas acid hydrolysis pineapple peel ultrasonic-assisted alkaline pretreatment xylose abstract the pineapple industry generates large amounts of unusable waste (peel and core) with adverse environmental impacts. this experimental study aims to systemize the potential of ultrasonic-assisted alkaline pretreatment for xylose production from pineapple peel waste. the best condition for single alkaline pretreatment (1 % naoh w/v, 100 c, 60 min) has obtained hemicellulose, cellulose, and lignin composition at 34.80 %, 32.16 %, and 8.66 %, respectively, retained in the biomass. meanwhile, a combination of alkaline (1 % naoh, w/v) and ultrasonic (frequency 40 khz, 45 min) pretreatment has obtained the percentage yield of hemicellulose and lignin at 51.15 % and 7.15 %, respectively. both single alkaline and ultrasonicassisted alkaline pretreated samples were subsequently hydrolyzed with 2 % h2so4 (w/v). after acid hydrolysis for 30 min, the maximum xylose concentration of 48.85 g.l-1 was achieved by using ultrasonic-assisted alkaline pretreatment, while single alkaline pretreatment contributed to the lowest yield of xylose (37.11 g.l-1). it is shown that the ultrasonic-assisted alkaline treatment is more favorable than single alkaline pretreatment as it can produce high xylose concentration after the subsequent hydrolysis. these results indicated that ultrasonic-assisted alkaline pretreatment and its subsequent acid hydrolysis were appropriate for producing xylose from pineapple peel waste. introduction smooth cayenne pineapple (ananas comosus l. merr.) is one of the most valuable and popular tropical fruits in the world. as stated by the ministry of agriculture and cooperatives of thailand, thailand is ranked the first in the production and export of pineapple, with approximately 50 % of the international market share (wattanakul et al. 2020). in thailand, different pineapple products are exported to the global market, including fresh, frozen, canned, and juice products. however, according to the agricultural informatics center (2018), the demand and supply of pineapple products are always fluctuated. as a result, production of pineapples is higher than domestic consumption and export demand, resulting in an oversupply of pineapple in thailand. this consequently leads to a decline in the price of pineapple products. the manufacturing of canned pineapple or pineapple juice usually generates large amounts of pineapple waste including 29 – 40 % (w/w) of peel, 9 – 10 % (w/w) of core, and 2 – 5 % (w/w) of stem, which is mainly used as a supplement in animal feed or discarded in landfills at a very low price (ketnawa mailto:choosit.ho@ssru.ac.thsk nova biotechnol chim (2022) 21(1): e1175 2 et al. 2012). in recent years, thailand’s manufacturing process of pineapple products generated approximately 1.62 million tons of pineapple residues (ritthisorn 2016; banerjee et al. 2019). the greater expansion of pineapple production and export will subsequently generate more pineapple waste. however, pineapple peel wastes contain a major source of lignocellulosic materials. the chemical composition of pineapple residues contains approximately 38% to 50 % of cellulose, 23 % to 32 % of hemicellulose, and 13% to 30 % of lignin (sierra et al. 2008). therefore, hemi-cellulosic resources, including agricultural and industrial residues, offer a suitable alternative for the extraction of high-value renewable products (kunaver et al. 2016). lignocellulosic waste has become an alternative natural resource for the extraction of a valuable sugar, xylose. the interesting challenges for sustainability in industrial chemistry and biotechnology have encouraged the development of renewable agricultural residues. apparently, the conversion of agricultural wastes to alternative raw materials requires additional techniques to develop economic and effective procedures (binder and raines 2010). the typical conversion of lignocellulosic residue to reducing sugars consists of two main steps: (1) pretreatment and (2) hydrolysis. the removal and depolymerization of unwanted components and other impurities found in pineapple peel waste by various pretreatments have been widely studied. the valuable sugar can be extracted by different hydrolysis methods using chemicals and enzymes (chongkhong and tongurai 2017). the application of ultrasonication in solid-liquid extraction processes is considered as mechanical energy by particles vibrating or moving within a medium. theoretically, the formation of microbubbles during sonication treatments allows pretreated substrates to be more readily hydrolyzed by increasing accessible surface area, decreasing particle size and crystallinity (yunus et al. 2010). some studies reported that pretreatment of lignocellulosic materials with ultrasonic irradiation at working frequency higher than 20 khz could be advised for the intensification of bioconversion with different physical and chemical effects (asakura et al. 2008). the utilization of sonication for the improvement of agricultural by-product seems to be a promising technology that can be readily applied for the extraction of value-added sugar from pineapple waste (ong et al. 2019). however, the excessively long reaction time and the complicated procedure for enzymatic hydrolysis as well as the higher costs compared to chemical method have limited process applicability on an industrial scale (niwaswong et al. 2014). in addition, the direct usage of lignocellulosic residue from the pineapple industry as a hemicellulose extract for xylose production has been limited. agriculturalists and local enterprises play an important role in the utilization of agricultural residues. nevertheless, they have limited professional knowledge and lack the ability to use novel technology for converting agricultural waste into value-added products. consequently, the government should provide a policy environment and adequate financial support that encourages the sustainable development of agricultural waste utilization (xia and ruan 2020). the improvement of pretreatment processes to produce xylose and its derivatives is therefore necessary. the effect of ultrasonication on the pineapple peel prior to acid hydrolysis was evaluated. this experimental study aims to demonstrate the potential of ultrasoundassisted alkaline pretreatment and acid hydrolysis for xylose extraction from pineapple peel waste in a systematic way. experimental fresh pineapple peels were collected from the fruit market in prachuap khiri khan province, thailand. firstly, the pineapple peels were washed with tap water to remove foreign materials and left under the sun to dry. washed and dried peels were cut into small pieces and further dried at 60 °c in a hot-air oven until the moisture content is less than 10 % of wet basis. after that, the dried peels were ground and sieved to obtain particle sizes of less than 2 mm. the ground dried peels were then packed in sealed plastic bags and stored at room temperature before use. the smaller particle size is expected to increase the accessible surface area, improving the efficiency of ultrasonic treatment (zheng et al. 2009). proximate analysis of pineapple peel wastes was evaluated in accordance with the standard aoac (2012). nova biotechnol chim (2022) 21(1): e1175 3 chemical pretreatment dried pineapple peel waste (20 g) was treated under different solvent conditions: water; 1 %, 2 %, and 4 % h2so4 (w/v); 1 %, 2 %, and 4 % naoh (w/v); a solid-to-liquid ratio of 1 : 10 (w/v) and stirred at ambient temperature for 15 min. the chemical pretreated sample was heated at 100 °c and atmospheric pressure for 60 min in a sealed 1 l glass beaker placed in a water bath with temperature controller (sukruansuwan and napathorn 2018). it was then neutralized and filtered by water washing to remove a solvent on the surface of the sample. the neutralized pineapple peel was dried overnight at 60 °c in a hot air oven. the dried sample was then ground to a mesh size of 0.75 – 1 mm by a laboratory mill machine (ct 293 cyclotectm, foss, hillerød, denmark). the chemical composition of pretreated samples was analyzed for hemicellulose, cellulose, and lignin following the detergent fiber analysis according to van soest et al. (1991). the best conditions for chemical pretreatment of the pineapple peel obtained were used for the next experiment. ultrasonic pretreatment the ultrasonic pretreatment procedure of pineapple peels was performed with 1 % w/v naoh (the pretreatment condition obtained from the previous section) in a solid-to-liquid ratio of 1 : 10 (w/v). the mixture samples then underwent sonication using 4 different ultrasonication times (15, 30, 45, and 60 min) under the following conditions: temperature 50 °c; working frequency 40 khz; and ultrasonic power 200 w (lt-200-pro, tierratech®, guarnizo, spain). the control sample was unsonicated (0 min) but was added to 1 % naoh (w/v), incubated at 50 °c and stirred for 60 min. after ultrasonication, the pretreated samples were washed using distilled water and filtered using a filter paper. the solid residue was then dried at temperature of 60 °c overnight in a hot air oven until a constant weight was reached. the ultrasonic pretreated samples were kept in vacuum packaging before subsequent chemical hydrolysis (koutsianitis et al. 2015). acid hydrolysis pretreated pineapple peel (10 g) was completely mixed with 2 % h2so4 (w/v) in a solid-to-liquid ratio of 1 : 10 (w/v). the acid hydrolysis treatments were conducted at 100 °c and atmospheric pressure for 30 min in a sealed 1 l glass beaker placed in a water bath with temperature controller. after hydrolysis, the hydrolysates were neutralized by 6 m naoh and filtered using a 0.22 µm membrane filter. the filtrates (hemicellulosic fraction) were then kept in vials prior to xylose analysis by hplc (yunus et al. 2010). characterization of pineapple peel the detergent fiber method (van soest et al. 1991) for the analysis of fiber-rich feeds, and currently most frequently applied for fiber analysis in forage, provides a more suitable alternative to better characterize the carbohydrates in the plant cell walls. in this technique, the fractions of fiber that are insoluble either in acid detergent or in neutral detergents were measured, and the residue after treatment of acid detergent fiber (adf) fraction with 12 mol.l-1 sulfuric acid was considered to be acid detergent lignin (adl) and calculated by the following equations (eq. 1; eq. 2): % cellulose = adf – adl (1) % hemicellulose = ndf adf (2) where ndf is the neutral detergent fiber (%, w/w) and adf is the acid detergent fiber (%, w/w), while adl represents the acid detergent lignin (%, w/w). hplc analysis the oligomer composition of sugar supernatant was determined by high performance liquid chromatography (hplc) (shimadzu, kyoto, japan) equipped with two lc-20ad pumps, a dgu-20a5 degasser, an sil-20ac auto sampler and a refractive index detector (rid-10a). the column was an inertsil nh2 column (5 µm particle size, 250 mm x 4.6 mm, gl sciences inc., nova biotechnol chim (2022) 21(1): e1175 2 tokyo, japan) and its temperature was maintained at 40 c. the mobile phase was 85 % acetonitrile and 15 % ultra-pure water at a flow rate of 0.50 ml/min and 10 μl of sample was injected through a 0.22 µm filter into the hplc (veena et al. 2018). d-(+)-xylose standard purchased from merck life science uk limited (gillingham, uk) was used as standard. the peak areas were used to plot the calibration curve for the determination of the amount of oligomer in the sample, which were determined from the calibration curves of the corresponding standards. statistical analysis all data were statistically considered by analysis of variance (anova) followed by post hoc test using duncan‘s multiple range test (dmrt) and mean plots treatment. statistical processing was analysed by spss 19.0 software (ibm, somer ny, usa) for the window statistical package. the differences between the mean values were carried out at 95 % confidence interval (p < 0.05). all data described in figures and tables were the mean values of triplicate determinations. results and discussion proximate composition of pineapple peel the chemical compositions of the pineapple peels were determined following the methods described above. the results obtained are given in table 1. it is evident that the values given compare favorably with the normal values for fiber and carbohydrate content (37.30 % and 52.33 %, respectively) reported by zakaria et al. (2021). the fiber content of pineapple peels was about 31.31 %, while the total carbohydrate content is approximately 56.94 %. in general, pineapple waste was rich in lignocellulosic material, especially the peels and the leaves of the fruit (sukruansuwan and napathorn 2018). table 1. proximate composition on % (w/w) dry basis of pineapple peel. sample chemical compositions [%, dry basis] moisture ash protein fat fiber carbohydrate pineapple peel 12.51 ± 0.62 4.82 ± 0.35 6.29 ± 0.55 0.64 ± 0.10 31.31 ± 0.91 56.94 ± 2.03 effects of different chemical pretreatments on pineapple peels the major lignocellulosic components, such as cellulose, hemicellulose and lignin, were determined by the detergent fiber analysis based on the gravimetric method. as shown in table 2, the percentage yields of cellulose, hemicelluloses, and lignin in the raw pineapple peel powder were 31.56 %, 26.35 %, and 10.70 %, respectively. in the current study, the effect of pretreatment using different solvents, such as water, acid, and alkaline, was systematically investigated. it is clear from table 2 that pineapple peels pretreated with water and acid solution (h2so4) yielded the lower amount of hemicellulose, whereas pretreated with alkaline solution (naoh) still retained a high hemicellulose content of 31.57 % to 34.80 %. this observation suggests that hemicellulose degraded more easily under acid treatment than under alkaline treatment (ying et al. 2014). owing to its amorphous structure, hemicellulose is more prone to hydrolysis by mild acid solution compared to crystallized cellulose which likely requires more severe treatment conditions (zhang et al. 2012). considering the utilization of hemicellulose, its component is usually composed of xylan which can further be converted into xylose monosaccharides. for lignin analysis, the lignin contents from water and acid pretreatment were similar or slightly lower than that of the untreated sample, which demonstrated that a small part of the lignin was removed during pretreatment (ying et al. 2014). noticeably, the removal of hemicellulose and cellulose may slightly increase the percentage of lignin in fiber. in contrast, alkaline pretreatment was more capable in removing lignin; where up to 33.36 % of lignin content was removed resulting in 4 nova biotechnol chim (2022) 21(1): e1175 2 the availability of cellulose and hemicellulose for chemical hydrolysis (pandey et al. 2000). considering, both hemicellulose yield and lignin removal, alkaline pretreatment using 1 % naoh was chosen for obtaining the highest hemicellulose content and deemed to be suitable for further experiments. table 2. effects of different chemical pretreatments on characterization of pineapple peel. pretreatment condition composition of pineapple peel [%, dry basis] hemicellulose cellulose lignin untreated 31.56 ± 1.90b 26.35 ± 1.45b 10.70 ± 1.04a water 28.72 ± 1.79c 23.48 ± 2.33c 11.16 ± 1.02a 1 % naoh 34.80 ± 1.10a 32.16 ± 2.16a 8.66 ± 0.98b 2 % naoh 33.36 ± 1.94a 31.36 ± 1.45a 7.56 ± 0.81c 4 % naoh 31.57 ± 1.35b 28.83 ± 2.11b 7.13 ± 0.86c 1 % h2so4 26.97 ± 1.90 c 23.44 ± 1.45c 10.30 ± 0.98a 2 % h2so4 24.43 ± 1.78 d 21.53 ± 1.28cd 10.95 ± 1.32a 4 % h2so4 20.28 ± 1.54 e 20.51 ± 1.22d 9.46 ± 1.07ab * untreated sample is raw pineapple peel. ** percent composition is percentage of retained lignocellulosic materials in a sample. *** values with different superscripts (a-e) in the same column are statistically different (p ≤ 0.05). effect of ultrasonic-assisted alkaline pretreatment on pineapple peel the ultrasonic-assisted alkaline pretreatment of pineapple peel powder was undertaken under five conditions depending on varying ultrasonication time from 0 to 60 min. based on the results of the previous experiment; an alkali pretreatment (1 % naoh) was chosen to determine the effect of ultrasonic-assisted alkaline pretreatment on the composition of pineapple peel. table 3 demonstrates that the combination of ultrasonic and alkaline pretreatments could significantly decrease the total lignin content with time up to 60 min to reach a minimum value of 6.94 %. a significant percentage of hemicellulose increases gradually with irradiation time up to 45 min, and then it decreases slightly to 50.63 %. the application of excessive ultrasonication time did not further increase hemicellulose yield. during pretreatment, ultrasonication helped in delignification due to cleavage of interand intramolecular linkages and the cavitation of microbubbles which increased the available surface area of the cellulose and hemicellulose (koutsianitis et al. 2015). table 3. effects of ultrasonication time and 1% naoh pretreatment on characterization of pineapple peel. ultrasonication time [min] after pretreatment with 1 % naoh [%, dry basis] hemicellulose cellulose lignin 0 33.22 ± 2.13d 28.31 ± 1.32c 9.96 ± 0.94a 15 40.88 ± 2.45c 26.80 ± 1.90bc 8.67 ± 0.86b 30 47.19 ± 2.16b 27.62 ± 1.10bc 7.46 ± 0.98bc 45 51.15 ± 1.90a 29.82 ± 1.83ab 7.15 ± 0.97c 60 50.63 ± 2.77a 30.01 ± 1.68a 6.94 ± 1.18c * percent composition is percentage of retained lignocellulosic materials in a sample. ** values with different superscripts (a-d) in the same column are statistically different (p ≤ 0.05). a similar research was demonstrated by zhang et al. (2018) who stated that there was a reduction in lignin content after ultrasonication on rice straw. this is also in agreement with the report of loow et al. (2016), who stated that the ultrasonic method helped to decrease quantities of lignin in biomass 5 nova biotechnol chim (2022) 21(1): e1175 2 for reducing sugar recovery. in addition, ultrasonic application has been shown to increase the delignification of lignocellulosic materials, as the degradation of lignin-carbohydrate bonds would increase the accessibility for solvent penetration which may improve the extraction of reducing sugar (ong et al. 2019). therefore, ultrasonication time of 45 min is suitable for obtaining the highest hemicellulose yield from pineapple peel. effect of ultrasonic-assisted alkaline pretreatment and acid hydrolysis on xylose production basically, xylose is a reducing sugar obtained by hydrolysis of hemicelluloses, as it can be converted to valuable by-products such as xylitol, ethanol, and furfural. as shown in table 4, the ultrasonication time of 45 min followed by 2 % h2so4 with hydrolysis time of 30 min could yield a maximum xylose concentration around 48.85 g.l-1 which is a considerable improvement in comparison with the highest xylose concentration (24.1 ± 0.4 g.l-1) obtained in previous studies (sukruansuwan and napathorn 2018; banerjee et al. 2019; ariffin et al. 2020). an upward trend in sugar yield by using ultrasonic-assisted alkaline pretreatment was observed with a reduction in lignin content. these results were obtained due to the breakdown of the lignin matrix leading to an increase in the accessible surface of hemicelluloses within the pineapple peel. however, an excessive ultrasonic irradiation time of more than 45 min caused no further increment in xylose yield. this finding suggested that prolonged ultrasound duration would not be necessary for producing higher sugar yield but unfavorably it may cause adverse effects due to collision and aggregation between particles (baruah et al. 2018; ong et al. 2019). similar findings were revealed by ong et al. (2019) and yunus et al. (2010) who stated that ultrasonic irradiation helps to increase xylose contents extracted from oil palm fronds and empty fruit bunches, respectively. under the conditions obtained from this study (naoh concentration of 1 %, ultrasonication time of 45 min, and hydrolysis time of 30 min), the maximum xylose yield was achieved. thus, the data obtained from the best conditions of xylose production from pineapple peel waste using combination pretreatment would be potentially useful information not only for producing value-added product but also helps solve the environmental pollution. table 4. effect of ultrasonic-assisted alkaline pretreatment and acid hydrolysis on xylose production. pretreatment with 1 % naoh after 2 % h2so4 hydrolysis 30 min ultrasonication time [min] xylose [g.l-1] 0 37.11 ± 2.10d 15 40.13 ± 2.94c 30 44.05 ± 2.76b 45 48.85 ± 2.45a 60 47.20 ± 3.12ab * values with different superscripts (a-d) in the same column are statistically different (p ≤ 0.05). conclusions the feasibility of using pineapple peel waste as a lignocellulosic material for xylose production was evaluated. the present work represents a systematic attempt to investigate the effects of ultrasonic-assisted alkaline pretreatment on the best conditions of xylose production. the results have shown that alkaline pretreatment using simple ultrasonic technology is a practical alternative for production of valuable xylose sugar compared to costly catalysts or expensive enzymes. in this study, the best ultrasonic condition at 40 khz for 45 min with 1 % naoh pretreatment and hydrolysis time of 30 min successfully achieved 33.18 % delignification while producing high xylose concentration up to 48.85 g.l-1. the ultrasonicassisted alkaline pretreatment with acid hydrolysis exhibited better xylose yields and lower costs of extraction in comparison with an enzymatic method. thus, the data obtained from the effect of ultrasonication on alkaline pretreatment and acid 6 nova biotechnol chim (2022) 21(1): e1175 2 hydrolysis would be potentially useful for the application of pineapple peel waste as raw material for large scale xylose production. acknowledgements the authors are grateful to thailand science research and innovation fund for providing financial support (grant no. 0002406). the authors would also like to thank science center, faculty of science and technology, suan sunandha rajabhat university for facilitating hplc analysis. conflict of interest the authors declare that they have no conflict of interest. references agricultural informatics center (2018) agricultural statistics of thailand, 2017. office of agricultural economics. ministry of agriculture and cooperatives, bangkok, 232 p. aoac (2012) official methods of analysis of aoac international. 19th ed. aoac international, gaithersburg, md, usa. methods 930.15, 930.05, 990.03, 945.16, 942.05, and 985.01. ariffin kk, masngut n, seman mna, saufi sm, jamek s, sueb msm (2020) dilute acid hydrolysis pretreatment for 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(2021) microwave-assisted extraction of pectin from pineapple peel. mal. j. fund. appl. sci.17: 33-38. 7 nova biotechnol chim (2022) 21(1): e1175 3 zhang d, ong yl, li z, wu jc (2012) optimization of dilute acid-catalyzed hydrolysis of oil palm empty fruit bunch for high yield production of xylose. chem. eng. j. 181182: 636-642. zhang h, zhang p, ye j, wu y, liu j, fang w, xu d,wang b, yan l, zeng g (2018) comparison of various pretreatments for ethanol production enhancement from solid residue after rumen fluid digestion of rice straw. bioresour. technol. 247: 147-156. zheng y, pan z, zhang r (2009) overview of biomass pretreatment for cellulosic ethanol production. int. j. agric. biol. eng. 2: 51-68. 8 microsoft word att00007.doc nova biotechnologica 8-1 (2008) 45 dna damage by oxidized fatty acids detected by dna/spe biosensor ľudmila sirotová, marcela matulová food research institute, department biocentre, kostolná 7, sk900 01 modra, slovak republic (sirotova@vup.sk) abstract: electrochemical dna/screen-printed electrode biosensor (dna/spe biosensor) was tested for the detection of alterations in dna formed as a consequence of the reaction between dna and oxidative products of fatty acids. interaction of dna with a mixture of products generated during the oxidation of linoleic and oleic acids manifested dna damage depending on a tested fatty acid and the presence of hydroperoxides and thiobarbituric acid reactive substances (tbars) determined after the oxidation of fatty acids. a bigger extent of the dna damage was registered in the case of the interaction with oxidized linoleic acid with the high content of tbars. the results achieved suggest the possible application of dna/spe biosensor in the detection of an interaction between dna and products of fatty acid oxidation. key words: dna/spe biosensor, fatty acid oxidation, dna damage 1. introduction the damage of dna and its consequences have become the closely observed topics in the last years (marnett, 2000; marnett et al., 2003). mutagenicity and genotoxicity of various endogenous and exogenous reactive compounds acting on dna have been connected with ageing, the formation of such illnesses as cancer, cardiovascular and neurodegenerative diseases and immune system decline (hwang and bowen, 2007). some of the studies suggest that the oxidation of fatty acids and the consequent dna damage play an important role in such processes (marnett, 2002; kanner, 2007). the polyunsaturated fatty acids are extremely sensitive to attack of reactive oxygen species. the first products of polyunsaturated fatty acid oxidation are relatively short-lived lipid hydroperoxides. they are reduced to unreactive fatty acid alcohols or react with metals to aldehydes, ketones, alcohols, short fatty acids, esters, hydrocarbons, furans, and lactones, named as secondary products (burcham, 1998). some products are rather long-lived and can drift far from membranes and damage nucleic acids. dna damages may occur as single-strand breaks, double-strand breaks, abasic site formation, sister chromatide exchange, dnadna and dna-protein cross-links, damages to deoxyribose and base adduct formation. the phosphodiester backbone can be also damaged, leaving abnormal ends. such alterations to dna have been shown to disrupt transcription, translation, dna replication and lead to mutations, cell senescence or death (termini, 2000; blair, 2001). methods used for evaluation of dna damage assess the overall state of dna (cleavage of dna strand, changes in structure, presence of bound compounds affecting the properties of dna) or they are based on detecting the formed adducts. gel electrophoresis (bozko et al., 2005; philips et al., 2005) and comet assay (detection of cell dna damage) (gontijo et al., 2001) are the methods currently 46 sirotová, ľ. and matulová, m. employed for assessing the changes in dna. methods for detection of formed adducts allow qualitative and quantitative assessment of damage of individual bases. the detection of the adducts is possible using 32p-postlabelling hplc method (nath et al., 1996), by the chromatographic techniques as gas chromatography/electron capture/negative chemical ionization/mass spectrometry (gc/ec nci/ms) (rouzer et al., 1997), liquid chromatography with electrospray tandem mass spectrometry (lc/esi-ms/ms) (chaudhary et al., 1995; jeong et al., 2005; singh and farmer, 2006) or by immunochemical techniques (kawai et al., 2002). biosensors bring the new possibilities in the area of monitoring of the dna damage (drummond et al., 2003). particularly electrochemical dna/screen printed electrode biosensor (dna/spe biosensor) constitutes a device for a rapid, cheap but sensitive detection of the changes on dna (tudorache and bala, 2007). the detection schemes are based on a redox signal of the dna base (adenine or often guanine) (xie et al., 2007) and/or the special electrochemical indicators (tansil et al., 2005; niu et al., 2006). biosensors have been applied for observing of the alterations of dna due to multiple chemical nucleases, antibiotics (labuda et al., 2000), samples from the environment (mascini, 2001) and have also been used for observing the impacts of the antioxidatively active substances on dna (heilerová et al., 2003; labuda et al., 2003; liu et al., 2006). in our study we have tested dna/spe biosensor as a detection system for the assessment of the influence of oxidized fatty acids on dna. 2. material and methods 2.1 materials oleic acid, linoleic acid and tween 20 were purchased from sigma (steinheim, germany). stock solution of calf thymus dna (calbiochem, darmstadt, germany) 1 mg.ml-1 was prepared in te solution (10 mm tris-hcl with 1 mm edta, ph 8). electrochemical marker [co(phen)3]clo4 was supplied by fchpt stu (bratislava, slovakia). all other chemicals were of analytical grade. 2.2 fatty acid oxidation both linoleic and oleic acid (3 g) were oxidized in rancimat 743 (metrohm, herisau, switzerland) test tube at 150°c for 4 h. the amount of 0.01 g of oxidized fatty acid was homogenized with 100 μl of tween 20 solution (0.5 g/10 ml deionized water). 2.3 peroxide value determination peroxide value was determined by the idf method (shantha and decker, 1994). briefly, oxidized fatty acid (0.01-0.3 g) was mixed in test tube with a mixture of chloroform:methanol 7:3 (v/v). then nh4scn and subsequently fe(ii) solutions were added to the fatty acid solution. the absorbance was measured nova biotechnologica 8-1 (2008) 47 spectrophotometrically at 500 nm against blank solution after 5 min incubation of the mixture in dark. peroxide value was expressed in milliequivalents of peroxides per kg of fatty acid. 2.4 tbars value determination oxidized fatty acid and 2 ml of each 1% tba and 20% iced acetic acid and 1 ml of deionized water were added to the mixture and then heated in a water bath to 100°c for 1 h. after cooling, 5 ml of chloroform were added to the mixture, then the entire mixture was centrifuged at 2 000xg for 10 min. the absorbance of supernatant was measured spectrophotometrically at 532 nm. the value of tbars was expressed in nmol of mda equivalent per g of fatty acid. 2.5 dna/spe biosensor a computerized voltammentric analyzer ecapol 110 (istran, bratislava, slovakia) was equipped by a screen-printed three electrode assembly (vup biocemtrum, modra, slovakia) including a carbon working electrode and the silver/silver chloride reference and counter electrodes. the working electrode, used without any chemical preconditioning, was modified by covering with 5 μl of the dna stock solution and leaving the electrode to dry overnight. dna/spe biosensor was pretreated by immersion in 5 mm phosphate buffer ph 7.0 under stirring for 2 min, then rinsed with water. the [co(phen)3] 3+ indicator was accumulated under stirring for 120 s at an open circuit from 5 ml of its 5.10-5 m solution in 5 mm phosphate buffer. the differential pulse voltammogram (dpv) was recorded immediately from 400 to -400 mv at a pulze amplitude of 100 mv and 2 mv scan step at the scan rate of 25 mv/s. the indicator peak current (i0) was evaluated against the base-line using analyzer software and corrected by a subtraction of the mean indicator peak current measured at the unmodified spe under the same conditions. then, the dna/spe biosensor was regenerated by a removal of the accumulated [co(phen)3] 3+ ions from the dna layer by treating the sensor in 100 mm phosphate buffer ph 7.0 under stirring for 120 s. the peak current i0 was obtained in triplicate. the dna layer was covered with 5 µl of the oxidized fatty acid sample. after 20 min the dna/spe biosensor was treated for 120 s in surfactant solution (0.5 g/100 ml deionized water) (procter and gamble, rakona, czech republic) under stirring at open circuit conditions. the sensor was rinsed with deionized water and then immersed into 5 mm phosphate buffer with [co(phen)3] 3+ indicator for 120 s for its immobilization. the dpv was recorded immediately at the same conditions as above. the peak current i was obtained in triplicate. the degree of dna damage was expressed as the ratio i/i0, the indicator peak current after interaction of dna with oxidized fatty acid (i) against the indicator peak current of unmodified dna on spe (i0). both i and i0 were corrected by a subtraction of the mean indicator peak current measured at the unmodified spe under the same conditions. 48 sirotová, ľ. and matulová, m. 2.6 statistical analysis all data are expressed as the mean ± standard deviation. all raw data were processed using standard ms-excel statistical package. 3. results and discussion dna immobilized on a screen-printed electrode interacted with the solution of oxidized linoleic and oleic acid. the interaction was evaluated using the current response signal of the electrochemical intercalating indicator [co(phen)3] 3+ measured by the dpv technique. a drop in the current response of the indicator indicates the damage of a dna strand or the presence of a competing compound, creating the steric obstacles to the intercalation of the indicator. the lower value of i/i0 ratio the bigger dna damage occurs. the dna damage by oxidized linoleic and oleic acids is showed in fig. 1. the extent of the dna damage was dependent on the conditions of the fatty acid oxidation. the influence of unoxidized fatty acids under the selected conditions showed a moderate decrease in the current response signal of the indicator (by 13% for linoleic acid and by 3% for oleic acid). this could be due to the oxidative products already present in the samples, what can be confirmed by pv (peroxide value) and tbars (thiobarbituric acid reactive substances) values determined for the respective fatty acids (fig. 2 and 3). the dna damage was bigger with the increasing time of oxidation of the tested fatty acid. the course of this dependence had an exponential character. after a 4-hour oxidation the current response signal of the indicator was lowered by 57% in the case of linoleic acid and by 48% for oleic acid. the achieved degree of the dna damage is a result of the interaction between the products formed in the respective stage of fatty acid oxidation and their reactivity towards dna. the dna/spe biosensor detected the bigger extent of the dna damage in the case of the reaction mixture of oxidized linoleic acid compared to oxidized oleic acid. 0 0,1 0,2 0,3 0,4 0,5 0,6 0,7 0,8 0,9 1 0 1 2 3 4 t (h) i/i 0 linoleic acid oleic acid fig. 1: the dependence of the dna damage on the time of fatty acid oxidation assessed by dna/spe biosensor. nova biotechnologica 8-1 (2008) 49 during oxidation of fatty acids a mixture of products is formed depending on the type of fatty acid and the conditions of oxidation. oxidation of fatty acids may be initiated by various ways, such as the presence of reactive oxygen species or other oxidatively active compounds, the activity of the specific enzymes or the increased temperature. as a consequence of oxidation of fatty acid, primary carbon centered radicals l• are produced to give rise to peroxyl radicals loo• which are transformed to hydroperoxides looh. these compounds are further transformed to alkoxyl radicals lo• or decompose rapidly into a multitude of volatile and non-volatile products. alcohols, saturated aldehydes, α,β-unsaturated aldehydes and epoxy compounds have been reported as the major secondary oxidation products (frankel et al., 1992; burcham, 1998). the presence of the respective compounds determines the degree of fatty acid oxidation and this can be detected by laboratory tests such as determination of the peroxide value (determines the amount of hydroperoxides produced – primary products) or tbars value (determines the amount of substances able to react with thiobarbituric acid – secondary products). the comparison of linoleic and oleic acid shows that with the increasing time of oxidation the peroxide value fell but the tbars value rose (fig. 2 and 3). at the same time, the peroxide value was higher in the case of oleic acid, while the tbars value was higher for linoleic acid. a drop in the peroxide value and a rise in the tbars value indicate the successive transformation of hydroperoxides of fatty acids to the secondary products. this transformation is more noticeable in the case of linoleic acid compared with oleic acid. this can be explained by the fact that linoleic acid is more prone to oxidation when compared to oleic acid because of the higher number of multiple bonds. 0 5 10 15 20 25 30 0 1 2 3 4 t (h) p v (m ili ek vi va le nt o f pe ro xi de .k g1 ) linoleic acid oleic acid fig. 2: peroxide value of oxidized fatty acids. based on the comparison of a mixture of oxidized fatty acids and the dna damage it is possible to suggest that under the selected conditions the presence of the secondary products has a more significant influence on the dna damage than the presence of hydroperoxides. the extent of the dna damage is increased with the increasing tbars value. studies on interactions between the dna and hydroperoxides indicate that these compounds react with the dna and cause cleavage 50 sirotová, ľ. and matulová, m. of the double-stranded dna or formation of the hydroperoxide-induced dna adduct (termini, 2000; blair, 2001; kawai et al., 2002; williams et al., 2006). 0 100 200 300 400 0 1 2 3 4 t (h) tb a r s (n m ol .g -1 ) linoleic acid oleic acid fig. 3: tbars amount in oxidized fatty acids. base adducts are preferentially formed by α,β-unsaturated aldehydes, ketones and their epoxides and alkenes (eide et al., 1995). especially the adducts with acrolein, crotonaldehyde (marnett, 1994), malondialdehyde (mda) (marnett, 1999) and 4-hydroxy-2-nonenal (yang et al., 2003), which serve as biomarkers of certain diseases have been thoroughly studied. therefore, the lowered current response signal of the indicator could be the result of the structural changes in the dna strand or due to the base adducts formed, which hinder the indicator from intercalating into the minor and major grooves of dna. 4. conclusions under the selected conditions dna/spe biosensor sensitively responded to the dna damage caused by oxidized linoleic and oleic acids. though the biosensor and the given indicator system does not enable to define the concrete type of the dna damage, it can be used for proving the oxidative alterations in fatty acids or other lipidic samples. to effectively use the biosensor for evaluation of interactions between dna and the oxidative products of fatty acids it is important to take into consideration reactivity of individual generated products towards dna, a mechanism of their action, a type of the damage they cause and the selection of the proper technique and indicator for detection of the dna damage. the mentioned parameters are a subject of further studies. acknowledgement: this work was supported by science and technology assistance agency under the 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(2008) 53 williams, m.v., lee, s.h., pollack, m., blair, i.a.: endogenous lipid hydroperoxide-mediated dna-adduct formation in min mice. j. biol. chem., 281, 2006, 10127-10133. xie, h., yang, d., heller, a., gao, z.: electrocatalytic oxidation of guanine, guanosine and guanosine monophosphate. biophys. j., 2007, l01-l02. yang, y., sharma, r., sharma, a., awasthi, s., awasthi, y.c.: lipid peroxidation and cell cycle signaling: 4-hydroxynonenal, a key molecule in stress mediated signaling. acta bioch. pol., 50, 2003, 319-336. microsoft word farago nb 9-3.doc nova biotechnologica 9-3 (2009) 279 the use of biotechnology in hop (humulus lupulus l.) improvement juraj faragó1,2, ivana pšenáková2, natália faragová1 1plant production research centre, research institute of plant production (ripp), bratislavská cesta 122, piešťany, sk-921 68, slovak republic (farago@vurv.sk) 2department of biotechnology, university of ss. cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic abstract: hop (humulus lupulus l.) is a clonally propagated, dioecious, perennial, climbing plant used commercially for their secondary metabolites. the resins containing αand β-acids, and essential oils produced by the lupulin glands, present on the female flowers are used to add bitterness, aroma and flavour to beer. recently, flavonoids, including chalcones and flavanones, of hops have been shown to exert a variety of biological activities, including oestrogenic and anticancerogenic characteristics. in this review, we provide a overview of the techniques and opportunities presented by the integration of plant biotechnology into hop improvement. the use of tissue culture techniques such as micropropagation, meristem culture, in vitro storage, adventitious shoot induction, callus culture and cell suspension culture in hops are briefly reviewed. the usefullness of genetic transformation technology to introduce novel traits into hop is also discussed. keywords: hops, biotechnology, tissue culture, genetic transformation, secondary metabolites 1. introduction the hop plant (humulus lupulus l.) is widely cultivated throughout the temperate zones of the world for its female inflorescences (commonly referred to as ‘cones’), which are used in the brewing industry to add bitterness, aroma and flavour to beer. before using in brewing industry, hops were traditionally used as herbal medicines, mainly for the treatment of sleeping disorders, as a mild sedative, and for the activation of gastric functions as bitter stomachic (zanoli and zavatti, 2008). currently, the beer brewing industry accounts for 98% of the world use of hops (moir, 2000). hop oil fractions and hop extracts are also used as flavoring products in nonalcoholic beverages and foods. in addition to improving the agronomic traits, hop breeding also aims to tailor the components of the plant important for brewing to the demands of the market. thus, there is an ever increasing need for cultivars exhibiting superior performance in multiple traits, such as high levels of α-acids, excellent flavour, good storage stability and high yield. until very recently, plant breeding relied solely on the accumulated experience of generations of farmers and breeders, that is, on sexual transfer of genes between related plant species. in the last 150 years, however, plant breeding has developed into a complex discipline that now incorporates information from many branches of science and mathematics. the most recent development is the utilization of biotechnology for plant improvement (pauls, 1995). for the purposes of this review, 280 faragó, j. et al. plant biotechnology can be defined as the application of tissue culture and molecular genetics to develop or produce a commodity from plants. plant tissue culture refers to the maintenance and propagation of plant parts (organs, tissues, and single cells) in biologically pure (axenic) and controlled environments, while molecular genetics includes the techniques for isolating, characterizing, recombining, and transferring discrete fragments of dna containing genes coding for specific traits into other, nonrelated, genetic backgrounds. the purpose of this review is to provide a brief overview of the techniques and opportunities presented by the integration of plant biotechnology into improvement of hop (h. lupulus l.) species. 2. biological characteristics of hops 2.1 taxonomy the genus humulus belongs to the family of cannabinaceae, previously placed in the order urticales, but in 2003 incorporated in the order rosales (bremer et al., 2003). the genus consists of three species: humulus lupulus linneus, humulus japonicus siebold & zucc. and humulus yuannensis hu (small, 1978; neve, 1991). the centre of origin of the genus is considered to be china, because all humulus species have been found in this area (neve, 1991; murakami et al., 2006). h. japonicuc is native to japan, taiwan and china, while h. yuannensis is native to high altitudes of the yunan province in china. h. lupulus, which is almost exclusively cultivated for brewing purposes, was first domesticated in central europe in the middle of the ninth century, and is currently naturalized throughout the north temperate regions of the world as well as some temperate regions in australia, south africa, and south america (chadwick et al., 2006). based on their morphological characteristics and geographical locations small (1978) classified the species humulus lupulus into five taxonomic varieties: var. lupulus small (european hops), var. cordifolius small (japanese hops), var. neomexicanus nelson & cockerell, var. pubescens small and var. lupuloides small (north american hops). 2.2 botany common hop is a dioecious perennial plant which produces new shoots each year in early spring from rhizomes of an underground rootstock. the outgrowing climbing vine grows up to 6-9 m in length and senesces to the perennial rootstock in autumn (krištín, 1987; rybáček, 1980). the stems twist around their support in a clockwise direction. the dioecious nature of the plant means that the male and female flowers are on separate plants (fig. 1). however, individual monoecious plants have been found in some wild north american hop populations (haunold et al., 1993). the male flowers are 7-14 cm long racemes (fig. 1a), while the female inforescences are 2.5-5.5 cm long cone-like catkins (strobiles, fig. 1b), made up of overlapping flattened membranaceous bracts. at the base of cone bracts a number of yellow glandular trichomes can be found, which secrete a resinous substance, known as lupulin (rybáček, 1980). only female plants are cultivated in hop gardens, while nova biotechnologica 9-3 (2009) 281 male plants are essential in hop breeding programs aimed at developing new varieties through controlled hybridization (rybáček, 1980; neve, 1991). the cultivated hop is a short-day plant that initiates flowering when the plant is at a critical size (about 6 m, 20-24 nodes) and critical daylength is about 16 h, beyond which flowering cannot be induced (villacorta et al., 2008). the minimum daylength, below which the plant ceases vegetative growth and forms dormant terminal buds, is considered to be 8-10 h. from the cytological point of view, cultivated hop is a diploid (2n = 20) species with heteromorphic sex chromosomes (xx in female plants, xy in males) (danilova and karlov, 2006). fig. 1. male (a) and female (b) inflorescences of hop. (foto: j. farago) 2.3 breeding at the earliest hop plants were collected in the wild. according to wilson (1975) the cultivation of hops started in germany the middle of the ninth century, between a.d. 859 and 875. the interest in selection of new and improved hop variants grew significantly during the nineteenth century when selections were made by the growers from variants observed in their own gardens (moir, 2000). hop breeding started with these clonal selections from adapted wild hops, which has lead to cultivation of lanraces like fuggle and goldings in england, tettnanger and hallertauer mittlefruer in germany and saazer in czech republic. these varieties and their derivatives are still in production today and are typical representatives of european aroma hops with relatively low yield and resin content (stajner et al., 2008). modern cultivars of hops are derived by sexual hybridization which allows the tailoring of hop aroma and bitterness, as well as the introduction of new traits. current breeding practices are aimed primarily at improving the disease resistance (verticillium wilt, downy mildew, and powdery mildew), increasing the resin content, and combining traits by utilization of cultivars and breeding lines or wild hops with favourable properties. today’s basic sources of plant breeding material are maintained in hop germplasm collections, which have been established at main hop breeding centres (stajner et al., 2008). hop is sensitive to different types of pathogens, such as viruses, viroids, bacteria and fungi, which adversely affects its yield and product quality. there is still a shortage of effective chemicals for pest and disease control, and crop yields are consequently subject to dramatic seasonal variation. in most hop-growing countries 282 faragó, j. et al. one of the main objectives of recent breeding programs have been to raise the α-acid content. there is also an increased demand for improved varieties of hops which differ in their resin content, produce different bitterness levels in beers and have increased ability to preserve beer. in some countries, for example in australia and england, tetraploid parents play an important role in hop breeding, as they can be crossed with diploids to produce triploid progeny. the large number of grown hop varieties fall generally into two groups: alpha (or bitter hops) and aroma hops. bitter hops are high alpha acid content, whereas aroma hops have much lower content (<5%). 2.4 phytochemistry more than 1000 chemicals have been identified from hops (chadwick et al., 2006). the main structural classes of chemical compounds identified in hops include terpenes, bitter acids, and chalcones. hundreds of terpenoid compounds identified in the essential oil component of hops account for 0.3-1.0% of strobile weight. the study of the composition of hop essential oils revealed that hydrocarbons usually constitute 40–80% of the oil and, apart from a few simple alkanes, they all are of terpenoid origin. a complex group of at least 40 acyclic, monocyclic, bicyclic, and tricyclic sesquiterpenes is usually dominated by α-humulene, β-caryophyllene, and farnesene. of the monoterpenes, myrcene is the primary component of hop essential oils (moir, 2000; roberts and lewis, 2002). the analysis of hop essential oils helps in determining both hop quality and varietal discrimination (roberts and lewis, 2002). the bitter acids comprise 5-20% of hop strobile weight. they are classified as either α-acids or β-acids which are, respectively, dior tri-prenylated phloroglucinol derivatives. in addition, they each contain a 3-, 4-, 5-, or 6-carbon oxo-alkyl side chain (verzele and keukeleire, 1991). the bitter acids are present in hop cones as a complex mixture of variable composition and concentrations, depending on the variety and growing conditions. the α-acids, particularly humulone (35–70% of total α-acids), cohumulone (20–65%), and adhumulone (10–15%) are regarded as the most important constituents in determining the quality of hops (verzele and keukeleire, 1991; chadwick et al., 2006). the biochemistry (biosynthesis, isomerization, oxidation and degradation) of hop bitter acids have been extensively studied (verzele and keukeleire, 1991; goese et al., 1999). the dried hop cones contain 4–14% polyphenols, mainly phenolic acids, prenylated chalcones, flavonoids, catechins and proanthocyanidins (gerhäuser, 2005). the flavonoids of hops include flavonol glycosides, condensed tannins, and prenylflavonoids (stevens et al., 1998). the majority of known flavonoids from hops can be considered as derivatives of the compound 2',4,4',6'-tetrahydroxy-3'prenylchalcone, commonly known as desmethylxanthohumol (dmx) (chadwick et al., 2006). the most abundant and most important prenylated flavonoid in fresh, and properly preserved hops, is the chalcone xanthohumol, present at concentrations of 0.01–0.5% (stevens et al., 1999). recently, xanthohumol (xn) was identified as a broad-spectrum cancer chemopreventive agent with inhibitory mechanisms in the initiation, promotion and progression phase of carcinogenesis (miranda et al., 1999). in addition, another prenylated flavonoid of hop, 8-prenylnaringenin (8-pn) was identified as a very potent phytoestrogen (milligan et al., 1999). nova biotechnologica 9-3 (2009) 283 3. biotechnology of hop improvement 3.1 micropropagation traditionally, hop cultivars are vegetatively propagated by layering young vines under the soil or by rooting soft-wood nodal cuttings during the growing season (neve, 1991). tissue culture techniques can be used as alternative means of plant multiplication. the clonal propagation of plants in vitro is called micropropagation. thus micropropagation can be characterized as the multiplication of genetically identical individuals by asexual reproduction. a significant advantage offered by the aseptic methods of clonal propagation over the conventional methods is that in a relatively short span of time and space a much larger number of plants can be produced from an individual (chawla, 2002). in vitro micropropagation of hop is feasible starting from node cuttings, apical tip explants (roy et al., 2001; smýkalová et al., 2001), meristems (adams, 1975), and parts of the shoot or leaves (batista et al., 1996; peredo et al., 2006). roy et al. (2001) used nodal explants of hop variety h138 to test the effect of plant growth regulators and different media formulations on shoot multiplication efficiency. they achieved efficient culture establishment (96.6% of explants) on murashige and skoog (ms) media supported with plant growth regulators indoleacetic acid (iaa, 0.57 μm) and 6-benzylaminopurine (ba, 2.22 μm). however, in subsequent multiplication media, addition of the cytokinin n-phenyl-n'-1,2,3-thidiazol-5-ylurea (tdz) resulted in significantly higher number of shoots and nodes generated per explant compared to media containing ba, 6-(γ,γ-dimethylallylamino)purine (2ip) or kinetin (kin). smýkalová et al. (2001) developed an efficient in vitro micropropagation system for czech and several foreign hop mericlones using low sugar, starch-gelrite media. the use of this medium resulted in lower cost of micropropagation of healthy hop cultures without exhibition of vitrification. in clonal propagation of plants, such as commercial cultivars of hops, it is very important to keep the genetic stability of recovered plants. however, due to genetic and epigenetic changes induced by the in vitro culture environment, the phenotype of the regenerated plants may be different from the original mother plant in some cases (kaeppler and phillips, 1993). the use of molecular techniques as a method for evaluating genetic stability of tissue culture derived plants is frequently described in the literature since molecular markers can characterize the fenomenon of somaclonal variation with much greater precision and lesser effort than karyological and phenotypic analyses. in hops, peredo et al. (2006) used the amplified fragmentlength polymorphism (aflp) and methylation-sensitive amplified polymorphism (msap) techniques to characterize the genetic and epigenetic variation in hop plants regenerated from sequential subcultures of organogenic calli. they detected no major genetic rearrangements in the callus-derived plants since none of the aflp loci were polymorphic, however, epigenetic changes due to a demethylation process were detected by the msap technique. the epigenetic changes were found to increase when the calli were maintained over a longer period in tissue culture. micropropagation is often used to mass propagate virus-free stock plants obtained by the use of meristem culture technique. 284 faragó, j. et al. 3.2 meristem culture among the prevalent tissue culture techniques used in agricultural biotechnology, the meristem and shoot tip culture have been exploited at a much wider scale primarily due to their potential applicability in diverse areas, such as virus elimination and production of virus-free stock plants, rapid clonal multiplication of vegetatively propagated plants, and germplasm preservation of both vegetatively and seed propagated crop species (nehra and kartha, 1994). the meristem-tip propagation technique used for production of virus-free plants was the first direct application of tissue culture technology to hop improvement by vine and jones (1969) at east malling research station in united kingdom. this approach proved to be very successful and was extended by gippert et al. (1974) in germany, by adams (1975) in the uk, by kubo et al. (1975) in japan, by samyn and welvaert (1983) in belgium, by popov et al. (1985) in the previous ussr, and by probasco and winslow (1986) in the usa. more recently the meristem culture technique was applied to produce virus-free stock plants also in czech republic (svoboda, 1992) and slovakia (faragó and nešťáková, 1998), respectively. in our laboratory at ripp piešťany, meristem culture was successfully applied to all ten cultivars tested. in average around 70% of meristems developed 1 to 4 shoots during the 28 day-long culture period on msc induction medium. in total 299 mericlones were obtained and subjected to thermotherapy. the viability of cultures after thermotherapy was in average 65% (faragó and nešťáková, 1998). starting with year 1996, the hop yards in slovak republic were replanted with meristem culture-derived virus-free plants, which caused a substantial increase in yield parameters in subsequent years (for example almost doubled α-acid content) (košútová, 2002, pers. comm.). now, the cultivation area of meristem culturederived hops in slovakia is cca. 350 ha, representing about 0,8% of the total production in the european union. meristem-tip culture has been widely used for the production of virus-free plant material in many species propagated mainly or exclusively by vegetative means. this technique enables the mother plant’s genetic features to be conserved maximally in the regenerated plants. virus elimination through tissue culture techniques, however, requires efficient plant regeneration systems. 3.3 in vitro storage hop germplasm is traditionally preserved in the form of field collections in areas of cultivation (revilla and martínez, 2002). however, conservation of plants in natural conditions is costly in terms of land utilization, labour and risks of losses through environmental hazards and diseases (watt et al., 2000). in addition, virus diseases can accumulate in a field collection and be transferred to additional sites by vegetative propagation (reed et al., 2003). in vitro techniques have been found to be useful in ex situ conservation of a number of plant species (villalobos and engelmann, 1995), including meristem culture-derived virus-free germplasms (fletcher et al., 1998). the storage longevity of in vitro collections depends on many important factors such as explant type, culture medium composition and culture conditions (aynalem et al., 2006; faragó et al., 2008) nova biotechnologica 9-3 (2009) 285 according to reed et al. (2003) the u.s. department of agriculture, ars, national clonal germplasm repository at corvallis (oregon, usa) maintains about 700 accessions of humulus spp. germplasm in field collections, in pots in the screen house, and as tissue cultures in cold storage or as cryopreserved shoot tips in liquid nitrogen. at the plant production research centre – research institute of plant production (piešťany, slovak republic) we maintain more than 100 accessions of 10 cultivars (osvalds clones 31, 72 and 114, bor, sládek, siřem, aromat, lučan, zlatan and premiant) of predominantly meristem culture-derived virus-free hop genotypes (94 clones) using an optimized in vitro storage system (tab. 1). eight clones were introduced into in vitro culture in 1994, 94 clones in 1996 and 11 clones in the year 2000. accessions are represented by 4 culture vessels (baby food jars, fig. x) with 67 nodal explants in each. the subculture interval of cultures maintained in slow growth conditions ranges from 12 to 18 weeks. the cultures are regularly inspected for the potential occurrence of latent endocontaminating bacteria and the genetic stability of in vitro stored plant material is studied by molecular analysis of microsatellite markers (faragó et al., 2008). table 1. optimization of tissue culture system for in vitro storage of meristem culture-derived hop germplasm. variants marked with bold tetters were chosen to slow down the growth of in vitro shoot cultures. parameter variant mineral content of medium full strength, ½ strength, ¼ strength sugar concentration 2, 3, 4 and 6% glucose; 2, 3, 4 and 6% sucrose solidifying agent 2,5 % phytagel, 7 % agar plant growth regulators 0, 0.05, 0.1, 0.15, 0.2, 0.25 mg.l -1 bap; 0, 0.5, 1.0, 1.5, 2.0 mg.l-1 ga3 culture vessel type baby food jars, industrial glass, magenta vessels, test tubes vitrovent vessels explant type growth tip, defoliated nodal segment, non-defoliated nodal segment cold treatment 25/20°c, 15/10°c and 5±2°c plant growth retardants ancymidol and paclobutrazol at 0, 1, 2.5, 5 and 10 μm; mannitol and sorbitol at 0, 10, 20, 30 and 40 mg.l-1 fig. 2. in vitro storage of hop germplasm using the optimized slow growth method (photo: j. farago). 286 faragó, j. et al. 3.4 adventitious shoot regeneration beside the importance in different tissue culture techniques, regeneration of plants in in vitro culture is also an essential prerequisite for generation of transgenic plants. however, only a few reports are available to date on the regeneration of hop tissues other than meristems (motegi, 1976; rakouský and matoušek, 1994; batista et al., 1996; gurriarán et al., 1999). motegi (1976) reported a successfulr regeneration of plants from callus cultures derived from leaf explants. rakouský and matoušek (1994) published a protocol for direct organogenesis of two commercial czech hops on media containing bap or zeatin. they achieved the highest regeneration of shoots from either petioles or internodes at frequencies 2l % and 52 %, respectively. batista et al. (1996) tested the organogenic ability of petiole and stem segments of two hop varieties on three different basal media supplemented with 0.025 mg.l-1 indole-3-acetic acid (iaa) and 2.0 mg.l-1 6benzylaminopurine (bap). these conditions induced rather heterogeneous responses, which depended mainly on the explant source and the genotype. the regeneration rate of cultures was also highly correlated with the production of green, nodular areas in the compact calli. gurriarán et al. (1999) established a very efficient protocol for plant regeneration from two commercial hop cultivars, brewers gold and nugget, and studied the morphogenetic potential of explants cultured on adams modified medium supplemented with several concentrations of cytokinins and auxins. regeneration rates of 60 and 29% were achieved for nugget and brewers gold, respectively. we developed a highly efficient in vitro system for adventitious shoot regeneration from leaf and internode explants of 12 hop genotypes (fig. 3; faragó and kollárová, results not published). the highest percentage of plant regeneration (52.7 %) was achieved in genotype zlatan/1/2t from internode explants cultured on media supplemented with 2.0 mg.l-1 bap and 2.0 mg.l-1 naa and when maltose was used as carbon source. all the tested genotypes produced adventitious shoots with average frequencies of 1.4-17.4%. the regeneration frequency depended on the explant type (internode segment vs. leaf segment), auxin type (2,4-d vs. naa), and csource (glucose vs. maltose). fig. 3. adventitious shoot regeneration from internode and leaf segment explants of the hop genotype k72/6/13 (photo: j. farago). nova biotechnologica 9-3 (2009) 287 3.5 callus culture secondary metabolites of hops important for the brewing of beer include α-acids and ß-acids, however, another group of compounds present in hops, such as prenylated chalcones, xanthohumol, and desmethylxanthohumol, were recently found to exhibit interesting bioactive properties. the increased demand for medicinally important secondary metabolites increases the pressure to produce these compounds via alternative ways, especially using cell/tissue cultures and transgenic plants, respectively. griffin and coley-smith (1968) first initiated hop callus cultures with the aim of study in aseptic conditions the infection process of fungus pseudoperonospora humuli. callus cultures in hops have been used experimentally to provide a source of regenerationg green nodular callus, for attempted selection of novel disease resistance to verticillium albo-atrum in somaclonal variants, as well as providing a sterile source of leaf mesophyll protoplasts (connell and heale, 1986b; heale et al., 1989). there were also attempts to establish regenerating, organogenic callus caltures from different types of explants (motegi, 1976; batista et al., 1996). undifferentiated, white calli was produced from stem internodal segments, petioles, and leaf segments (connell and heale, 1986b; heale et al., 1989; pšenáková et al., 2009) currently, in line with a growing interest in the health benefits of medicinal plants, hop has received particular attention by the researchers due to the identification of pharmacologically relevant compounds, such as flavanones, chalcones, and phloroglucinol derivatives in hop cones (zanoli and zavatti, 2008). therefore, we study the possibility to establish a convenient in vitro system, based on the induction of callogenesis and establishment of cell suspension culture in hops for chemical analyses of constituents of in vitro cultures and for potential production of interesting flavonoids in in vitro culture systems (pšenáková et al., 2009). our system is based on induction of callus formation from two types of explants (internodal segments and leaf segments isolated from in vitro grown shoot cultures) on media containing the combination of auxin and cytokinin growth regulators bap, naa, and 2,4-d. content of total polyphenols depended on culture conditions and ranged from 76.6 to 158.5 mg.l-1 of gallic acid equivalent (gae) in our callus cultures (pšenáková et al., 2009). 3.6 cell suspension culture the culture of plant cells on a large scale has long been regarded as a potential source of secondary products. large-scale tissue cultures were and are seen as a more convenient and reliable source of secondary products than intact plants (collin, 2001). plant cell suspension cultures offer the manufacturer independence from fluctuations in supply of the raw plant material that might have been created by vagaries in the climate, agriculture and political activities of the source country. growing plant cells in vitro also permit a stricter control of the quality of the products. problems connected with gathering, storing, processing and disposal of huge amounts of biomass, connected with extraction of active substances from in vivo plants are also 288 faragó, j. et al. solved (ionkova, 2007). suspension cultures are of special interest due to their high growth rate and short cycle of reproduction. the first cell suspension cultures of hops have been established by robbins and ratcliffe (1984) to study the intracellular distribution of phosphate in hop cells growing in media with elevated phosphate concentrations. later, cell suspension cultures were established with the aim of attempted production of α-acid compounds (robbins et al., 1985; furze et al., 1987). connell et al. (1986a) studied the interaction of verticillium wilt toxins with suspension cells. various research groups performed some biological and phytochemical studies on hop callus and cell cultures. for example langezaal and scheffer (1992) initiated cell suspension cultures of various hop cultivars and screened them for the presence of bitter acids by hplc and of volatile compounds by capillary gc. however, they could not detect neither bitter acids nor volatile compounds. trevisan et al. (1997) studied the effect of elicitation on peroxidase activity in cell suspension cultures of one variety and four cultivars of hop. we are interested in the potential of plant cell cultures to produce secondary metabolites, such as polyphenols, flavonoids and prenylated chalcons. as a model system we use hop callus and cell suspension cultures. we established cell suspension cultures from stabilized callus cultures of hop cultivar osvald's clone 72 in liquid ms media containing different combinations of plant growth regulators. cell suspension cultures were derived from two types of explants, stem segments and leaf segments and were cultured in two types of culture conditions. they showed high biomass accumulation (fw and dw), depending on the explant type, medium composition and culture conditions. the viability of cells (assessed as % of ttc-positive cells) depended on the concentration of pectinase added to liquid media to liberate cells from cell clumps and ranged from 60.9-90.6 % in media without pectinase to 36.2-65.4 % in media with 1000 μl pectinase.g-1 tissue fw. content of total polyphenols depended on the type of in vitro culture and ranged 60.5-137.1 mg.l-1 of gae in comparison to 121.4 mg.l-1 gae in the source shoot cultures of hops. using hplc analysis, we were able to detect also the production of xanthohumol in cell suspension cultures of hops. the highest production of xanthohumol was observed in cell suspension cultures established from leaf segment-derived calli in medium containing 1.0 mg.l-1 bap in combination with 1.0 mg.l-1 2,4-d without pectinase and cultured in dark conditions (pšenáková et al., 2009). 3.7 genetic transformation genetic engineering, or the ability to transfer genetic information from one species to another, has been possible for about three decades. the advantages of genetic engineering in hop breeding are obvious. in contrast to conventional breeding programs involving cross-pollination, the agronomic and qualitative traits of hops can be improved by inserting a single (or a few) gene(s) of interest with no other changes in the genome. a renewed interest in genetic transformation of hops has arisen from the finding that some hop compounds have remarkable bioactive properties showing strong estrogenic and anticancer activities, and therefore hop is regarded as strong candidate to molecular farming. nova biotechnologica 9-3 (2009) 289 genetic transformation of hop using agrobacterium tumefaciens is regarded as the most promising approach since hop in one of the natural hosts of this soil bacterium (de cleene and de ley, 1976). however, only a few reports have been published on genetic transformation of hop using this technique, moreover, these experiments were not successful (becker, 2000), or irreproducible (oriniaková and matoušek, 1996). the first report on successful transformation of hop tissues by a. tumefaciens, and regeneration of transgenic plants of cv. tettnanger was reported by horlemann et al. (2003). only two other papers have been reported on the successful production of transgenic hop plants containing gus reporter and/or nptii selection genes with the use of a. tumefaciens-mediated system [okada et al., 2003 (cv. osvald’s clone 72); škof and luthar, 2005 (cv. aurora)]. recently schwekendiek et al. (2007) reported on hop (cv. tettnanger) transformation with a grapevine stilbene synthase gene using the system developed by horlemann et al. (2003). biolistic transformation has proven to be a powerful and versatile technique and an alternative to agrobacterium-mediated transformation. recently batista et al. (2008) developed a successful transformation system for hops using particle bombardment. they were able to establish a reproducible and efficient method for gene transfer and transgenic plant regeneration in hop var. eroica. 4. conclusions biotechnology is now applicable to many aspects of hop improvement. to be effective, plant biotechnology must be well integrated into established plant breeding programs and crop production practices. plant cell cultures of hops can produce many valuable secondary metabolites including novel medicinal agents and in combination with synthetic chemistry, the tissue culture techniques can afford an attractive route to synthesis of complex natural products and related compounds of industrial importance. application of biotechnology to hop improvement will also make diverse germplasm sources more valuable than ever before, because genetic material from different species, genera and even kingdoms can now be stably incorporated and expressed in hops. very few reports on genetic transformation of hop have been published so far, and, in part, this can be explained by the difficulty to establish efficient plant regeneration systems that are still highly genotype dependent. nevertheless, genetic transformation may be a powerful tool for improving agronomic and qualitative traits of hops as well as enhancing the productivity of secondary metabolites in transgenic cell cultures. references adams, a.n.: elimination of viruses from the hop (humulus lupulus) by heat and meristem culture. j. hort. sci., 50, 1975, 151-160. aynalem, h.m.; righetti, t.l.; reed, b.m.: iron formulation affects in vitro storage of hops an image analysis. in vitro cell. dev. biol. – plant, 42, 2006, 405-410. 290 faragó, j. et al. batista, d.; sousa, m.j.; pais, m.s.: plant regeneration from stem and petiolederived callus of humulus lupulus l. 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zavatti, m.: pharmacognostic and pharmacological profile of humulus lupulus l. j. ethnopharmacol., 116, 2008, 383-396. microsoft word farago nb.doc nova biotechnologica vii-i (2007) 63 biotechnological tools to improve ethanol production from plant biomass juraj farago1,2 1slovak agricultural research center, research institute of plant production, bratislavská cesta 122, piešťany, sk-921 68, slovak republic (farago@vurv.sk) 2department of biotechnology, university of ss. cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic abstract: increasing concerns for security of the fossil fuel supply emphasizes the need to complement fossil fuel-based energy sources with renewable energy sources. plant biomass represents an abundant renewable resource for the production of bioenergy and biomaterials. this review summarizes the last advancements in the use of biotechnological tools to improve bioethanol production from plant biomass through genetic engineering the starch content and composition and lignocellulosic matter characteristics, and increasing the capacity of plants to produce harvestable yield and ameliorating the negative abiotic stresses on plants so as to increase yield. key words: biotechnology, genetic engineering, starch, lignocellulose, crop yield 1. introduction the production of ethanol for use as a transportation fuel is not a new technology. it was first introduced in the u.s.a. in the 1930s, when the ford model t was able to run on either gasoline or ethanol (kovarik, 1998). post world war ii, however, the interest in the use of agricultural crops for ethanol production dropped, mainly because of the availability of cheap and abundant fuel from fossil sources. renewed interest in ethanol as fuel developed in the 1970s (bothast and schlicher, 2005). brazil was the world’s first country to run large-scale program for using ethanol as fuel (de oliveira et al., 2005), and in the united states ethanol has been utilized as a fuel source since the turn of the century (bothast and schlicher, 2005). in slovak republic, the production of corn-based bioethanol started in this year (p. kostík, enviral, personal communication). it is now understood, that it is important to use plant biomass energy, that would complement solar, wind, and other intermittent energy sources. biomass is considered an interesting energy source for several reasons (see lin and tanaka, 2006). most agricultural biomass containing starch or sucrose can be used as a substrate for ethanol fermentation by microbial processes. these “energy crops” include maize (corn), wheat, rice, potato, cassava, sugarcane and sugarbeet. currently used crops, however, are non-optimized for biofuel production. thousands of years of traditional breeding through phenotypic selection have resulted in modifications that are better fit for harvesting for feed or food uses (mclaren, 2005). genetic engineering can offer viable opportunities to increase bioethanol production from crop plants principally in two ways: modifying the biomass properties 64 farago, j. and/or increasing biomass yield. this article will review the latest advancements in the research and development focused on these two topics. 2. biomass properties 2.1 starch content and structure starch is by far the most important storage carbohydrate found in plants. annually, 20-30.106 tons of starch are produced to serve a wide range of industrial applications such as coating of textiles and paper, or as a thickening or gelling agent in the food industry (heyer, 2000). most of the starch is isolated from corn, but also potato, wheat and cassava are sources of starch. starch is deposited in the plastidic compartment of plants as granular material, for example in the amyloplasts of plant storage organs, such as seed andosperms or tubers. it is composed of two glucose polymers, amylose and amylopectin. in the linear polymer amylose, the glucose monomers are linked by α-1,4-glycosidic linkages. in contrast, the molecule of amylopectin is branched and various amount (about 5% in maize) of its glucose units are linked by α-1,6-glycosidic linkages. the molecular weight of amylopectin is higher (107-108 da) than that of amylose (105-106 da). normally, starches contain 70-80% amylopectin in contrast to 20-30% amylose (heyer et al., 1999). the biosynthesis of starch is sufficiently understood to allow genetic engineering of plants for higher accumulation or modified composition. alteration of starch structure and content can be achieved by modifying genes coding for enzymes responsible for starch synthesis (heyer, 2000; jobling, 2004). transgenic plants with modified expression of different starch synthases, starch branching enzymes or starch debranching enzymes have been produced to increase the accumulation of starch (tjaden et al., 1998; mckibbin et al., 2006) or to alter the crystallinity of starches and thus increase the accessibility to enzymatic digestion (baga et al., 1999; otani et al., 2007). stark et al. (1992) demonstrated an increase of up to 135% of control starch content was obtained following the constitutive expression of a regulatory variant of bacterial adpglucose pyrophosphorylase (agpase). another possibility is to decrease the gelatinization temperature of modified starches to reduce the energy requirement for the conversion of starch to ethanol. recently, for example, chiang et al. (2005) showed that overexpression of a thermostable and bifunctional starch hydrolase, amylopullulanase (apu) from thermoanaerobacter ethanolicus 39e in rice seeds resulted in starch, that could be hydrolyzed with optimal temperatures between 85 and 95 °c to complete conversion into soluble sugars. 2.2 lignocellulosic biomass lignocellulusic biomass is renewable, cheap and readily available with over over 10-50.109 tons produced per year at the global level (sticklen, 2006). lignocellulose is a more complex substrate than starch. it is composed of a mixture of different carbohydrate polymers (cellulose and hemicelluluse) and lignin. nova biotechnologica vii-i (2007) 65 the biological process for converting the lignocellulose requires several steps: (1) delignification to liberate cellulose and hemicellulose from their complex with lignin, (2) depolymerization of the carbohydrate polymers to produce free sugars, and (3) fermentation of mixed hexose and pentose sugar to produce ethanol (lin and tanaka, 2006). the major costs of biomass refineries include the pre-treatment processing of the lignocellulosic matter at the delignification step, and the cost of production of the microbial cellulases needed to convert the cellulose biomass into fermentable sugars (kabel et al., 2005; sticklen, 2006). genetic engineering provides tools to decrease both of these costs. several approaches have been use to accomplish these goals. firstly, genetic transformation of plants can decrease the lignin content and/or change the composition of lignin. lignins are complex three-dimensional polymers embedded in the cell walls of plant cells. in order for cellulases to access the cellulose for degradation, costly and harsh heat or acid pretreatment of biomass is required to remove lignin and hemicellulose from the lignocellulosic matter. transgenic manipulation of different lignin biosynthetic pathway genes have been attempted to decrease lignin content (piquemal et al., 2002; chen and dixon, 2007) or alter lignin composition (ralph et al., 2006) and thus reduce the pre-treatment costs. secondly, transgenic plants can be designed to overexpress enzymes for cellulases, such as endoglucanases, exoglucanases and βglucosidases, or produce recombinant (microbial) cellulases within the biomass crop. recently, montalvo-rodriguez et al. (2000) have used this approach to generate transgenic plants constitutively producing either a hyperthermofilic αglucosidase or β-glycosidase using genes derived from the archeon sulfolobus solfataricus. the authors showed that transgenic plant protein extracts released glucose from purified polysaccharide substrates at appreciable rates during incubation in high-temperature reactions. in another study, oraby et al. (2007) constitutively expressed the catalytic domain of acidothermus cellulolyticus thermostable endoglucanase gene (e1) in rice and observed that approximately 30% of the cellulose of ammonia fiber explosion-pretreated maize biomass was converted into glucose using rice e1 heterologous enzyme. lastly, genetic engineering can be employed to produce recombinant microbial cellulases and/or ligninases in bioreactors (e.g. galliano et al., 1988, jin et al., 2004). 3. biomass yield biomass yield is a very complex trait. unlike the genes for starch, cellulose and lignin biosynthesis, the majority of genes involved in the yield traits remain elusive. therefore, it was believed, that yield as a trait can not be easily manipulated through genetic engineering approaches. however, current achievements in genetic transformation technology suggest, that biomass yield increase and stabilization can be achieved through understanding and enhancing such mechanisms as stress tolerance (vinocur and altman, 2005, umezawa et al., 2006), nitrogen assimilation (harrison et al., 2000), and carbohydrate metabolism (sakamoto and matsuoka, 2004). crop yields can be increased by increasing leaf photosynthetic rates. considerable effort has been focused, for example, on molecular modification of 66 farago, j. photosynthesis by introducing the precursor pathway for organic acid fixation of co2 (c4 pathway) into c3 species (matsuoka et al., 2000; evans and von caemmerer, 2000). another way to improve photosynthesis may be modifying plant architecture to adjust to the high planting density currently used in agriculture (sakamoto and matsuoka, 2004). in cereals, grain yield is the main target for genetic improvement. adpglucose pyrophosphorylase is frequently referred as the rate limiting enzyme in starch biosynthesis and as such the key enzyme regulating sink strength. recent reports on transgenic deregulation of agp suggest a possibility to increase plant sink strength and subsequently the seed and biomass yield (smidansky et al., 2003, 2007). enhanced stress tolerance in plants through genetic engineering has been achieved through manipulation of effector genes (e.g. biosynthetic enzymes, ion transporters) or regulatory genes (e.g. transcription factors or signal transduction components) (fao, 2001). 4. conclusion in the future, fuel ethanol will remain an attractive option, at least because it is a renewable energy source, creating a substantial new market for different high energy crop supplies and new jobs. genetic engineering can effectively contribute to and provide great potential for future agriculture and biofuel production. however, to fully exploit the potential of modern biotechnology tools, it is necessary to increase the public acceptance of biotech-derived crops. also, in many countries the legislation concerning plant biotechnology and the regulatory system lags behind the advancement of a technology. however, genetic engineering to improve biomass characterization will be economically feasible if the social benefits from the adoption of the technology will be greatest than its social costs. references båga, m, repellin, a., demeke, t., caswell, k., leung, n., chibbar, r.n., abdel-aal, l.-s., hucl, p.: wheat starch modification through biotechnology. starch-stärke, 51, 1999, 111-116. bothast, r.j., schlicher, m.a.: biotechnological processes for conversion of corn into ethanol. appl. microbiol. biotechnol., 67, 2005, 19-25. chen, f., dixon, r.a.: lignin modification improves fermentable sugar yields for biofuel production. nature biotechnol., 25, 2007, 759-761. chiang, c.-m.; yeh, f.-s.; huang, l.-f.; tseng, t.-h.; chung, m.-c.; wang, c.-s.; lur, h.-s.; shaw, j.-f.; yu, s.m.: expression of a bi-functional and thermostable amylopullulanase in transgenic rice seeds leads to autohydrolysis and altered composition of starch. mol. breed., 15, 2005, 125-143. de oliveira, m.e.d., vaughan, b.e., rykiel, e.j.: ethanol as fuel: energy, carbon dioxide balances, and ecological footprint. biosci., 55, 2005, 593-602. evans, j.r., von caemmerer, s.: would c4 rice produce more mass than c3 rice?. in: j.e. sheehy et al. 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biotechnol., 17, 2006, 113-122. vinocur, b., altman, a.: recent advances in engineering plant tolerance to abiotic stress: achievements and limitations. curr. opin. biotechnol., 16, 2006, 123-132. nova biotechnol chim (2022) 21(1): e1083 doi: 10.36547/nbc.1083 1 nova biotechnologica et chimica isolation and statistical optimization of rhodanese (a thiosulphate sulphur transferase) production potential of klebsiella oxytoca jcm 1665 using response surface methodology babamotemi oluwasola itakorode1,2,, raphael emuebie okonji2 1department of chemical sciences, oduduwa university ipetumodu, ile-ife, osun state, nigeria 2department of biochemistry and molecular biology, faculty of science, obafemi awolowo university ile-ife, osun state, nigeria  corresponding author: itakorgsoli29@gmail.com article info article history: received: 2nd august 2021 accepted: 20th december 2021 keywords: klebsiella oxytoca optimization polymerase chain reaction response surface methodology rhodanese 4 abstract microorganisms are increasingly being used in cyanide bioremediation. several organisms have been reported to thrive in cyanide contaminated wastewater due to their ability to produce cyanide detoxifying enzymes. however, to improve the production efficiency of these enzymes combinations of process variables need to be optimized. in this study, klebsiella oxytoca jcm 1665 was isolated from industrial wastewater, identified by sequencing its 16s rrna gene and subjected to rhodanese production using submerged fermentation. the conditions for production were optimized using response surface methodology (rsm). central composite design was employed to evaluate the effects of three production parameters – peptone (1 – 5 %), kcn (0.1 – 0.5 %), and time of incubation (1 – 24 h). second-order polynomial model was used to predict the response. rhodanese activity in the experiments varied from 0.05 to 7.5 ru.mg-1. under the optimum conditions of 4.35 % peptone, 0.4 % kcn and incubation time of 13 hr., the value for rhodanese yield was 7.810 u.ml-1. the r2 value for the model was 0.9925 (r2 = 0.9925). also, the experimental values are in accordance with those predicted, indicating the suitability of the employed model and the success of rsm in optimizing the production conditions. introduction cyanides are toxic chemicals that are widely present in both the abiotic and biotic components of an ecosystem. it acts as a defense mechanism in various organisms such as fungi, bacteria, algae and plants. however, the amount of cyanide generated by these organisms is insignificant when compared to the ones generated through anthropogenic activities (luque-almagro et al. 2016). in industries, cyanide is used for gold extraction and in the synthesis of various agrochemicals such as fertilizers, liming and pesticides. cyanide toxicity is due to its high binding affinity to metal ions; it inhibits metalloenzymes especially the cytochrome c oxidase in the electron transport chain (luquealmagro et al. 2016). the amount of cyanide in the environment has been observed to have increased greatly due to rapid industrialization and cyanide leaching methods have been the major techniques in gold extraction. the demand for gold jewellery in countries like the united states, russia and most african countries has led to the increase mailto:itakorgsoli29@gmail.com nova biotechnol chim (2022) 21(1): e1083 2 in mining activities (mudder et al. 2000). industrial processes such as mining and electroplating have contributed significantly to the cyanide contamination in water bodies. to minimize environmental disasters, cyanide-containing liquid must be properly treated before releasing into the water bodies. the removal of cyanide from the effluent is one of the challenges in the cyanidebased industries to fulfil their standards and recycling of the water (kuyucak and akcil 2013). despite the toxicity of cyanide, cyanotrophic microorganisms such as pseudomonas sp. (akcil and mudder 2003; oyedeji et al. 2013), bacillus pumilus (kandasamy et al. 2015), and bacillus cereus (itakorode et al. 2019) has been reported to survive in the presence of cyanide due to their ability to synthesize cyanide metabolizing enzyme such as rhodanese. rhodanese catalyzes cyanide detoxification by transferring sulfur from a suitable substrate such as thiosulfate to cyanide. this leads to the formation of a less toxic compound (thiocyanate) that can be excreted in the urine (eq. 1): s2o3 2+ cn scn+ so3 2 (1) where s2o3 2 – thiosulfate, cn– cyanide ion, scn– thiocyanate ion, so3 2– sulfite. its role as a detoxification enzyme is supported by its mitochondria and cytosolic localization (cipollone et al. 2007; steiner et al. 2018). although the use of microorganisms has been proven to be viable in cyanide bioremediation, enzymatic proteins may be of good alternative (gianfreda et al. 2004; 2010). enzymes can retain its activity at extreme conditions that limit microbial activities. also, they are not inhibited by inhibitors of microbial metabolism and the technique is eco-friendly. therefore, the importance of producing cyanide metabolizing enzymes for industrial application cannot be overemphasized. many factors including incubation time, the temperature, the ph, carbon and nitrogen sources contribute to the efficacy of metabolite production by organisms (adekunle et al. 2017; itakorode et al. 2019). optimization of metabolites production may be achieved by either one factor at a time or statistical means (rodrigues et al. 2008; annegowda et al. 2012). response surface methodology (rsm) is a statistical experimental protocol used in mathematical modelling (triveni et al. 2001; gong et al. 2012). rsm technique reduces the experimental assays and improves the statistical interpretation and interaction between variables (tsapatsaris et al. 2004; yim et al. 2012). the rsm can give a mathematical equation. it is also helpful to calculate the response value when different levels of variables are set. central composite design is a widely used protocol in response surface methodology (yang et al. 2008; rao 2010). the impact of industrialization on the quality of the environment is evident and there is a need to have eco-friendly strategies to treat effluent for the sustainable development of industries. hence, this study aims to investigate optimal production conditions of rhodanese by klebsiella oxytoca. experimental wastewater was collected from iron and steel smelting company in sterile plastic bottles and stored at 4 oc. it was centrifuged at 5,000 × g for 10 min. the clarified supernatant was collected and used for further analysis. physicochemical parameters such as ph, turbidity, chemical oxygen demand, total dissolved solids, dissolved oxygen, cadmium and lead were determined using the methods described by ademoroti (1996). isolation and screening for rhodanese production a loopful of diluted sample was spread on a modified bushnell hass agar plate and incubated at 37 °c for 96 h to select for cyanide degrading bacteria. rhodanese producing potential of the isolates was done by employed the method described by zlosnik and williams (2004). production medium consists of nacl (0.5 g/100 ml), bacteriological peptone (1 g/100 ml) and kcn (0.3 g/100 ml) at ph of 6.0. the growth media prepared were inoculated with standardized cells suspension. the culture media were checked for rhodanese activity for 24 h at an interval of 2 h. rhodanese nova biotechnol chim (2022) 21(1): e1083 3 isolates identification and characterization the most productive strain was identified by sequencing its 16s rrna gene. this was carried out at the bioscience centre of the international institute of tropical agriculture (ibadan, oyo state, nigeria). dna extraction was carried out using modified method of trindade et al. (2007). the assay mixture for polymerase chain reaction (pcr) amplification consists of 4 µl of the dna solution, 0.4 µl of 10 mm dntps, 2 µl of 25 mm mgcl2, 1 µl of 10 pmol each of primer (forward 5’-ccagcagccgcggtaatacg-3’ and reverse 5’-tcggctaccttgttacgacttc-3’) (yamamoto and harayama 1995), 0.24 µl of taq polymerase (1 u.µl-1) (promega usa) and the 5 µl of 5× pcr buffer. sterile dnase free water was added to make a volume of 25 µl. pcr was conducted in an automated thermal cycler. the thermal conditions were as follows: denaturation at 94 oc for 1 min, annealing at 56 oc for 1 min and 1 min extension at 72 oc. the pcr amplicons were visualized using 1.5 % agarose gel electrophoresis. enzyme assay and experimental design sodium thiosulfate (na2s2o3) and potassium cyanide (kcn) were used as substrates for rhodanese activity. 1 ml of the assay mixture consists of 50 mm borate buffer (ph 9.4), 0.25 m kcn, and na2s2o3 and 0.1 ml of the enzyme. the enzyme reaction was terminated with 0.5 ml 38 % formaldehyde after 1 min of incubation at 25 oc (lee et al. 1995). concentration of thiocyanate produced was quantified by the addition of 1.5 ml sorbo reagent (which is made up of 10 g fe (no3)2·9h2o, 20 ml hno3 and 80 ml distilled water) (sorbo 1953). the absorbance of the reaction medium was taken at 460 nm. the unit of rhodanese activity (ru) is defined as the micromoles of the product (thiocyanate) formed in one minute. the protein concentration was determined by the method of bradford (1976), bovine serum albumin (bsa) was used as standard. the extracellular production of rhodanese was established by rsm which was employed to determine the best combination of variables for optimum rhodanese production by k. oxytoca. the independent variables used in this study were peptone concentration (a – % (w/v)), potassium cyanide (b – % (w/v)), and time (c – h) while response was rhodanese activity (ru.mg-1). the coded and uncoded levels of the independent variables are presented in table 1. table 1. coded and decoded levels of independent variables used in the rsm design. run a: peptone b: kcn c: time 1 -1 (0.36) 0 (0.30) 0 (12.50) 2 -1 (1.00) +1 (0.50) -1 (1.00) 3 +1 (6.30) 0 (0.30) 0 (12.50) 4 0 (3.00) 0 (0.30) 0 (12.50) 5 -1 (1.00) -1 (0.10) +1 (24.00) 6 +1 (5.00) +1 (0.50) -1 (1.00) 7 0 (3.00) 0 (0.30) 0 (12.50) 8 -1 (1.00) +1 (0.50) +1 (24.00) 9 +1 (5.00) -1 (0.10) +1 (24.00) 10 0 (3.00) -1 (0.03) 0 (12.50) 11 0 (3.00) 0 (0.30) +1 (31.84) 12 0 (3.00) 0 (0.30) 0 (12.50) 13 0 (3.00) +1 (0.60) 0 (12.50) 14 0 (3.00) 0 (0.30) 0 (12.50) 15 0 (3.00) 0 (0.30) 0 (12.50) 16 +1 (5.00) +1 (0.50) +1 (24.00) 17 0 (3.00) 0 (0.30) -1 (6.84) 18 +1 (5.00) -1 (0.10) -1 (1.00) 19 0 (3.00) 0 (0.30) 0 (12.50) 20 -1 (1.00) -1 (0.10) -1 (1.00) statistical analysis the experimental data were analyzed using jmp 11’s response surface regression algorithm (statistical analysis system inc., sas). p-values under 0.05 (p < 0.05) were considered significant. anova was used to assess the quality of the mathematical models fitted by rsm, based on the f-test and the percentage of total explained variance (r), as well as the adjusted determination coefficient (r2adj), which provide a measurement of how much of the variability in the observed response values could be explained by the experimental factors and their linear and quadratic interactions (granato et al. 2012). to fit the data, a second-order polynomial quadratic equation (eq. 2) was used. (2) nova biotechnol chim (2022) 21(1): e1083 2 where y is the predicted response, β0, βi, βii, βij, are the correlation coefficients for intercept, linear, quadratic and interaction terms, respectively and xi and xj are the levels of the independent variables. experimental data were fitted to the chosen regression model to have a better understanding of the relationship between each variable and response. the predictive equation of rsm was used to find the optimal conditions for the production of rhodanese. the validity of the model was determined by comparing the experimental and predicted response values. results isolation and identification of the bacteria isolate table 2 shows the physicochemical properties of the wastewater such as the chemical oxygen demand, ph, turbidity, total dissolved solids, dissolved oxygen, lead, and cadmium. the selection of microorganisms from the wastewater led to the isolation of nine gram-positive and twogram negative bacteria. one strain was chosen for further study due to its appreciable rhodanese production. molecular analysis based on 16s rrna gene sequencing revealed that isolates jcm 1665 shared 99.65 % homology with k. oxytoca ay873801, 99.72 % homology with k. oxytoca mf144436 and 99.79 % homology with k. oxytoca mt568561 strain (table 3). table 2. physiochemical analysis of the wastewater. parameter ph 6.0 ± 1 concentration of parameter [mg.l-1] turbidity 8.23 ± 2.74 chemical oxygen demand 74.38 ± 5.19 total dissolved solids 536 ± 10.6 lead 0.02 ± 0.002 cyanide 67.49 ± 9.2 cadmium 0.024 ± 0.006 dissolved oxygen 3.94 ± 0.88 table 3. sequence identity of k. oxytoca (mn590525) with other klebsiella oxytoca. klebsiella oxytoca % identity accession in the genbank database mt568561 99.79 mt568561 mf144436 99.72 mf144436 ay873801 99.65 ay873801 the sequence was deposited in the genbank database of the ncbi as accession mn590525 (https://www.ncbi.nlm.nih.gov/nucleotide/). analysis of the model the result for the analysis of the model for the production optimization is shown in table 4. in this model, two linear (b and c) and five quadratic models (ab, ac, a2, b2, and c2) were found to be significant at the level of p < 0.05. table 4. experimental and predicted result for rhodanese activity. run response (activity u.mg-1) actual value predicted value 1 5.00 5.00 5.30 2 2.50 2.50 2.13 3 6.00 6.00 5.69 4 7.10 7.10 7.25 5 5.70 5.70 5.50 6 5.50 5.50 5.71 7 7.20 7.20 7.25 8 5.70 5.70 5.71 9 2.00 2.00 2.38 10 3.50 3.50 3.35 11 3.50 3.50 3.43 12 7.10 7.10 7.25 13 6.50 6.50 6.64 14 7.50 7.50 7.25 15 7.20 7.20 7.25 16 6.00 6.00 5.94 17 0.05 0.05 0.10 18 2.00 2.00 2.00 19 7.40 7.40 7.25 20 1.70 1.70 1.77 the result for the fitting quadratic model is listed in table 5. the result of the analysis of variance (anova) indicates that the model was significant (p < 0.05) for the response of the dependent variables (rhodanese activity). the result also indicates a good model performance with correlation coefficient (r2) values of 0.9925. the fitted quadratic model for rhodanese production is shown in eq. 3. 4 https://www.ncbi.nlm.nih.gov/nucleotide/ nova biotechnol chim (2022) 21(1): e1083 3 table 5. analysis of variance (anova) for response surface quadratic model for the production of rhodanese. source ss df ms f-value p-value model 99.35 9 11.04 147.52 < 0.0001* a-peptone 0.1832 1 0.1832 2.45 0.1487 b-kcn 13.04 1 13.04 174.28 < 0.0001* c-time 13.35 1 13.35 178.40 < 0.0001* ab 5.61 1 5.61 74.99 < 0.0001* ac 5.61 1 5.61 74.99 < 0.0001* bc 0.0112 1 0.0112 0.1503 0.7063 a² 5.56 1 5.56 74.36 < 0.0001* b² 9.18 1 9.18 122.69 < 0.0001* c² 54.15 1 54.15 723.62 < 0.0001* ss – sum of squares; df – degrees of freedom; ms – mean square. r2 = 0.9925; r2 adj = 0.9858; cv = 5.52 %. (*values statistically significant at p < 0.05). analysis of response surface the best way of expressing the relationship between the independent variables and dependent variables is to graphically plot the response surface plots generated by the model (fig. 1, 2, 3). fig. 1 showed the interaction between potassium cyanide (kcn) and incubation time while holding peptone at the center point (0). fig. 2 showed the interaction between potassium cyanide (kcn) and peptone while incubation time is held constant. fig. 3 showed the interaction between incubation time and peptone while kcn is held constant. fig. 1. response surface plots showing the effects of kcn (% w/v) and peptone (% w/v) on rhodanese production. fig. 2. response surface plots showing the effects of incubation time (hr) and peptone (% w/v) on rhodanese production. 5 nova biotechnol chim (2022) 21(1): e1083 2 fig. 3. response surface plots showing the effects of incubation time (hr) and kcn (% w/v) on rhodanese production. discussion klebsiella oxytoca was isolated from an industrial effluent, identified and subjected to extracellular rhodanese production. rhodanese production ability has been identified in a variety of bacteria species such as e. coli (ray et al. 2000), p. aeruginosa (cipollone et al. 2008), azotobacter vinelandii (kaewkannetra et al. 2009), bacillus brevis (oyedeji et al. 2013) and bacillus cereus (itakorode et al. 2019). enzyme production by an organism is often dependent on the growth of the bacterium in the appropriate media composition. the optimization of culture media and environmental conditions is essential for effective production as it tends to reduce cost of production by increasing yield (george-okafor et al. 2012). the optimum nutritional requirement for rhodanese production was determined to obtain maximum enzyme production by k. oxytoca. a central composite design (20 runs) was chosen with start and center points. the design was rotatable; this means that the designs have points that are equidistant from the center. experiments at the center were carried out to obtain an estimation of the experimental error. the designed experiment matrix and the experimental results are presented in tables 1 and 4. the rhodanese yield varied (from 0.05 to 7.5 ru.mg-1). the rhodanese production yield reached its maximum value (7.5 ru.mg-1) at 3 % of peptone, 0.3 % of kcn and incubation time of 12.5 h (run 17). as noted, rhodanese producing ability of k. oxytoca was affected by the time of incubation. the analysis of the overall data set indicated that incubation time, kcn and interaction ac had the most pronounced effects on the response (table 5). also, from eq. 3, it is evidence that kcn (b) concentration and incubation time (c) had the highest positive effect on the rhodanese production while interaction (ac) and (c2) had the highest negative effect on production. analysis of variance (anova) was important in determining the adequacy and significance of the quadratic model. anova summary is shown in table 5. the fitness of the model was expressed by the r2 value, which is 0.9925, indicating that 99.25 % of the variability in the response can be explained by the model. the adjusted r2 value of 0.9858 suggested that the model was significant. a very low value of coefficient of the variation (cv) 5.52 % indicated a very high degree of precision and a good deal of reliability of the experimental values. the interaction between kcn and peptone concentration at a constant time of incubation is shown in fig. 1. the result showed that rhodanese production increases as the concentration of both variables increases. at high concentrations, a gradual fall in production was observed. research had shown kcn and peptone to influence the production of cyanide detoxifying enzymes (adekunle et al. 2017). itakorode et al. (2019) reported kcn as the best carbon source for b. cereus. the ability of p. putida and b. pumilus to make use of cyanide as carbon source was also reported by kandasamy et al. (2015). okonji et al. (2018) also reported the ability of pseudomonas straminea to make use of peptone as nitrogen source. the high cyanide tolerance of k. oxytoca observed was probably due to its ability to synthesize rhodanese as a means of surviving in cyanide contaminated environment. fig. 2 showed the interaction effect of peptone concentration and incubation time while keeping kcn concentration constant. in this interaction, minimal rhodanese production was observed at a low concentration of peptone. however, as concentration and incubation 6 nova biotechnol chim (2022) 21(1): e1083 3 time increases, an increase in rhodanese activity was recorded. the same trend was also observed in the interaction between incubation time and kcn. however, a decline in production was noted at high time of incubation. the decline in rhodanese production may be due to exhaustion of the nutrients or accumulation of other products or metabolites which are both inhibitory to the growth of the bacterium and rhodanese production. this result agrees with the findings of okonji et al. (2018) who observed a decrease in metabolite production after 15 hours of incubation. linawati et al. (2002) also reported the influence of environmental conditions on the production of pigment by serratia marcescens. the optimal value of the independent variables for rhodanese production was examined using the maximum desirability. the result of optimal conditions used to obtain the highest rhodanese production by k. oxytoca were 4.35 % peptone, 0.4 % kcn and incubation time of 13 hours, at which rhodanese yield was 7.810 ru.mg-1. conclusion it can be concluded that the regression equations obtained in this study can be used to maximize the rhodanese production by k. oxytoca. also, further study is required to improve the production of the enzyme through genetic engineering and to examine the cyanide bioremediation potential of the rhodanese synthesized by the organism. conflict of interest the authors declare that they have no conflict of interest. references adekunle ap, torimiro n, okonji re (2017) a study on 3mercaptopyruvate sulphurtransferase (3-mst) produced under submerged 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(2004) method of assaying cyanide in bacterial culture supernatant. lett. appl. microbiol. 38: 360-365. 8 microsoft word jeric nb 9-2.doc nova biotechnologica 9-2 (2009) 155 chemometric characterization of textile waste waters from different processes tina jerič1, alenka majcen le marechal1, darja kavšek2, darinka brodnjak vončina3 1faculty of mechanical engineering, university of maribor, smetanova 17, 2000 maribor, slovenia 2regional technological centre zasavje, chemical-technological laboratory, nasipi 48, 1420 trbovlje, slovenia 3faculty of chemistry and chemical engineering, university of maribor, smetanova 17, 2000 maribor, slovenia abstract: the aim of this work is focused on water quality classification of the textile waste water streams and evaluation of pollution. data from the chemical characterization of the effluents were elaborated to identify a useful separation in potentially treatment for reuse. this was done with the aim of realizing a full scale characterization of effluents. in the two textile companies analyzed, machineries are used to carry out different production processes such as sizing and desizing, weaving, scouring, bleaching, mercerizing, carbonizing, fulling, dying and finishing. different process effluents from the same machinery were found to be very diverse in pollution level. 25 and 49 samples of textile waste waters from two different textile companies were analysed and physical chemical measurements were performed. the following physicochemical and chemical water quality parameters were controlled: absorbance measured at three different wavelengths, ph, conductivity, turbidity, total suspended solids, volatile suspended solids, chemical oxygen demand, metals content (ba, ca, cu, mn, k, sr, fe, al, na) and total nitrogen content. for handling the results, basic statistical methods for the determination of mean and median values, standard deviations, minimal and maximal values of measured parameters and their mutual correlation coefficients, were performed. different chemometric methods, namely, principal component analysis (pca), cluster analysis (ca), and linear discriminant analysis (lda) were used to find hidden information about textile waste water quality. key words: textile waste waters, water quality, chemometrics, principal component analysis, classification 1. introduction the chemical and physicochemical studies on textile waste water streams from two textile companies were performed in the time period 2008-2009. the quality of the textile waste water streams was followed and the classification has been made according to different textile process outlets. the classification is based on 19 chemical and physicochemical parameters. the aim of this work is to find the correlation between different textile process outlets and the variables obtained by physicochemical and chemical measurements, which can be used to construct a fast decision model for separating different textile waste water quality outlets. chemometric methods have been often used for the classification and comparison of different water samples (massart et al., 1997). some examples of chemometric characterizations of waste water and pollution of water are described, for instance, in the case of chemi-thermo-mechanical pulp mill (tønning et al., 2005), micro156 jerič, t. et al. electronics industry (velinova and koumanova, 1995), and in the case of waste waters in the lagoon of venice (carrer and leardi, 2006). chemometric methods have been used also for surface water quality and pollution estimation (astel et al., 2008; kowalkowski et al., 2006; astel et al., 2007), for characterization of water springs (ragno et al., 2007), for natural mineral waters (sarbu and zwanziger, 2001; silva et al., 2002), for classification of ground waters (panero and da silva, 2008), and for the oceanographic characterization of water (ferreira et al., 1999). the quality of the textile waste water streams was studied through the years 2008 and 2009. the monitoring programme was performed on different textile process waste water effluents (outlets) from two textile companies. textile waste water effluents were gathered from different textile processes (printing, finishing, dyeing, bleaching, washing, rinsing, mercerizing, softening and desizing) and from different machinery. altogether 19 characteristic features were measured for 25 and 49 samples of textile waste waters from two textile companies, respectively. water samples were collected and analysed during two years. several chemometric methods were applied in order to visualize multivariate data and to enable a quick classification of samples, regarding to textile process waste water effluents (outlets). 2. materials and methods a standard method was used for sampling (iso 5667-01: 1996 (e)). textile waste water samples were collected in polyethylene bottles at the outlet. standard analytical methods were used for the determination of 19 chemical and physicochemical variables. all reagents were analytical grade. the milli-q system was used for purifying the water. 25 and 49 samples of textile waste water from two textile companies respectively, are characterized by 19 chemical and physicochemical variables: (1) ba, (2) cu, (3) mn, (4) k, (5) sr, (6) fe, (7) al, (8) na, (9) ca, (10) total nitrogen, (11) ph, (12) conductivity, (13) turbidity, (14) chemical oxygen demand, (15) total suspended solids, (16) volatile suspended solids, (17) absorbance at 436 nm, (18) absorbance at 525 nm, and (19) absorbance at 620 nm. the results of all measurements have been investigated by different chemometric methods (massart et al., 1997): the basic statistical methods for the determination of mean and median values, standard deviations, minimal and maximal values of measured variables and their mutual coefficients. the principal component analysis (pca) (massart et al., 1997; teach/me datalab 2.002, 1999) was applied for grouping of textile waste water samples due to measured variables. all the calculations and plots in the following (pca) section were done with the teach/me software (teach/me datalab 2.002, 1999) using teach/me data analysis option. 3. results and discussion 3.1 statistical screening of data the mutual correlation was sought for all measured variables. the maximal correlation coefficient for the data of 25 waste water samples from the first textile nova biotechnologica 9-2 (2009) 157 company was found between measurements of absorbance at 620 nm and copper (r = 0.99), between absorbance at 620 nm and absorbance at 525 nm (r = 0.99), between absorbance at 525 nm and copper (r = 0.98), between total suspended solids and volatile suspended solids (r = 0.98), between absorbance at 620 nm and potassium (r = 0.97), and between absorbance at 525 nm and potassium (r = 0.96). the maximal correlation coefficient for the data of 49 waste water samples from second textile company was found between measurements of absorbance at 525 nm and absorbance at 436 nm (r = 0.99), between measurements of sodium content and electrical conductivity (r = 0.98), between total suspended solids and volatile suspended solids (r = 0.98), between potassium and manganese (r = 0.90), between absorbance at 620 nm and calcium (r = 0.86), and between absorbance at 436 nm and sodium (r = 0.86). fig. 1. dendrogram of 49 textile waste water samples from the second textile company. different shades correspond to 9 different textile process waste water outlets (classes). cluster analysis resulted in dendrogram shown in fig. 1, where 49 textile waste water samples are divided into number of clusters, depending on the level of similarity based on ward distance. first group of textile waste water samples (the right-most cluster) is quite well distinguished from others. this was also the most polluted water stream, as it was first outlet after dyeing process. 3.2 principal component analysis (pca) pca was performed to find the correlation of 25 or 49 textile waste water samples from two different textile companies, respectively, described with physicochemical 158 jerič, t. et al. and chemical variables (fig. 2). quality of textile waste waters depends on different textile processes and different waste water outlets. first outlet is always the most polluted one, as it belongs to the dyeing process. all other outlets are less polluted as they belong to rinsing processes. pca was applied on the matrix composed of 25x19 and 49x19 elements. 25 or 49 rows represent textile waste water samples from two textile companies, respectively, composed of 19 variables. "column centering" of the data was used, which means that the mean value of each column was subtracted from individual (25 or 49) elements. fig. 2. pca for 25 textile waste water samples from five different textile process waste water outlets denoted by class numbers from 1 to 5 and for 49 textile waste water samples from nine different textile process waste water outlets denoted by class numbers from 1 to 9. fig. 3. pca for textile waste water samples from nine and five different textile process waste water outlets; the loadings in 19 pc axes are shown. the pca of the textile waste water samples represented with 19 variables is shown in fig. 3. it can be seen that the first component, pc1, is associated with a group of variables such as conductivity and concentration of sodium, describing inorganic nova biotechnologica 9-2 (2009) 159 pollution, while the second component pc2 represents mainly the dependence on chemical oxygen demand, which is responsible for organic pollution. 3.3 linear discriminant analysis (lda) lda is a supervised learning method, which can determine the classification into predetermined classes. from figures 4a and 4b it can be seen that first class (first outlet from dyeing) for samples from both textile companies is well distinguished from all other outlets, belonging to rinsing processes. plot of discriminant functions -13 -3 7 17 27 37 47 function 1 -5,4 -3,4 -1,4 0,6 2,6 4,6 fu nc tio n 2 class 1 2 3 4 5 centroids fig. 4a. linear discriminant analysis for 25 samples. plot of discriminant functions -4,6 -2,6 -0,6 1,4 3,4 5,4 function 1 -7 -4 -1 2 5 8 fu nc tio n 2 class 1 2 3 4 5 6 7 8 9 centroids fig. 4b. linear discriminant analysis for 49 samples. 4. conclusions the aim of this work is to find the best solution for both textile companies for reuse of waste waters. for water recycling it is necessary to find correlation between different textile waste water streams. chemometric methods can help in characterization of textile waste water effluents and thus can be used for separation of concentrated textile waste water streams from non concentrated ones. after collecting concentrated textile waste waters, evapoconcentration treatment process will be used before additional cleaning at waste water treatment plant. for treatment of non concentrated textile waste water streams aop processes, like h2o2/uv process, and 160 jerič, t. et al. membrane filtration processes will be used. the cleaned waste water with the best quality can then be reused in different textile production processes. references astel, a., tsakovski, s., barbieri, p., simeonov, v.: comparison of selforganizing maps classification approach with cluster and principal components analysis for large environmental data sets. water res., 41, 2007, 4566-4578. astel, a., tsakovski, s., simeonov, v., reisenhofer, e., piselli, s., barbieri, p.: multivariate classification and modeling in surface water pollution estimation. anal. bioanal. chem., 390, 2008, 1283-1292. carrer, s., leardi, r.: characterizing the pollution produced by an industrial area: chemometric methods applied to the lagoon of venice. sci. total environ., 370, 2006, 99-116. ferreira, m.m.c., faria, c.g., paes, e.t.: oceanographic characterization of northern sao paulo coast: a chemometric study. chemometr. intell. lab. syst., 47, 1999, 289-297. kowalkowski, t., zbytniewski, r., szpejna, j., buszewski, b.: application of chemometrics in river water classification. water res., 40, 2006, 744-752. massart, d.l., vandeginste, b.g.m., buydens, l.m.c., de jong, s., lewi, p.j., verbeke, j.s.: handbook of chemometrics and qualimetrics: part a, elsevier, amsterdam, 1997. panero, f.s., da silva, h.e.b.: application of exploratory data analysis for the characterization of tubular wells of the north of brazil. microchem. j., 88, 2008, 194-200. ragno, g., de luca, m., ioele, g.: an application of cluster analysis and multivariate classification methods to spring water monitoring data. microchem. j., 87, 2007, 119-127. sarbu, c., zwanziger, h.w.: fuzzy classification and comparison of some romanian and german mineral waters. anal. lett., 34, 2001, 1541-1552. silva, f.v., kamogawa, m.y., ferreira, m.m.c., nobrega, j.a., nogueira, a.r.a.: geographical discrimination of mineral waters from são paulo state through exploratory analysis. ecletica quim, 27, 2002, 91–102. teach/me, sdl software development lohninger; teach/me datalab 2.002, 1999, springer, berlin, developed by h. lohninger and the teach/me people. tønning, e., sapelnikova, s., christensen, j., carlsson, c., winther-nielsen, m., dock, e., solna, r., skladel, p., nørgaard, l., ruzgas, t., emnéus, j.: chemometric exploration of an amperometric biosensor array for fast determination of wastewater quality. biosens. bioelectron., 21, 2005, 608-617. velinova, r.r., koumanova, b.k.: statistical modelling of wastewater quality: the case of micro-electronics industry. water res., 29, 1995, 2541-2547. water quality-samplingpart 10: guidance on sampling of waste water iso 5667-01: 1996 (e). microsoft word vrtoch nb.doc nova biotechnologica vii-i (2007) 41 bioaccumulation of 60co2+ ions in tobacco plants ľuboš vrtoch, martin pipíška, miroslav horník, jozef augustín department of biotechnology, university of ss. cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic (vrtochl@ucm.sk) abstract: tobacco has previously been used in investigations of metals and radionuclide uptake. this study presents determination of bioaccumulation and translocation of 60co2+ ions in tobacco plants (nicotiana tabacum l.) grown in hoagland’s nutrient solution. cobalt concentration in tobacco plants increased with increasing concentration in nutrient solution. bioaccumulation from the initial concentration c0 = 0.96 μm co reached 90% after 7 day cultivation. only small amounts of co accumulated in roots, up to 2 4 % were removable from roots by washing with 0.1 m cocl2, indicating that this portion of co is bound to the root surface in ion-exchangeable form. tobacco roots retained approximately 2/3 of accumulated cobalt and 1/3 was transported to shoots. autoradiography revealed that 60co was preferentially localized in younger leaves. prolongation of cultivation time did not change the [co]roots : [co]shoots ratio significantly. relationships between growth rate, transpiration rate, uptake and distribution of cobalt in plant tissue are discussed. key words: cobalt, 60co2+, nicotiana tabacum l., accumulation, hydroponics, autoradiography 1. introduction many papers explaining mechanism of uptake, translocation and detoxication of cobalt have been published (bakkaus et al., 2005; perez-espinoza et al., 2005; woodard et al., 2003; moreno-caselles et al., 1997). a number of mechanisms have been proposed on how cobalt is taken up and transported through the plant (woodard et al., 2003). early literature suggested that cobalt was present in xylem tissues in tomato as an inorganic cation (tiffin, 1967). others have suggested an organic anion of molecular weight from 1000 to 5000 da as found in ricinus communis (wiersma and van goor, 1979). it has been reported previously that cobalt is one of those metals that do not activate phytochelatin synthase (zenk, 1996). it was therefore suggested that cobalt cannot be detoxified via the phytochelatin system in plant cell (oven et al., 2002). this is in contrast with results obtained for other metals such as cd and zn. on the other hand, oven et al. (2002) identified cysteine as a compound involved in co complexation in cobalt hyperaccumulator crotalaria cobalticola suspension cells. cobalt also induced cysteine increase in non-hyperaccumulator species, suggesting that there are also other cellular mechanisms that enable cobalt tolerance and hyperaccumulation. tobacco has previously been used in other investigations of metals and radionuclides uptake (fuhrmann and lanzirotti, 2005; mench and martin, 1991). an excellent review on utilization of genetically modified tobacco 42 vrtoch, ľ. et al. and other plants for phytoremediation of toxic metal contaminated soil was published by eapen and d´souza (2005). in our paper, the accumulation of 60co by tobacco plants nicotiana tabacum l. has been studied with the aim to characterize cobalt bioaccumulation and translocation in roots, stems and leaves at hydroponic cultivation. the tobacco was chosen as a model system due to its high biomass production, easy hydroponic cultivation, and as a model of widely cultivated agricultural plant. 2. material and methods 2.1 plant material seeds of tobacco were germinated and grown in pots filled with granulated moist perlite as an inert carrier in day/night photoperiod 12/12 h (illumination with two fluorescent tubes fluora 550 lm, l18w/77, osram; one tube cool white 1150 lm, f18w/33, tungsram), temperature 22 ± 1°c, and relative humidity 50%. plants were irrigated with 25% hoagland nutrient medium (hoagland, 1920). after 2 months, seedlings were removed from perlite, roots were washed free of any adhering perlite granules by distilled water and pre-cultured for 7 days in 25 % hoagland nutrient medium in erlenmeyer flasks and used for experiments. plants used were about 15 cm tall and about 4.0 – 6.0 g of fresh weight. 2.2 bioaccumulation experiments plants were cultivated in 25 or 50% hoagland´s medium supplemented with 0.96; 9.6; 25 or 50 µmol.l-1 cocl2 spiked with 60cocl2 (125 kbq.l -1 ) for 7 or 14 days under the conditions as described in the previous section. bioaccumulation experiments were replicated three times. in 24 h intervals aliquot samples of nutrient solution were taken and 60co radioactivity measured by gamma spectrometry. at the end of experiments plants were harvested and roots carefully rinsed in 0.1 m cocl2 and distilled water. growth value (gv) was calculated following the equation gv = (m – m0) / m0, where m and m0 is plant fresh weight at the end and at the beginning of experiments respectively (soudek et al., 2006). radioactivity incorporated in roots, stems and leaves was measured by gamma spectrometry. material was dried in oven at 60 °c to a constant weight. after cultivation in the presence and in the absence of co2+ ions, tobacco leaves were observed with jenatech light microscope (carl zeiss). micrographs were taken with digital camera olympus camedia 4000. 2.3 radiometric analysis a gamma spectrometric assembly using the well type scintillation detector 54bp54/2-x, nai(tl) (scionix, the netherlands) and data processing software scintivision32 (ortec, usa) were used for 60co determination in plant and solution. counting time 600s allowed obtaining data with relative measurement error <2%, nova biotechnologica vii-i (2007) 43 which do not reflect other source of errors. standardized 60cocl2 solution (20 mg/l cocl2 in 3 g/l hcl) with specific radioactivity 5.181 mbq/ml was obtained from the czech institute of metrology, prague, czech republic). before autoradiography, roots were rinsed with distilled water, drops were wiped off; plants were pressed between two layers of filter papers and dried at laboratory temperature. dried plants were mounted on the x-ray film (hr-gb 100 nif, fujifilm, japan), and developed after 40 days. developed films were scanned and black and white film was converted to color scale gradient by software photoshop cs2 ver. 9.0 (adobe, usa). 2.4 transpiration rate transpiration rates (tr) were calculated from the daily weight losses of cultivation vessels containing plants, corrected for water evaporation of vessels media without plants. transpired water was daily replenished with distilled water to the initial volume. leaf area (m2) was calculated from weights of leaf copies (g) made from the paper sheet of known specific weight (g/m2). 3. results and discussion 3.1 cobalt uptake tobacco plants (nicotiana tabacum l.) cultivated in 25 % hoagland’s medium were tested to the ability accumulate co2+ ions from nutrient solutions. bioaccumulation at the initial cobalt concentration c0 = 0.96 μm reached 90 % within 7 days (fig. 1). the same kinetics (data not shown) and comparable uptake values 89.5±1.9 and 86.8±3.3% were observed for c0 = 9.6 and 25 μm respectively. at c0 = 50 μm cocl2, toxic effects appeared and total uptake decreased to 54.2±5.5% (table 1). transpiration rate (ml/day) at 22 ± 1°c and 50 % humidity was linear within 7 days (fig. 1). only small amount of cobalt, up to 2-4 % was removable from roots at the end of the experiment by washing with 0.1 m cocl2, indicating that this portion of cobalt was bound to the surface of the roots in ion-exchangeable form. at concentrations c0 ≥ 50μm cocl2, significant decrease in biomass production expressed by growth values (table 1), decrease in co uptake and transpiration rates (table 3) and chlorosis localized in interveinal areas of younger and new leaves were observed. the cobalt treatments within concentration range c0 = 0.96 25 μm had no significant effect on transpiration rates and therefore induced no toxic effect. the average transpiration rates 11.5, 11.6 and 11.9 ml.m-2.h-1 at 0.96, 9.6 and 25 μm respectively were obtained. the transpiration rate of tobacco plants was reduced to 8.3 ml.m-2.h-1 under higher co exposure (50 μm) (table 3). on the other hand, increasing amounts of co in the shoots was observed (table 1), indicating that under higher co exposure, the co transport mainly through the path of phloem and driven by the concentration gradient of co in the roots. similar cu transport in rice seedlings under extreme cu exposure observed chen et al., (2004). 44 vrtoch, ľ. et al. uptake of cations by root system is influenced by other ions present in solution. the increase of hoagland´s strength from 25 % to 50 % caused decrease of cobalt uptake from 90 % to 54 % at co = 9.6 μm cocl2 (table 2). this fact can be explained by competitive effects of bivalent cations. in more concentrated hoagland’s solution such as 50 %, also suppression of transpiration rate and lower gv values were also observed (table 2 and 3). inhibition of cobalt uptake by sunflower from 50 % hoagland´s medium was described in our previous paper (hornik et al., 2005). inhibition of transpiration by higher nutrient concentrations was described by kang and van iersel (2004). 0 30 60 90 120 150 180 0,0 0,2 0,4 0,6 0,8 1,0 c o2 + [μ m ol .l -1 ] t [h] 0 10 20 30 40 50 t ranspiration [m l] fig. 1. kinetic of co2+ bioaccumulation (□-□) and transpiration ( ) by tobacco plants grown in 25% hoagland medium at 22±1°c; c0 = 0.96 μm co2+. each point is the mean of three replicates. error bars represent standard deviation (sd) of the mean. tab. 1. uptake and distribution of co2+ ions in roots and aboveground parts of tobacco plants cultivated 7 days in 25 % hoagland’s hydroponic medium. co2+ [μg.g-1 dw ± sd] co2+ [μmol.l-1] gv co uptake [%] [co]root / [co]shoot] root stem leaves 0.96 0.26±0.06 90.5±0.2 9.3 27.2±12.0 1.8±1.6 1.1±0.6 9.6 0.25±0.07 89.5±1.9 11.8 582±97 27±11 22±3 25 0.23±0.06 86.8±3.3 10.7 1077±113 51±10 50±14 50 0.12±0.01 54.2±5.5 3.5 711±119 124±9 80±20 3.2 translocation of cobalt tobacco roots retained approx. 2/3 of bioaccummulated cobalt and only 1/3 was translocated into shoots. these data expressed in term of the cobalt ratio in root to shoot (65:35) changed only slightly with the increase of the initial cobalt concentration within the range c0 = 0.96 to 25 μm. more pronounced translocation of cobalt to shoots was observed at 50 μm cobalt in medium where cobalt ratio in root to shoot has changed to 44:56 (fig. 2). nova biotechnologica vii-i (2007) 45 autoradiography also demonstrated that 60co is preferentially localized in the roots and in young leaves. in leaves 60co is distributed around the veins and significant amount is also localized in leafstalks (fig. 4). gamma spectrometry showed the following cobalt 60co distribution: root 68 %; young leaves (leaf no. 4, 5, 6) approx. 20 %. stem and older leaves (leaf no 1, 2, 3) contained 8.7 % and 3.2 % 60co respectively. however, higher concentrations of nutrient salts in cultivation medium did not influence cobalt translocation in tobacco plants significantly (fig. 3a). 0 20 40 60 80 100 r el at iv e c o2 + di st rib ut io n in p la nt [% ] cocl2 [μmol.l -1] root stem leaves 0,96 9,6 25 50 fig. 2. relative distribution of co2+ ions in tobacco roots, stems and leaves after 7 days cultivation in 25% hoagland medium with initial concentration c0 = 0.96, 9.6, 25 and 50 μmol/dm3 cocl2 at 20 ± 2°c. each column is the mean of three replicates. error bars represent standard deviation (sd) of the mean. tab. 2. influence of strength of hoagland medium and cultivation time on uptake and translocation of co2+ ions by tobacco plants. c0 = 9.6 umol/l cocl2. time [day] gv hoagland´s strength [%] co uptake [%] co (root/shoot) ratio [μg.g-1 dw] /[μg.g-1 dw] 7 0.25±0.07 25 89.5±1.9 11.8 7 0.15±0.04 50 54.8±4.1 4.7 14 0.46±0.04 25 85.8±0.8 8.8 tab. 3. relation between co2+ uptake and transpiration rate (tr) of tobacco at different initial co2+ concentration in cultivation medium after 7 days cultivation. co2+ [μmol.l-1] co uptake [%] tr [ml.m-2.h-1] hoagland´s strength [%] 0.96 90.5±0.2 11.5±1.5 25 9.6 89.5±1.9 11.8±0.6 25 9.6 54.8±4.1 8.8±0.9 50 25 86.8±3.3 11.9±0.8 25 50 54.2±5.5 8.3±0.9 25 in our experiments cobalt was added to the nutrient solution as a single dose in such amounts that more than 90 % uptake was reached within 7 days of cultivation. we expected that during prolonged cultivation in the same cultivation medium, where 46 vrtoch, ľ. et al. cobalt was depleted, would result in additional cobalt translocation from roots to shoots by transpiration stream. this hypothesis was not confirmed. prolongation of cultivation from 7 to 14 days did not change root to shoot cobalt ratio significantly. as can be seen in fig. 3b, additional translocation of cobalt primarily localized in roots into shoots was not observed. the only cobalt movement was slight translocation from stems to leaves. on the contrary, page and feller (2005) observed negligible mobility of cobalt in wheat. cobalt 57co was trapped mainly in roots and bound so tightly, that was not significantly translocated to wheat shoots during the next 50 days of cultivation. differences in cobalt mobility in plant organs described in literature are explained by differences in biochemical composition of plant organs and differences in transport systems. 0,0 0,2 0,4 0,6 0,8 1,0 r el at iv e c o2 + di st rib ut io n in p la nt 9.6 μm co2+ 25% hoag 9.6 μm co2+ 50% hoag root leaves stem a 0,0 0,2 0,4 0,6 0,8 1,0 r el at iv e c o2 + di st rib ut io n in p la nt 9.6 μm co2+ 7 days 9.6 μm co2+ 14 days root leaves stem b fig. 3. relative distribution of co2+ ions in tobacco roots, stems and leaves in dependence on the concentration of hoagland nutrient medium (a), and on the cultivation time (b). each column is the mean of three replicates. error bars represent standard deviation (sd) of the mean. 3.3 phytotoxicity of cobalt it has been established that co like other pollutant elements are relatively toxic to plants when given in supranormal doses (chatterjee and chatterjee 2000; pandey et al., 2002; gopal et al., 2003). after 50 μm co treatment, tobacco showed interveinal chlorosis on young leaves and significant suppression of growth (fig. 5, table 1). similar toxic effect of cobalt on tomato plants was described by gopal et al., (2003). chlorosis is considered as indirect effect caused by: alterations nova biotechnologica vii-i (2007) 47 fig. 4. autoradiography of 60co2+ distribution in root, stem and leaves of tobacco after 7 days cultivation in 25% hoagland medium with initial concentration c0 = 1,9 μmol/l cocl2 (263 kbq/l 60cocl2) at 20 ± 2°c. autoradiogram was converted to color scale gradient by software photoshop cs2. single leaves are numbered as: 1 – the oldest (lower), 7 – the youngest (upper). relative distribution of 60co in plant parts calculated from gama-spectrometric data: 68.0% root; 8.7% stem; 0.8% leaf 1; 1.2% leaf 2; 1.4% leaf 3; 2.8% leaf 4; 5.4% leaf 5; 11.7% leaf 6+7. fig. 5. visible symptoms of tobacco plants to excess supply of co2+ (50 μm) after 7 day cultivation in nutrient solution: a-plant cultivated in the absence of co2+ (magnification 0,4 ×), b – plant cultivated in the presence of 50 μm co2+ (magnification 0,5 ×), c – leaf of co2+ non-treated plant (magnification 30 ×), d – leaf of 50 μm co2+ treated plant with developed interveinal chlorosis (magnification 10 ×). 5 6 1 2 3 7 4 48 vrtoch, ľ. et al. in the concentrations of essential mineral nutrients, a decrease in net photosynthesis as a consequence of stomatal closure, reduced intercellular spaces and by alterations within chloroplasts (chatterjee and chatterjee 2000; vazquez et al., 1987). on molecular level it was found, that co in supranormal concentrations caused inhibition of catalase activity, decrease of chlorophyll content connected with chlorosis (chatterjee and chatterjee, 2000; pandey and sharma, 2002). toxicity of cobalt at c0 50 μm resulted in both decrease of tobacco transpiration rates and cobalt uptake. 4. conclusion uptake of co2+ ions from nutrient hydroponic solution by tobacco plants is a process dependent on transpiration rate. cobalt is translocated from root to shot biomass in the ratio 70: 30. at concentrations c0 ≥ 50 μm co 2+, phytotoxic effects such as intervenial chlorosis was observed. uptake of co2+ ions by tobacco roots and translocation to shoots is influenced by the presence of other bivalent metal ions. cobalt can be considered as a next toxic agents accumulating in tobacco grown in contaminated soils. on the other hand, roots contain cobalt in concentrations 27 times higher than in the aboveground part calculated on dry weight biomass, what have to be taken in consideration in calculations of cobalt and radiocobalt persistence in soil/plant system. references bakkaus, e., gouget, b., gallien, j.p., khojda, h., carrot, f., morel, j.l., collins, r.: concentration and distribution of cobalt in higher plants: the use of micro-pixe spectroscopy. nucl. instrum. methods phys. res. section b, 231, 2005, 350-356. chatterjee, j., chatterjee, c.: phytotoxicity of cobalt, chromium and copper in cauliflower. environ. pollut., 109, 2000, 69-74. chen, ch-t., chen, t-h., lo, k-f., chiu, ch-y.: effects of proline on copper transport in rice seedlings under excess copper stress. plant sci., 166, 2004, 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23 metals recovery from acid mine drainage alena luptakova1, magdalena balintova2, jana jencarova1, eva macingova1, maria prascakova1 1department of mineral biotechnologies, institute of geotechnics of the slovak academy of sciences, watsonova 45, košice, sk-043 53, slovak republic (luptakal@saske.sk, jencarova@saske.sk, macingova@saske.sk, prascak@saske.sk) 2institute of building and environmental engineering, civil engineering faculty, technical university of košice, vysokoškolská 4, košice, sk-042 00, slovak republic (magdalena.balintova@tuke.sk) abstract: the objectives of the present work give the results view of some physicochemical, chemical and biological-chemical methods for the heavy metals removal from acid mine drainage (amd). the background of the studied physicochemical methods was the adsorption by turf, chemical methods the heavy metals precipitation by the neutralization with naoh. the principles of the biological-chemical methods were the bioprecipitation by the applications of sulphate-reducing bacteria (srb), the sorption by the bacterially produced iron sulphides and sorption by brown coal bio-modified by micromycetes. key words: acid mine drainage, neutralization, bioprecipitation, sorption, biosorption 1. introduction acid mine drainage (amd) is unique among industrial contaminants on the subject of mainly the mining industry of the sulphide minerals. amd generation proceeds increased considerably after the closure of mines. acid mine waters have low ph-values, and typically high concentrations of sulphates, iron and non-ferrous metals (kontopoulos, 1988), which serve as buffering systems. development of cost-effective and sustainable remediation solutions for the mine water problem has been the subject of extensive review. in addition to monitored natural attenuation, the two broad philosophies which have been pursued in the treatment and abatement of mine water pollution include measures directed towards prevention at source, usually involving physical intervention of one form or another, and measures directed at the resulting effluent, including active or passive remedial systems. both active and passive systems may be implemented using physicochemical, chemical or biological-chemical treatment technologies (skousen et al., 1998; kadukova and stofko, 2006a). nowadays is pay attention to physical, chemical and biological methods for the selective recovery of metals from amd. these methods constitute the possibility of the recovery metals in the suitable forms for commercial value. current research of heavy metals removal in water environment is aimed to application of natural materials as well as industrial wastes that are regarded as cost effective sorbents 24 luptakova, a . et al. (garcia sanchez et al. 1999). among the most often tested sorbents of heavy metals belong: zeolite, carbonate, clays, turf, oxide and hydroxide of iron. deorkar and tavlarides (1998) development of amd physicochemical treatment by application of an adsorption process comprised of inorganic chemically active adsorbents to selectively recover of fe, cu, zn, cd and pb from amd without neutralization. jacke and diebold (1983) evaluated the chemical treatment of amd on the ground of metal recovery from amd by addition of sulphides followed by oxidation and selective titration. cu and zn precipitated as sulphides and fe, al, mn and mg were recovered as hydroxides. tabak et al. (2003) conducted the biotreatment of amd by selective sequential precipitation to recover metals as hydroxides and sulphides. for the metals removal from amd can be used different biosorbents on the base of sawdust, algae, microscopic fungi, biogenous ferrous sulphides biomass and etc. (kadukova and stofko, 2006b; kadukova and vircikova, 2003). in slovak republic there are some localities with existing amd generation conditions. our previous research demonstrates the amd critical values in the abandoned cu – fe ore deposit smolnik (luptakova et al., 2006). it is necessary to develop methods for their treatment. that was the reason for starting a systematic monitoring of geochemical development in acid mine drainage in 2004 in order to prepare a prognosis in terms of environmental risk and use of these waters as an atypical source of a wide range of elements. on this account was our research oriented on the development suitable methods or their combination for the amd effluent treatment from deposit smolnik. we studied some physicochemical, chemical and biological-chemical methods. heavy metals model solutions and amd from smolnik were used for experiments. the background of the used physicochemical methods was the adsorption by turf brush peatsorb. experiments of the chemical methods were oriented on to study of the metals selective precipitation in the hydroxides form by the neutralization with naoh. the principle was the endpoint titration. the backgrounds of the biological-chemical methods were the bioprecipitation by the applications of sulphate-reducing bacteria (srb), the sorption by the bacterially produced iron sulphides and sorption by brown coal modified by different micromycetes strains. the metabolic process of srb is the anaerobic reduction of sulphates by the formation of hydrogen sulphide reacting in the water with cations of metals forming little soluble sulphides. investigated was the process of the heavy metals precipitation by bacterially produced hydrogen sulphide with the combination of the metals precipitation by sodium hydroxide at the various amd ph values. in the literature this methods is named as the selective sequential precipitation (ssp) (tabak et al., 2003). besides srb application gives rise to fe sulphides (fexsy) with the magnetic properties, which are suitable bio-sorbents of heavy metals and are utilizable for amd treatment in combination with the magnetic separation. for the heavy metals removal from solutions also unconventional sorbents prepared from brown coal by micromycetes were used. it was studied bio-modification of brown coal sorption materials with the aim to enhance its sorption properties. the micromycetes (aspergillus niger, aspergillus clavatus, nova biotechnologica 10-1 (2010) 25 penicillium glabrum and trichoderma viride) have been selected for biological activation of coal samples. 2. material and methods 2.1 model solutions stock solutions of each metal: cu(ii) containing 30-300 mg/l, zn(ii) containing 30-300 mg/l and cd(ii) containing 50-100 mg/l were prepared by dissolving cuso4.5h2o, znso4.h2o and 3cdso4.8h2o of analytical grade in distilled water. 2.2 acid mine drainage the experiments were conducted with amd coming from the abandoned and flooded deposit of smolnik (slovak republic). the average values of ph and the major metals composition of acid mine drainage was following: ph 3.9, so4 2 2 938 mg/l, fe 307 mg/l, mn 26 mg/l, cu 5 mg/l, zn 11 mg/l, al 77 mg/l. 2.3 adsorption metals by turf based on our previous results, where various adsorbents were tested (balintova and kovalikova, 2008) for our study of cu, fe, al, zn ions removal from acid mine drainage by adsorption, turf brush peatsorb (reo amos slovakia) was used. the dependence of cu, fe, al, zn concentration decreasing on time (1, 3, 5 and 10 min), was investigated under dynamic conditions using turf brush peatsorb. to intensify the adsorption process, sample of amd was continuously stirred with 5 g of turf brush peatsorb. in filtrate was determined ph (mettler toledo) and cu, fe, al, zn by colorimeter dr 890 (hach lange). 2.4 metals precipitation by naoh the precipitation by 1m naoh solutions was used for the removal of metals as hydroxides from amd. experiments were carried out by raw amd samples of 100 ml and each were titrated to ph end points ranging from 5 to 9 using 1m naoh. when the preset ph end point was reached, the titrated solution was filtered to precipitated metals removing. during titration the amd solution was continuously stirred, the ph was monitored and the concentration of metals was determined too. 2.5 metals precipitation by biogenic h2s and naoh for the production of the bacterially h2s the cultures of srb (genera desulfovibrio) were used. these bacteria were isolated from a mixed culture obtained from the potable mineral water (gajdovka spring, the locality kosice-north, slovakia). 26 luptakova, a . et al. this biological-chemical method contains several process steps and can be divided in to these main steps, as well as: the bacterially h2s production by srb; the heavy metals precipitation by the bacterially produced h2s; the heavy metal sulphides separation by the filtration; the setting ph of the filtrate from previous steps by 1m naoh (the precipitation of metals as hydroxides); the heavy metal hydroxides separation by the filtration; the subsequent precipitation of the heavy metals by bacterially produced h2s. values of ph for the heavy metals precipitation were assigned on the ground of the study of the orientation conditions for the selected metal removal from amd by precipitation using naoh and our previous works and enumerations (luptakova et al., 2003). the concentration of metals was determined by atomic absorption spectrometry using spectrometer aa-30 varian instrument. a glass ph electrode combined with the reference ag/agcl electrode was used to measure ph. digital phmeter gprt 144 agl was used. 2.6 sorption of metals by bacterially produced iron sulphides the preparation of biogenic sulphides was realized in the bioreactor filled with 400 ml of modified nutrient medium dsm-63 and inoculated with 100 ml of a culture of srb during 21 days at 30°c under anaerobic conditions. these conditions were generated by introducing an inert gas (n2) and chemically with sodium thioglycolate. the ph of the medium was adjusted to the value 6.8 with sodium hydroxide. preparation was realized under 2 different modes. during discontinuous mode the bioreactor worked without addition of fresh nutrient medium. during semicontinuous process of preparation the bioreactor worked 4 days in batch mode and then 3 days in continuous mode (i.e. fresh medium was supplied into reactor). batch sorption experiments were performed in 100 ml erlenmeyer flasks with the sorbent dose 1 g/l. sampling was conducted during 90 minutes. the concentration of zinc and cadmium was determined by atomic absorption spectrometry. 2.7 sorption by bio-modified brown coal the cultures of selected micromycetes were grown in sabouraud agar medium. suspension was injected (5 ml) of every 14-day-old culture spores in sab to the 10 g of brown coal mixed with 10 ml of sab medium. the cultivation was executed in the dark at ambient temperature. the leaching process took 7 weeks. after leaching, the suspensions were filtered, washed with distilled water, dried and prepared for adsorption experiments. all the adsorption experiments were conducted at ambient temperature in a laboratory shaker. metal solutions of known concentrations were introduced into the glass erlenmeyer bottles containing defined amounts (10 g/l) of the adsorbent. the bottles were shaken horizontally and the adsorbent was removed by filtration after 1 hour adsorption. the equilibrium concentrations of heavy metals were determined by atomic adsorption spectroscopy and the metal uptake was calculated from the difference. the langmuir adsorption isotherms have been constructed and the maximum adsorption capacity of the adsorbents has been nova biotechnologica 10-1 (2010) 27 determined. for cu(ii) sorption the ph reached 5, as cu(ii) ions undergo hydrolysis reactions in water and form insoluble aqueous complexes with increasing ph. zn(ii) sorption experiments were performed at ph 7 for the same reason as in case of cu(ii) adsorption. 3. results and discussion 3.1 adsorption metals by turf table 1 documents the physical-chemical method studies and there are also given the results of ph measuring in amd turf brush mixture depending on time and influence of adsorption processes on cu, fe, al, zn concentrations in individual samples. from the results follows, that it is possible to decrease the cu, fe, al and zn concentrations in polluted surface water by physical adsorption. the highest turf brush efficiency was observed for zinc removal, where the decrease of concentration in solution was 95.71%. then follows copper (decreasing in amd about 55.88%), iron (21.19%) and aluminium (15.6%). based on experimental results we can also state that chosen adsorbent have not influenced the ph increasing above 4 that is connected with precipitation of metals. table 1. dependence of cu, fe, al and zn removal from amd versus adsorption time. cu fe al zn adsorption time ph [mg/l] amd 3.95 1.36 358.2 54.5 17.5 1 min 3.10 0.86 347.8 52.7 1.5 3 min 2.95 0.61 353.3 46.4 1.2 5 min 2.97 0.61 333.5 46.2 1.0 10 min 2.93 0.60 282.3 46.0 0.75 3.2 metals precipitation by naoh the results of the titration test amd by 0.2m naoh documents fig. 1. it is a documentation of the titration curve and elemental amd analysis. the titration curve of amd can be divided into a number of by its different slopes. it shows that the optimum ph for metals precipitation is different for each metal: for al – ph 5; for cu – ph 6; for zn – ph 7; for fe – ph 8; for mn – ph 9. table 3 demonstrates results of metals precipitation by naoh that is titration of amd to ph end points for the individual metals ranging from 5 to 9 using 1m naoh. as it is seen from table 2 was removed 97% of al at ph 5; 99.9% of cu at ph 6; 99.9% of zn at ph 7; 99.9% of fe at ph 8 and 99.9% of mn at ph 9. initial assumption about precipitation of followed metals up to ph 9 has been confirmed. 28 luptakova, a . et al. 3.3 metals precipitation by biogenic h2s and naoh the selective sequential precipitation of heavy metals form amd sample was performed in two interconnected bioreactors with a capacity 1000 ml (the first bioreactor) and 250 ml (the second bioreactor), which operated at the semi-continual conditions. using the operating conditions and obtained results of the selective sequential precipitation of heavy metals form amd sample illustrated in table 3. the bacterially produced hydrogen sulphide by srb at ph 3.9 (initial ph of amd), 4.5 and 6.0 realized the selective sequential precipitation of cu, zn and fe, respectively (i.e. steps 1, 3 and 5). al and mn were precipitated as aluminium and manganese hydroxide at ph 6.0 and 9.0, respectively (i.e. steps 4 and 6). fe was precipitated predominantly as hydroxide (steps 2, 4 and 6). fig. 1. titration curve and metal amd analysis of amd from the deposit of smolnik. table 2. precipitation of al, cu, zn, fe and mn in ph dependence (initial ph of amd – 3.9). ph al (mg/l) cu (mg/l) zn (mg/l) fe (mg/l) mn (mg/l) 3.9 58.8 1.38 6.88 338.6 22.88 5 0.4 0.65 6.75 268.8 22.88 6 0.4 <0.02 5.38 9.8 22.88 7 0.4 <0.02 <0.03 2.5 20.38 8 0.4 <0.02 <0.03 <0.03 12.25 9 0.4 <0.02 <0.03 <0.03 0.03 table 3. metals precipitation by bacterially produced h2s and naoh (initial amd ph – 3.9). step 1. step 2. step 3. step 4. step 5. step 6. ph 3.9 4.5 4.5 6.0 6.0 9.0 precipitating agent h2s naoh h2s naoh h2s naoh removed metals cu fe, al zn al, fe fe mn, fe form of removed metals (solid phase) cus fe(oh)3 al(oh)3 zns al(oh)3 fe(oh)3 fes mn(oh)2 fe(oh)2 filtrate composition concerning of metals presence (liquid phase) fe, al, zn, mn fe, al, zn, mn fe, al, mn fe, mn fe, mn ----- nova biotechnologica 10-1 (2010) 29 3.4 sorption of metals by bacterially produced iron sulphides fig. 2 shows sorption of cadmium and zinc ions from model solutions by iron sulphides during 90 minutes by semi-continuous and discontinuous sorbents, when initial concentration of metal ions in model solutions was 50 mg/l. 0 5 10 15 20 25 0 10 20 30 40 50 60 70 80 90 time [min] so rp ti on [ m g/ g ] cd-ss (50) cd-ds (50) zn-ds (50) zn-ss (50) fig. 2. sorption of cadmium and zinc ions from model solutions. the quantities of metal ions that iron sulphides captured from 100 ml of solution are in calculation on 1 g weights of dry the sorbent. we can see that the sorption value for cadmium after 90 minutes for semi-continuous sorbent (cd-ss) is 21.96 mg/g and 21.83 mg/g for discontinuous sorbent (cd-ds). values of zinc sorption are 9.49 mg/g for semicontinuous sorbent (zn-ss) and 5.22 mg/g for discontinuous sorbent (zn-ds). 0 5 10 15 20 25 30 35 40 45 50 0 10 20 30 40 50 60 70 80 90 time [min] so rp ti o n [ m g /g ] cd-ss (100) cd-ds (100) zn-ds (100) zn-ss (100) fig. 3. sorption of cadmium and zinc ions from model solutions. 30 luptakova, a . et al. fig. 3 compares sorption of zinc and cadmium ions during 90 minutes by semicontinuous and discontinuous sorbents, when initial concentration of metal ions in model solutions was 100mg/l. in this case the highest value was obtained for zinc sorption by semi-continuous sorbent (zn-ss) 43.13 mg/g and the lower value belong to cadmium sorption by semicontinuous sorbent (cd-ss) 22.75 mg/g. 3.5 sorption by bio-modified brown coal fig. 4 presents adsorption isotherms of copper and zinc adsorption by biomodified coal adsorbents. experimental data were fitted by langmuir equation. the correlation coefficient ranged from 0.96 to 0.99. experimental results showed that maximum increase of metals uptake for biologically activated brown coal was achieved by the activation by penicillium glabrum (sample s3), i.e. 8.8 mg cu(ii)/g of sorbent and 14.3 mg zn(ii)/g of sorbent. 0 50 100 150 200 0 2 4 6 8 10 cu adsorption q [m g/ g] c e [mg/l] coal + a. niger coal + a. clavatus coal + p. glabrum coal + t. viride coal 0 50 100 150 200 0 2 4 6 8 10 coal + a. niger coal + a. clavatus coal + p. glabrum coal + t. viride coal zn adsorption q [m g/ g] c e [mg/l] fig. 4. langmuir adsorption isotherms of cu (a) and zn (b) adsorption on brown coal treated by different microorganisms. the results of adsorption experiments showed that selected type of sorbent preparation had positive influence on sorption properties of activated material and prepared sorbents had good affinity to selected metals. obtained results confirmed that there is a possibility to prepare the sorbents by new non-conventional methods and the obtained results appear as promising for the research and development in utilisation of non-energetic coal. 4. conclusions the major metal ions in the amd from the abandoned and flooded deposit of smolnik (slovak republic) were fe, al, ca and mg, among which fe and al were potentially valuable, while others such as cu, zn and mn were present as minor metals at significantly low concentrations. the value of ph, contend of fe, al, zn, cu, mn nova biotechnologica 10-1 (2010) 31 and mg of amd did not meet the effluent limitation of nv sr no. 296/2005 z.z. up to now amd was not treated at the site. results of the amd titration test document that the titration curve can be divided into four ranges (i to iv). its show the different optimum ph for metals precipitation of each metal: for al – ph 5; for cu – ph 6; for zn – ph 7; for fe – ph 8; for mn – ph 9. the metals precipitation using 1m naoh confirms that was removed 97% of al at ph 5; 99.9% of cu at ph 6; 99.9% of zn at ph 7; 99.9% of fe at ph 8 and 99.9% of mn at ph 9. metals removal by precipitation is possible up to ph 9. the study of the selective sequential precipitation and bio recovery of metals from aforementioned amd was realized by the combination of the metals precipitation by the bacterially produced hydrogen sulphide and the precipitation of metals by sodium hydroxide at the various values of ph amd. for the removal of cu and zn in the form of sulphides were received excellent results. was not come to good results point of view of the fe, al and mn the selective precipitation, because was determined the co-precipitation of fe and al or fe and mn. obtained results can be used for suggestion of technology for selective metal recovery from acid mine drainage from smolnik. the base this technology will be the combination of chemical and biological agent application. acknowledgements: this work was supported by the slovak research and development agency under the contract no. apvv-51-027705 and bilateral project apvv sk-cz-0105-07. references balintova, m., kovalikova, n.: removal of heavy metals from acid mine drainage using adsorption methods. proceedings of the 8th international scientific conference modern management of mine producing, geology and environmental protection sgem 2008, albena, 2008, 155-160. boonstra, j., van lier, r., janssen, g., dikman, h., buisman, c.j.n.: biological treatment of acid mine drainage. proceedings of the 13th international biohydrometallurgy symposium, biohydrometallurgy and the environment toward the mining of the 21st century ii., ibs, madrid, 1999, 559-566. deorkar, n.v., tavlarides, l.l.: adsorption process for metal recovery from acid mine waste: the berkeley pit problem. environ. prog., 17, 1998, 120-125. foucher, s., battaglia-brunet, f., ignatiadis, i., morin, d.: treatment by sulfate-reducing bacteria of chessy acid-mine drainage and metals recovery. chem. eng. sci., 56, 2001, 1639-1645. garcia sanchez, a., alavarez ayuso, e., jimenez de blas, o.: sorption of heavy metals from industrial waste water by low-cost mineral silicates. clay miner., 34, 1999, 469-477. janke, d.r., diebold, f.e.: recovery of valuable metals from acid mine drainage by selective titration. water res., 17, 1983, 1639-1645. kadukova, j., vircikova, e.: minerálne biotechnológie iii., biosorpcia kovov z roztokov, všb tu ostrava, 2003, isbn 80-248-0244-9. 32 luptakova, a . et al. kadukova, j., stofko, m.: environmentálne biotechnológie pre hutníkov, equilibria, košice, 2006a, isbn 80-8073-496-8. kadukova, j., stofko, m.: biosorption of heavy metals ions from aqueous solutions. environmental research trends, nova publishers, 2006b, isbn 160021-556-4. kalin, m., fyson, a., wheeler, n.w.: the chemistry of conventional and alternative treatment systems for the neutralization of acid mine drainage. sci. tot. environ., 366, 2006, 395-408. kontopouls, a.: acid mine drainage control. in: castro, s.h., vergara, f., sánches, m.a. (eds.) effluent treatment in the mining industry. university of concepcion, chile, 1988, 57-118. luptakova, a., kusnierova, m., bezovska, m., fecko, p.: the selective precipitation of heavy metals by sulphate-reducing bacteria. proceedings of the 15th international biohydrometallurgy symposium, nereus congress and conferences, athens, greece, 2003, 665-672. luptakova, a., kusnierova, m., slesarova, a.: environmental risks and impact of old mine loads in the slovak republic. proceedings of 2nd international conference on environmental research and assessment, university of bucharest, centre for environmental research and impact studies, bucharest, 2006, 254-257. skousen, j., rose, a., geidel, g., foreman, j., evans, r., hellier, w.: a handbook of technologies for avoidance and reclamation of acid mine drainage, morgantown, wv: national mine land reclamation center, west virginia university, 1998. tabak, h.h., scharp, r., burckle, j., kawaharai, f.k., govind, r.: advances in biotreatment of acid mine drainage and biorecovery of metals: 1. metal precipitation for recovery and recycle. biodegradation, 14, 2003, 423436. veeken, a.h.m., rulkens, w.h.: innovative developments in the selective removal and reuse of heavy metals from waste-waters. water sci. technol., 47, 2003, 9-16. microsoft word sunovska et al 2013_nbec_final.doc nova biotechnologica et chimica 12-2 (2013) 141 doi 10.2478/nbec-2013-0016 © university of ss. cyril and methodius in trnava characterization of soil additive derived from sewage sludge anna šuňovská, miroslav horník, martin pipíška, juraj lesný, jozef augustín, stanislav hostin department of ecochemistry and radioecology, faculty of natural sciences, university of ss. cyril and methodius in trnava, nám. j. herdu 2, sk-917 01 trnava, slovak republic (anna.sunovska@ucm.sk) abstract: the aim of the present work is to characterize the soil additive derived from sewage sludge as potentially economically acceptable material for agricultural production as well as for soil and environment protection. the soil additive consisting of sewage sludge obtained from the wastewater treatment plant pannon-víz zrt. (győr, hungary) and agricultural byproducts represented by wastes from grain mill industry and crushed corn cobs was prepared using the low-capacity granulator equipment constructed by energy agency public nonprofit ltd. (hungary). the characterization of sewage sludge as primary composite and prepared soil additive includes the determination of physico-chemical parameters such as ph determined in suspension with distilled water, 0.01 mol/dm3 cacl2 or 1 mol/dm3 kcl solutions, phzpc predicted by potentiometric titration and protofit software, water holding capacity (whc), cationexchange capacity (cec) and total organic carbon (toc). the elemental analysis by x-ray fluorescence spectrometry revealed that sewage sludge as well as prepared soil additive contain significant amount of zn and cu as important microelements in plant nutrition. also, it was found that prepared soil additive represents the considerable source of a significant proportion, strong bound and in this way gradually released microelements. obtained results suggest on the application potential of prepared soil additive in agricultural production as well as in remediation and reclamation of contaminated or degraded soil. key words: sewage sludge, waste, soil additive, agriculture, remediation, lysimeter 1. introduction in the 20th century, industrialization and ore mining led to the increasing of the number of sites contaminated with metals or organic xenobiotics. nowadays, environmental issues also have been broadened in connection with concepts involving sustainable development, which implies not only ecological, but economical and social responsibilities as well. however, globally the intensification of production processes and relative human activities raise the production of gaseous, liquid and solid wastes. the european community generates approximately two billion tons of waste per year (düring and gäth, 2002). the handling of sewage sludge (ssl) represents one of the most significant challenges in wastewater management (fytili and zabaniotou, 2008). ssl is defined by the u.s. environmental protection agency (epa) as the “solid, semi-solid, or liquid residue generated during the treatment of domestic sewage in a treatment works” (nrc, 2002). within wastewater treatment plant the ssl represents the residue generated during the primary (physical and/or chemical), the secondary (biological) and the tertiary (additional to secondary, often nutrient removal) treatment (fytili and zabaniotou, 2008). the composition of ssl is bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:46 utc 142 šuňovská, a. et al. dependent on its origin in terms of the type of wastewater treatment, and therefore is variable and unpredictable as well. in this way, the public concern and definition of regulations or directives are primarily associated with toxic metals, organic xenobiotics or pathogen occurrence in this type of wastes. ssl treatment by a variety of processes including aerobic digestion, anaerobic digestion, composting, heat drying, air drying, lime stabilization, and chemical fixation is the possible key to minimizing the risks in terms of the quantitative occurrence or negative impacts of mentioned components (mathney, 2011). also, the proportion of macroor microelements and ph levels, alkalinity or organic acid content are important parameters from the point of view of the ssl ultimate disposal as well as the process of anaerobic digestion (tchobanoglous et al., 2003), respectively. all these factors play an important role in decision with regard to the ultimate ssl disposal, which can involve: composting, landfilling, agricultural reuse as well as sea or surface waters disposal and incineration of ssl (donatello and cheeseman, 2013). during the last decades there has been a major change in the ways ssl is disposed (fytili and zabaniotou, 2008). prior to 1998, municipal ssl was primarily disposed at seawaters or was used in agriculture (odegaard et al., 2002). additional solutions include incineration of ssl or landfilling. since 1998 onwards, european legislation prohibits the sea disposal of ssl (fytili and zabaniotou, 2008). large differences between individual eu countries exist in current ssl disposal concerning on the character of disposal operations or their proportion on ssl disposal. some papers have been reported that ssl, except the conventional methods of disposal, can be disposed by pyrolysis or incineration for biochar (méndez et al., 2013) or ash production as building construction materials (chen and lin, 2009) as well as can be used in remediation of soils contaminated with heavy metals (garrido et al., 2012). approximately 5.6 million tons of dry ssl are used or disposed of annually in the united states, of which 60 % is used for land application or public distribution (nrc, 2002). in europe, dry weight per capita production of ssl resulting from primary, secondary and even tertiary treatment represents more than 90 g per person per day (davis, 1996). in conditions of slovak republic the production of ssl within the last decade is relative constant, e.g. in 2002 represent 51,270 tons per year and in 2012 58,706 tons per year. in mentioned year 2012, the ssl was predominantly used for compost production (62.7 %), reclamation (16.4 %), landfilling (13.5 %), incineration (5.5 %) and direct application into the soil (1.9 %) (according to data of mžp sr, 2012). previous works deal with the possibility of application of the sludge originated from sewage treatment plants as potential sorbent for co removing from contaminated solutions (frišták et al., 2013) or application of simultaneous and sequential extraction protocols as tools for determination of zinc bioavailability in dried anaerobic sludge (frišták et al., 2012). the aim of the present work is to characterize the soil additive derived from ssl as potentially economically acceptable material for agricultural production as well as for remediation and reclamation of contaminated or degraded soil. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:46 utc nova biotechnologica et chimica 12-2 (2013) 143 2. materials and methods 2.1 sewage sludge and soil samples dried samples of sewage sludge (ssl) as primary composite for soil additive preparation were obtained from the wastewater treatment plant pannon-víz zrt. (győr, hungary). the sample represented concentrated, anaerobically digested, dewatered and dried ssl. soil samples as a model of agricultural used soil were obtained from experimental fields of plant production research center piešťany (pprc piešťany) in borovce (spring period, 2013; altitude 160 m, north latitude 48°34´, east longitude 17°44´). all obtained samples were kept under laboratory conditions without their special treatment. dry weight of studied matrices was determined at 105 °c in drying chamber and the distribution of particles size of individual samples was evaluated by sieve analysis with standard sieves using. 2.2 soil additive derived from sewage sludge dried samples of soil additive consisting of mentioned ssl and agricultural byproducts represented by wastes from grain mill industry and crushed corn cobs (top feed & cargo hungary holding zrt., hungary) were prepared in volume ratio 1 : 1.5 using the low-capacity granulator equipment (fig. 1) designed by energy agency public nonprofit ltd. (budapest, hungary). the low-capacity granulator provided the mixing of both primary composites and thermal treatment (~ 75 °c) for inhibition of present microorganisms. fig. 1. low-capacity granulator equipment designed by energy agency public nonprofit ltd. (hungary) (a) for production of designed soil additive (b) – primary pellets (left) and crushed material applied in experiments (right). 2.3 determination of ph and cation-exchange capacity the ph determination or cation-exchange capacity (cec) of ssl, prepared soil additive and agricultural used soil were realized according to iso standard method no. 10390 or no. 11260, respectively. a b bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:46 utc 144 šuňovská, a. et al. according to mentioned standard method soil suspensions with deionized water, 1 mol/dm3 kcl or 0.01 mol/dm3 cacl2 at volume ratio v(matrix) : v(solution) = 1 : 5 were stirred on orbital incubator shaker (150 min-1) within 1 h at 25 ºc and subsequently the ph value of these suspensions was measured using glass electrode. in the case of cec determination the studied matrix was suspended in bacl2 solution for the reason ba binding in matrix and removing of others present cations. subsequently, the matrix saturated with ba was suspended with mgso4 solution and remaining, non-binding amount of mg2+ cations was analyzed by chelatometric titration using edta-na2 on eriochrome black t indicator. 2.4 elemental and total organic carbon analysis the elemental analysis of ssl and prepared soil additive samples was performed by x-ray fluorescence spectrometry using the high performance x-ray fluorescence spectrometer x-lab 2000, spectro (germany). the content of as, ca, cd, cr, cu, fe, mg, mn, ni, pb, sb, se and zn was analyzed in samples treated to granularity < 0.063 mm. total organic carbon (toc) was determined using toc analyzer toc-vcpn shimadzu (japan). 2.5 potentiometric titration with the aim to prediction of protonation constants pka and binding sites concentration of functional group can on the surface of studied matrices the potentiometric titration according to modified procedure described by zhang et al. (2010) was carried out. the sample was transferred into erlenmeyer flask containing a mixture of 0.1 mol/dm3 hcl and 0.1 mol/dm3 nacl, stirred on orbital shaker and centrifuged. the studied matrix was suspended in 0.1 mol/dm3 nacl solution and in this suspension the titration solution 0.l mol/dm3 naoh was gradually added with the parallel measuring ph. the obtained data describing the relationship between the volume of added titration solution and the measured ph values were analyzed by modelling program protofit ver. 2.1.(turner and fein, 2006). 2.6 determination of water holding capacity the determination of water holding capacity (whc) value was realized in 30 cm length glass column with internal diameter 2.5 cm. the defined amount (in grams) of individual samples of ssl, soil additive and soil or the mixture soil additive : soil in weight ratios 1 : 9; 1 : 4; 1 : 1.5 or 1 : 1.25 was transferred into the column with the bottom cap. subsequently, the defined amount of distilled water (in grams) equivalent with the amount of matrix sample was added into the mentioned system. after 30 min the bottom of the column was opened and the water eluate was collected into erlenmeyer flask during the next 30 min. the whc value was calculated bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:46 utc nova biotechnologica et chimica 12-2 (2013) 145 according to gravimetrically evaluation of water balance between added water into system and obtained amount of eluate. 2.7 single extraction of zn and cu from studied matrices for the evaluation of available microelements zn and cu amount in studied matrices the mehlich method was used. the suspension of matrix and mehlich-iii solution in weight ratio 1 : 10 was stirred on orbital shaker during 10 min. the mehlich-iii extraction solution consisted of 0.2 mol/dm3 ch3cooh, 0.25 mol/dm3 nh4no3, 0.015 mol/dm 3 nh4f, 0.013 mol/dm 3 hno3 and 0.001 mol/dm3 edta (mehlich, 1984). subsequently, the suspension was filtered and in solution the concentrations of zn and cu were analyzed by atomic absorption spectrometer (aa-7000 shimadzu, japan) with electrothermal atomization (gfa-7000 shimadzu, japan). from the obtained concentration of zn and cu the available amount of zn and cu in milligrams per kilogram of matrix was calculated. 2.8 laboratory lysimetric experiment a plastic laboratory lysimeter (ecotech, germany) with diameter 30 cm and height 50 cm was filled with 45 kg of dried agricultural used soil (content of water max. 2.1 %). mentioned laboratory lysimeter was equipped with: sprinkling head for soil watering, temperature sensors and tensiometers located in soil column within 10 cm, 20 cm or 30 cm from the surface, suction bottom with controlled vacuum pump for sampling of soil eluates, and datalogger for data acquisition with communication and evaluation software. the whole lysimeter system containing soil column with 0.28 m2 of surface and 40 cm height was maintained under defined conditions of plant growth chamber (kbwf 720 binder, germany) and in the given time intervals weighted for water balancing in the system. 3. results and discussion 3.1 physico-chemical characterization of studied matrices in the first step of sewage sludge (ssl), prepared soil additive and model of agricultural used soil characterization the analyses aimed to the determination of ph (phh2o, phcacl2 and phkcl), cation-exchange capacity (cec) and total organic carbon (toc) values were carried out. obtained results showed that studied matrices were significantly differed in all evaluated values (table 1). the lowest ph value was determined for designed soil additive consisting of ssl as primary studied composite and agricultural byproducts represented by wastes from grain mill industry and crushed corn cobs. on the other side, the sample of soil additive showed higher values of cation-exchange capacity (cec) and total organic carbon (toc) in comparison with ssl and agricultural used soil. this fact suggests on the potential bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:46 utc 146 šuňovská, a. et al. positive effect of such soil additive, particularly in the case of basic soils, in terms of the increasing metals availability for plant production purposes as well as in remediation of soils contaminated with toxic metals using selected plant species applied in phytoremediation methods (chiu et al., 2006). table 1. determined values of ph (phh2o, phcacl2 and phkcl), cation-exchange capacity (cec) and total organic carbon (toc) for studied matrices. matrix phh2o phcacl2 phkcl cec (meq/100 g) toc sewage sludge* 6.73 6.66 6.57 28.2 28.6 % soil additive ** 5.75 5.61 5.38 33.2 37.4 % soil *** 7.26 6.78 6.30 29.0 1.10 % (cox) * sewage sludge obtained from the company pannon-víz zrt. (hungary) as primary composite of prepared soil additive; ** soil additive consisting of sewage sludge and agricultural byproducts represented by wastes from grain mill industry and crushed corn cobs was prepared using the low-capacity granulator equipment constructed by energy agency public nonprofit ltd. (hungary); *** soil obtained from the experimental fields of pprc piešťany as a model of agricultural used soil.   2 3 4 5 6 7 8 9 10 11 12 0.0 0.5 1.0 1.5 2.0 2.5 3.0 ph soil additive sewage sludge a dd iti on o f 0 .1 m ol /d m 3 n ao h [c m 3 ] 0 20 40 60 80 100 soil soil additive p ro po rt io n of fr ac tio ns [% ] sewage sludge < 0.15 mm 0.31 mm 0.15 mm 0.63 mm 0.31 mm 1.20 mm 0.63 mm > 1.2mm fig. 2. a. potentiometric titration curves for sewage sludge and designed soil additive (3.0 g/dm3). the titration was performed with addition of 0.1 mol/dm3 naoh and 0.1 mol/dm3 nacl as background electrolyte and at 25 °c. b. sieve analysis of studied matrices for determination of fraction proportion of individual particles on the basis of their size. in the context with the cec value, the potentiometric titration analysis of ssl and prepared soil additive was realized (fig. 2a). this analysis confirmed that prepared soil additive containing except the evaluated ssl also agricultural byproducts represented by wastes from grain mill industry and crushed corn cobs showed higher proportion of important functional groups from the point of view of metal cations binding such as carboxyl (–cooh), hydroxyl (–oh), phosphate (–po3h2) or amino (–nh2) groups. protofit software predicted that in prepared soil additive the concentrations of mentioned functional groups were minimally 4-times higher in comparison with the primary composite – sewage sludge, particularly a b bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:46 utc nova biotechnologica et chimica 12-2 (2013) 147 in the case of basic functional groups (–nh2 and –oh). from the potentiometric titration data fitted by the program protofit the values of phzpc were also predicted, whereby the phzpc value (ph of zero point charge) represents the ph at which the matrix has a net zero surface charge. the matrix surface has a net positive charge at ph < phzpc, while at ph > phzpc, the surface has a net negative charge (sun et al., 2011). ssl showed practically neutral value of phzpc = 7.8 in contrast to the prepared soil additive, when the phzpc reached the value 9.4. in cation binding the specific surface of matrix particles plays also a decisive role. fig. 2b depicts the fraction proportion of individual particles on the basis of their size for studied matrices determined by sieve analysis. 0 20 40 60 80 100 120 mixture soil + soil additive 80 %40 %20 %10 %soil additive sewage sludge soil w h c [g h 2o /1 00 g ] weight proportion of soil additive in mixture fig. 3. water holding capacity (whc) determined for individual studied matrices or for mixture of model agricultural used soil and prepared soil additive with different weight proportion of soil additive. in the last decades, the climatic changes in terms of floods and dry season rotation play an important role in agricultural production. therefore, the soil additive of this type and its characteristics should take into account the mentioned negative effects of climatic changes on the soil quality. in experiments evaluating the values of water holding capacity (whc), we found that soil additive prepared from ssl and agricultural by-products represented by wastes from grain mill industry and crushed corn cobs showed the highest values of whc in comparison with ssl and model of agricultural used soil. also, the addition of prepared soil additive had the positive effect on the increasing of whc values of mixture soil additive : soil (fig. 3). from the point of view of ssl application into the soil is very important to know the presence and concentration of toxic substances as well as microbial contamination. these factors are reflected in the relevant eu legislative directions. as we mentioned, the ssl added as composite into the designed soil additive was thermally treated with the aim of microorganisms inhibition. in the context of toxic substances presence in ssl, we focused on toxic metals as well as important macroand microelements content (table 2). bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:46 utc 148 šuňovská, a. et al. united states environmental pollution agency (us epa) developed parameters the effects range low (erl) and the effects range median (erm) as predictive tools for contamination characterizing in sediments. the erl represents the tenth percentile of the effects database, below which harmful effects on aquatic biota are rarely observed. the erm represents the fiftieth percentile of the effects data and is indicative of concentrations above which harmful effects are often observed (us epa, 2002). also, these parameters can be applied for ssl as water sediments. from the elemental analysis by x-ray fluorescence spectrometry, we found that studied ssl showed overload of the erl parameter in the case of cr and ni and overload of the erm parameter for cu and zn. despite this fact, it can be concluded that the concentrations of cr and ni do not represent a serious risk of soil contamination with heavy metals after designed soil additive application into the soil in the case of observance of rules defined by legislation of the slovak republic (act no. 188/2003) determining the maximal amount of applied ssl into the soil 15 tons (dry weight; d.w.) per ha and per 5 years. also, this act no. 188/2003 determines the limits of maximal concentrations for mentioned metals cr and ni in ssl applied into soil, which represent the values 1,000 and 300 mg/kg (d.w.), respectively. on the other hand, in the case of soils deficient in zn or cu as important microelements in plant nutrition, the prepared soil additive containing zn and cu in this level can represents a valuable source of these nutrients. table 2. elemental analysis of studied matrices by x-ray fluorescence spectrometry. element sewage sludge* soil additive** as 8.0 ppm 6.5 ppm ca 4.74 % 3.21 % cd < 2 ppm < 2 ppm cr 84.7 ppm a 67.5 ppm cu 654 ppm b 583 ppm b fe 3.92 % 3.13 % mg 0.61 % 0.21 % mn 0.03 % 0.03 % ni 42 ppm a 44 ppm a pb 36 ppm 26 ppm sb 4.67 ppm < 2 ppm se 2.67 ppm < 1 ppm zn 1,940 ppm b 1,510 ppm b a overload of the effects range low (erl); b overload of the effects range median (erm). 3.2 single extraction of zn and cu from studied matrices in the context with previous results indicating the fact that ssl as well as prepared soil additive showed high content of zn and cu as important microelements in plant bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:46 utc nova biotechnologica et chimica 12-2 (2013) 149 nutrition, the experiment evaluating availability of these metals for plants were carried out. for these purposes, the method according to mehlich (mehlich, 1984) was applied. from the fig. 4a, it is evident that more than 2-times higher amount of zn was extracted by mehlich-iii solution from prepared soil additive in comparison with ssl (130 mg/kg; d.w.) as primary composite. in the case of cu up to 6-times higher extractable amount for soil additive (10 mg/kg; d.w.) was found. for comparison, the extractable amount of zn and cu for sample of agricultural used soil is also mentioned in fig. 4a. within these results, the fact of higher total content of zn and cu in the case of ssl as well as 3-times higher total amount of zn in comparison with cu in studied matrices should be taken into account (table 2). in this way, the proportion of available zn and cu for soil additive represents more than 19 % and 11 %, respectively (fig. 4b). it can be concluded that the addition of agricultural by-products represented by wastes from grain mill industry and crushed corn cobs and the treatment of ssl at production of designed soil additive using the low-capacity granulator equipment caused the changes responsible for increasing of available zn and cu proportion in this matrix. also, it can be supposed that the proportion of zn and cu will be lower in the case of agricultural by-products represented by wastes from grain mill industry and crushed corn cobs in comparison with ssl. therefore the mentioned changes probably take place significantly within the ssl. 0 50 100 150 200 250 300 e xt ra ct ab le a m ou nt [m g/ kg ]; d. w . zn cu soil sewage sludge soil additive soil soil additive sewage sludge 0 5 10 15 20 25 p ro po rt io n of a va ila bl e m et al [% ] zn cu soil additive sewage sludge sewage sludge soil additive fig. 4. the single step extraction of zn and cu from agricultural used soil, sewage sludge and designed soil additive by mehlich-iii solution expressed as the total extractable amount of metal (in mg/kg) (a) or the ratio of extracted amount of metal to the total amount of metal in matrix (b). yu et al. (2004) found that between the total amount of cu in soil and extractable amount of cu by mehlich-iii solution the linear dependence exists. also, these authors observed the proportion of extractable amount of cu in comparison with the total amount of cu in degraded soil more than 50 %. it is generally known that the availability of heavy metal such as zn and cu is also strongly determined by factors e.g. ph, organic matter, clay minerals, oxyhydroxides, and others (kabata-pendias, 2011). obtained results showed that the availability of zn and cu in soil additive is relatively low. this fact suggests that prepared soil additive represents the source of a significant proportion, strong bound and in this way gradually released a b bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:46 utc 150 šuňovská, a. et al. microelements. these characteristics correspond with suitable parameters for agricultural production. strong binding of metals or relative high cec values can be also utilized in remediation and reclamation of contaminated or degraded soil. 3.3 laboratory lysimetric experiment in this part the potential of laboratory lysimetric system application in further study of positive or negative characteristics of soil additive derived from ssl for agricultural production or remediation and reclamation of contaminated or degraded soil is demonstrated. the following preliminary experiment under laboratory conditions was focused on evaluating the possibility to imitate the behaviour of mentioned soil additive in conditions of agricultural used, contaminated or degraded soils. in this term, the possibility to control the soil column watering, the obtaining of soil eluate and vertical distribution of soil moisture, as well as the effect of temperature, relative humidity or illumination on these processes were studied. 0 100 200 300 400 500 600 -800 -700 -600 -500 -400 -300 -200 -100 0 100 2b -10 0 10 20 30 40 5 0 6 0 70 80 90 100 110 120 13 0 -800 -700 -600 -500 -400 -300 -200 -100 0 100 p re ss u re p o te n tia l [ h p a ] t im e [h] 1 2 a 3 a 3b p re ss ur e po te nt ia l [ hp a] time [h] 10 cm from the soil surface 20 cm from the soil surface 30 cm from the soil surface 1 2a a 3c 3d 3e a 4 fig. 5. the changes in the soil moisture within the soil column (diameter 30 cm; height 40 cm) located in the laboratory lysimeter caused by watering, suction of soil eluate, evapotranspiration of water under given conditions in plant growth chamber (temperature, relative humidity or illumination). 1. start of the experiment with column of dried soil (content of water max. 2.1 %); 2. watering of soil with distilled water using lysimeter sprinkling head: a – during 6 h with the watering rate 0.66 dm3/h, b – during 3 h with the watering rate 0.66 dm3/h; 3. suction of soil eluate by controlled vacuum pump: a – during 4 h under pressure 20 – 40 hpa, b – during 6 h under pressure 20 – 40 hpa, c – during 1 h under pressure 50 – 100 hpa, d – during 24 h under pressure 20 – 40 hpa, e – during 72 h under pressure 20 – 40 hpa; 4. activation of illumination 16 h day / 8 h night with 11 450 lx intensity up to end of experiment. the fig. 5 depicts the tensiometric data of water pressure potential defining the changes in the soil moisture within the soil column (diameter 30 cm; height 40 cm) installed in the laboratory lysimeter caused by watering, suction of soil eluate or evapotranspiration of water under given conditions in plant growth chamber (temperature, relative humidity or illumination). at the start of experiment the sample bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:46 utc nova biotechnologica et chimica 12-2 (2013) 151 of agricultural used soil in individual 10 cm layers from the soil surface showed the values of water pressure potential up to 700 hpa, which correspond with the water content approx. 2 %. the values of water pressure potential near to 0 hpa represent the water saturated soil. it can be seen that the application of 4 dm3 distilled water in the amount and rate typical for natural rain conditions caused significant increasing of water content in soil column (45 kg; d.w.) near to soil saturation with water, but without soil eluate obtaining. within the next 6 days the gradually decreasing of soil moisture in all analyzed vertical soil layers supported by 2 suction under pressure was observed. subsequently, the repeated soil watering with 2 dm3 distilled water was carried out. the next decreasing of soil moisture was sequentially supported by suction of soil eluate in different time duration as well as illumination (16 h day / 8 h night with 11 450 lx intensity) provided by plant growth chamber. it was found that under mentioned conditions, it is possible to significantly change the soil moisture within short time correlating with the real natural conditions. moreover, the different quantitative distribution of soil moisture within the vertical location of analyzed soil layers was obtained. in the fig. 6, the conditions related with temperature and relative humidity within lysimetric experiment are described. 0 100 200 300 400 500 600 0 5 10 15 20 25 30 temperature relative humidity time [h] t em pe ra tu re [° c ] day night 0 20 40 60 80 100 r elative hum idity [% ] fig. 6. the changes in the values of temperature and relative humidity within the lysimetric experiment described in the fig. 5. 4. conclusions the soil additive consisting of sewage sludge and agricultural by-products represented by wastes from grain mill industry and crushed corn cobs, and prepared by designed low-capacity granulator equipment was characterized on the basis of physico-chemical parameters such as ph, phzpc, cation-exchange capacity (cec), water holding capacity (whc), total organic carbon (toc) and the content of toxic metals or microelements. the elemental analysis revealed that applied sewage sludge as well as prepared soil additive contain significant amount of zn and cu as important microelements in plant nutrition. in this context, it was found that prepared soil bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:46 utc 152 šuňovská, a. et al. additive represents the considerable source of a significant proportion, strong bound and in this way gradually released microelements. these characteristics correspond with suitable parameters for agricultural production as well as for remediation and reclamation of contaminated or degraded soil. in a separate part of the work the potential of laboratory lysimetric system application in further study of positive or negative characteristics of soil additive derived from sewage sludge for mentioned purposes was evaluated. acknowledgement: this work was supported by the project of the cross-border co-operation programme and co-financed with european regional development fund (erdf), the grant number husk/1101/1.2.1/0148 as well as the project of the operational program research and development and co-financed with european regional development fund (erdf), the grant number itms 26220220106. also, authors want to thank dr. daniela mackových for x-ray fluorescence spectrometric and toc analyses. references act no. 188/2003 (zákon č. 188/2003 z. z.): zákon o aplikácii čistiarenského kalu a dnových sedimentov do pôdy a o doplnení zákona č. 223/2001 z. z. o odpadoch a o zmene a doplnení niektorých zákonov v znení neskorších predpisov, národná rada slovenskej republiky, 2003. davis, r.d.: the impact of eu and uk environmental pressures on the future of sludge treatment and disposal. water environ. j., 10, 1996, 65-69. donatello, s., cheeseman, c.r.: recycling and recovery routes for incinerated sewage sludge ash (issa): a review. waste manag., 33, 2013, 2328-2340. düring, r.a., gäth, s.: utilization of municipal organic wastes in agriculture: where do we stand, where will we go? j. plant nutr. soil sci., 165, 2002, 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mohamed m. el-zahed, m. i. abou-dobara, ahmed k.a. el-sayed, zakaria a. m. baka department of botany and microbiology, faculty of science, damietta university, new damietta, egypt  corresponding author: mohamed.marzouq91@du.edu.eg article info article history: received: 20th june 2021 accepted: 8th november 2021 keywords: antimicrobial biosynthesis escherichia coli nanocomposite silica silver abstract silica (sio2) has a fundamental role in the recuperation of plants in response to environmental stresses, besides the induction of resistance against plant diseases. silver nanoparticles (agnps) have a superior antimicrobial activity. the combination between sio2 and agnps is a promising approach due to their antimicrobial activity, biological activity, low toxicity, and high stability of the produced nanocomposite. the current study postulated a green method for silver/silica nanocomposite (ag/sio2nc) synthesis at room temperature using the crude metabolites of escherichia coli d8 (mf062579) strain in the presence of sunlight. uv-vis spectrophotometry, x-ray diffraction (xrd), fourier transforminfrared spectroscopy (ftir), and transmission electron microscopy (tem) analyses have characterized the biosynthesized nanocomposite. tem study of ag/sio2nc showed an average particle size of ~32 – 48 nm whereas agnps showed a mean size of 18 – 24 nm. the negative charged ag/sio2nc (-31.0 mv) showed potent antimicrobial activity against bacillus cereus atcc6633, klebsiella pneumoniae atcc33495, staphylococcus aureus (atcc25923), e. coli (atcc25922), candida albicans (atcc10231), and botrytis cinerea (pers: fr.). the minimum inhibitory concentration (mic) test showed a dose-dependent manner of ag/sio2nc antimicrobial action. mic values of ag/sio2nc against the tested pathogens exhibited 125 and 6.25 μg.ml-1 as antibacterial and antifungal agents, respectively. tem micrographs showed changes in the pathogens treated with ag/sio2nc including wrinkling, damage, and rupture of the bacterial cell membrane. in addition, the formation of a mucilage matrix connecting the hyphal cells, the appearance of big vacuoles and lipid droplets with severe leakage of cytoplasmic contents of the treated b. cinerea were also recorded. introduction nowadays, there is a tendency to use materials after converting them into their nano-form, because of the new and promising advantages and unique properties gained in the new nano-form such as antimicrobial activity, chemical, magnetic, electronic, or mechanical properties because of the change of quantum and surface boundary effects compared with their bulk materials (chhipa and joshi 2016; musere et al. 2021). nanomaterials can be described as materials with a size of 1 – 100 nm, known as the nano-scale range. synthesis of nanometals can be done using different methods such as chemical, physical or biological techniques. conventional hypothesis of chemical synthesis of nanoparticles (nps) might possess several serious problems due to using expensive toxic chemicals (zhang et al. 2021). mailto:mohamed.marzouq91@du.edu.eg nova biotechnol chim (2022) 21(1): e1023 2 physical methods include high radiation and stabilizing agents that might be dangerous for human health and to the environment (awwad et al. 2020). accordingly, the green synthesis of nps by plant extracts or microbial metabolites plays an important role in the reduction of metal ions into nps and capping them in supporting their stability (parveen et al. 2016). biological nps have different characters compared with chemical or physical nps, with superior stability and suitable dimensions due to the one-step technique (narayanan and sakthivel 2011). silver nanoparticles (agnps) were used as a potent antimicrobial agent during the last decades (hamad et al. 2020). it showed antimicrobial activity against pathogens such as escherichia coli (yang et al. 2021), staphylococcus aureus (enan et al. 2021), klebsiella pneumoniae (pareek et al. 2021), candida albicans (takamiya et al. 2021), and botrytis cinerea (ouda 2014). the aggregation of agnps is a common problem that decreases their biological activity (el-dein et al. 2021). one way to enhance the metal nps stability is by stabilizing them by embedding them inside a polymer, which prevents their aggregation, even at high-volume fractions (baheiraei et al. 2012). several previous studies have focused on the synthesis of stable monodisperse silica-coated with nanometals, mainly ag and gold (au) (chen et al. 2017; si et al. 2019; li et al. 2021). silica (sio2) can act as the platform for developing nps moreover having antimicrobial properties owing to their large surface area, positive surface charge, and monodispersity. gankhuyag et al. (2021) reported that sio2 might increase the stability of the nanometals and prevent their aggregation. in addition, the net positive charge of sio2 facilitates a greater number of agnps to interact with the negatively charged surface of bacteria, resulting in highly efficient antimicrobial activity (jayasuriya 2017). egger et al. (2009) and sohrabnezhad et al. (2020) demonstrated the antibacterial activity of silver/silica nanocomposite (ag/sio2nc) against both e. coli and s. aureus. ag/sio2nc revealed marked changes in the bacterial cell contents, including the cell wall integrity, metabolism, and genetic stability of pseudomonas aeruginosa (anas et al. 2013). also, xu et al. (2009) reported the antibacterial effects of ag/sio2 core-shell particles against e. coli and s. aureus. ag/sio2nc had antifungal potential against b. cinerea as reported by oh et al. (2006). youssef and roberto (2021) demonstrated the antifungal activity of chitosan/silica nanocomposite against b. cinerea. ag/sio2nc showed fungicidal activity against the pathogenic fungi in the soybean plants (fusarium oxysporum and rhizoctonia solani) as reported by nguyen et al. (2016) and aspergillus flavus as reported by diagne et al. (2020). hence, new distinctive structures of ag/sio2nc could present a new prospect for its antimicrobial activity. the present study aimed to evaluate the ability of the crude metabolite of e. coli d8 (mf062579) for reducing the silver nitrate (agno3) into agnps extracellularly and also their binding with sio2 in a new one-step green approach. the antimicrobial potential of ag/sio2nc was studied against some pathogenic strains, comparing their activity to the standard commercial antibiotics. experimental microbial cultures e. coli d8 (ac: mf062579) and the pathogenic bacterial and fungal strains were obtained from the culture collection of botany and microbiology department, faculty of science, damietta university, egypt. chemicals the chemicals included silver nitrate (panreac quimica s.l.u, barcelona, spain), silica (silicon dioxide nanoparticles, particle size 190 – 250 nm, mesoporous, pore size 4 nm, sigma-aldrich), culture media, and other chemicals (sigma aldrich chemical pvt. ltd., india). penicillin g potassium (buffered pfizerpen) and fluconazole (diflucan) were purchased from pfizer inc., new york, ny. biosynthesis of silver nanoparticles and silver/silica nanocomposite silver nanoparticles were prepared according to elzahed et al. (2021). in brief, e. coli d8 agar slants were sub-cultured on nutrient agar plates (37 °c, 24 h). then the grown colonies were inoculated into a nutrient broth medium with 0.5 mcfarland standard (1 – 2 × 108 cfu.ml-1) and incubated at nova biotechnol chim (2022) 21(1): e1023 3 37 °c/150 rpm for 48 h. later, the cell-free metabolites of e. coli d8 were collected by centrifugation (3h24ri intelligent high-speed refrigerated centrifuge, herexi instrument, and equipment co., ltd) at 8,000 rpm for 20 min and filtration through a sterile 0.22 µm syringe filter (millex gv, millipore). for the synthesis of agnps, 1.5 mm of agno3 solution was mixed with cell-free metabolites (1 % v/v) at room temperature and sunlight. for the synthesis of ag/sio2nc, 0.5g of agno3 was dissolved into 50 ml of distilled water and then added to another beaker that included 100 g of sio2. at room temperature, the previous solution was mixed well with 20 ml of e. coli d8 cell-free metabolites in the presence of sunlight. the first indicator for the agnps and nanocomposite (nc) formation was the color change from colorless (agno3) or white (sio2) into brown. after 20 min, the agnps and ag/sio2nc were collected separately by centrifugation at 10,000 rpm for 15 min several times and then dried in an oven at 50 °c for 24 h. then, the nps and nc were dried at 185 °c for 5 h (sadeghi et al. 2013). characterization of silver/silica nanocomposite silver/silica nanocomposite spectra were scanned by uv/vis/nir spectrophotometer (v-630, jasco corporation, japan). the x-ray diffraction (xrd) pattern of the ag/sio2nc was performed at 2θ values (l = 1.54 °a in the range 10 – 80 °) using a cu x-ray tube at 40 kv and 30 ma with the xray diffractometer (model labx xrd-6000, shimadzu, japan). fourier transform infrared spectroscopy (ftir) spectrum of the ag/sio2nc was recorded by jasco ft/ir-4100typea in the 400 – 4,000 cm-1 range. the size and morphology of agnps and ag/sio2nc were investigated by tem (jeol, jem-2100, japan) at an accelerating voltage of 200 kv and using a carbon-coated copper grid (type g 200, 3.05 μm diameter, taap, usa). charge of agnps and size distribution by volume were recorded by zeta potential analyzer (malvern zetasizer nano-zs90, malvern, uk). antimicrobial potential the antimicrobial potential of ag/sio2nc was tested against gram-positive bacteria (s. aureus atcc25923 and bacillus cereus atcc6633), gram-negative bacteria (e. coli atcc25922 and k. pneumoniae atcc33495), yeast (c. albicans atcc10231), and the phytopathogenic fungus (b. cinerea pers: fr.) by agar well diffusion and broth dilution methods. the bacterial, yeast and fungal strains were grown and tested using mueller hinton agar (mha), bacto-casitone agar, and potato dextrose agar (pda) plates, respectively. 200 μl of 0.5 mcfarland standard (1 – 2 × 108 cfu.ml-1) of microbial suspension was used as an initial inoculum for each test. agar well diffusion method agar well diffusion assay was performed in vitro against the microbial strains according to the guidelines of the clinical and laboratory standards institute (clinical and laboratory standards 2006). about 200 μl of 150 μg.ml-1 of sio2, ag/sio2nc, agno3, penicillin g potassium (antibacterial), and fluconazole (antifungal) were prepared and added separately into small wells (5 mm diameter of size) that were made into the solidified agar plates. plates were incubated at 37 °c for 48 h, 30 °c for 48 h, or 28 °c for 5 days, for bacteria, yeast, and fungi, respectively. after the incubation period, inhibition zones were measured in millimeters (mm). broth dilution method mueller hinton, bacto-casitone and potato dextrose broth media test tubes were prepared, autoclaved, and inoculated by 100 μl of microbial suspensions (0.5 mcfarland standard (1 – 2 × 108 cfu.ml-1)) in three sets of test tubes containing different dosages of ag/sio2nc and penicillin g potassium (antibacterial) or fluconazole (antifungal) concentrations (6.25 – 125 μg.ml-1). then, the tubes were incubated at 37 °c/120 rpm for 24 h, 30 °c/120 rpm for 24 h, or 28 °c/120 rpm for 5 days, for bacteria, yeast, and fungi, respectively. the minimal inhibition concentration (mic) for the tested pathogenic strains was determined by measuring their growth spectrophotometrically at nova biotechnol chim (2022) 21(1): e1023 2 600 nm against negative controls (exclusive of ag/sio2nc). the growth inhibition percentage was calculated using the following formula (eq. 1): % growth inhibition = (1) where the negative control (broth media exclusive of ag/sio2nc) optical density; odc and the ag/sio2nc-treated tested sample optical density; odt (clinical and laboratory standards 2008; 2017). ultrastructural study the ultrastructure of ag/sio2nc treated e. coli and b. cinerea was studied with tem (jeol, jem2100, japan, 200kv) according to bozzola (2007). the tested strains were subjected to ag/sio2nc (mic, 6.25 μg.ml-1) for 2 h and compared with untreated bacteria and fungi as controls. the samples were fixed in 2.5 % glutaraldehyde in 0.1m cacodylate buffer at ph 7.0 and then postfixed in 1 % osmium tetroxide, dehydrated with a graded series of ethanol, embedded in a plastic resin, and sectioned on an ultramicrotome. ultrathin sections were double‐stained with uranyl acetate and lead citrate and then loaded on carboncoated copper grids (type g 200, 3.05 μm diameter, taap, u.s.a.). statistical analysis spss software version 18 was used for all the statistical analysis. all values in the experiments were expressed as the mean ± standard deviation (sd) and were analyzed with a one-way analysis of variance (anova) with a significant level set at p < 0.05. results and discussion synthesis and characterization of ag/sio2nc synthesis and characterization of ag/sio2nc have attracted the attention of the materials community because of their promising properties (zaferani 2018). the green synthesis approach of those ncs with controllable size and properties has applications in miniaturized catalysts, photonics, optical devices, medical applications moreover it could be used as a potential nanomicrobicide and nanoscale growth regulator in agriculture (das et al. 2019). endless progression of microbial antibiotic-resistant mechanisms claims continuous searching for alternative approaches to deal with their risk to humans and plants (rai et al. 2012). the present study provided a green approach for the synthesis of antimicrobial ag/sio2nc mediated by the cell-free metabolites of e. coli d8. ftir spectrum confirmed the presence of proteins during the bio-reduction process. these proteins, in the e. coli d8 metabolite, might be including the reducing enzymes and/or some redox agents such as sulfurcontaining proteins resulting in the bio-reduction of silver ions (ag+) into agnps (krishnaraj et al. 2012). also, quinones (menaquinone, demethylmenaquinone, and ubiquinone) found in the e. coli d8 metabolite act as an electron shuttle compound and reduced ag+ into agnps in the presence of sunlight as reported by duan et al. (2015) and sharma et al. (2012). the biosynthesis of agnps was confirmed through visual observation of the color change of the mixture into brown color producing an obvious absorption peak at 430 nm (fig. 1). the brown color is because of the excitation of the agnps surface plasmon resonance (el-dein et al. 2021). granbohm et al. (2018) found the uv-vis spectra of ag/sio2nc powders showed the silver spr peak at 410 nm. fig. 1. the uv-vis spectra of sio2 and ag/sio2nc. the xrd patterns of sio2 were examined and showed an amorphous sio2 characteristic diffraction peak at 22.4 °. ag/sio2nc xrd pattern revealed peaks at 2θ angles of 32.25 °, 38.25 ° and 44.4 ° corresponding to the reflections of (110), (111) and (200) crystalline planes of the face4 nova biotechnol chim (2022) 21(1): e1023 3 centered cubic (fcc) structure of agnps (fig. 2). also, we had found no other diffraction peaks for silver oxide in the ag/sio2nc xrd pattern which showed the coverage of the nc with pure agnps (xu et al. 2015). fig. 2. the xrd patterns of sio2 and ag/sio2nc. the ftir spectra of ag/sio2nc were analyzed in the region of 400 – 4,000cm-1 (fig. 3). the vibration bands around 3,431 and 1,613 cm-1 are attributed to the oh and carbonyl group (c=o), respectively. these signals clearly confirm the presence of bacterial compounds bounded on the surface of ag/sio2nc that affect protection and stability of the nc. the intense peaks around 3,431 and 2,914 cm-1 are attributed to the primary and secondary amines vibrations bands, respectively. the stretch c-n vibration of aliphatic amines existed at 1,078 cm-1 bands. these signals confirmed the presence of proteins in the ag/sio2nc synthesis. water bands were appeared at around 1,613 cm-1 corresponding to bending vibrations indicating the hygroscopic character of the powdered samples (singh and ahmed 2012). si–o–si and si–oh absorptions bands have been observed at 1,078; 783; and 462 cm-1. the si–o–ag linkages stretching were also seen at around 691 cm-1. the band appears in the ag/sio2nc suggesting bonding between the agnps and the oxygen bonded to sio2. the peaks 450 – 800 cm-1 are probably related to the pseudolattice vibrations (mathur et al. 2006). fig. 3. the ftir spectra of sio2 and ag/sio2nc. the ag/sio2nc was examined by the tem (fig. 4) to investigate the morphology and size of the agnps (fig. 4b). agnps are embedded within the matrix and on the surface of the sio2. tem image showed small spherical shaped agnps having a diameter between 18 – 24 nm. gu et al. (2011) reported that the agnps average particle size on the surfaces of sio2 had a little increase from 10 to 25 nm as reaction temperature increased. this should be attributed to the higher reduction rate of ag+ at the elevated reaction temperature. sio2 has a net positive charge, while ag/sio2nc may have a positive or negative surface charge depending on the surface functional group and solution ph (jana et al. 2007; jayasuriya 2017). the synthesis of ag/sio2nc included binding primary amines as confirmed by the ftir analysis. the primary amines were deprotonated during the bio-reduction process, were leading to a gradual decrease in the surface positive charge of sio2 and might approach zero (jana et al. 2007). on the other hand, the binding between the agnps which are capped with highly negative proteins (el-dein et al. 2021), and sio2 to give negatively charged ag/sio2nc. the biosynthesized ag/sio2nc had a negative charge, -31.0 mv (fig. 5), which matched with shanthil et al. (2012) results, -33 ± 2 mv and was better than zhao et al. (2016) and elsheshtawy et al. (2020) results (-16.10 mv and -15 mv, respectively). different studies (verma and stellacci 2010; anas et al. 2013) have studied the interaction of charged nanomaterials with cells showing that positively charged nanomaterials have 5 nova biotechnol chim (2022) 21(1): e1023 2 the greatest efficacy in penetrating the cell membrane. other studies (fuller et al. 2008; martin et al. 2008) have examined the cellular uptake of negatively charged nanomaterials and proposed that negatively charged nanomaterials generate reactive oxygen species (ros) contributes towards potent bacterial toxicity (ivask et al. 2010; agnihotri et al. 2013). a further study of the synthesized ag/sio2nc should be taken into account to improve the antimicrobial efficacy of ag/sio2nc to have a positive surface charge. the positive charge of the nanomaterials increases the efficient electrostatic interaction with the negative charges of the microbial cell wall (li et al. 2011). fig. 4. (a) tem micrograph of sio2. (b) tem micrograph of ag/sio2nc. fig. 5. zeta potential measurement analysis of ag/sio2nc (-31.0 mv). antimicrobial potential of ag/sio2nc the pathogenic bacteria, yeast, and fungi appeared to be more tolerant to sio2 than ag/sio2nc. in this study, ag/sio2nc was investigated to determine its antimicrobial action (fig. 6 and table 1). the nc revealed very good antimicrobial potential against a wide range of microorganisms such as k. pneumoniae, s. aureus, and b. cinerea. the inhibition of microbial growth due to surface contact with the sio2 nanocomposite containing agnps demonstrated that nc functionalized with 6 nova biotechnol chim (2022) 21(1): e1023 2 the agnps has better antimicrobial action than bulk sio2. the antibacterial potential results of ag/sio2nc in he et al. (2012) study revealed that ag/sio2nc were sensitive to s. aureus and e. coli and with the inhibition zone diameter 15.3 mm and 10.4 mm, respectively. lu et al. (2017) studied the combination between chlorhexidine and ag/sio2nc and recorded that combination might produce synergistic bactericidal and candidacidal effects and improve the microbicidal efficiency. in addition, ag/sio2nc showed antifungal potential against b. cinerea besides the antibacterial and anticandidal actions. rodríguez-cutiño et al. (2018) confirmed the antimicrobial properties of ag/sio2nc against bacteria such as e. coli, b. cereus, s. typhimurium, and s. aureus in addition to the green squash fungi: b. cinerea and r. solani. fig. 6. antimicrobial activity of sio2, agnps, and ag/sio2nc; (a) b. cereus, (b) e. coli, (c) k. pneumoniae, (d) s. aureus, (e) c. albicans, and (f) b. cinerea. table 1. antimicrobial activity of sio2, agnps and ag/sio2nc against the pathogenic microbial strains (highly significant = *p < 0.05; n = 3). antibacterial activity (inhibition zone, mm ± sd) substance b. cereus e. coli k. pneumoniae s. aureus agno3 24 ± 0.06* 26 ± 0* 34 ± 0* 29 ± 0* sio2 -ve -ve -ve -ve agnps 30 ± 0.14* 30 ± 0.14* 38 ± 0* 37 ± 0* ag/sio2nc 20 ± 0.06* 22 ± 0.14* 36 ± 0* 34 ± 0* penicillin g potassium 29 ± 0* 30 ± 0* -ve 26 ± 0.06* antifungal activity (inhibition zone, mm ± sd) substance c. albicans b. cinerea agno3 13 ± 0.06* 13 ± 0.14* sio2 -ve -ve agnps 16 ± 0.06* 21 ± 0.14* ag/sio2nc 14 ± 0.06* 24 ± 0.14* fluconazole 15 ± 0* 16 ± 0.14* agnps and penicillin g potassium showed a similar manner of mic values (6.25 μg.ml-1) against s. aureus, b. cereus, and e. coli compared to ag/sio2nc (mic value, 125 μg. ml -1). the 7 nova biotechnol chim (2022) 21(1): e1023 2 mic values against b. cinerea were 6.25 and 25 μg.ml-1 for ag/sio2nc and fluconazole, respectively. the better growth inhibition percentage of ag/sio2nc was against b. cinerea (50.2 %) followed by b. cereus (31.1 %), s. aureus (30.7 %), e. coli (26.6 %), and c. albicans (6.6 %) showing a dose-dependent manner of ag/sio2nc antimicrobial action (fig. 7). the minimum antibacterial concentration of the ag/sio2nc is 0.2 and 0.3 μg.ml-1 for bacillus sp. and e. coli, respectively (huang 2008). qasim et al. (2015) suggested ag/sio2nc to be a potential antifungal agent for c. albicans 077 showing that this tested human pathogenic fungus was sensitive to ag/sio2nc with mic∼6 μg.ml -1 of ag/sio2nc. vladkova et al. (2020) presented that tio2/sio2/ag nanocomposite totally inhibited the e. coli growth within 30 min to 2 h. the growth of b. cinerea was almost completely inhibited (98.4 %) by ag/sio2nc (6.4 µg.ml -1) treatment compared with agnps alone (72.43 %, 6.4 µg.ml-1 as reported by kim (2011). fig. 7. growth inhibition percentage of ag/sio2nc, agnps, and antibiotics at mic values against s. aureus, b. cereus, e. coli, c. albicans, and b. cinerea. it is known that both, ag+ and agnps are effective antimicrobial agents even though their antimicrobial mechanism is not fully understood (kędziora et al. 2018). several studies (feng et al. 2000; lara et al. 2011) reported the different mechanism of the antimicrobial action of nanomaterials such as penetrating the cell wall and plasma membrane, ending with damaging dna molecules. others suggested that nanomaterials might interact with thiol groups in proteins, which induces the inactivation of microbial proteins. in the presented study, agnps bonded on the surface of sio2 have an opposite charge with grampositive bacteria, in that way killing them more easily than gram-negative bacteria due to the electrostatic attraction. the antimicrobial activities of ag/sio2nc are investigated using e. coli and b. cinerea as two model microorganisms. as shown in fig. 8, untreated e. coli was typically rod-shaped with smooth and intact cell walls. after being treated with ag/sio2nc, cell walls became wrinkled and damaged. the separation between the bacterial cell wall and cell membrane was also noted. fig. 8. the antibacterial action of ag/sio2nc on the ultrastructure of e. coli. (a) a negative control (without ag/sio2nc). (b) a treated sample (150 μg.ml -1), there are irregular rods (arrows) with lysed cell walls (ly) and complete cell lysis (cl). also, note the separation that occurs between the bacterial cell wall and cell membrane. ag/sio2nc 8 nova biotechnol chim (2022) 21(1): e1023 3 with treated b. cinerea (fig. 9), tem micrographs showed many changes, including the reduced size of treated cells, the formation of a mucilage matrix connecting the hyphal cells together, the appearance of big vacuole and lipid droplets with severe leakage of cytoplasmic contents in comparing to the control. the separation between the fungal cell wall and plasma membrane was also detected in the treated cells. the observed damages of the e. coli and b. cinerea cells after the treatment by ag/sio2nc could be because of cellular interactions with the agnps. the combined action of adhesion and penetration of agnps might illustrate the biocidal action of the nc, plasma membrane being the target of rapid antimicrobial action of agnps in e. coli and b. cinerea (rai et al. 2012). eckhardt et al. (2013) reported that the binding of agnps with microbial proteins might inactivate the electron transport chain, in that way suppressing the respiration and growth of the microbial cells. to establish that the advantages of silver nanocomposites (agncs) and the possible mechanisms of their antimicrobial action outweigh the possible risks, the toxicity of agnps and agncs must be investigated. w cy v pm v l (a) (b) fig. 9. the antifungal activity of ag/sio2nc on the ultrastructure of b. cinerea. (a) negative control (without ag/sio2nc). note normal cell wall (w), plasma membrane (pm), vacuole (v), and compact cytoplasm (cy). (b) the treated sample, note, the big vacuole (v) and lipid droplets (l). also, note the separation that occurs between the fungal cell wall and plasma membrane (arrow). conclusion the embedded agnps in ag/sio2nc mediated by e. coli d8 were characterized as negativecharged (-31.0 mv) and spherical with an average size ranging between 18 and 24 nm. ag/sio2nc showed a good antimicrobial potential against gram-negative and gram-positive bacteria and pathogenic yeast and fungi. the ag/sio2nc has brought many biomedical and agriculture applications (non-toxic to humans in minute concentrations). further study will be designed to elucidate the mode of action of ag/sio2nc as an antimicrobial agent. conflict of interest the authors declare that they have no conflict of interest. references agnihotri s, mukherji s, mukherji s (2013) immobilized silver nanoparticles enhance contact killing and show highest efficacy: elucidation of the mechanism of bactericidal action of silver. nanoscale 5: 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hollow nanoparticles. sci. rep. 6: 1-12. 11 microsoft word juristová nb.doc nova biotechnologica vii-i (2007) 107 synthesis and reactions of [1]benzofuro[3,2-c]pyridine nadežda juristová1, eleonóra štefanovová1, tatiana ďurčeková1, naďa prónayová2, anton gatial3, alžbeta krutošíková1 1department of chemistry, faculty of natural sciences, university of ss. cyril and methodius, sk-917 01 trnava, slovak republic e-mail: alzbeta.krutosikova@ucm.sk 2institute of analytical chemistry, department of nmr and ms spectroscopy, slovak university of technology, radlinského 9, sk-812 37 bratislava, slovak republic 3institute of physical chemistry and chemical physics, slovak university of technology, radlinského 9, sk-812 37 bratislava, slovak republic abstract: (e)-3-(1-benzofuran-2-yl)propenoic acid (i) was prepared from 1-benzofuran-2-carbaldehyde under the doebner’s conditions. the obtained acid was converted to the corresponding azide ii, which was cyclized by heating in diphenyl ether to [1]benzofuro[3,2-c]pyridin-1(2h)-one (iii). this compound was aromatized with phosphorus oxychloride to chloroderivative iv which was reduced with zinc and acetic acid to the title compound v. [1]benzofuro[3,2-c]pyridin-2-oxide (vi) was synthesized by reaction of v with 3chloroperoxybenzoic acid in dichloromethane. treatment vi with benzoyl chloride and potassium cyanide (reissert-henze reaction) was shown to produce the corresponding [1]benzofuro[3,2-c]pyridin-1carbonitrile (vii). the title compound was used for preparation of complex compounds viii, ix key words: [1]benzofuro[3,2-c]pyridine, n-oxide, 1-carbonitrile, 1h, 13c nmr and ir spectra, metalorganic compounds 1. introduction furopyridines are of chemical interest due to their similarity to quinoline, isoquinoline, and benzofuran, which are important ring systems present in many biologically active compounds. the antihypertensitive drug cicletanine is a furo[3,2c]pyridine derivative. the furopyridine skeleton from which this compound is derived is not associated with any known pharmacological classes (sherman, 1996). in the past one of us has been interested in studying the synthesis and reactivity of various furo[3,2-c]pyridines (bobošík et al., 1995; krutošíková et al., 1992, 1994, 1995; krutošíková and sleziak, 1996). the authors (bencková and krutošíková, 1995; 1999) were concentrated on transformations on the pyridine ring of some of this type of compounds. later on some furo[3,2-c]pyridines have been used for preparation cu(ii) and ni(ii) complexes (krutošíková et al., 2001). furo[3,2-c]pyridine and its 2-methyl-, 2,3-dimethyl and benzo[4,5] derivative were used for the first time as ligands to synthesize potentially new werner clathrates and their structural characterization, spectral and magnetic properties of isothiocyanate nickel(ii) complexes (miklovič et al., 2004, mojumdar et al., 2005). magneto structural correlations in heteroleptic furo[3,2-c]pyridineni(ii) complexes were 108 juristová, n. et al. published by the research group (baran et al., 2005). recently two papers dealing about the syntheses and crystal structures of tetra-μ-acetato-bis(1-benzofuro[3,2c]pyridinecopper(ii) and bis(1-benzofuro[3,2-c]pyridine-κn)dichlorocobalt(ii) were published (vrabel et al., 2007). in this paper, which continues our previous papers (bencková and krutošíková, 1999; krutošíková et al., 1992, 1994, 1995) we report the synthesis of [1]benzofuro[3,2-c]pyridine and its 2-oxide (scheme 1). o chα hβ c co2h o nh o o n o n cl ch2(co2h)2 et3n, clco2et o cho i ii iiiivv o n o nan3 2 2 2 vi o chα hβ c con3 2 pocl3 bu3n ph2o zn acoh scheme 1 3 4 5 6 7 3 4 5 6 73 4 5 6 3 4 56 7 6 7 3 4 5 6 7 8 9 8 99 8 9 111 1 8 7 4 5 3-clpba 2 2 3 2. experimental melting points were determined using kofler hot plate. all solvents were distilled and dried before use. all reagents were commercially available and were used without purification. elemental analyses were determined using an eager 300 at institute of inorganic chemistry, technology and materials stu in bratislava. ir spectra were taken on a ftir nicolet nexus 470 spectrophotometer using kbr technique (0.5 mg in 300 mg kbr) in region 4000 – 400 cm-1 at institute of physical chemistry and chemical physics, stu in bratislava. for interpretation of ir spectra following abbreviations are used: m = medium band (a value of transmittance: 36-50%) w = weak (a value of transmittance: over 50%), without marking are strong bands (a value of transmittance: 0-35%). 1h nmr spectra were measured in dmso-d6 using varian inova 600 (for 1h 599,782 mhz and for 13c 150.830 mhz) spectrometer at institute of analytical chemistry, department of nmr and ms spectroscopy, stu in bratislava. chemical shifts (δ-scale) are quoted in parts per million and following abbreviations are used: s = singlet; d = doublet; t = triplet; q = quartet; m = multiplet, coupling constants (j) are given in hz. 2.1 (2e)-3-(1-benzofuran-2-yl)propenoic acid (i) a mixture of 1-benzofuran-2-carbaldehyde (5.1 g; 35 mmol), malonic acid (3.7 g; 35 mmol), pyridine (39.3 cm3) and piperidine (17 drops) was heated on steam bath for 8 h. the reaction mixture was poured on ice, acidified with 0.5 m hydrochloric acid. the separate precipitate was filtered off and crystallized. yield: 11.74 g (88.9%); white crystals, m.p. 222-223 °c (ethanol). for c11h7n3o2 (mr = 188.18) wi (calc.): 70.21% c, 4.29% h; wi (found): 70.41% c, 4.26% h. nova biotechnologica vii-i (2007) 109 1h nmr spectrum: 12.6 ( bs co2h); 7.69 (d, 3j(4,5) = 7.8 hz, 4j(4,6) = 1.2 hz, h4); 7.59 (dd, 3j(7,6) = 8.1 hz, 4j(7,5) = 1.2 hz, h7); 7.57 (d, 3j(b,a) = 15.6 hz, hb); 7.39 (t, 3j(6,7) = 7.8 hz, 4j(6,4) = 1.2 hz, h6); 7.34 (s, h3); 7.28 (t, 3j(5,6) = 7.8 hz, 4j(5,7) = 1.2 hz, h5); 6.41 (d, 3j(a,b) = 15.6 hz, ha). 13c nmr spectrum: 167.1 (c=o); 154.9 (c7a); 152.1 (c2); 131.2 (cb); 128.1 (c3a); 126.7 (c6); 123.6 (c5); 122.2 (c4); 119.4 (ca); 111.7 (c3); 111.4(c7). ir spectrum: 1671; 1630; 1451; 1419; 1304; 1268; 1200; 1127; 1007w; 978w; 951; 882w; 834m; 753; 738; 664w; 568m; 456w. 2.2 (2e)-3-(1-benzofuran-2-yl)propenoyl azide (ii) propenoic acid i (3.76 g; 20 mmol) suspended in dry acetone (40 cm3) was cooled to -10 °c and triethylamine (3.2 cm3) in dry acetone (5 cm3) was added. then solution of ethyl chloroformate (2.4 cm3) in dry acetone (5 cm3) was added dropwise to the stirred reaction mixture at temperature lower than 0 °c. the reaction mixture was stirred for another 30 min at the same temperature. solution of sodium azide (2.0 g; 30.8 mmol) in water (10 cm3) was added at temperature below 0 °c. the mixture was stirred for an additional hour and allowed to warm to room temperature, poured onto crushed ice and precipitate was filtered off, washed with water and crystallized. yield: 4.07 g; (95.6%), m.p. 114-116 °c white crystals. for c11h7n3o2 (mr = 213.19) wi (calc.): 61.97% c, 3.31% h, 19.71% n; wi (found): 61.82% c, 3.27% h, 19.78% n. 1h nmr spectrum: 7.74 (d, 3j(b,a) = 15.5 hz, hβ); 7.73 (dd, 3j(4,5) = 8.2 hz, 4j(4,6) = 1.2 hz, h4); 7.61 (dd, 3j(7,6) = 8.2 hz, 4j(7,5) = 0.88 hz, h7); 7.50 (s, h3); 7.44 (t, 3j(6,5) = 7.2 hz, 4j(6,4) = 1.2 hz, h6); 7.30 (t, 3j(5,6) = 7.38 hz, 4j(5,7) = 0.88 hz, h5); 6.46 (d, 3j(a,b) = 15.5 hz, ha). 13c nmr spectrum: 170.9 (c=o); 155.2 (c7a); 151.5 (c2); 133.1 (cb); 127.9 (c3a); 127.4 (c6); 123.7 (c5); 122.5 (c4); 118.6 (ca); 114.2 (c3); 111.4 (c7). ir spectrum: 2150; 1677; 1619; 1544; 1471; 1448; 1348; 1330; 1272; 1169; 1127; 1096; 999; 951; 824; 788; 687; 630; 610m; 544m; 520m; 441m; 402m; 2.3 [1]benzofuro[3,2-c]pyridin-1(2h)-one (iii) azide ii (8.67 g; 41 mmol) dissolved in toluene (67 cm3) was added dropwise into diphenyl ether (35 cm3), and tributylamine (10.7 cm3) were at 180-200 °c for 45 min, while toluene was distilled out. then the reaction mixture was heated up 215 °c for 15 min. after cooling, diethyl ether was added the precipitate was filtered off and washed with diethyl ether. yield: 6.22 g (82.6%), m.p. 207-209 °c (ethanol) white crystals. for c11h7no2 (mr = 185.18) wi (calc.): 71.35% c, 3.81% h, 7.56% n; wi (found): 71.22% c, 3.78% h, 7.66% n. 1h nmr spectrum: 11.83 (bs, nh); 8.01 (dd, 3j(9,8) = 7.33 hz, 4j(9,7) = 1.76 hz, h9); 7.678 (dd, 3j(6,7) = 7.04 hz, 4j(6,8) = 1.76 hz, h6); 7.41 (t, 3j(7,8) = 7.33 hz, 4j(7,9) = 1.47 hz, h7); 7.407 (t, 3j(8,7) = 7.33 hz, 4j(8,6) = 1.47 hz, h8); 7.56 (d, 3j(3,4) = 7.34 hz, h3); 6.76 (d, 3j(4,3) = 7.34 hz, h4). 13c nmr spectrum: 162.5 (c4a); 159.5 (c1); 154.1 (c5a); 135.2 (c3); 125.7 (c7); 124.2 (c8); 123.6 (c9a); 120.8 (c9); 111.3 (c6); 110.0 (c9b); 94.4 (c4). 110 juristová, n. et al. ir spectrum: 1647; 1565; 1486; 1453; 1428; 1389; 1388m; 1258m; 1233; 1183; 1068; 1000m; 947m; 906m; 846m; 788; 760; 677m; 653m; 587; 543; 43. 2.4 1-chloro[1]benzofuro[3,2-c]pyridine (iv) a pyridone iii (4.5 g; 24 mmol) was refluxed in phosphorus oxychloride (8.6 cm3) for 4 h. pocl3 was removed at reduced pressure and the ice was added to the residue. the mixture was then made basic with diluted aqueous ammonia. the precipitate was filtered out, washed with water, dried and crystallized. yield: 4.71 g (91.2%), m.p. 65 67 °c (hexane) white crystals. for c11h6clno (mr = 203.62) wi (calc.): 64.88% c, 2.97% h, 6.88% n; wi (found): 64.73% c, 2.95% h, 6.79% n. 1h nmr spectrum: 8.44 (d, 3j(3,4) = 5.57 hz, h3); 8.16 (dd, 3j(9,8) = 7.8 hz, 4j(9,7) = 1.8 hz, h9); 7.798 (d, 3j(4,3) = 5.57 hz, h4); 7.782 (dd, 3j(6,7) = 8.3 hz, 4j(6,8) = 0.88 hz, h6); 7.64 (t, 3j(7,8) = 7.6 hz, 4j(7,9) = 1.8 hz, h7); 7.50 (t, 3j(8,7) = 7.6 hz, 4j(8,6) = 0.88 hz, h8). 13c nmr spectrum: 161.5 (c4a); 155.1 (c5a); 147.1 (c3); 143.6 (c1); 129.3 (c7); 124.5 (c8); 122.1 (c9); 119.7 (c9b); 118.8 (c9b); 112.0 (c6); 107.6 (c4). ir spectrum: 1589; 1561; 1457m; 1428; 1331m; 1294m; 1261m; 1233m; 1186; 1152m; 1016w; 995w; 947; 842m; 829; 755; 614m; 520w; 434w. 2.5 [1]benzofuro[3,2-c]pyridine (v) zinc powder (12.07 g; 185 mmol), was added to iv (9.0 g; 44 mmol) and acetic acid (15 cm3) and mixture was refluxed for 8 h, then filtered and the solvent was distilled off under reduced pressure. the residue was alkalized with diluted sodium hydroxide solution and extracted with chloroform. the solution was dried with sodium sulfate and the solvent was evaporated. yield: 4.65 g (62.5%), m.p. 74-76 °c (hexane) white crystals. for c11h7no (mr = 169.18) wi (calc.): 78.09% c, 4.17% h, 8.28% n; wi (found): 78.12% c, 4.01% h, 8.16% n. 1h nmr spectrum: 9.42 (d, 5j(1,4) = 0.88 hz, h1); 8.65 (d, 3j(3,4) = 5.8 hz, h3); 8.25 (dd, 3j(9,8) = 7.6 hz, 4j(9,7) = 1.2 hz, h9); 7.785 (dd, 3 j(6,7) = 8.2 hz, 5 j(6,9) = 0.88 hz, h6); 7.78 (dd, 3 j(4,3) = 5.8 hz, 5 j(4,1) = 0.88 hz, h4); 7.60 (t, 3 j(7,6) = 8.2 hz, 4 j(7,9) = 1.2 hz, h7); 7.49 (t, 3 j(8,7) = 7.6 hz, 4 j(8,6) = 0.88 hz, h8). 13c nmr spectrum: 160.4 (c4a); 155.7 (c5a); 147.6 (c3); 143.9 (c1); 128.6 (c7); 124.1 (c8); 121.5 (c9); 121.1 (c9b); 120.7 (c9a); 111.9 (c6); 107.5 (c4). ir spectrum: 3063-3037; 1590; 1577; 1481m; 1463; 1446; 1331m; 1293m; 1266m; 1243w; 1207; 1186; 1162; 1106m; 1009m; 995m; 862; 838; 823; 776; 751; 734; 595. 2.6 [1]benzofuro[3,2-c]pyridin-2-oxide (vi) a mixture of v (1.42 g; 8.4 mmol) and 3-chloroperoxybenzoic acid (70%, 3.69 g; 14.6 mmol) in dichloromethane (50 cm3) was stirred at room temperature for 4 h. the nova biotechnologica vii-i (2007) 111 reaction mixture was filtered and extracted with sodium carbonate (10%), and water. the organic layer was dried over sodium sulfate, filtered and solvent was evaporated and residue was crystallized. yield: 1.01 g, 65%., m.p. 205-206 °c (toluene). for c11h7no2 (mr = 185.18) wi (calc.): 71.35% c, 3.81% h, 7.56% n; wi (found): 71.42% c, 3.79% h, 7.38% n. 13c nmr spectrum: 9.21 (d, 4j(1,3) = 1.8 hz, h1); 8.32 (dd, 3j(3,4) = 7.1 hz, 4j(3,1) = 1.8 hz, h3); 8.20 (dd, 3j(9,8) = 7.6 hz, 4j(9,7) = 1.4 hz, h9); 7.82 (d, 3j(4,3) = 7.1 hz, h4); 7.76 (dd, 3j(6,7) = 8.2 hz, 4j(6,8) = 1.7 hz, h6); 7.64 (t, 3j(7,6) = 8.2 hz, 4j(7,9) = 1.4 hz, h7); 7.48 (t, 3j(8,9) = 7.6 hz, 4j(8,6) = 1.7 hz, h8). 13c nmr spectrum: 156.8 (c5a); 151.3 (c4a); 138.3 (c3); 132.6 (c1); 129.7 (c7); 124.2 (c6); 123.0 (c9b); 122.5 (c9); 120.2 (c9a); 112.2 (c8); 109.9 (c4). ir spectrum: 1661; 1470; 1440; 1308m; 1288; 1205; 1158; 1098; 1010m; 929m; 828; 769; 742; 596; 526; 425. 2.7 [1]benzofuro[3,2-c]pyridine-1-carbonitrile (vii) to solution of potassium cyanide (1.25 g, 19 mmol) in water (2 cm3) a solution of [1]benzofuro[3,2-c]pyridin-2-oxide (vi) (3.42 g, 1.85 mmol) in dichloromethane (10 cm3) was added and then dropwise a solution of benzoyl chloride (0.3 cm3, 2.15 mmol) in dichloromethane (10 cm3). after vigorous stirring at room temperature for 2 days, the organic layer of the reaction mixture was separated and aqueous layer was extracted with chloroform. after drying over magnesium sulfate, the combined organic layers were evaporated and residue was purified by column chromatography on silica gel (hexane-ethyl acetate 3:1). the obtained vii was crystallized. yield: 3.05g, (85%), m.p. 135-137 °c (hexane) 139-141 °c (bencková and krutošíková, 1999). for c12h6n2o (mr = 194.19) wi (calc.): 74.22% c, 3.11% h, 14.43% n; wi (found): 74.32% c, 3.18% h, 14.36% n. 13c nmr spectrum: 8.81 (d, 3j(3,4) = 5.57 hz, h3); 8.21 (d, 3j(9,8) = 7.63 hz, h9); 8.14 (d, 3j(4,3) = 5.57 hz, h4); 7.89 (d, 3j(6,7) = 8.5 hz, h6); 7.76 (t, 3j(7,6) = 7.92 hz, 3j(7,8) = 7.63 hz, h7); 7.62 ((t, 3j(8,7) = 7.63 hz, 3j(8,9) = 7.63 hz, h8). 13c nmr spectrum: 160.4 (c4a); 155.8 (c5a); 148.8 (c3); 130.9 (c7); 125.0 (c8); 124.9 (c9b); 124.2 (c1); 121.4 (c9); 118.4 (c9a); 116.2 (cn); 112.6 (c6); 111.4 (c4). ir spectrum: 3093; 2227m; 1627w; 1591; 1567; 1483w; 1458; 1422; 1336; 1295w; 1263; 1231; 1182; 1109; 1072w; 1015m; 1005; 944w; 841; 806; 784w; 748; 641w; 568w; 543m. 2.8 tetra-μ-acetato-bis[([1]benzofuro[3,2-c]pyridine)copper(ii)] (viii) to a cu(ch3co2)2.h2o (1.5 mmol) in ethanol (5 cm 3) was added the solution of the title compound (3.2 mmol) in ethanol (2 cm3). small blue-green crystals were 112 juristová, n. et al. collected after 2 d. these were filtered off, washed with ethanol and crystallized from tetrahydrofuran. for c30h26n2cu2o10 (mr = 701.63) wi (calc.): 51.35% c, 3.73% h, 3.99% n, 18.11% cu; wi (found): 51.43% c, 3.65% h, 3.99% n, 18.15% cu. ir spectrum: 3852; 3820; 3674; 3628; 3441; 3085; 3053; 2569; 2527; 1633; 1605; 1592; 1485; 1466; 1448; 1333; 1292; 1251; 1212; 1177; 1154; 1146; 1041; 1024; 878; 838; 821; 774; 758; 596; 574w; 562w; 523w. 2.9 bis([1]benzofuro[3,2-c]pyridine-κn)dichloridocobalt(ii) (ix) to a cocl2.6h2o (1 mmol) solution in ethanol (4 cm 3) was added the solution of v (3 mmol) in ethanol (4 cm3) at room temperature. small blue crystals were formed after 3 d, which were filtered off, washed with ethanol and crystallized from tetrahydrofuran. for c22h14cl2con2o2 (mr = 468.21) wi (calc.): 56.43% c, 3.01% h, 5.98% n, 12.58 co; wi (found): 56.67% c, 2.96% h, 5.96% n, 11.96 co. ir spectrum: 1626; 1596; 1484m; 1484; 1467; 1450; 1433; 1210m; 1187; 1165; 1018w; 872; 840m; 777; 757m; 681m; 629; 598w; 567w; 523w. 3. results and discussion (e)-3-(1-benzofuran-2-yl)propenoic acid (i) was prepared from 1-benzofuran-2carbaldehyde under the doebner’s conditions. the obtained acid i was converted to the corresponding azide ii, which was cyclized by heating in diphenyl ether to [1]benzofuro[3,2-c]pyridin-1(2h)-one (iii). this compound was aromatized with phosphorus oxychloride to chloroderivative iv which was reduced with zinc and acetic acid to the title compound v. [1]benzofuro[3,2-c]pyridin-2-oxide (vi) was synthesized by reaction of v with 3-chloroperoxybenzoic acid in dichloromethane. treatment vi with benzoyl chloride and potassium cyanide (reissert-henze reaction) was shown to produce the corresponding [1]benzofuro[3,2-c]pyridine-1-carbonitrile (vii). this transformation was easily verified by means of infrared spectra, loss of n-oxide band at 1205 cm-1 in the spectra of vii and appearance of cyano group absorption at 2227 cm-1. disappearance of the most downfield signal in the 1h nmr spectrum (at 9.21 ppm) of the starting compound vi also supported the structure of the compound vii. for the assignment of carbon signals in the synthesized compounds 2d-spectra,gcosy, ghsqcad and ghmbcad were used. 4. conclusions the title compound [1]benzofuro[3,2-c]pyridine (v) was prepared five step synthesis and was used for preparation of complex compounds. the structures of viii, ix were proved by x-ray analysis (figures 1,2). the structural data are presented in (vrabel, 2007). nova biotechnologica vii-i (2007) 113 fig. 1. the molecular structure of the complex compound viii (vrabel et al. 2007). fig. 2. the molecular structure of the complex compound ix (vrabel et al. 2007). acknowledgements: this work was supported by the grant agency of the ministry of education of the slovak republic vega (grant no. 1/3584/06). nmr experimental part of this work was facilitated by support of slovak national research and development program no. 2003sp200280203. references baran, p., boča, m., boča, r., krutošíková, a., miklovič, j., pelikán, j., titiš, j.: structural characterization, spectral and magnetic properties of isothiocyanate nickel(ii) complexes with furopyridine derivatives. polyhedron, 24, 2005, 1510-1516. 114 juristová, n. et al. bencková, m., krutošíková, a.: synthesis of pyrrolo[2´,3´:4,5]furo[3,2c]pyridines. monatsh. chem., 126, 1995, 753-758. bencková, m., krutošíková, a.: 5-aminofuro[3,2-c]pyridinium tosylates and substituted furo[3,2-c]pyridine-n-oxides: synthesis and reactions. collect. czech. chem. commun., 64, 1999, 539-547. bobošík, v., krutošíková, a., jordis, u.: synthesis and reactions of 2,3dimethyfuro[3,2-c]pyridines. monatsh. chem., 126, 1995, 747-752. krutošíková, a., dandárová, m., chylová, j., végh, d.: condensed on-heterocycles by the transformation of azidoacrylates. monatsh. chem., 123, 1992, 807-815. krutošíková, a., dandárová, m., alföldi, j.: substituted vinyl azides in the synthesis of condensed nitrogen heterocycles. chem. papers, 48, 1994, 268273. krutošíková, a., sleziak, r: synthesis of 2-arylfuro[3,2-c]pyridines and their derivatives. collect. czech. chem. commun., 61, 1996, 1627-1636. krutošíková, a., mitasová, b., jóna, e., bobošíková, m.: synthesis, thermal and spectral properties of cu(ii) and ni(ii) complexes with furopyridines or quinoline. chem. papers, 55, 2001, 290-293. miklovič, j., krutošíková, a., baran, p.: two furopyridine complexes of nickel(ii) isothiocyanate. acta cryst., c60, 2004, m227-m230. mojumdar, s.c., miklovič, j., krutošíková, a., valigura, d., stewart, j. m.: furopyridines and furopyridine-(ni(ii) complexes: synthesis, thermal and spectral characterization. j. therm. anal. cal., 81, 2005, 211-215. sherman, a.r.: bicyclic 5-6 systems: two heteroatoms 1:1. in: c.a. ramsden (ed.) comprehensive heterocyclic chemistry ii. pergamon press, oxford, 1996, 167-227. vrábel, v., švorc, ľ., juristová, n., miklovič, j., kožíšek, j.: tetra-μacetato-bis[(benzofuro[3,2-c]pyridine]copper(ii). acta cryst., e63, 2007, m2112m2113. vrábel, v., švorc, ľ., juristová, n., miklovič, j., kožíšek, j.: bis(1benzofuro[3,2-c]pyridine-κn)dichloridocobalt(ii). acta cryst., e63, 2007, m24272428. nova biotechnologica et chimica 13-1 (2014) 13 doi 10.2478/nbec-2014-0002 © university of ss. cyril and methodius in trnava interplay between bacteriophages and restriction-modification systems in enterococci peter pristas, anna vandzurova, peter javorsky institute of animal physiology, slovak academy of sciences, soltesovej 4-6, 040 01 kosice, slovakia, (pristas@saske.sk) abstract: the complete genomes of enterococcus faecalis bacteriophages were analyzed for tetranucleotide words avoidance. very similar tetranucleotide composition was found in all tested genomes with strong underrepresentation of palindromic gatc and ggcc words. this avoidance could be explained as a protection mechanism against host restriction-modification systems as a clear correlation was found between avoidance of palindromic words and the specificity of e. faecalis restriction and modification systems. no similar avoidance of tetranucleotide words was observed for non-palindromic words. a weak correlation was observed between avoidance of tetranucleotide palindromes in bacteriophage genomes and the possession of phage encoded dna methyltransferases confirming the interrelation between bacteriophage genomes composition and restriction and modification systems in enterococci. key words: enterococcus, bacteriophage, restriction modification systems, palindrome avoidance 1. introduction type ii restriction-modification systems entail a dna methyltransferase and an endonuclease of the same recognition sequence specificity. the endonuclease digests foreign dna that enters the cell, thereby protecting the bacteria from genetic subversion. the methylase modifies the cell's dna, thereby protecting it from similar digestion. it is generally accepted that restriction systems in bacteria primarily act to protect the organism from foreign dna, particularly from infection by bacteriophages (bickle and kruger, 1993). bacteriophages on other hand have evolved antirestriction mechanisms, encode for their own methyltransferases, and are frequently deficient in recognition sites for restriction endonucleases (samson et al., 2013). the aim of our study was to analyze the tetranucleotide composition of enterococcal bacteriophage genomes, to analyze the effect of phage encoded modification methyltransferases on avoidance of tetranucleotides, and to compare the frequency and variability of restriction endonucleases encoded by enterococci. enterococci are ubiquitous bacteria present in the environment, in the gastrointestinal tract of healthy animals and humans, and in foods, especially those of animal origin such as dairy products (giraffa, 2003). enterococci entry into milk and milk products through the water supply, equipment, and unsanitary and unhygienic conditions during production and handling. in milk products, they are used as probiotics resulting in positive effects on human digestibility. thanks to the efficient utilisation of organic acids, enterococci contribute to the development of unique sensory characteristics in fermented dairy products. in contrast to these positive roles, some enterococcal strains were suspected to have pathogenic properties for bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:56 utc 14 pristas, p. et al. humans (hunt, 1998). enterococcal bacteriophages with very effective bactericidal activity are potentially used as novel antibacterial agents to control enterococcal infections (deresinski, 2009), however in dairy industry the bacteriophage infections result in unacceptably low production of lactic acid and flavour compounds along with reduced proteolysis and led to the major losses in fermentation processes (mc grath et al., 2007). better understanding of bacteriophage genetics and biology could improve this dual role of enterococcal bacteriophages. we have used markov chain analysis to evaluate which nucleotide dna words are overor underrepresented in the genomes of e. faecalis bacteriophages. markov analysis seems to be the most widely used to evaluate palindrome distribution (panina et al., 2000). briefly, using this model it is possible to calculate how often a word should appear in a sequence on the basis of knowledge of the distribution of the word’s fragments. under the maximum applicable order of the markov model, the expected count of a particular tetranucleotide (k), e.g. gatc sequence, is defined as: ( ) ( ) ( ) ( )atatcgatgatc nnnk /×= (1) where n(gat), n(atc) and n(at) are the observed counts of oligonucleotides. similar formulas have been widely used (fuglsang, 2003). this number can then be compared with the actual count of the word in the sequence. however, the difference itself does not tell to what extent a word is overor underrepresented. for this purpose, the normalized statistic z is used, as proposed by schbath (1997), and used by others for similar purposes. z (contrast value) is positive for overrepresented words and negative for underrepresented words, and is calculated as: ( ) ( )[ ] ( )gatc gatcgatc v nkn z /− = (2) where n is number of nucleotides in analysed sequence and the variance v(gatc) is calculated as: ( ) ( ) ( ) ( )[ ] ( ) ( )[ ] ( )at gatatatcat gatcgatc n nnnn kv 2) −×− = (3) based on the normalized nature of z, the probability of random observation of |z| > 3.29 is <0.001. the data obtained indicate strong underrepresentation of palindromic tetranucleotides in e. faecalis bacteriophage sequences which could be probably explained as a protection mechanism against host restriction-modification systems. 2. materials and methods complete genome sequences of e. faecalis bacteriophages and e. faecalis genome (refseq accession number nc_004668) were taken from the refseq ncbi reference bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:56 utc nova biotechnologica et chimica 13-1 (2014) 15 sequence database available at http://www.ncbi.nlm.nih.gov/refseq/. the presence (marked as y in table 1) or absence (marked as n in table 1) of modification methyltransferase in the genomes of bacteriophages was taken from annotations available in refseq database. for the list of bacteriophage sequences used through the study see table 1. the frequency of restriction endonucleases in e. faecalis was taken from rebase database (roberts et al., 2010). table 1. the list and corresponding z score of bacteriophage sequences used in the study. tetranucleotide average z-score bacteriophage accession number genome size (bp) mtase a all palindrome the most underreprese nted word (score) reference phifl4a nc_013644 37856 y 0 -3.62 gatc (-9.55) yasmin et al. 2010 phifl3a nc_013648 39576 y 0 -3.39 gatc (-9.34) yasmin et al. 2010 phifl2a nc_013643 36270 y 0 -3.19 gatc (-9.52) yasmin et al. 2010 phifl1a nc_013646 38764 y 0 -3.14 gatc (-8.77) yasmin et al. 2010 phief24c nc_009904 142072 n 0 -5.85 gatc (-27.68) uchiyama et al. 2008 phief11 nc_013696 42822 y 0 -3.21 gatc (-9.09) stevens et al. 2011 efrm31 nc_015270 16945 n 0 -2.95 gatc (-8.85) fard et al. 2010 efap-1 nc_012419 21115 n 0 -2.77 gatc (-12.76) son et al. 2010 ef62phi nc_017732 30505 n 0 -2.82 cgcg (-6.07) brede et al. 2011 bc-611 nc_018086 53996 n 0 -5.55 gatc (-19.79) horiuchi et al. 2012 ay in the mtase column indicate the presence, n the absence of modification methyltransferase in the genome of bacteriophage tetranucleotide counts, z score values, and the pearson’s correlation coefficients were calculated using tetra software (teeling et al., 2004).the matrix of correlation coefficients was converted into distance matrix using dambe software version 5 and similarity dendrogram was constructed using neighbor-joining algorithm implemented in the software (xia, 2013). statistica® software package (statsoft, tulsa, oklahoma) was used to compare the z (contrast value) distribution between datasets using pearson’s correlation coefficient. 3. results and discussion bacteriophages, although simple in organization, are the most diverse life forms in the biosphere (ackermann and kropinski, 2007). bacteriophage life cycle completely relies on bacterial host. during the lytic cycle, bacteriophage infection redirects host metabolism towards the replication of the phage nucleic acid and assembly of new phage particles, which are then released upon cell death and lysis. the bacteriophages thus have an important role in bacterial evolution and have led to a great variety of defense mechanisms. bacteriophages, for their part, have developed bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:56 utc 16 pristas, p. et al. counter defense mechanisms to evade the bacterial defense mechanisms (samson et al., 2013). one of the best studied systems to protect bacteria form invading bacteriophages is the possession of restriction-modification systems. these systems entail a dna methyltransferase and an endonuclease of the same recognition sequence specificity. the endonuclease recognizes short, usually palindromic oligonucleotides and digests bacteriophage dna that enters the cell, thereby protecting the bacteria from genetic subversion. the methylase modifies the cell's dna, thereby protecting it from similar digestion (wilson, 1991). bacteriophages have developed antirestriction systems and are frequently deficient in oligonucleotides recognized by restriction endonucleases. bacteriophages changed their genomes by adopting point mutations which reduce the number of restriction sites (tock and dryden, 2005). using tetra software palindrome deficiency in genomes of all available enterococcal bacteriophages was analyzed. a very similar pattern of palindrome avoidance was observed in genomes of enterococcal bacteriophages as well as in e. faecalis genome. while the frequencies of all tetranucleotide words were found to be normally distributed around z value 0, frequencies of palindromes were found to be strongly underrepresented in both bacteriophage and e. faecalis genomes (fig. 1). for bacteriophages z values of tetranucleotide palindromes were in range from 7.51 to 27.68. average z value of tetranucleotide palindromes for all bacteriophages were in range from -2.77 to -12.09, indicating strong underrepresentation of tetranucleotide palindrome words in genomes of e. faecalis bacteriophages. the most underrepresented word in all but one tested bacteriophage genome was gatc word (average z value -12.09, see table 1). fig. 1. correlation of z values of enterococcus faecalis v583 complete genome (refseq accession number nc_004668) and genome of phief11 bacteriophage (refseq accession number nc_013696). correlation of tetranucleotide palindromes (part a) compared to all palindromes (part b) is shown. several authors showed that the lowest contrast values show palindromes which serve as a recognition sites of most frequently occurring endonucleases. rocha et al. (1998), reported that gatc and ggcc palindromes are between 6 the most underrepresented tetranucleotide palindromes in complete genome of bacillus subtilis. surprisingly, much higher degree of tetranucleotide palindrome avoidance was bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:56 utc nova biotechnologica et chimica 13-1 (2014) 17 observed in the genome of e. faecalis v583 compared to bacteriophage genomes (table 2). while average z score observed for bacteriophage genomes was -3.70 much lower z score (-30.55) was observed for e. faecalis v583 chromosome. however a correlation was observed between z values of bacteriophages and chromosome (pearson correlation coefficient r=0.68). gatc and ggcc tetranucleotide palindromes are among 4 the most underrepresented words in both genomes. clear correlation was observed between the word avoidance and the existence of restrictionmodification systems with given specificity (table 2). from the e. faecalis bacterium restriction endonucleases recognizing gatc, ggcc, ccgg, and cgcg tetranucleotide are described (vanat et al., 1993; radlinska et al., 2005; anonymous at rebase.neb.com, and our unpublished data) and these 4 tetranucleotide words are the most underrepresented in the genome of e. faecalis. these 4 words show the lowest z score compared to other words as well. significant underrepresentation of other tetranucleotide words was observed in the genome of e. faecalis v583 indicating that much higher number of restriction-modification systems than currently known has occurred in the genome of the e. faecalis, each of them leaving a trace of underrepresentation of a short palindrome. table 2. correlation between the frequency of tetranucleotide palindromes in the genomes of e. faecalis bacteriophages and e. faecalis v583 complete genome and frequency of restriction-modification systems in e. faecalis. a denotes lack of rms, + the presence of rms bacteriophages frequently employ additional strategies to overcome host restriction and modification systems e.g. site specific modification of the phage genome by bacteriophage encoded modification methyltransferases (samson et al., 2013). among e. faecalis bacteriophages modification methyltransferase was found in the genomes of 5 from 10 tested bacteriophages (table 1). based on degree of 4 bp palindromes avoidance the matrix of similarity coefficients between all pairs of bacteriophage genomes was constructed and the similarity tree was constructed indicating that bacteriophages encoding bacteriophages chromosome tetranucleotide z-score rank z-score rank known rmsa aatt -6.21 3 -29.54 11 agct -2.16 12 -34.78 7 acgt -3.66 8 -10.78 14 atat 1.03 15 -5.00 15 gatc -12.69 1 -66.48 1 + ggcc -4.81 4 -51.21 2 + gcgc -2.81 11 -3.93 16 gtac 1.09 16 -14.21 13 catg -6.27 2 -30.05 10 cgcg -4.79 5 -43.59 4 + ccgg -4.34 6 -44.99 3 + ctag -3.27 9 -15.07 12 tata -3.98 7 -36.53 6 tgca -1.82 12 -31.68 8 tcga -2.93 10 -31.25 9 + ttaa -1.54 14 -39.77 5 bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:56 utc 18 pristas, p. et al. methyltransferase (phifl4a, phifl3a, phifl2a, phifl1a, and phief11, shown in bold in fig. 2) have slightly different 4 bp palindrome composition. while average z score of palindrome avoidance in bacteriophages possessing modification methyltransferase was -3.31, z score in bacteriophages lacking modification methyltransferase was -3.99. this is probably due to protective effect of methyltransferases and decreased pressure on avoidance of tetranucleotide words. fig. 2. neighbor-joining tree showing the relatedness of palindrome avoidance in bacteriophages possessing modification methyltransferase gene (shown in bold) or not. the bar indicates distance level 0.05. 4. conclusions strong underrepresentation of palindromic tetranucleotide words was observed in genomes of enterococcus faecalis bacteriophages and host bacterium. the most underrepresented are gatc and ggcc words. this avoidance could be explained as a protection mechanism against host restriction-modification systems as a clear correlation was found between avoidance of palindromic words and the specificity of e. faecalis restriction-modification systems. no similar avoidance of tetranucleotide words was observed for non-palindromic words. a weak correlation was observed between avoidance of tetranucleotide palindromes in bacteriophage genomes and the possession of phage encoded dna methyltransferases confirming the interrelation between bacteriophage genomes composition and restriction-modification systems in enterococci. acknowledgments: the work was financially supported by the european regional development fund project 26220220065. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:56 utc nova biotechnologica et chimica 13-1 (2014) 19 references ackermann, h.w., kropinski, a.m.: curated list of prokaryote viruses with fully sequenced 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30, 2013, 1720-1728. yasmin, a., kenny, j. g., shankar, j., darby, a.c., hall, n., edwards, c., horsburgh, m. j.: comparative genomics and transduction potential of enterococcus faecalis temperate bacteriophages. j. bacteriol., 192, 2010, 1122-1130. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 15:56 utc nova biotechnol chim (2022) 21(1): e1320 doi: 10.36547/nbc.1320 1 nova biotechnologica et chimica genetic diversity and phylogenetic analyses of vitex agnus-castus l. populations using issr-pcr and chloroplast dna trnl intron and trnl-f sequences emre sevindik faculty of agriculture, department of agricultural biotechnology, aydın adnan menderes university, cakmar, turkey  corresponding author: ph.d.-emre@hotmail.com article info article history: received: 12th december 2021 accepted: 2nd march 2022 keywords: issr-pcr trnl intron trnl-f phylogenetic vitex agnus-castus abstract in this study, genetic diversity and phylogenetic analysis of some vitex agnus-castus l. populations were conducted based on issr-pcr and chloroplast dna trnl intron, and trnl-f sequence analyses. vitex agnus-castus populations were detected in aydın province, turkey. fresh leaf samples from the populations were collected and brought to the laboratory for genomic dna isolation. 15 issr primers were used to determine the genetic diversity ofe vitex agnus-castus populations. a total of 138 bands were obtained in issr analysis, 85 of which were polymorphic and 53 were monomorphic. polymorphism rate was determined as 61.59 %. trnc, trnd, trne, and trnf primers were used for pcr amplification of the chloroplast trnl intron and trnl-f region. a total of 138 bands were obtained by issr analysis. for trnl intron analyses, nucleotide lengths of 13 populations were between 508 and 516. the average nucleotide composition consisted of 38.5 % t, 18.3 % c, 27.5 % a and 15.7 % g. in trnl-f assays, the nucleotide lengths of the 13 populations ranged from 330 to 353. the average nucleotide composition consisted of 29.4 % t, 18.1 % c, 32.9 % a and 19.6 % g. the results of the phylogenetic trees constructed using some trnl intron and trnl-f sequences of vitex doniana, vitex trifolia, vitex triflora, vitex turczaninowii, vitex queenslandica, vitex axillariflora, vitex rotundifolia and vitex negundo species obtained from ncbi were compared. as a result of the study, polymorphisms were obtained at a rate of 61.59% from the issr analysis. in addition, the phylogenetic relationship between chloroplast trnl intron and trnl-f sequences of vitex agnus-castus populations along with the other species was revealed. introduction medical and aromatic plants have a long history of being used globally for medicinal purposes and have traditionally been an important component of health services throughout human history due to their health benefits (eryigit et al. 2015; chaachouay et al. 2019). the vitex genus includes about 250 species and many of these have important medicinal effects (yao et al. 2016). vitex agnus-castus l., known as chasteberry, belongs to the lamiaceae family (previously included in the verbenaceae family), and it is a 1 – 3 m long highly branched small tree. its trunk is covered with short, dense, soft and grey hairs. it is a deciduous shrub native to europe and central asia (stojković et al. 2011; hürkul and köroğlu 2018; souto et al. 2020; ilhan 2021). this plant is mailto:ph.d.-emre@hotmail.com nova biotechnol chim (2022) 21(1): e1320 2 naturally found in many cities throughout turkey, including amasya, antalya, bursa, muğla, trabzon and çanakkale (yilar et al. 2016). vitex agnuscastus, used in conventional medicine, has a long tradition in folk medicine, and its use dates back to 2,500 years ago (sorensen and katsiotis 1999; lataoui et al. 2014; uçak koç et al. 2017). it is widely used in anatolian folk medicine as diuretics, appetizers, antifungals, antispasmodics, for preterm labor and for pain relief (ilhan 2021). its fruits, flowers and leaves have been reported to contain flavonoids, tannins, iridoids and diterpenoids (sağlam et al. 2007; sarikurkcu et al. 2009). v. agnus-castus fruits have been used as a flavor and spice component in meals, as a hormone-like remedy for menstrual problems and a mild sedative and digestive tool in iranian traditional folk medicine (ghannadi et al. 2012). the aromatic leaves are used as a spice (stojković et al. 2011; mari et al. 2015). genetic diversity is a prerequisite for the short and long-term survival of plant species in their natural environment (verma et al. 2017). morphological, biochemical, and dna markers are used to determine the genetic diversity of plants (sevindik et al. 2020). dna-based molecular markers offer many advantages in determining genetic diversity. among the polymerase chain reaction (pcr) based marker techniques, the issr technique is one of the simplest and most widely used markers. it is also a marker system utilized in the determination of genetic relationships and linkage mapping (alansi et al. 2016; atasagun et. al. 2018; güngör et al. 2020). chloroplast (cp) is an important organelle for green plants as it is the place where photosynthesis, carbon fixation and pigment synthesis take place. the cp is an independent genome (cp genome) with a preserved circular structure and a low molecular weight (zhou et al. 2019; munyao et al. 2020; zhu et al. 2021). chloroplast dna (cpdna), which is inherited by the female in most angiosperm plants, is generally accepted as a single non-recombinant inheritance unit and is widely used to reveal plant phylogenies in interspecies studies (taberlet et al. 1991; gielly and taberlet 1994; dizkirici et al. 2019; sun et.al. 2019). non-coding regions of the chloroplast genome are used in molecular systematic and plant population genetic studies (kalmer and tekpınar 2017). within this study the chloroplast regions with both variable and highly conserved primer sequences were used. the first of these regions is the trnluaa intron; and the second is the trnl(uaa)f(gaa) intergenic spacer (igs). noncoding cpdna trnl-f is located between trnl (uaa) 3' exon and trnf (gaa) gene. in addition, it is more variable towards the coding regions, and some studies have revealed that it shows higher variations and more frequent mutations than the coding regions (taberlet et al. 1991; hartana 2010). the trnl intron is the first group i intron identified in chloroplast dna and is also the first intron identified to cut a trna gene (bakker et al. 2000). in this study, we performed a genetic diversity analysis using issr and cpdna trnl intron and trnl-f region markers for some vitex agnus-castus populations grown in the aydın region of turkey. experimental plant materials, genomic dna isolation and pcr leaf samples belonging to the vitex agnus-castus populations to be used in this study were collected from the center, koçarlı, çine, germencik, i̇ncirliova, and köşk districts of aydın province (fig. 1). fig. 1. location of collecting places in the aydın/turkey (https://www.google.com/maps). leaf samples of the collected vitex agnus-castus plant were brought to the laboratory and prepared for genomic dna isolation. a commercial kit (genemark) was used for the genomic dna isolation from the plant specimens. the obtained gdna samples were stored at -20 °c. the primers, pcr mix and protocol used for the amplification of https://www.google.com/maps nova biotechnol chim (2022) 21(1): e1320 3 issr-pcr, cpdna trnl intron and trnl-f regions are given in table 1 and table 2. table 1. primers used in the issr-pcr reactions, pcr protocols and their tm degrees. issr primers dna sequences (5’-3’) tm [oc] pcr amplification (35 cycle) amplification ubc-831 5’-ctctctctctctctctt-3’ 50 °c 94 °c/1min 94 °c/1min 48-55 °c/1min 72 °c/1 min 72 °c/10min + ubc-830 5’-tgtgtgtgtgtgtgtgg-3’ 52 °c + ubc-807 5'-agagagagagagagagt-3' 50 °c + ubc-808 5’-agagagagagagagagc-3’ 52 °c + ubc-836 5'-agagagagagagagagya-3’ 52 °c + ubc-856 5'–acacacacacacacacya-3’ 52 °c + ubc-853 5'tctctctctctctctcrt-3' 52 °c + ubc-892 5’tagatctgatatctgaat-3’ 52 °c ubc-810 5' -gagagagagagagagat-3' 50 °c + ubc-826 5’-acacacacacacacacc-3’ 52 °c + ubc-811 -gagagagagagagagac-3’ 53 °c + ubc-834 5’-agagagagagagagayt-3’ 52 °c + ubc-873 5’-gacagacagacagaca-3’ 48 °c + ubc-855 5’-acacacacacacacac 52 °c + ubc-880 5’-ggagaggagaggaga-3’ 55 °c + table 2. trnl intron and trnl-f primers used in this study with their designers and pcr protocols. primer name 5’ to 3’ primer sequence pcr amplification (35 cycle) based on (the source publication) forward trnc 5’-cgaaatcggtagacgctacg-3’ 94 °c/4min. 94 °c/1min 50 °c/1min. 72 °c/1 min. 72 °c/10min. taberlet et al. 1991 reverse trnd 5’-ggggatagagggacttgaac-3’ taberlet et al. 1991 forward trnle 5’-ggttcaagtccctctatccc-3’ taberlet et al. 1991 reverse trnff 5’-atttgaactggtgacacgag-3’ taberlet et al. 1991 1 % agarose gel 1x tbe buffer was used for electrophoresis of pcr products. 5 µl of the reaction mixture in pcr tubes was added to 1 µl loading buffer (loading dye solution) and mixed, and 6 µl of this mixture was placed in the wells of the gel. after loading 3 kb dna marker into the first well, the device was subjected to electrophoresis at 100 v for 90 min. then, the dna bands were imaged under uv light and their photos were taken (fig. 2 – 4). fig. 2. gel image of issr-pcr bands amplified with ubc811 primer. fig. 3. gel image of pcr bands amplified with cpdna trnl intron. fig. 4. gel image of pcr bands amplified with cpdna trnlf region. issr-pcr analyses nova biotechnol chim (2022) 21(1): e1320 2 after the pcr analyses, dna bands were scored as follows: “1” was given if there was dna and “0” was given if there was no dna in the bands. a “?” was given for missing data. using bands, the genetic relationships of vitex agnus-castus populations used in the study were analysed using the paup 4.0b10 (swofford 2001) program. cpdna trnl intron and trnl-f sequences service procurement from biotechnology company triogen (istanbul, turkey) was obtained for pcr reactions and purification. to ensure healthy analyses, it was necessary to visually check the accuracy of dna sequences one by one. to this end, professional computer programs bioedit (hall 1999) and finch tv, which are frequently used in molecular systematic studies worldwide, were utilized. a maximum likelihood phylogenetic tree was constructed using the mega 6.0 (tamura et al. 2013) to extract phylogenetic relationships among the sequenced vitex agnus-castus populations. to evaluate the degree of support for given clades, a bootstrap analysis (1,000 replicates) was applied (felsenstein 1985). in addition, the genetic distance matrix between populations was also performed using the same software. results and discussion in recent years, some pcr-based molecular markers have been developed and tested in genetic studies of various organisms (poyraz et al. 2016). in previous studies, genetic diversity, phylogenetic and molecular analyses of vitex species have been conducted using rapd (sevindik et al. 2019), issr (gıachıno and avcı 2017; saedyani et al. 2020), rps14 gene (ayaz et al. 2020; malik et al. 2021), nrits dna, chloroplast ndhf, trnh-psba, trng-trns sequences (bramley et al. 2009; sun et al. 2019), chloroplast rbcl and ndhf sequences (wagstaff et al. 1998), and chloroplast matk and psba-trnh intergenic spacer (phoolcharoen and sukrong 2013). issr analysis in recent years, pcr-based dna marker systems such as aflp, rflp, rapd, ssr and issr have been common for investigating the genetic makeup of populations, genetic characterization, genetic diversity, divergence and phylogenetic studies (li and ge 2001; gajera et al. 2010; chen et al. 2017; hocaoglu-ozyigit et al. 2020). issr markers have been proposed as a new source of genetic markers that are inherited in mendelian fashion and are scored as dominant markers (paul et al. 2020). these markers have the role of analyzing genetic diversity through the classification of varieties (kiani and siahchehreh 2018). in issr analysis 15 primers were used of which 14 yielded positive results while 1 primer did not (table 1). a total of 138 bands were obtained in issr analysis, 85 of which were polymorphic and 53 were monomorphic. polymorphism rate was determined as 61.59 %. the upgma tree generated based on the issr dataset consisted of two clades (fig. 5). fig. 5. the upgma tree generated using issr data. clade 1 was divided into 2 subclades. subclade a consisted of only the çine purple flowered population. çine purple flowered population was found together with koçarlı white flowered, çakmar white flowered, germencik purple flowered and erbeyli white flowered populations in rapd analysis (sevindik et al. 2019). in the subclade b, çine white flower, çine pink flower, çakmar pink flowered, aydın purple flowered and aydın white flowered appeared in the same group. according to sevindik et al. (2019), these populations were found together according to the rapd results. in subclade b, çakmar purple flowered, germencik purple flowered, erbeyli white flowered, çakmar white flowered and i̇ncirliova purple flowered populations emerged together. according to sevindik et al. 4 nova biotechnol chim (2022) 21(1): e1320 3 (2019), germencik purple flowered, çakmar white flowered and erbeyli white flowered were found together, while i̇ncirlova purple flowered and çakmar purple flowered populations detected in separate groups. clade 2 consisted of köşk purple flower and koçarlı white flower populations. according to sevindik et al. (2019), both populations emerged in different groups. according to paup analysis, the closest genetic distances were between germencik purple flowered and erbeyli white flowered populations with a value of 0.10145; and the greatest genetic distance was between çine purple flowered and koçarlı white flowered populations with a value of 0.36957 (table 3). giachino and avci (2017) used 6 of 21 issr primers for vitex agnus-castus populations collected from various parts of the yunt mountain of manisa. the discrimination power of issr primers was evaluated by calculating various marker parameters such as percent polymorphism, polymorphism information content (pic), resolving power (rp), and marker index (mi). in the study, 31 (65.95 %) of a total of 47 useable bands were found to be polymorphic. the polymorphic band ratios of the primers varied from 25 % to 85.7 %. polymorphism information content (pic) values of 6 primers ranged from 0.22 to 0.35, and the mean pic value was calculated as 0.30. the resolution power (rp) values ranged between 0.5 and 3.25, and the marker index (mi) ranged between 0.11 and 1.72. saedyani et al. (2019) determined genetic diversity for 19 vitex agnus-castus genotypes using 13 issr primers. in their study, 74 bands were obtained and the polymorphism rate was 95% on average. they determined the genetic distance of the genotypes between 0.195 and 0.593 using the dice coefficient. cpdna trnl intron and trnl-f sequence analysis phylogenetic analyses of molecular sequences are part of many molecular and phylogenetic biology studies (anisimova et al. 2013). the cpdna trnlf region is located in the large single-copy region of the chloroplast genome and is widely used for phylogenetic analyses (hocaoglu-ozyigit et al. 2020). for the cpdna trnl intron, the base lengths of vitex agnus-castus populations ranged from 508 to 516. the genetic distance between populations was between 0.000 and 0.002 (table 4). the mean nucleotide ratio for the trnl intron was 38.5 % t, 18.3 % c, 27.5 % a, and 15.7 % g. using the mega 6.0 program, tajma's neutrality test (tajima 1989) was calculated based on cpdna trnl intron sequences of vitex agnus-castus populations. numbers of sequences (m) yielded one segregation site (s) revealing very low nucleotide diversity (π) of 0.001422 (table 5). the maximum likelihood phylogenetic tree constructed using 13 populations consisted of two large groups (fig. 6). the first clade is divided into two subgroups. subclade a consisted of i̇ncirliova purple flowered, koçarlı white flowered, germencik purple flowered, çine purple flowered, çakmar white flowered and çakmar purple flowered, and this group was supported with a bootstrap value of 55 % (fig. 6). in the study of sevindik et al. (2019), çakmar purple flowered and i̇ncirliova purple flowered populations were found in a separate group, while koçarlı white flowered, germencik purple flowered, çine purple flowered and çakmar white flowered populations were found in the same group. subclade b consisted of çakmar pink flowered, çine pink flowered, erbeyli white flowered and köşk purple flowered, and this group was supported with a 60 % bootstrap value (fig. 6). sevindik et al. (2019) found erbeyli white flowered and köşk purple flowered populations in separate groups, while çakmar pink flowered and çine pink flowered populations in the same group. clade 2 consisted of aydın white flowered, aydın purple flowered and çine white flowered populations. within this group, aydın white flowered and aydın purple flowered populations were monophyletic with a bootstrap value of 63 % (fig. 6). 5 nova biotechnol chim (2022) 21(1): e1320 3 table 3. pairwise genetic distance matrix obtained from pcr with issr primers. populations 1 2 3 4 5 6 7 8 9 10 11 12 13 çine purple flower 0.19565 0.23915 0.22464 0.20455 0.24638 0.27536 0.30435 0.26087 0.26812 0.26812 0.31159 0.36957 çine white flower 27 0.17391 0.15952 0.13636 0.23913 0.22464 0.21014 0.18116 0.18841 0.20290 0.26087 0.33333 çine pink flower 33 24 0.13043 0.15152 0.15217 0.16667 0.19565 0.19565 0.18841 0.20290 0.27536 0.31884 çakmar pink flower 31 22 18 0.12879 0.13768 0.18116 0.23913 0.21014 0.20290 0.20290 0.27536 0.36232 aydın purple flower 27 18 20 17 0.15152 0.13636 0.20455 0.19697 0.19637 0.18939 0.28788 0.29545 aydın white flower 34 33 21 19 20 0.17391 0.27536 0.24638 0.22464 0.23913 0.32609 0.35507 çakmar purple flower 38 31 23 25 18 24 0.17391 0.17391 0.12319 0.13768 0.25362 0.25362 çakmar white flower 42 29 27 33 27 38 24 0.11594 0.13768 0.13768 0.19565 0.29710 i̇ncirliova purple flower 36 25 27 29 26 34 24 16 0.13768 0.13768 0.19565 0.32609 germencik purple flower 37 26 26 28 26 31 17 19 19 0.10145 0.21739 0.26087 erbeyli white flower 37 28 28 28 25 33 19 19 19 14 0.15942 0.23188 köşk purple flower 43 36 38 38 38 45 35 27 27 30 22 0.20290 koçarlı white flower 51 46 44 50 39 49 35 41 45 36 32 28 6 nova biotechnol chim (2022) 21(1): e1320 2 table 4. pairwise genetic distance matrix obtained from cpdna trnl intron sequences. populations 1 2 3 4 5 6 7 8 9 10 11 12 13 aydın purple flower aydın white flower 0.000 cakmar pink flower 0.002 0.002 cakmar purple flower 0.002 0.002 0.002 cakmar white flower 0.002 0.002 0.002 0.000 cine pink flower 0.002 0.002 0.000 0.002 0.002 cine purple flower 0.002 0.002 0.002 0.000 0.000 0.002 cine white flower 0.002 0.002 0.002 0.002 0.002 0.002 0.002 erbeyli white flower 0.002 0.002 0.000 0.002 0.002 0.000 0.002 0.002 germencik purple flower 0.002 0.002 0.002 0.000 0.000 0.002 0.000 0.002 0.002 incirliova purple flower 0.002 0.002 0.002 0.000 0.000 0.002 0.000 0.002 0.002 0.000 kocarlı white flower 0.002 0.002 0.002 0.000 0.000 0.002 0.000 0.002 0.002 0.000 0.000 kösk purple flower 0.002 0.002 0.000 0.002 0.002 0.000 0.002 0.002 0.000 0.002 0.002 0.002 table 5. tajima’s neutrality test values based on cpdna trnl intron of date vitex agnus-castus populations. no. of sequences “m” no. of segregating sites “s” ps=s/n θ = ps/a1 nucleotide diversity ‘’ π ‘’ tajima test statistic ‘’d’’ 13 1 0.001980 0.000638 0.001422 2.700233 7 nova biotechnol chim (2022) 21(1): e1320 3 fig. 6. the maximum likelihood tree generated using cpdna trnl intron sequences. according to sevindik et al. (2019), these three populations were in the same group. there are both similarities and differences between the upgma dendrogram generated by rapd analysis and the phylogenetic trees constructed with trnl intron sequences. additionally, vitex doniana (mk187249.1), vitex trifolia (aj505539.1), vitex triflora (mk797715.1), vitex turczaninowii (mg836415.1), vitex queenslandica (mg836414.1), vitex axillariflora (mg836413.1), vitex rotundifolia (ab817427.1; ab817638.1; ab817574.1) and vitex negundo (dq304786.1; dq304787.1) species were added to the analyses after obtaining their trnl intron sequences from ncbi. a maximum likelihood phylogenetic tree was generated and the relationship of vitex agnuscastus populations with other species was revealed. the phylogenetic tree consists of 2 clades (fig. 7). the first clade consists of vitex agnus-castus populations, vitex axillariflora, vitex trifolia, vitex rotundifolia and vitex negundo species formed and is supported by a bootstrap value of 95 %. clade 2 is divided into two subclades. subclade a, consists of vitex triflora and vitex doniana species and is supported by a bootstrap value of 97 %, and subclade b, consists of vitex turczaninowii vitex queenslandica species and is supported by a 75 % bootstrap value (fig. 7). fig. 7. the maximum likelihood tree generated using cpdna trnl intron sequences and other species sequences retrieved from ncbi (bootstrap values greater than 50 % are given above branches). for the cpdna trnl-f region, the base lengths of vitex agnus-castus populations ranged from 330 to 353. the genetic distance matrix between populations turned out to be 0.000 (table 6). 8 nova biotechnol chim (2022) 21(1): e1320 3 table 6. pairwise genetic distance matrix obtained from cpdna trnl-f sequences. populations 1 2 3 4 5 6 7 8 9 10 11 12 13 aydın purple flower aydın white flower 0.000 cakmar pink flower 0.000 0.000 cakmar purple flower 0.000 0.000 0.000 cakmar white flower 0.000 0.000 0.000 0.000 cine pink flower 0.000 0.000 0.000 0.000 0.000 cine purple flower 0.000 0.000 0.000 0.000 0.000 0.000 cine white flower 0.000 0.000 0.000 0.000 0.000 0.000 0.000 erbeyli white flower 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 germencik purple flower 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 incirliova purple flower 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 kocarlı white flower 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 kösk purple flower 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 9 nova biotechnol chim (2022) 21(1): e1320 3 the mean nucleotide ratio for the trnl-f region was 29.4 % t, 18.1 % c, 32.9 % a, and 19.6 % g. using the mega 6.0 program, tajma's neutrality test (tajima 1989) was calculated based on cpdna trnl-f sequences of vitex agnus-castus populations. numbers of sequences (m) gave one segregation site (s) revealing very low nucleotide diversity (π) of 0.000000 (table 7). table 7. tajima’s neutrality test values based on cpdna trnl –f of date vitex agnus-castus populations. no. of sequences “m” no. of segregating sites “s” ps=s/n θ = ps/a1 nucleotide diversity ‘’ π ‘’ tajima test statistic ‘’d’’ 13 0 0.000000 0.00000e+000 0.000000 n/c the maximum likelihood tree constructed using trnl-f sequences consists of two clades (fig. 8). clade 1 is divided into 3 subclades in itself. subclade a consists aydın purple flowered, aydın white flowered, çakmar pink flowered, çakmar purple flowered, çine pink flowered and çine purple flowered populations. fig. 8. the maximum likelihood tree generated using cpdna trnl-f sequences. sevindik et al. (2019) detected the çine purple flowered population in a different group, while all other populations were determined in the same group. in subclade b, erbeyli white flowered and köşk purple flowered populations were sister groups, while i̇ncirliova purple flowered populations were close to these two populations. sevindik et al. (2019) identified three populations in different groups. subclade c consists of only the germencik purple flowered population. clade 2 consisted of çine white flowered and koçarlı white flowered populations, which was supported by a bootstrap value of 99 %. according to sevindik et al. (2019), these two populations were included in separate groups. in this study, a maximum likelihood phylogenetic tree was generated using trnl-f sequences of vitex trifolia (aj505539.1), vitex turczaninowii (mg836415.1), vitex queenslandica (mg836414.1) and vitex axillariflora (mg836413.1) from ncbi. the relationship of vitex agnus castus populations with other species was revealed. the phylogenetic tree consists of 2 clades (fig. 9). the first clade consists of vitex agnus castus populations and vitex trifolia species, and this group has a bootstrap value of 94 %. clade 2 consists of vitex turczaninowii, vitex queenslandica and vitex axillariflora species. in trnl intron analysis, vitex agnus-castus populations coexisted with vitex axillariflora and vitex trifolia species. in addition, in trnl-f analysis, vitex turczaninowii, vitex queenslandica and vitex axillariflora were found in one group. vitex axillariflora and vitex trifolia species were found together with vitex agnus-castus populations, and vitex turczaninowii and vitex queenslandica species were found in a separate group in trnl intron analysis. malik et al. (2021) determined the phylogenetic relationship of some species belonging to the lamiaceae family with the chloroplast rps14 gene. vitex agnus-castus and vitex trifolia species were found in the same group in the study. in our trnl intron and trnl-f sequence studies, vitex agnuscastus and vitex trifolia were found in the same group (fig. 7 and fig. 9). ayaz et al. (2020) performed phylogenetic analysis of some species belonging to lamiaceae in pakistan using the rps14 gene. in their study, vitex agnus-castus var pseudonegundo and vitex negundo species were found in the same group. in the ml tree constructed using trnl intron sequences and sequences taken from 10 nova biotechnol chim (2022) 21(1): e1320 2 ncbi, the vitex agnus-castus populations were in the same clade with vitex axillariflora and vitex negundo. wagstaff et al. (1998) used chloroplast rbcl and ndhf sequences to reveal the phylogenetic relationships of some lamiaceae taxa. vitex agnus-castus species formed a sister group with petitia domingensis species in the strict consensus tree of rbcl and ndhf sequences. fig. 9. the maximum likelihood tree generated using cpdna trnl-f sequences and other species sequences retrieved from ncbi (bootstrap values greater than 50 % are given above branches). conclusion as a result of the study, approximately 61.59 % polymorphism were detected among vitex agnuscastus populations based on issr analyzes. in general, the results of this research aiming to analyze the genetic diversity and phylogenetic analysis of vitex agnus-castus populations through issr, cpdna trnl intron and trnl-f sequence comparisons will be used to determine the phylogenetic relationship between vitex agnuscastus species and other species. acknowledgments this research was supported by the aydın adnan menderes university (project 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wang et al. 2020). the core of the vitamin b12 consists of a tetrapyrrolic corrin ring with a central cobalt atom, grouped with four nitrogen’s, one nucleotide base group and one upper ligand. the recommended intake of the vitamin b12 for healthy adults is 2.4 μg/day. (mohammed et al. 2014a). vitamin b12 plays a significant role in the normal functioning of the nervous system, formation of blood, dna synthesis and regulation, fatty acid synthesis and energy production. the deficiency of the vitamin b12 leads to complications such as pernicious anaemia, neurological dysfunctions such as inhibition of the physiological formation of the myelin sheath, altering correct nerve transmission (mohammed et al. 2014b). plants, fungi, prokaryotes, and animals, including humans cannot synthesis vitamin b12 while synthesis is restricted to few classes of bacteria and archaea. four main types of the vitamin b12 are cyanocobalamin (cn-cbl), methylcobalamin (mecbl), hydroxocobalamin (oh-cbl), and deoxyadenosylcobalamine (ado-cbl). the cobalamins have different bioand photochemistries. the predominant forms of vitamin b12 are me-cbl and ado-cbl and they are actively used as cofactors for enzymes methionine synthase and mailto:projectsagnlabs@gmail.com nova biotechnol chim (2023) 22(1): e1339 2 methylmalonyl coa mutase, while oh-cbl and cn-cbl are not used directly instead they are first converted into an active form of b12. all forms of cobalamins are light sensitive, with me-cbl and ado-cbl identified as extremely labile, photodegrading into oh-cbl in a matter of seconds after light exposure. all forms of cobalamin are converted to cn-cbl to use for pharmacological and commercial purposes, because it is the most stable form of the vitamin b12 in the presence of light (heal et al. 2014; mohammed et al. 2014b). when the consumption of animal foods is very low or absent and scarce presence in plant foods, an adherent importance to the molecule is created, making it essential, either through supplements or fortified foods. this deficiency is common among vegetarians. hence, the production of the vitamin b12 has received a great attention due to increasing global requirements. production of cobalamin relies solely on microbes since chemical methods remain economically not feasible due to the technical complexity of the synthetic process. the natural process of the vitamin b12 synthesis consists of approximately 30 enzymes mediated steps proceeding either through aerobically evident in pseudomonas denitrificans, or anaerobically as witnessed in bacillus megaterium, propionibacterium shermanii, salmonella typhimurium, and lactobacillus reuteri (mohammed et al. 2014a). lactobacillus reuteri is a gram-positive, heterofermentative lactic acid bacterium, prevalent throughout the gastrointestinal tract of humans and other animals (santos et al. 2011; walter et al. 2011). lactobacillus reuteri is known to has probiotic properties (taranto et al. 2003) and a functionally active b12 biosynthetic gene cluster (santos et al. 2009). the bacteria were also able to secrete reuterin, a broad-spectrum antimicrobial agent produced during anaerobic sugar-glycerol cofermentation (talarico et al. 1988; talarico and dobrogosz 1989). whey, a by-product of the dairy industry is rich in lactose, proteins, and minerals. lactose and protein content vary from 39 to 45 g.l−1 and 9 – 14 g.l−1 respectively. about 0.7 % (w/v) of the total solid content of whey consists of whey proteins. the notable whey proteins are β-lactoglobulin, α-lactalbumin, bovine serum albumin, immunoglobulins (igg) (kumar et al. 2012; priyanka and rastogi 2018; kaur et al. 2020). the global production of whey is around 160 million tons per year and out of the total production of whey, only 70 % is used in the production of various products, while 30 % is disposed of in rivers and seas. regardless of all, whey is one of the major pollutants in the food processing industry. a million tons of whey are disposed into rivers, lakes, other water bodies which possess serious threat to the ecosystem due to its high biological and biochemical oxygen demand. in india, the production of whey is scattered, unorganized and the production levels vary from small (20 – 50 l/day) to large scale (50,000 – 1,000,000 l/day) hence, may not be processed at one location (kakan et al. 2018). hence, it is crucial to devise strategies for proper utilization of whey. many optimization studies have been carried out using experimental design techniques such as plackett-burman design, box–behnken design and central composite design have been widely used in the literature (şensoy et al. 2020). boxbehnken design, a response surface methodology statistical design was widely used to explore the correlation between process variables and the responses using minimal experiments (jeganathan et al. 2014). the current study aimed to investigate the practicability to use paneer whey as a growth medium for production of the vitamin b12 and to optimize the media components to achieve the maximum vitamin b12 production using boxbehnken design. experimental materials vitamin b12 (cyanocobalamin, 99.9 % pure), hplc water, and methanol was purchased from sigma aldrich chemicals private limited (bangalore, india). all other chemicals and reagents used were of analytical grade. whey procurement and characterization liquid unprocessed paneer whey (lpw) was obtained from a cottage dairy industry in chennai, nova biotechnol chim (2023) 22(1): e1339 3 tamilnadu. lpw was analysed for ph and water activity. the protein and ash content were determined according to indian standard method is 4684-1975 (1976). fat content was estimated by the aoac method 922.06. the carbon and nitrogen content were determined using the chns analyzer at csir-clri, chennai. strain and culture conditions the bacterial strain used in the study was l. reuteri dsm 20016, acquired from metabolic engineering laboratory, anna university, chennai. to obtain a working culture, from the frozen stock, 100 µl of the thawed culture was transferred to 10 ml of the mrs broth (de man et al. 1960) and incubated for 24 h at 37 °c. daily transfer to fresh medium was performed to maintain the cell viability prior to use. cells were cultivated in nonstirred batch cultures under anaerobic conditions (95 % n2 and 5 % co2) unless stated otherwise. preparation of growth medium production of vitamin b12 by l. reuteri dsm 20016 was done in lpw medium consisting of 20 g lpw, 5 g yeast extract, 1 g polysorbate 80,2 g ammonium citrate, 5 g sodium acetate, 0.1 g magnesium sulphate, 0.05 g manganese sulphate and 2 g dipotassium hydrogen phosphate in 1 l of distilled water (ph 6.5). the medium composition was adapted from the mrs medium in which lpw was replaced as a carbon source instead of dextrose. glycerol and cobalt chloride were used as supplements to enhance the vitamin b12 production. the composition of the media was modified according to the experiments. optimization of vitamin b12 production the growth kinetics of l. reuteri dsm 20016 was monitored in mrs and lpw medium at 37 °c. the preliminary screening assessed the effect of varying individual components of lpw yeast extract (2.5 – 15 g.l-1), polysorbate 80 (1 – 6 g.l-1), lpw (20 – 120 g.l-1). the effect of varying levels enhancers glycerol (1 – 8 g.l-1) and cobalt chloride (1 – 8 g.l-1) were studied individually on the production of vitamin b12 was also evaluated. the other components were maintained at a fixed level. the starter culture of od600 = 0.961 (corresponds to cfu =1.14 × 104 cfu.ml-1) was used as inoculum. all experiments were conducted in duplicates and average values were reported. the spss 11.5 software package was used for statistical evaluation of data. the difference between the runs was evaluated using duncan’s test at 5 % significance level. response surface methodology as the subsequent step, the response surface methodology (rsm) was conducted by applying box–behnken design to study the optimal medium formulation and the interactions between the factors for the vitamin b12 production. boxbehnken designs a three-level second-order design developed to fit the second-order response surface model (vellaisamy singaram et al. 2021). the factors of box behnken design along with the levels are as follows – lpw (20 – 80 g.l-1), yeast extract (2.5 – 5 g.l-1), glycerol (1 – 3 g.l-1) and cobalt chloride (1 – 3 g.l-1). the model was developed using a design expert (stat-ease) software version 11.1. the design matrix with actual values and experimental results are shown in table 2. the experimental results were fitted with a second order polynomial function (eq. 1): y= βo + xi + + + (1) where y is the predicted response, k is the number of factors, xi and xj are the coded variables; β0 is the offset term; βi, βj, and βij are the first-order, quadratic, and interaction effects, respectively; i and j are the index numbers for factor; and eij is the residual error. the fit quality of the model was evaluated by r2 and analysis of variance (anova). the lack of fit was used for controlling the statistics adequacy and efficiency of the model. statistical testing of the model was done by fisher’s statistical test (kumar et al. 2012). nova biotechnol chim (2023) 22(1): e1339 2 extraction and analysis of vitamin b12 the vitamin b12 (cyanocobalamin) was quantified using high performance liquid chromatography. hydroxocobalamin is a natural form of cobalamin, formed in the bacterial cell. since it is highly unstable, it is converted to cyanocobalamin using kcn (hajfarajollah et al. 2015). for highperformance liquid chromatography (hplc) analysis, the cell culture broth (40 ml) was centrifuged (9,000 × g for 10 min at 4 °c) to harvest the cells. the supernatant was discarded, and the pellet was washed with 10 ml 0.2 m potassium phosphate buffer (ph 5.5), centrifuged (10,000 × g for 15 min) and re-suspended in 1 ml of 0.2 m potassium phosphate buffer (ph 5.5) containing 0.1 % potassium cyanide. in order to lyse the cells for release of the vitamin b12, the resuspended cells were vortexed and autoclaved (121 °c, 15 min). finally, the samples were vortexed again and centrifuged (10,000 × g, 15 min). the supernatant was filtered (0.22µm syringe filter) and analysed with hplc (hugenschmidt et al. 2010). a shimadzu chromatography system with c18 column (shodex c18-4e, i.d. × length, mm 4.6 × 250) and uv-vis detector was used for the analysis of vitamin b12. the uv detection wavelength, flow rate of a mobile phase, oven temperature, and injection volume were set to 361 nm, 1 ml.min-1, 30 °c, and 20 μl, respectively. the mobile phase was a mixture of hplc water: methanol (50 : 50). an external standard (cyanocobalamin) was used for calibration. each sample was injected twice, and the mean values were reported. results and discussion characterization of liquid paneer whey the compositional characteristics of lpw are shown in table 1. the proximate composition of lpw was 0.44g/100g protein, 4.91 % lactose, 0.16g/100g ash. the lpw has 97.63 % moisture content, and it is devoid of fat. the carbon and nitrogen contents of lpw were determined as 52.941 % and 1.187 %, respectively. the water activity value suggests lpw as a suitable medium for bacterial growth. similar observations on the composition of paneer whey have been reported in the literature (ranvir and adil 2018; singh et al. 2019). table 1. compositional analysis of lpw. s. no. parameters value 1 moisture [%] 97.63 2 ash [g/100g] 0.16 3 protein [g/100g] 0.44 4 fat [g/100g] 0.001 5 lactose [%] 4.91 6 water activity [aw] 0.98 7 ph 5.73 8 density [g.l-1] 1.0178 growth analysis the growth curve of l. reuteri dsm 20016 strain in mrs and lpw medium was studied (fig. 1 and fig. 2). fig. 1. growth curve of l. reuteri dsm 20016 in mrs medium (experiments were conducted in triplicates and the standard deviation was denoted as error bars). fig. 2. growth curve of l. reuteri dsm 20016 in lpw medium (experiments were conducted in triplicates and the standard deviation was denoted as error bars). 4 nova biotechnol chim (2023) 22(1): e1339 3 the exponential phase in the mrs medium reached a peak at 8 h and the stationary phase existed till 18 h. the carbon source in the mrs medium is glucose, which is easily metabolized by lactobacillus sp. after 18 h the amount of nutrients will be depleted, resulting in cell death. lpw was reported to be an excellent liquid carrier on the basis of bacterial shelf-life and presence of lactose and proteins which can serve as carbon and nitrogen sources for microorganisms (tan and li 2018; prakash and arora 2020). in the lpw media the exponential phase reached peak at 18 h and the stationary phase extended till 44 h. the delayed cell growth in the lpw media might be due to the complex nature of lactose since bacterial βgalactosidase activity is necessary to metabolize lactose. l. reuteri possesses low proteolytic activity and therefore supplementation with extra nitrogen sources might improve growth (jantzen et al. 2013). the number of cells obtained in mrs and lpw medium at 18 h is 1.46 × 107 cfu.ml-1 and 2.41 × 109 cfu.ml-1 respectively. since the vitamin b12 is a primary metabolite, the sampling time point in the experiment is chosen as 18 h. effect of media components on vitamin b12 production the effect of media components – yeast extract, polysorbate 80, and lpw on the vitamin b12 production was studied and the results are presented as follows. yeast extract yeast extract is commonly used for the growth of lactic acid bacteria due to their composition in amino acids and vitamins, which is necessary for the cell growth. yeast extract is the most common nitrogen source employed in the published studies concerning l. reuteri (couvreur et al. 2017; ichinose et al. 2020; nguyen et al. 2021). in the present study, the effect of varying the amount of yeast extract (2.5 g – 15 g) on the vitamin b12 production was analysed. the other components of lpw media are as follows – 20 g lpw, 1 g polysorbate 80, 2 g ammonium citrate, 5 g sodium acetate, 0.1 g magnesium sulphate, 0.05 g manganese sulphate, and 2 g dipotassium hydrogen phosphate in 1 l of distilled water (ph 6.5). as shown in fig. 3, the increase in amount of yeast extract from 2.5 g.l-1 – 5 g.l-1 significantly improved (p < 0.05) the vitamin b12 production from 25.578 ± 0.282 µg.l-1 to 32.728 ± 0.215 µg.l1. further increase in the amount of yeast extract reduced the vitamin b12 production. the lowest vitamin b12 (14.861 ± 0.037 µg.l -1) was obtained at 15 g.l-1 of yeast extract. the negative effect of yeast extract might be due to toxicity of yeast extract at higher concentration which in turn decreases the cell concentration. similar results on the negative effect of yeast extract on the growth of lactobacillus have been reported in the literature (ghaly et al. 2003; miloud et al. 2017). the optimal concentration of yeast extract for the production of the vitamin b12 was found to be 5 g.l-1. fig. 3. effect of varying amount of yeast extract on vitamin b12 production. values with different superscripts are significantly different (p < 0.05). polysorbate 80 to further investigate the influence of polysorbate 80 on the vitamin b12 production, polysorbate 80 concentrations from 1 to 6 g.l-1 were used, and other media components are as follows – 20 g lpw, 5 g yeast extract, 2 g ammonium citrate, 5 g sodium acetate, 0.1 g magnesium sulphate, 0.05 g manganese sulphate, and 2 g dipotassium hydrogen phosphate in 1 l of distilled water (ph 6.5). polysorbate 80, a surfactant, is a crucial growth factor in culture media for lactobacilli as it brings unsaturated fatty acids that allow reducing intracellular energy consumption (nguyen et al. 2021). as shown in fig. 4, highest and lowest vitamin b12 production was obtained at 3 g.l -1 (35.796 ± 0.012 µg.l-1) and 6 g.l-1 (30.846 ± 0.058 5 https://www.sciencedirect.com/topics/biochemistry-genetics-and-molecular-biology/lactobacillus nova biotechnol chim (2023) 22(1): e1339 2 µg.l-1). higher concentrations of polysorbate 80 decreased the vitamin b12 production because polysorbate 80 became toxic at higher concentration due to the destruction of the cell membrane structure and/or loss of the cell membrane function caused by the solubility of lipid bilayer by the surfactant (qi et al. 2009). hence, the optimal concentration of polysorbate 80 to produce the vitamin b12 was found to be 3 g.l -1. fig. 4. effect of varying amount of polysorbate 80 on vitamin b12 production. values with different superscripts are significantly different (p < 0.05). paneer whey for analysis of the effect of lpw on the vitamin b12 production, the yeast extract and polysorbate 80 levels were set at 5 g.l-1 and 3 g.l-1. the level of lpw was varied between 20 to 120 g.l-1 and other components were fixed as follows – lpw medium consisting of, 2 g ammonium citrate, 5 g sodium acetate, 0.1 g magnesium sulphate, 0.05 g manganese sulphate, and 2 g dipotassium hydrogen phosphate in 1 l of distilled water (ph 6.5). as shown in fig. 5, the vitamin b12 production was significantly increased with the increase of lpw percentage from 20 to 80 g.l-1. the highest vitamin b12 was achieved at cultures with 80 g.l -1 lpw. it has been reported that lpw is rich in various components, such as carbohydrate, vitamins and organic acids (patowary et al. 2016). due to the complex nutritional requirements of the lactobacillus, their survival is favoured in the presence of increased carbohydrate, protein, and vitamin sources (gomes et al. 2015). when further increasing the lpw amount into 100 g.l-1 or more, it drastically decreased the production of the vitamin b12. hence, the highest vitamin b12 produced was 65.179 ± 0.093 µg l-1 and the optimal concentration of lpw was 80 g.l-1. after determining the optimal concentration of yeast extract, polysorbate 80 and lpw, the effect of glycerol and cobalt chloride on the vitamin b12 production was analysed. fig. 5. effect of varying amount of lpw on vitamin b12 production. values with different superscripts are significantly different (p < 0.05). effect of glycerol on vitamin b12 production the effect of glycerol was analysed in a medium containing 80 g lpw, 5 g yeast extract, 3 g polysorbate 80, 2 g ammonium citrate, 5 g sodium acetate, 0.1 g magnesium sulphate, 0.05 g manganese sulphate, and 2 g dipotassium hydrogen phosphate in 1 l of distilled water (ph 6.5) with varying amounts of glycerol (1 g.l-1 to 8 g.l-1). l. reuteri was not capable of growing in glycerol as a sole carbon and energy source, even in the presence of complex ingredients of mrs broth (gopal ramakrishnan et al. 2015). during glycerol fermentation of l. reuteri, glycerol serves only as an external hydrogen acceptor (diraviam sriramulu et al. 2008). glycerol plays an important role in the growth of cells and acts as an inducer for vitamin b12 production. the genes responsible for the synthesis of cobalamin are cobt and cbia. the cbia catalyzed amidations to a side chain of cobyrinic acid in the biosynthesis of cobalamin (vitamin b12) from uroporphyrinogen iii. the lower ligand of cobalamin is covalently linked to a phosphoribosyl moiety through an alpha-glycosidic bond formed by the cobt enzyme. however, cobt was reported that it is responsible for the production of analogues. the expression of cbia and cobt was reported to raise significantly with an increase of glycerol supplementation (crofts et al. 6 nova biotechnol chim (2023) 22(1): e1339 3 2014; gu et al. 2015). in the present study, the highest and lowest vitamin b12 production was obtained at 3 g.l-1 (95.704 ± 0.022 µg.l-1) and 8 g.l-1 (29.640 ± 0.001 µg.l-1) (fig. 6). the higher concentrations of glycerol had a negative effect on vitamin b12 production. it was reported that the vitamin b12 production was enhanced with the supplementation of glycerol but high concentrations of glycerol supplementations inhibited the growth of cells which might be due to the activity of glycerol dehydratase inhibited by a quorum sensing of reuterin (bauer et al. 2010; gu et al. 2015). therefore, the optimal concentration of glycerol to produce the vitamin b12 was found to be 3 g.l-1. fig. 6. effect of varying amount of glycerol on vitamin b12 production. values with different superscripts are significantly different (p < 0.05). effect of cobalt chloride on vitamin b12 production lastly, the effect of cobalt chloride was analysed in medium containing 80 g lpw, 5 g yeast extract, 3 g polysorbate 80, 2 g ammonium citrate, 5 g sodium acetate, 0.1 g magnesium sulphate, 0.05 g manganese sulphate, and 2 g dipotassium hydrogen phosphate in 1 l of distilled water (ph 6.5) with varying concentrations of cobalt chloride from 1 g.l-1 to 8 g.l-1. glycerol was not included in the media to study the individual effect of cobalt chloride on the vitamin b12 production. cobalt chloride is a part of the metabolic pathway of the vitamin b12 production. the availability of cobalt chloride ions in the culture medium is essential to the vitamin b12 biosynthesis because it is a central component of the corrinoid ring (burgess et al. 2009). the amount of cocl2.6h2o is significant in affecting the final concentration of the vitamin b12 (hajfarajollah et al. 2015). as shown in fig. 7, maximum vitamin b12 production of 147.633 ± 0.367 µg.l-1 was achieved at the concentration 3 g.l-1. similarly, results of the increasing concentrations of cobalt chloride in enhancing the vitamin b12 production in bacillus megaterium and propionibacterium freudenreichii subsp. shermanii atcc 13673 has been reported in literature (mohammed et al. 2014a; de assis et al. 2020). however, further increase in the concentration to 4 g.l-1 or more depleted the vitamin b12 production. fig. 7. effect of varying amount of cobalt chloride on vitamin b12 production. values with different superscripts are significantly different (p < 0.05). response surface methodology the components in lpw medium, sodium acetate, k2hpo4, ammonium citrate, mgso4·7h2o and mnso4·h2o were considered not to have a significant effect on the biomass production (griet et al. 2018) and based on the single variable experiments, polysorbate 80 doesn’t induce a significant increase in the vitamin b12 production. hence, in the present study, the effect of four factors – paneer whey (a), yeast extract (b), glycerol (c) and cobalt chloride (d) on the vitamin b12 production were optimized using box behnken design. the design matrix along with the experimental values is in table 2. the production of the vitamin b12 varied from 54.863 µg.l -1 to 213.449 µg.l-1 and the maximum production was achieved at the following conditions – paneer whey (80 g.l-1), yeast extract (5 g.l-1), glycerol (2 g.l-1) and cobalt chloride (2 g.l-1). a modified quadratic model was developed to model the experimental data. 7 nova biotechnol chim (2023) 22(1): e1339 2 table 2. box behnken design matrix with actual values and experimental results. std run lpw (a) yeast extract (b) [g.l-1] glycerol (c) [g.l-1] cobalt chloride (d) [g.l-1] vitamin b12 [µg.l-1] 1 2 20 2.5 2 2 54.8634 3 20 20 5 2 2 80.2672 9 17 20 3.75 2 1 72.616 11 25 20 3.75 2 3 81.4221 17 16 20 3.75 1 2 76.8487 19 13 20 3.75 3 2 80.4883 5 28 50 3.75 1 1 108.055 6 7 50 3.75 3 1 121.639 7 24 50 3.75 1 3 124.885 8 18 50 3.75 3 3 129.369 13 26 50 2.5 1 2 85.7037 14 14 50 5 1 2 134.839 15 15 50 2.5 3 2 93.8982 16 21 50 5 3 2 141.774 21 27 50 2.5 2 1 83.4567 22 10 50 5 2 1 131.367 23 23 50 2.5 2 3 91.8839 24 29 50 5 2 3 143.159 25 22 50 3.75 2 2 109.055 26 12 50 3.75 2 2 109.609 27 4 50 3.75 2 2 110.545 28 1 50 3.75 2 2 110.748 29 3 50 3.75 2 2 110.532 30 30 50 3.75 2 2 110.58 2 19 80 2.5 2 2 138.321 4 9 80 5 2 2 213.449 10 6 80 3.75 2 1 175.385 12 8 80 3.75 2 3 189.326 18 5 80 3.75 1 2 176.45 20 11 80 3.75 3 2 190.726 the analysis of variance (anova) results for the model are presented in table 3. table 3. anova for reduced quadratic model. source sum of squares df mean square f-value p-value model 44259.68 12 3688.31 3300.21 < 0.0001 significant a-lpw 33830.15 1 33830.15 30270.42 < 0.0001 b-yeast extract 7337.31 1 7337.31 6565.25 < 0.0001 c-glycerol 217.71 1 217.71 194.80 < 0.0001 d-cobalt chloride 379.98 1 379.98 340.00 < 0.0001 ab 618.12 1 618.12 553.08 < 0.0001 ac 28.28 1 28.28 25.31 0.0001 ad 6.59 1 6.59 5.90 0.0265 cd 20.70 1 20.70 18.52 0.0005 a² 1443.02 1 1443.02 1291.18 < 0.0001 b² 47.83 1 47.83 42.80 < 0.0001 c² 273.95 1 273.95 245.13 < 0.0001 d² 158.43 1 158.43 141.76 < 0.0001 residual 19.00 17 1.12 lack of fit 16.67 12 1.39 2.98 0.1183 not significant pure error 2.33 5 0.4663 cor total 44278.68 29 8 nova biotechnol chim (2023) 22(1): e1339 3 the model was found to be significant (p < 0.05) and the statistical significance of the model was analysed using the fisher test. in the current study, the significant model terms are found to be a, b, c, d, ab, ac, ad, cd a2, b2, c² and d2. the lack of fit f-value of 2.98 implies the lack of fit is not significant.the high value of the coefficient of determination (0.9996) indicates the model is significant. in addition to this, the predicted r2 (0.9983) and adjusted r2 (0.9993) values must be less than 20 % which further suggests the adequacy of the model. the coded equation for the modified quadratic model is given as follows eq. 2: vitamin b12 (µg.l -1) = +110.18 + 53.10 a + 24.73 b + 4.26 c + 5.63 d + 12.43 ab + 2.66 ac + 1.28 ad 2.27 cd + 14.51 a2 2.64 b2 + 6.32 c2 + 4.81 d2 (2) the influence of the process variables on the vitamin b12 production was studied with the help of 3d surface plots (fig. 8). the vitamin b12 production was increased with respect to increasing lpw and yeast extract concentrations. the interactive effect between lpw and yeast extract was positive. the interactive effect of glycerol and cobalt chloride on the vitamin b12 production was negative. the negative effect might be due to the toxic nature of the compounds. fig. 8. 3d surface plots showing the influence of process variables on the vitamin b12 production. conclusion from the current study, it could be concluded that paneer whey is an excellent substrate for the vitamin b12 production. the concentrations of paneer whey, yeast extract, glycerol and cobalt chloride has most distinct effects on the biosynthesis of the vitamin b12 by l. reuteri dsm 20016. response surface methodology was used to optimize the process variables and the optimal condition for the vitamin b12 production was found to be paneer whey (80 g.l-1), yeast extract (5 g.l-1), glycerol (2 g.l-1) and cobalt chloride (2 g.l-1). the maximum of the vitamin b12 production obtained was 213.449 μg.l-1. the current study proposes valuable insights on cost effective carbon source to produce the vitamin b12. acknowledgement this research was funded by the ministry of food processing industries, government of india (research & development project: q-11/38/2018-r&d). conflict of interest the authors declare that they have no conflict of interest. 9 nova biotechnol chim (2023) 22(1): e1339 2 reference aoac 922.06-1922 fat in flour. 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tamilnadu, india abstract: in this study, hypnea valentiae, a red alga is used as a sorbent for the removal of chromium from aqueous solutions. the biosorption potential of hypnea valentiae was investigated in batch experiments. the process parameters were optimized using response surface methodology. based on the central composite design, quadratic model was developed to correlate the variables to the response. the most influential factor on each experimental design response was identified from the analysis of variance (anova). the optimum conditions for the maximum biosorption of chromium are ph – 2.8, temperature – 48.2oc, sorbent dosage – 5.3 g/l, metal concentration – 103 mg/l and contact time – 27 min. at these optimized conditions the maximum removal was found to be 94.5%. key words: hypnea valentiae, optimization, rsm, chromium, algae, biosorption 1. introduction toxic heavy metals are detrimental to human health and ecosystem stability. the removal and recovery of heavy metals from wastewater is important in the protection of the human health and environment. the most toxic metals are aluminium, chromium, iron, cobalt, nickel, copper, zinc, cadmium, mercury, and lead. the major industries that contribute to water pollution by chromium are mining, leather tanning, textile dyeing, electroplating, plants producing industrial inorganic chemicals etc. chromium (cr) bearing wastewater resulted from all these industries must be disposed off after treatment. traditional methods such as chemical precipitation, evaporation, electroplating, adsorption and ion exchange processes have been used to remove chromium from wastewater. however, these technologies are most suitable in situations where the concentrations of the heavy metal ions are relatively high. they are either ineffective or expensive when heavy metals are present in the wastewater at low concentrations, or when very low concentrations of heavy metals in the treated water are required. hence new technologies are required that can reduce heavy metal concentrations to environmentally acceptable levels at affordable costs. biological approaches, especially application of sorbents, have been suggested in the last decade. the advantages offered by sorbents are higher metal loading capacity and greater selectivity for transition and heavy metals. marine algae have been found to be potential suitable sorbents because of their low cost, relatively high surface area and high binding affinity. the use of marine algae for heavy metal removal has been reported by several authors (tien, 2002; jalali et al., 2002; prasannakumar et al., 2007; deng et al., 2007; ozer et al., 2009). 108 rajasimman, m. and murugaiyan, k. rsm is a collection of statistical techniques for designing experiments, building models, evaluating the effects of factors and searching for the optimum conditions. it is widely used for multivariable optimization studies in several processes (ravikumar et al., 2005; korbahti, 2007; aleboyeh et al., 2008; garg et al., 2008; rajasimman et al., 2009; rajeshkannan et al., 2009). so far no work has been carried out for the removal of chromium using h. valentiae. hence the objectives of the present investigation are to quantify the biosorption of chromium to unmodified h. valentiae and to optimize the process parameters for the biosorption of chromium using h. valentiae using response surface methodology. 2. materials and methods 2.1 preparation of adsorbent the red colored marine alga hypnea valentiae was used in the present study. it was collected from the coastal belt of gulf of mannar, tamilnadu, india. the collected algae were washed with deionized water several times to remove impurities. the washing process continued till the wash water contained no dirt. the washed alga was then completely dried in sunlight for 10 days. the dried alga was then cut into small pieces and was powdered using domestic mixer. in the present study the powdered materials in the range of 500–700 μm particle size were then directly used as sorbents without any pre-treatment. 2.2 preparation of solution batch experiments were performed with a magnetic stirrer (remi, india) at 200 rpm using 250 ml beakers containing test solutions. the stock chromium solution (1 g/l) was prepared by dissolving potassium dichromate (sd fine chemicals, india) of analytical grade in deionized water. other concentrations were prepared by dilution of this stock solution and fresh dilutions were used in each experiment. 2.3 experimental design by rsm a full factorial design, which includes all possible factor combinations in each of the factors, is a powerful tool for understanding complex processes for describing factor interactions in multifactor systems. rsm is an empirical statistical technique employed for multiple regression analysis by using quantitative data obtained from properly designed experiments to solve multivariate equations simultaneously. the experiments with different ph, adsorbent dosage, temperature, initial metal concentration and processing time were employed simultaneously covering the spectrum of variables for the removal of chromium in the central composite design. the coded values of the process parameters were determined by the following equation: δx ox ix ix = (1) nova biotechnologica 10-2 (2010) 109 where xi coded value of the i th variable, xi uncoded value of the i th test variable and x0 uncoded value of the i th test variable at center point. the range and levels of individual variables are given in table 1. the experiment design is given in table 2 along with experimental data and predicted responses. the regression analysis was performed to estimate the response function as a second order polynomial ∑ = ∑ = +∑ = +∑ = += k 2j j x ix ijβ 1-k 1i k li 2 i x iiβ i x k 1i iβ 0β y (2) where y is the predicted response, βi, βj, βij are coefficients estimated from regression, they represent the linear, quadratic and cross products of x1,x2,x3 on response. table 1. experimental range and levels of independent process variables. range and levels independent variable 2.38 -1 0 1 +2.38 ph (a) 1 2 3 4 5 temperature, (b) °c 25 35 45 55 65 sorbent dosage, (c) g/l 3 4 5 6 7 chromium concentration, (d) mg/l 50 75 100 125 150 contact time, (e) min 10 20 30 40 50 a statistical program package design expert 7.1.5, was used for regression analysis of the data obtained and to estimate the coefficient of the regression equation. the equations were validated by the statistical tests called the anova analysis. the significance of each term in the equation is to estimate the goodness of fit in each case. response surfaces were drawn to determine the individual and interactive effects of test variable on percentage removal of chromium. after biosorption, the contents of the beakers were centrifuged at 4500 rpm for 3 min and the sorbent was successfully separated from aqueous solution. the supernatants were analyzed for residual chromium concentration using an atomic absorption spectrophotometer (elico, india). 3. results and discussion 3.1 fitting models experiments were performed according to the ccd experimental design given in table 2 in order to search for the optimum combination of parameters for the biosorption of chromium using the red alga. a model f-value of 94.93 implies that the model is significant. the fisher f-test with a very low probability value (pmodel > f = 0.0001) demonstrates a very high significance for the regression model. the fitness of the model is checked by the determination coefficient (r2). the coefficient of determination (r2) was calculated to be 0.9850. this implies that more than 98.5 % of experimental data was compatible with the data predicted by the model (table 2) and only less than 1.5 % of the total variations are not explained by the model. the r2 value is always between 0 and 1, and a value >0.75 indicates aptness of the model. 110 rajasimman, m. and murugaiyan, k. table 2. ccd matrix for the experimental design and responses for chromium removal. % chromium removal run no. a b c d e experimental theoretical 1 1 1 -1 -1 1 65.2 66.50 2 1 1 1 -1 1 76.3 75.51 3 0 0 0 2.38 0 82.5 81.37 4 1 1 -1 -1 -1 69.2 68.84 5 1 -1 1 1 1 79.2 80.92 6 -1 1 1 -1 1 80.3 80.93 7 0 0 0 0 0 93.6 93.41 8 -1 -1 1 1 -1 74.6 73.72 9 -1 1 1 1 1 83.2 82.13 10 -1 -1 -1 -1 -1 79.8 80.67 11 0 0 0 0 0 93.5 93.41 12 -1 -1 1 -1 -1 83.6 82.78 13 -1 1 1 1 -1 86.2 86.73 14 0 2.38 0 0 0 82.2 81.18 15 1 -1 1 -1 -1 83 83.71 16 0 0 0 -2.38 0 79.6 79.17 17 -1 -1 1 1 1 70.8 71.67 18 1 -1 -1 -1 1 78.4 78.82 19 1 -1 -1 1 -1 79.6 79.24 20 0 0 0 0 -2.38 82.3 81.37 21 -1 1 1 -1 -1 87.6 88.72 22 2.38 0 0 0 0 75 73.84 23 1 -1 -1 -1 -1 77.2 78.60 24 -1 -1 1 -1 1 76.2 77.55 25 1 -1 1 1 -1 80.6 80.42 26 1 -1 1 -1 1 81.9 81.02 27 -2.38 0 0 0 0 76.3 75.90 28 1 1 1 -1 -1 80.3 80.76 29 0 0 0 0 0 93.6 93.41 30 1 -1 -1 1 1 83.1 82.66 31 -1 1 -1 1 -1 80.6 81.75 32 -1 -1 -1 1 1 76.2 76.44 33 0 0 0 0 0 93.4 93.41 34 1 1 1 1 -1 83.1 84.55 35 1 1 -1 1 1 76.4 77.40 36 0 0 0 0 0 93.6 93.41 37 1 1 -1 1 -1 76.8 76.55 38 0 0 0 0 0 93.4 93.41 39 -1 -1 -1 -1 1 79.9 78.36 40 0 0 2.38 0 0 76.2 75.44 41 -1 -1 -1 1 -1 74.2 75.56 42 -1 1 -1 -1 1 73.8 74.93 43 0 0 0 0 0 93.5 93.41 44 0 0 0 0 0 93.5 93.41 45 1 1 1 1 1 82.3 82.47 46 0 -2.38 0 0 0 80.9 80.36 47 -1 1 -1 -1 -1 81.2 79.80 48 0 0 0 0 2.38 76.8 76.17 49 0 0 -2.38 0 0 67.7 66.90 50 -1 1 -1 1 1 80.1 80.07 nova biotechnologica 10-2 (2010) 111 for a good statistical model, r2 value should be close to 1.0. the adjusted r2 value corrects the r2 value for the sample size and for the number of terms in the model. the value of the adj r2 (0.9746) is also high to advocate for a high significance of the model. the pred r2 0.9451 is in reasonable agreement with the adj r2. the experimental results are analyzed through rsm to obtain in empirical model for the best response. the results of theoretically predicted response are shown in table 2. the mathematical expression of relationship to the response with variables are shown below % removal of chromium = 93.38-0.43 a + 0.17 b + 1.79c + 0.46 d – 1.09 e – 3.27 a2 – 2.23 b2 – 3.93c2 – 2.32d22.58 e2 – 2.22 ab + 0.75ac + 1.44ad + 0.63 ae + 1.70bc + 1.77bd – 0.64 be – 0.98cd – 0.73ce + 0.80 de (3) the results of multiple linear regressions conducted for the second order response surface model are given in table 3. the significance of each coefficient was determined by student’s t-test and p-values, which are listed in table 3. the larger the magnitude of the t-value and smaller the p-value, the more significant is the corresponding coefficient. values of "prob > f" less than 0.0500 indicate model terms are significant. in this case, a, b, c, d, e, ab, ac, ad, ae, bc, bd, be, cd, ce, de, a2, b2, c2, d2, e2 are significant model terms for the biosorption of chromium. values greater than 0.10 indicate the model terms are not significant. this implies that the linear, square and interactive effects of ph, temperature, sorbent dosage, chromium concentration and contact time are more significant factors. table 3. analysis of variance (anova) for response surface quadratic model source coefficient factor f value p model a b c d e a*a b*b c*c d*d e*e a*b a*c a*d a*e b*c b*d b*e c*d c*e d*e residual lack of fit pure error cor total 93.38 -0.43 0.17 1.79 0.46 -1.09 -3.27 -2.23 -3.93 -2.32 -2.58 -2.22 0.75 1.44 0.63 1.70 1.77 -0.64 -0.98 -0.73 0.80 94.93 6.54 1.01 111.85 7.41 41.58 477.44 221.62 687.34 239.54 297.47 126.72 14.56 53.27 10.33 74.45 80.02 10.53 24.87 13.61 16.30 235.65 < 0.0001a < 0.0160a 0.0328 < 0.0001 0.0109 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 0.0007 <0.0001a 0.0032 <0.0001 <0.0001 0.0030 <0.0001 0.0009 0.0004 <0.0001 std. dev.-1.12 ; r2 0.9850; adj. r2-0.9746; pred. r2 0.9451; c.v.% 1.38; adeq precision 37.158 112 rajasimman, m. and murugaiyan, k. 3.2 response surfaces and contour plots response surface plots as a function of two factors at a time, maintaining all other factors at fixed levels are more helpful in understanding both the main and the interaction effects of these two factors. the response surface curves were plotted to understand the interaction of the variables and to determine the optimum level of each variable for maximum response. the response surface curves for the removal of chromium are shown in figs 1-4. there was a relative significant interaction between every two variables, and there was a maximum predicted yield as indicated by the surface confined in the smallest ellipse in the contour diagrams. figure 1-4 shows the effect of solution ph on chromium removal. the results indicate that the percentage removal of chromium varies from 65% to 93% in the ph range 1 to 5, suggesting that the removal was highly ph-dependent. the biosorption capacity of h. valentiae was high at initial ph 2.8, but decreased considerably from 93% to 71% as the ph of experimental solution increased to 5.0. from fig. 1 it was observed that the biosorption of chromium increased from 65% to 93% with increase in temperature from 25 to 49°c. a maximum biosorption of 93% chromium has been obtained at 49°c. this suggests that biosorption between seaweed and chromium could involve a combination of chemical interaction and physical adsorption. with the increase in temperature, pores in the seaweed enlarge, resulting in increased surface available for the biosorption, diffusion and penetration of chromium ions within the pores of seaweed causing increased biosorption (saleem et al., 2007). amount of sorbent used for the treatment studies is an important parameter, which determines the potential of sorbent to remove chromium at a given initial concentration. as shown in fig. 2, the removal of chromium increased with an increase in sorbent dosage (upto 5 g/l) and then decreased. therefore, the optimum value of sorbent dosage was found to be 5.3 g/l. with increasing the quantity of seaweed, beyond this optimum condition, biosorption capacity decreases for h. valentiae. the decrease in biosorption capacity may be due to splitting effect of concentration gradient between sorbate and sorbent with increasing seaweed concentration causing a decrease in amount of chromium adsorbed onto unit weight of h. valentiae. -2.38 -1.19 0.00 1.19 2.38 -2.38 -1.19 0.00 1.19 2.38 49 60.25 71.5 82.75 94 % r em ov al o f c hr om iu m a: ph b: temperature fig. 1. 3d plot showing interactive effect of ph and temperature on cr removal. nova biotechnologica 10-2 (2010) 113 percentage removal of chromium has been found to be higher at lower concentration of chromium solution (100 mg/l); a maximum chromium removal of 93% has been obtained for h. valentiae (fig. 3). the increase of chromium biosorption capacity of sorbent with an increase in chromium concentration is probably due to higher interaction between metal ions and the sorbent. as seen in fig. 4, the percentage of chromium removal increased by contact time up to 27 min. after that point, there was no considerable change in chromium removal. therefore, optimum contact time was considered as 27 min. -2.38 -1.19 0.00 1.19 2.38 -2.38 -1.19 0.00 1.19 2.38 43 55.75 68.5 81.25 94 % r em ov al o f c hr om iu m a: ph c: sorbent dosage fig. 2. 3d plot showing interactive effect of ph and sorbent dosage on cr removal. -2.38 -1.19 0.00 1.19 2.38 -2.38 -1.19 0.00 1.19 2.38 51 61.75 72.5 83.25 94 % r em ov al o f c hr om iu m a: ph d: chromium concentration fig. 3. 3d plot showing interactive effect of ph and chromium concentration on cr removal. -2.38 -1.19 0.00 1.19 2.38 -2.38 -1.19 0.00 1.19 2.38 55 64.75 74.5 84.25 94 % r em ov al o f c hr om iu m a: ph e: contact time fig. 4. 3d plot showing interactive effect of ph and contact time on cr removal. 114 rajasimman, m. and murugaiyan, k. 3.3 optimum condition for chromium removal optimum conditions for the removal of chromium from aqueous solution using a red alga h. valentiae were found. second order polynomial models obtained in this study were utilized for each response in order to determine the specified optimum conditions. the sequential quadratic programming in matlab 7 is used to solve the second-degree polynomial regression equation 3. the optimum values obtained by substituting the respective coded values of variables are: ph – 2.8, temperature – 48.2oc, sorbent dosage – 5.3 g/l, chromium concentration – 103 mg/l, contact time – 27 min. at this point, the maximum chromium removal was found to be 94.5%. 4. conclusions the biosorption of chromium on h. valentiae, a red alga, was investigated in a batch system. the biosorption conditions of chromium on h. valentiae were optimized by using rsm. the relationship between the response and the independent variables was developed via the quadratic approximating function of chromium biosorption capacity of sorbent. the optimum conditions were determined as initial ph – 2.8, temperature – 48.2°c, biosorbent concentration – 5.3 g/l, initial chromium concentration 103 mg/l and contact time – 27 min. as a result, a chemical waste containing chromium can be removed by using a red alga such as h. valentiae which is abundant and cheaply available. this study also clearly showed that response surface methodology was one of the suitable methods to optimize the operating conditions and maximize the chromium removal. analysis of variance showed a high coefficient of determination value (r2 = 0.9850), thus ensuring a satisfactory adjustment of the second-order regression model with the experimental data. references aleboyeh, a., daneshvar, n, kasiri, m.b.: optimization of c.i. acid red 14 azo dye removal by electrocoagulation batch process with response surface methodology. chem. eng. process., 47, 2008, 827–832. deng, l., su, y., su, h., wang, x., zhu, x.: sorption and desorption of lead (ii) from wastewater by green algae cladophora fascicularis. j. hazard. mater., 143, 2007, 220–225. garg, u.k., kaur, m.p., garg, v.k., sud, d.: removal of nickel(ii) from aqueous solution by adsorption on agricultural waste biomass using a response surface methodological approach. bioresour. technol., 99, 2008, 1325–1331. jalali, r., ghafourian, h., asef, y., davarpanah, s.j., sepehr, s.: removal and recovery of lead using nonliving biomass of marine algae. j. hazard. mater., b92, 2002, 253–262. korbahti, b.k.: response surface optimization of electrochemical treatment of textile dye wastewater. j. hazard. mater., 145, 2007, 277–286. ozer, a., gurbuz, g., alimli, a.c., korbahti, b.k.: biosorption of copper (ii) ions on enteromorpha prolifera: application of response surface methodology. chem. eng. j., 146, 2009, 377–387. nova biotechnologica 10-2 (2010) 115 prasanna kumar, y., king, p., prasad, v.s.r.k.: adsorption of zinc from aqueous solution using marine green algae—ulva fasciata sp. chem. eng. j., 129, 2007, 161–166. rajasimman, m., sangeetha, r., karthic, p.: statistical optimization of process parameters for the extraction of chromium (vi) from pharmaceutical wastewater by emulsion liquid membrane. chem. eng. j.l, 150, 2009, 275-279. rajeshkannan, r., rajamohan, n., rajasimman, m.: removal of malachite green from aqueous solution by sorption on hydrilla verticillata biomass using response surface methodology. front. chem. eng. china, 3, 2009, 146-154. ravikumar, k., pakshirajan, k., swaminathan, t., balu, k.: optimization of batch process parameters using response surface methodology for dye removal by a novel adsorbent. chem. eng. j., 105, 2005, 131–138. saleem, m., pirzada, t., qadeer, r.: sorption of acid violet 17 and direct red 80 dyes on cotton fiber from aqueous solutions. colloids surf. a: physicochem. eng. asp., 292, 2007, 246–250. tien, c.j.: biosorption of metal ions by freshwater algae with different surface characteristics. process biochem., 38, 2002, 605 -/613. microsoft word farago nb 2010-2.doc nova biotechnologica 10-2 (2010) 137 community level physiological profiling of microorganisms in the rhizosphere of transgenic plants – a review juraj faragó1, natália faragová2 1department of biotechnology, university of ss. cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic 2plant production research centre, research institute of plant production, plant biology section, bratislavská cesta 122, piešťany, sk-921 68, slovak republic abstract: since 1996, when the first genetically modified seeds were planted in field conditions, the commercial growing of genetically modified crops increased to over 134 millions of hectares in 2009 worldwide. along with the great potential of transgenic plants for future agriculture, considerable concerns on their biosafety have been raised, including their potential impact on soil microbial communities. this review briefly summarizes the important features of soil microorganisms for plant health and ecosystem stability, the numerous methods available for microbial ecologists to study soil microbial diversity, with emphasis on the method of community level physiological profiling (clpp) based on carbon substrate utilization patterning, and finally the use of clpp for assessing the effects of transgenic crops on soil microbial communities. key words: clpp, soil microbial community, transgenic plants, carbon sources 1. introduction the first transgenic plant, tobacco containing a selectable marker gene nptii from a bacterium conferring resistance to kanamycin, was produced at the university of ghent, belgium, in 1983 (zambryski et al., 1983), only 30 years after the discovery of the structure of dna. now, some 27 years later, genetically modified (or transgenic) crops became a common feature of the agricultural landscape in 25 countries of the both americas, europe, asia, africa and australia (james, 2009). the unprecedented high growth rate of adoption of transgenic crops started in the u.s.a. in 1996 with 1.7 million hectares. in 2009, the global area of genetically modified (gm) crops reached 134 million hectares (james 2009), which is more than the total land area of six neighboring countries: slovakia, czech republic, poland, hungary, ukraine and austria together (122 mil. ha). the first commercially grown transgenic crops contained one gene of interest or one introduced novel trait (single trait gm crops). at present, however, combination or stacking different traits or genes in one plant is rapidly gaining popularity and recent growth of gm crops hectarage over the last few years comes largely from deployment of these so called “stacked traits” gm crops (taverniers et al., 2008; james, 2009). several transgenic plants containing two, three or more genes of interest are currently under evaluation by national authorities of different countries for deliberate release of transgenic plants into environment (taverniers et al., 2008). 138 faragó, j. and faragová, n. along with the increasing potential for widespread commercial use and the benefits of transgenic crops, considerable concerns on their safety have been raised, including safety aspects relating to their potential impact on the environment (widmer, 2007). the rapid development of agricultural biotechnology and release of transgenic plants into environment have provided many agronomic and economic benefits, however they also raised a multitude of concerns over the potential ecological effects of transgenic plants. these concerns include unintended consequences of transgene flow to indigenous organisms through pollen transfer, plant invasiveness, the development of resistance in target pests, and direct or non-direct effects on nontarget flora, fauna and microorganisms and ecosystems (seidler and levin, 1994; nielsen et al., 2001; dale et al., 2002; bruinsma et al., 2003; filion, 2008). in addition to the relatively abundantly studied aboveground effects, underground impacts of gm crops have also been recognized as a result of recent methodological advances in soil microbial ecology (bruinsma et al., 2003; zhang et al., 2005). nevertheless, the impact of gm crops on soil-associated microfauna, including soil microbial communities, still represents one of the least studied and understood areas, probably due in part to the inherent technical difficulties involved in the study of soilborne living organisms (filion, 2008). recently several excellent reviews on the effects of transgenic plants on soil microbial communities have been published (e.g. bruinsma et al., 2003; dunfield and germida, 2004; widmer, 2007; filion, 2008). in this review, we focused on the methodological aspects, as well as the use of community level physiological profiling (clpp) based on sole carbon source utilization analysis to study the functional diversity of microbial communities in the rhizosphere of transgenic plants. we provide also a brief overview of the microbial characteristics of soils and methods used for analyses of soil microbial communities. 2. microbial characteristics of soils soil is a complex and dynamic physical, chemical and biological system and a major component in agro-ecosystems (nannipieri et al., 2003). it is considered to be the greatest reservoir of biodiversity on the planet (crawford et al., 2005). prokaryotic organisms comprise more than half of the biodiversity on earth and their diversity in soil has been estimated to be about three orders-of-magnitude greater than in all other environments combined (curtis et al., 2002). microorganisms are fundamentally important components of the soil habitat where they play key roles in ecosystem functioning through controlling nutrient cycling reactions essential for maintaining soil fertility, and they also contribute to the genesis and maintenance of soil structure (kirk et al., 2004). the microbial community of arable soils is a key agent in biologically mediated processes such as degradation of organic residues, transformation of organic matter, mineralization of nutrients, formation of soil aggregates, and soil nutrient balance. soil microorganisms are also a component with multiple functions of importance to soil fertility, such as catalysis of nutrient transformations, storage of nutrients, formation and stabilization of soil structure, and control of plant pathogens (kennedy and papendick, 1995; petersen et al., 2002; gömöryová et al., 2009a). nova biotechnologica 10-2 (2010) 139 soil microbial communities have great potential for temporal and spatial change, and thus represent a powerful tool for understanding community dynamics in both basic and applied ecological research (garland, 1997). the soil microbial community structure is considered as an early and sensitive indicator of anthropogenic effects on soil ecology (nielsen and winding, 2002). soil microorganisms are able to respond more quickly to environmental stress because, compared to higher organisms, they have a high surface-to-volume ratio, which means they are capable of a much more intense exchange of matter and energy with their environment. therefore, changes in size, composition and activity of microbial communities can frequently be observed before detectable changes in soil physical and chemical properties occur (nielsen and winding, 2002; widmer and oberholzer, 2003; gömöryová et al., 2009a). moreover, bacteria interact with plants during their entire life cycles and therefore can act as precise and fast indicators of environmental changes. plants depend on the ability of roots to communicate with microbes. the converse is also true; many bacteria and fungi are dependent on associations with plants that are often regulated by root exudates (bais et al., 2004). crop plants interact with soil microbial communities through a micro-zone at the root-soil interface that is under the influence of the plant root. this complex habitat composed of the fraction of soil adhering to plant roots and altered by root activity is referred to as rhizosphere. the rhizosphere environment hosts a complex microorganism network which interacts very closely with plant roots, the outcome of such interaction being seen in the strong influence plant type has on the microbial ecosystem of the soil (brusetti et al., 2004). it is well known, that rhizosphere exerts a selective influence on the associated microbial communities and these microorganisms in turn have a great impact on root biology, they influence plant growth, nutrition and development, and are important for long-term sustainability of agricultural soils (mantelin and touraine, 2004). a number of studies have shown that the rhizosphere has much higher population densities of bacteria and fungi compared with bulk soil (maloney et al., 1997; semenov et al., 1999). plants modify their rhizosphere environment through release of assimilates in the form of root exudates (uren, 2001). the four types of main ingredients in plant root exudates are carbohydrates, amino acids, fatty acids and nucleotides, other compounds, such as organic acids, steroids, growth hormones, flavones and enzymes are also involved (zhang et al., 2005). this complex mixture of organic compounds provides a source of reduced carbon, nitrogen, and other nutrients for soil inhabiting microorganisms (buyer et al., 2002). the composition of compounds which are released from the roots and interact with bacteria in the rhizosphere vary depending on the plant species, cultivar, and physiological status of the plants (sorensen, 1997; saxena et al., 1999). root exudates are known to mediate both positive and negative interactions in the rhizosphere. the positive interactions include enhancement of growth rates of bacteria (hartwig et al., 1991), acting as chemoattractants to attract bacteria towards the root (dharmatilake and bauer, 1992), and acting as transcriptional signals in the communication between soil bacteria and host plants during nodule formation and biological nitrogen fixation by plants (redmond et al., 1986). on the other side, plant-microbe interactions often involve also plant activities 140 faragó, j. and faragová, n. to suppress growth of bacteria in the rhizosphere, e.g., by secretion of bactericidal substances (garcia-olmedo et al., 1998). bactericidal substances naturally released from the plant roots may include toxic components like benzofurans, terpenoids, butyrolactones, and other phytoalexins (bowen and rovira, 1991). previous studies revealed that qualitative and quantitative differences in root exudation could strongly affect the structure of microbial communities in the rhizosphere (oger et al., 1997; savka and farrand, 1997; maloney et al., 1997). the composition of microbial communities in the rhizosphere is governed mainly by the quality and quantity of carbon substrates that are released as root exudates (maloney et al., 1997). root exudation may create a niche that influences which microorganisms colonize the rhizosphere, thereby altering the composition and diversity of rhizomicrobial communities in a plant-specific manner (grayston et al., 1998). even small modifications, as may exist between different cultivars of the same plant species may cause altered composition of root exudates, which can eventually result in the occurrence of different microbial communities in the rhizosphere (rengel et al., 1998). it was shown previously that microbial population density and diversity can be influenced by introducing genes into plants for the production of novel compounds (oger et al., 1997; savka and farrand, 1997). genetically engineered plants might change the bacterial consortia in the rhizosphere due to the release of transgene products or an altered composition of root exudates (oger et al., 1997). the insertion of transgenes may unintentionally alter plant characteristics of the transgenic crop others then the desired trait. in turn, these changes may influence the growth and species composition of soil microorganisms associated with the roots of these plants, and therefore they may have ecological effects (donegan et al., 1995). an altered composition of root exudates may induce a different community of rhizosphere microorganisms and even small modifications, as may exist between different cultivars of the same plant species, can result in the occurrence of different microbial communities in the rhizospheres (rengel et al., 1998). comparative studies assessing whether there are differences between microbial communities living in the rhizospheres of transgenic and non-transgenic plants represent an important first step in determining if the presence of transgenic material can catalyze changes in the environment. this knowledge of the impact of transgenic crops on soil microbial ecology is essential for understanding the long-term agronomic and environmental effects of genetically modified crops and for developing appropriate management practices for minimizing potential negative impacts (fang et al., 2007). 3. methods of studying soil microbial communities over the past ten years, approaches to studying soil microbial communities changed dramatically. a number of new techniques have been developed and are now available to soil microbiologists to gain deeper insight into community-level responses to changes in soil properties or management. commonly applied bulk soil microbial parameters include measurement of total microbial biomass (vance et al., 1987; liao and xie, 2007; lupwayi et al., nova biotechnologica 10-2 (2010) 141 2007), determination of activities of enzymes involved in c-, nand p-nutrient cycling, such as proteases, cellulases, phosphatases, dehydrogenases, arylsulfatases, and others (rasche et al., 2006; bradley et al., 2007; gorlach-lira and coutinho, 2007), basal soil respiration (visser et al., 1994; lupwayi et al., 2007; raubuch et al., 2010) and specific metabolites (raubuch et al., 2007). these methods can provide information on general microbial activities, but not on specific microbial groups that actually contribute to different types of soil enzymatic activities (liu et al., 2005). the methods for the analysis of microbiological soil characteristics and assessment of the impact of environmental or anthropogenic factors, including the cultivation of genetically modified crops, on soils are generally categorized into two broad groups: (1) culture-dependent methods and (2) culture-independent methods (hill et al., 2000; widmer, 2007). there are several cultivation-dependent methods which are used to retrieve microorganisms from soils. the plating method (syn. plate count method) offers a simple but useful tool to identify and characterize changes of specific microbial strains, or groups of species (brusetti et al., 2004; liu et al., 2005; faragová et al., 2005; mulder et al., 2006). it can be used to detect effects of transgenic plants on specific soil microorganisms such as symbiotic nitrogen-fixing bacteria, degraders of recalcitrant organic matter, nitrifying bacteria, denitrifying bacteria, cellulolytic bacteria, actinomycetes, and others (bruinsma et al., 2003; faragová et al., 2005, faragová and faragó, 2010). one limitation of the method is, however, that it is affected by the cultivation bias precluding analysis of the entire microbial diversity in soils (widmer, 2007). development of the metabolic fingerprinting method referred to as community-level physiological profiling (clpp), syn. community-level substrate utilization (clsu), based on parallel cultivation of soil microorgamisms on a set of different carbon sources have significantly improved the capacity and robustness of cultivation-dependent methods. this method is also a cultural technique, and as such, its use is restricted to culturable microorganisms only (preston-mafham et al., 2002; liu et al., 2005; widmer, 2007). nevertheless, clpp is often used as an efficient method capable of revealing the effects of transgenic plants on soil microbial communities (donegan et al., 1995; di giovanni et al., 1999; dunfield and germida, 2003; griffiths et al., 2000; heuer et al., 2002; tesfaye et al., 2003; brusetti et al., 2004; fang et al., 2005; lupwayi et al., 2007). inherent limitations of culture-based methods have lead soil microbiologists to explore culture independent methods of microbial community analysis. these methods allow to characterize the composition and diversity of soil microbial communities based on the extraction, identification and quantification of molecules from soil that are specific to certain microorganisms or microbial groups (hill et al., 2000). such molecules include fatty acids and nucleic acids. phospholipid fatty acid (plfa) analysis is based on the analysis of the presence and abundance of specific fatty acids in soil which are indicative of specific groups of microorganisms. a biochemical method fatty acid methyl ester (fame) analysis provides information on the microbial community composition based on separation and identification of methylated fatty 142 faragó, j. and faragová, n. acids extracted directly from soil. these methods are capable of providing a quantitative measure of the viable or potentially viable microbial biomass (liu et al., 2005). both, plfa and fame are extensively used to assess the effects of transgenic plants on soil microbial communities (dunfield and germida, 2003; griffiths et al., 2007). advances in molecular biology in last years considerably improved our knowledge of morphological, physiological, biochemical and ecological features of soil microorganisms. using the dna based methods specific marker sequences can be analyzed in soil dna extracts by means of polymerase chain reaction (pcr) amplification (hill et al., 2000; widmer, 2007). of the various marker genes used to estimate microbial community composition and diversity, the most used are those encoding 16s ribosomal rna (rrna) in prokaryotic, and 18s rrna in eukaryotic microorganisms. a number of molecular-based techniques have been developed to assess the microbial community diversity (hill et al., 2000; kirk et al., 2004; widmer, 2007). these include dna guanine plus cytosine content analysis (nusslein and tiedje, 1999), dna reassociation (torsvik et al., 1990), dnadna hybridization (guo et al., 1997), and different pcr-based methods such as terminal restriction fragment length polymorphism (t-rflp) (liu et al, 1997; rasche et al., 2006), amplified ribosomal dna restriction analysis (ardra) (liu et al., 1997; widmer et al., 2001; lottmann et al., 2010), denaturing gradient gel electrophoresis (dgge) (muyzer et al., 1993; castaldini et al., 2005; costa et al., 2006), temperature gradient gel electrophoresis (tgge) (muyzer and smalla, 1998), single-strand conformation polymorphism (sscp) (schweiger and tebbe, 1998; miethling-graff et al., 2010), and ribosomal intergenic spacer analysis (risa) (fisher and triplett, 1999; brusetti et al., 2004). the rflp and ardra techniques distinguish sequences based on different locations of restriction enzyme recognition sites. dgge and tgge rely on differences in the stability of dna duplex, while sscp analysis detects differences in secondary structures of single stranded dna. risa, on the other hand, resolves length differences of the amplified marker gene sequence (widmer, 2007). these methods, used for dna fingerprint analyses, enables cultivation-independent analysis of microbial community structure and diversity through the detection and characterization of microbial nucleic acid sequences within samples (liu et al., 2005), however, they do not provide quantitative analyses of microbial groups in soil. recently, a new dna-dna hybridization technique, taxonomic microarray analysis, has been adopted to assess soil microbial diversity (greene and voordouw, 2003). this technique has been shown to be able to discriminate and characterize bacterial community composition in related biological samples, offering extensive possibilities for systematic exploration of bacterial diversity in different ecosystems (sanguin et al., 2006). 4. community level physiological profiling to understand the role of microbial communities in different environments, it is essential to have knowledge of microbial community function and functional diversity nova biotechnologica 10-2 (2010) 143 (preston-mafham et al., 2002). although molecular techniques are now widely used to characterize soil bacterial communities, these techniques provide little information regarding functional properties of microbial communities, for example, on the ability of microbial communities to metabolize specific chemical compounds. to address these functional features of microbial communities, the method of community level physiological profiling (clpp) using biolog® microplates (biolog, inc., hayward, usa) have been developed. garland and mills (1991) were the first who introduced the use of commercially available biolog® microtitre plate bacterial identification system based on the utilization pattern of 95 different single carbon sources, to assess functional diversity of microorganisms in environmental samples. the biolog® system was originally developed for rapid identification of pure bacterial cultures by sole carbon source utilization, using plastic 96 well microtiter plates containing 95 different carbon substrates in separate wells, and no substrate in one well, which is used as control. among the 95 substrates on biolog gn and gp plates, there are several groups of chemical compounds, such as carbohydrates, amino acids, carboxylic acids, amines, amides and polymers (fig. 1). in addition, each well contains a colourless tetrazolium dye. upon inoculation of plate with a pre-grown isolate, metabolism of the substrate and the production of nadh via cell respiration lead to reduction of colourless tetrazolium to violet formazan (fig. 2). the colour development is measured colorimetrically at specific absorbance and a data set of optical density (o.d.) values is obtained (garland and mills, 1991; prestonmafham et al., 2002). individual species may be identified by a specific pattern of colour change on the plate, providing an identifiable metabolic fingerprint (preston-mafham et al., 2002). differences in sole carbon source utilization have been used successfully to distinguish among different bacterial isolates for more than 60 years. at present, the microbial identification database for biolog systems (biolog, inc.) contains more than 1950 entries for rapid identification of broad spectrum of aerobic and anaerobic bacteria, yeasts and filamentous fungi, mainly of medicinal importance. the commercially available 96 well biolog® microtitre plates were first used to compare metabolic activities of heterotrophic microbial communities from environmental habitats (water, soil and wheat rhizosphere) by garland and mills (1991). currently several different types of biolog plates are available to microbial ecologists, all of them containing different substrates appropriate for specific groups of microorganisms. the biolog gntm plates were developed for identification of gramnegative bacteria and contain substrates appropriate for this group of microorganisms (fig. 1a), whereas biolog gptm plates contain carbon sources appropriate for grampositive bacteria (fig. 1b). even though gn and gp plates were successfully used for ecological microbiology research, biolog ecotm plates have been developed specifically for ecological applications. contrary to gn and gp plates, the eco plates contain only 31 substrates (plus a control well without a substrate) in three replicates on the microtitre plate. these substrates have previously been found to have high relevance to soil bacterial communities, or are known to be included in plant root exudates (preston-mafham et al., 2002). the tetrazolium dye used in gn, gp 144 faragó, j. and faragová, n. and eco plates is not metabolizable by fungi, therefore specific biolog ff plates have been designed for identification of fungal microorganisms. the ff plates contain different carbon sources from gn, gp, and eco plates and a modified tetrazolium dye specifically metabolizable solely by fungi. to prevent interference of growth and colour development by bacteria, an appropriate combination of antibiotics is frequently included into ff plates (buyer et al., 2001). biolog mt plates, containing a redox dye and no substrate, are also available, which allow researchers to produce customized plates (preston-mafham et al., 2002; stefanowitz, 2006). a b fig. 1 carbon sources in gn2 (a) and gp2 (b) microplates (biolog, inc., hayward, usa) nova biotechnologica 10-2 (2010) 145 fig. 2 colour development in biolog gp microplate inoculated with a microbial suspension extracted from the rhizosphere zone of transgenic alfalfa (faragová et al., not published). the use of biolog microtitre plates enables analyzing microbial communities on both, the individualas well as community levels (garland, 1997). at the individual-level, the analysis of microbial communities requires the isolation of microorganisms, isolation and characterization of individual isolates, and description of the community based on the relative abundances and diversities of different isolates. the community-level approach, established by garland and mills (1991), bypasses the isolation step and the environmental samples are directly inoculated into microplates and the resulting response (colour change pattern) is used to describe differences in microbial communities (garland, 1997). community-level biolog analysis is generally accomplished in five consecutive steps: (1) sample processing to obtain suspension of microorganisms, (2) inoculation of aliquots of microbial suspension into wells of biolog® microplates, (3) incubation of plates for 2-8 days in defined culture conditions, (4) regular monitoring the colour development in each well and (5) data processing and statistical analysis of results. for analyses of pure culture isolates, the samples are prepared from freshly grown cells on a standard enriched medium (garland, 1997; konopka et al., 1998). in contrast, analyses of environmental samples have used a number of different sample processing techniques, including direct inoculation of aquatic samples into microtitre plates (garland and mills, 1991), shaking plant roots in a solution to release rhizosphere microorganisms (garland, 1996), and extraction of microbial cells from complex soil matrices using sieving, shaking, blending and sedimentation or centrifugation of samples (haack et al., 1999; konopka et al., 1998; dobler et al., 2001). for comparisons it is important that samples are of equivalent size, in term of volume and/or weight (preston-mafham et al., 2002). in most cases the processed sample is diluted prior to use as inoculum. as bacterial cell density in the inoculum affects colour development in biolog plates (garland and mills, 1991; haack et al., 1995; garland, 1996), it is very important to 146 faragó, j. and faragová, n. determine dilution levels that reduce additional colour development caused by excess utilizable organic matter in the sample (konopka et al., 1998; prestonmafham et al., 2002). it is known, that a minimum number of about 108 metabolically active cells per ml in a well is required for observable colour development (haack et al., 1995). therefore, in dilute inocula, the kinetics of colour development will be a function of time and will follow a sigmoidal curve with an initial lag phase, followed by linear growth phase and a final plateau phase. the lag phase represents the time period during which the inoculum grows to a population density of 108 cells ml-1, while during the linear phase the specific metabolic activity of a microorganism on a specific substrate causes accumulation of formazan and colour development. at the plateau phase the production of formazan upon the oxidation of a specific substrate by the activity of a microorganism reaches its maximum yield due to organic substrate depletion. especially when the goal is identification of pure cultures, it is recommended to adjust all microbial suspensions to a standardized cell density prior to inoculation into biolog® plates. alternatively, with community-level biolog analysis, adoption of appropriate data analysis can account for different inoculum densities (garland and mills, 1991). most studies of soil microbial community composition and diversity employing biolog® plates use fixed incubation temperatures between 15 and 28°c (prestonmafham, 2002). another important variable in biolog analysis is incubation time, as both the colour intensity in individual wells, and the number of positive wells will increase with incubation time. too short incubation times (48 h and less) may cause absence of colour development in some wells (especially with those of slow growing microorganisms), while longer incubations (>48 h) will result in more positive responses and reaching the colour saturation levels in some wells (konopka et al., 1998; preston-mafham et al., 2002). to reduce the effects of differential rates of colour development due to inoculum density and inoculation time, appropriate transformations of original raw data are recommended (garland and mills, 1991; preston-mafham et al., 2002). in principle, the biolog assay is done by colorimetrically measuring tetrazolium dye reduction that is coupled to substrate oxidation. any microtitre plate reader equipped with an appropriate filter (590 nm) can be used to quantify the colour development in individual wells of plates. the degree to which each of the 95 substrates is oxidized is determined after a fixed incubation period. a positive response is identified as an absorbance or optical density value greater than that occurring in the blank well (haack et al. 1995). the number and types of utilized substrates, as well as developed colour intensities, constitute a data set from which the functional diversity of microbial communities involved may be assessed. colour development in each well reflects species activity and density, as well as the ability of the bacterial community to respond to particular substrates (zak et al., 1994). the data obtained by quantifying the colour development in individual wells are usually expressed as individual well optical densities or average well colour development (awcd) (garland and mills, 1991; preston-mafham et al., 2002). the awcd value for each microplate is obtained by calculating the raw difference between the optical density in each well and that in the control well and then summing nova biotechnologica 10-2 (2010) 147 all these values and dividing by 95. on the other hand, sigler (2004) uses two parameters to describe the microbial community structure: the average metabolic response (amr), and community metabolic diversity (cmd). amr describes the average respiration of the c-sources by the microbial community and provides a single metric by which communities can be compared. the amr is calculated as the average of the mean difference between the o.d. of the c-source-containing wells and the control well. the second parameter, cmd, represents the number of substrates utilized by the microbial community and is analogous to community functional richness. cmd is calculated by summing the number of positive responses (violet-coloured wells) observed following incubation (sigler, 2004). the clpp generates a rich data set of 95 values for each sample (if gn or gp plates are used) or 31 values in triplicate (if eco plates are evaluated). data are corrected against the control well (without a carbon substrate) or the initial reading at time zero, before subjecting to multivariate statistical analysis. regardless of the chose of absorbance measurement, i.e. net o.d. of individual substrates, awcd, or parameters received from kinetic analyses, the use of multidimensional statistical analyses is necessary (konopka et al., 1998; stefanowicz, 2006). the most commonly used method is principal component analysis (pca) of the quantitative colour data, which reduces the number of variables to a few significant principal components. the use of cluster analysis based on the presence or absence of colour in wells (zak et al., 1994) is also possible. in kinetic studies, one may process the data by calculating the area under curve for each well o.d. for the entire period of incubation, or by estimation of kinetic parameters by fitting the curve of o.d. versus time to a density dependent logistic growth equation (guckert et al., 1996; lindstrom et al, 1998; insam and goberna, 2004). analysis of microbial community functional diversity using sole carbon source utilization profiles is, despite some limitations (garland, 1997; konopka et al., 1998; preston-mafham et al., 2002), a rapid, reproducible and useful tool to discriminate among bacterial communities from diverse environmental samples. its strength lies in the low manpower it requires, which enables intensive sampling across temporal and spatial scales, and the reliance of the method on metabolic traits that could lead to functionally relevant characterization of changes in microbial communities (garland, 1997). although clpp is a culture based assay, it has been found that non culturable cells also respond to this assay, and therefore this assay seems not to be as biased as the classical culture-based techniques (prestonmafham et al., 2002). 5. assessing the effect of transgenic crops on soil microbial communities using clpp the clpp using biolog® plates has been used to date for characterizing bacterial communities from a range of environments, including comparisons of rhizosphere bacterial communities of transgenic vs. non-transgenic plants. as the method can provide important insights into ecosystem function and stability, it was used to study the metabolic responses of microbial communities from rhizosphere and bulk soils 148 faragó, j. and faragová, n. (söderberg et al., 2004), from the rhizosphere of different plant species (grayston et al., 1998; miethling et al., 2003) or from different parts of the rhizosphere along the root (baudoin et al., 2001). the biolog method is also frequently applied for estimating the influences of different cropping systems (larkin and honeycutt, 2006), agronomic procedures such as tillage (griffiths et al., 2007), soil management (gomez and correa, 2008), or factors involved in ecosystem changes (gömöryová et al., 2009b) on microbial community physiological profiles. currently one of the most frequent applications of biolog® system is for assessing the impacts of different stressing factors, such as heavy metals (dobler et al., 2001; liao and xie, 2007), herbicides (mijangos et al., 2009), explosive elements (anderson et al., 2010) and high salinity and low ph (pankhurst et al., 2001). donegan et al. (1995) first used the biolog gn plates to assess changes in soil microorganisms associated with transgenic cotton plants expressing the bacillus thuringiensis endotoxin (bt). from that time, the clpp method using biolog® gn, gp or eco plates proved to be a quick, reproducible and useful method to discriminate among microbial communities associated with the roots of transgenic vs. nontransgenic plants (di giovanni et al., 1999; schmalenberger and tebbe, 2002; tesfaye et al., 2003; brussetti et al., 2005; fang et al., 2005; mulder et al., 2006; watrud et al., 2006; lupwayi et al., 2007; travis et al., 2007 and many others). some authors (brussetti et al., 2005; fang et al., 2005; griffiths et al., 2007) could not find any statistically significant differences in functional diversities of rhizosphere microorganisms between transgenic and non-transgenic plants using biolog® microplates. in these studies, whether in greenhouse or field conditions, soil texture, crop type and pest management regime, rather than cultivation of transgenic plants affected the rhizosphere microbial communities. other authors reported very few changes in functional diversity of rhizosphere soil bacteria associated with growing gm crops (lupwayi et al., 2007), or significant shifts in the carbon utilization patterns of culturable microbial communities in the rhizospheres of transgenic plants, or soils amended with residues from transgenic plants (di giovanni et al., 1999; tesfaye et al., 2003; fang et al., 2007; travis et al., 2007). at least some of these differences in carbon source utilization patterns may be explained by the possible effects of site of insertion or simply somaclonal variation on the availability of endogenous nutrients in the soil mix on microbial populations (watrud et al., 2006). fang et al. (2007) hypothesized, that amendment of soils with bt corn residues may affect selected activities of soil bacteria carried by specific enzymes. altered composition of root exudates of transgenic plants may also induce a different community of rhizosphere microorganisms. in general, however, if shifts in bacterial communities due to cultivation of transgenic plants were observed, these were similar to those observed when nontransgenic cultivars are compared. in comparison with other factors, the impact of the genetic modification of the plant on soil microbial communities was usually minor and transient, or comparable to variations due to plant genotype, plant physiological and developmental stage, soil type, agricultural practice used and pathogen exposure. nova biotechnologica 10-2 (2010) 149 nevertheless, despite the research performed up to now, it is not yet clear whether gm plants or their products exert any ecological effect on the microbiota and microbial processes in soil. to elucidate this question, more studies on the impact of transgenic plants on soil microbial communities is needed, preferably employing the polyphasic approach using different methods of soil microbial communities analysis, including plate count, biochemical and molecular methods. 6. conclusions community level physiological profiling is a quick and easy method of investigating the functional diversity of microbial communities from a range of environmental habitats. the method, which employs biolog® microplates containing 95 different carbon sources, are gaining increasing importance not only in general soil ecology, but also is increasingly used as a method which is able to provide functional information on the microbial community structure and diversity in the rhizosphere of transgenic plants. the simplicity, speed, and low cost of the method compared with other approaches are very attractive to microbial ecologists and other microbiologists. however, the researcher should keep in mind, that to fully exploit its potential the technique requires very careful data acquisition, appropriate statistical analysis and cautious interpretation of results. acknowledgement: this work was supported partially by the research and development project of the ministry of agriculture of slovak republic no. 2005 uo 27/050 02 06/050 02 06 granted to plant production research centre, piešťany, slovak republic. references anderson, j.a.h., canas, j.e., long, m.k., zak, j.c., cox, s.b.: bacterial community dynamics in high and low bioavailability soils following laboratory exposure to a range of hexahydro-1,3,5-trinitro-1,3,5-triazine concentrations. environ. toxicol. chem., 29, 2010, 38–44. bais, h.p., park, s.-w., weir, t.l., callaway, r.m., vivanco, j.m.: how plants communicate using the underground information superhighway. trends plant sci., 9, 2004, 26-32. baudoin, e., benizri, e., guckert, a.: metabolic fingerprint of microbial communities from distinct maize rhizosphere compartments. eur. j. soil biol., 37, 2001, 85-93. bowen, g.d., rovira, a.d.: the rhizosphere. in: waisel, y., eshel, a., kafkafi, u. 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studies china, 7, 2005, 28–34. 38 nova biotechnologica et chimica 13-1 (2014) doi 10.2478/nbec-2014-0005 © university of ss. cyril and methodius in trnava distribution of zinc and cadmium in tissues of giant reed (arundo donax l.): sequential extraction radiometric study barbora micháleková richveisová, zuzana dürešová, miroslav horník, jozef augustín, martin pipíška department of ecochemistry and radioecology, faculty of natural sciences, university of ss. cyril and methodius in trnava, j. herdu 2, trnava, sk-917 01, slovak republic (b.richveisova@gmail.sk) abstract: heavy metals are taken up by the vascular plant root system from water solutions in cationic forms. subsequently, during both short and long distance transport to other plant tissues, cation forms are incorporated to many bioorganic compounds differing in stability, ionic character and physico-chemical properties such as solubility in lipid structures and mobility across cell membrane systems. many sequential and single step extraction methods have been elaborated for characterization of the role of individual components of plant cells components in transport and detoxication of heavy metals. in our study, dry biomass of giant reed (arundo donax l.) grown in hydroponic media spiked with 65zncl2 and 109cdcl2 was treated with dithizone solutions as complexing ligand in order to convert free zn2+ and cd2+ ions to corresponding dithizonates. treatment with dithizone showed that up to 67 % of the total plant cd and 56 % of the total plant zn were transformed to dithizonate complexes extracted with chloroform. extraction of biomass with folch reagent showed that up to 48 % of the total root cadmium and up to 18 % of the total shoot cadmium is bound in lipid fraction. zinc was not found in lipid fraction of root and shoot. derivatization of the dried root and shoot lipid fraction by dithizone showed that two third of cd in root and practically all cd in shoot lipid fraction could be transformed to cd-dithizonate. methods of biomass treating with complexing ligands and a method of sequential extraction procedures with non-polar organic solvents and radiotracer methodology seem to be useful methods for the study of metal speciation and distribution in vascular plants. key words: 65zn, 109cd, arundo donax l., sequential extraction, dithizonate, speciation 1. introduction contamination of environment by heavy metals such as cu, cd, pb, hg and zn is a global problem. heavy metals and radionuclides spreading from the source of air pollution are dissolved by rainfall water and sorbed by leaf surface of higher plants or directly sorbed onto soil components. reversibility of the metal sorption at the end of vegetation period determine the next transport of contaminants to the soil and consequently into the food chain in the following vegetation period. plants can bind contaminants from soil and according to the way of binding, these metals are released to the environment in different speed. giant reed (arundo donax) can be considered both as an energy plant and as a tool for toxic metal removal from contaminated land. the plant can survive in wetlands bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 16:05 utc nova biotechnologica et chimica 13-1 (2014) 39 when the concentration of cu2+, pb2+, cd2+, zn2+, ni2+ and hg2+ is 100 mg/kg and cr6+ 50 mg/kg (han and hu, 2005). the concentration of heavy metals in soil declines with the growth of the plant due to the translocation of heavy metals from peripheral soil to rhizosphere and the phytoextraction and phytovolatilization. the characters of large biomass, exuberant root and good adaptability of a. donax suggested its great potential in remediation of polluted soils. giant reed can be considered also as a sensitive biomonitor of the presence of heavy metals in water and sediments. bonanno (2012) showed that concentrations of metals in plant tissues were significantly dependent on the kind of organ and element. trace element concentrations decreased according to the pattern of root > leaf > stem, implying that roots acted as the main centres of bioaccumulation, and stems as transit organs as a consequence of the general high translocation from roots to leaves. a. donax showed a significant capacity of bioaccumulation in agreement with ecologically similar macrophytes. positive correlations were found between trace concentrations in plant organs and sediment (al, cr, mn, ni, zn), and water (cu, ni, zn). the results of this study suggested that a. donax acts as an ecological indicator of environmental conditions, thus, its application may prove a useful tool during monitoring campaigns of wetlands. in the quantification of the efficiency of energy production processes based on biomass, energy returned on invested energy is an important parameter to be considered. in this context, a. donax showed the best results, thanks to the great yields reached in low input cultivation conditions, with respects to other herbaceous perennial species (pilu et al., 2012; takahashi et al., 2010). the annual stem production can reach from 12 to 23 t dm/ha (mavrogianopoulos et al., 2002). giant reed is therefore considered an important representative of energy plants. for extraction of heavy metals from soils and sediments, a variety of single and sequential extraction techniques can be used (tessier et al., 1979). these techniques were recently reviewed by babel and dacera (2006). however, owing to the wide range of extractants used in these extraction techniques, the results obtained were not comparable. in 1987, the community bureau of reference (bcr) started a programme to harmonize the methodology used in sequential extraction schemes for determination of metals in soils and sediments (ure et al., 1993). the methodology was also successfully applied to different types of biomass. the type of applied sequential extraction scheme can lead to the anomalies in the results, as sequential extraction schemes are greatly influenced by the type of extractants used, the operating conditions (ph, contact time and temperature) and the sequence in which the extraction steps are applied. van hullebusch et al. (2005) compared the sequential extraction procedure by tessier et al. (1979), the procedure according to stover et al. (1976), the bcr protocol and discussed the results of the fractionation of anaerobic metabolism of important metals (co, ni, cu, zn, mn and fe). the phytofiltration of cd and zn by giant reed (a. donax l.) was described and published in previous papers (horník, et al. 2011; dürešová et al., 2013; dürešová et al., 2013). sequential extraction has been successfully used for speciation study of elements in soils and other inorganic matrices (tessier, 1979; mehlich, 1953; mehlich, 1984; lindsay, 1978). however practical applicability for behaviour of toxic metals in plant tissues is rather limited. the use of bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 16:05 utc 40 micháleková richveisová, b. et al. method of sequential extraction of heavy metals in sewage sludge was reported in our previous paper frišták et al. (2012). the aim of this paper was to characterize mode of heavy metals binding in the process of root uptake and translocation to shoots in vascular plants. giant reed (a. donax l.) grown in nutrient media spiked with 65zn and 109cd was used as a model plant. sequential extraction of dried biomass was used in the presence of ligands able to bind heavy metal cations to complexes differing in stability constants log k and estimated in extracts by gamma-spectrometry. 2. material and methods 2.1 chemicals deionized water (conductivity 0.054 μs/cm) was prepared with simplicity 185 (millipore, f). commercially available chemicals of analytical grade, without pretreatment were used: dithizone (c13h12n4s; cas: 60-10-6), chloroform, methanol. 2.2 cultivation media hoagland medium (mg/dm3): nh4no3 – 160.1; h3bo3 – 8.5; na2moo4.2h2o – 0.06; mnso4.5h2o – 5.0; znso4.7h2o – 0.66; cuso4.5h2o – 0.8; mgso4.7h2o – 369.7; kno3 – 404.4; cacl2 – 443.9; nah2po4.2h2o – 291.7; na2hpo4.12h2o – 46.5; feso4.7h2o – 17.9; nano3 – 339.9; nh4cl – 213.9, ph 6.0. basal medium was diluted with deionized water in the ratio 1:3. mineral medium (mm) (mg/dm3): cocl2.6h2o – 0.3; feso4.7h2o – 5.8; kh2po4 – 23.4; mgso4.7h2o – 41.0; co(nh2)2– 91.7; nh4cl – 12.8; ch3coonh4 – 79.4. microelements (μg/dm3): cuso4.5h2o – 80; h3bo3 – 850; mnso4.5h2o – 500; na2moo4.2h2o – 6.0; znso4.2h2o – 66, ph 5.5. 2.3 plants arundo donax l. (var. versicolor) was obtained from the centre for research of plant production (piešťany, slovak republic). plants originated from tissue cultures grown in nutrition media (murashige et skoog, 1962) supplemented with synthetic cytokinine 6-benzylaminopurine and α-naphthylacetic acid for micropropagation of plants. in the next step, plants were cultivated for 2-4 weeks in 25 % hoagland nutrition media (hoagland, 1920) in cultivation box binder (germany), type kbwf 720. photoperiod light/dark 16h/8h at light intensity max 11 450 lx (stepwise 0, 40, 60 and 100 %) and at 28/15 °c, relative humidity 60-80 %. 2.4 zinc and cadmium root uptake pre-cultivated 20 plants (each approx. 20 cm, 40 mg d.w., shoot to root ratio 4:1 d.w.) were transferred to test tubes and cultivated in the first step for 24 h in mineral medium (mm), in the second step for 24 h in the same mineral medium supplemented with 65zncl2 and 109cdcl2 at 20 °c at day/night light cycle. roots were washed in bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 16:05 utc nova biotechnologica et chimica 13-1 (2014) 41 surplus of deionized water, roots and shoots were air dried, weighted and radioactivity was measured by gamma-spectrometry. 2.5 extraction procedures dried biomass (approx. 200 250 mg) divided to roots and shoots was separately treated according to scheme in fig. 2 and fig. 3. presented data are averages of three independent experiments. 2.5.1 sequential extraction of lipid fraction shoot or root biomass (approx. 110 mg) were subsequently extracted with 2 ml folch solution (chcl3 : meoh = 2 : 1) for 1 h at 25 °c according to the scheme in fig. 3. aliquots of extract solution removed from biomass and in both extract and biomass were 65zn and 109cd radioactivity by gamma-spectrometry measured. after this, all samples of biomass and folch extracts were dried for 1 day at 25 °c. subsequently, the dried samples were extracted with 2 cm3 1 mmol/dm3 chloroform solution of dithizone for 1 h at 25 °c. extracts were removed from biomass and samples of wet biomass were weighted and retained volume of extractants was calculated by subtraction of dry biomass used in experiments. concentration ratio of zn and cd species was calculated from the radioactivity of extracts and remaining biomass by gamma-spectrometry. 2.5.2 sequential extraction combined with derivatization to dithizonates biomass of a. donax (approx. 200-250 mg, d.w.) was separated to roots and shoots, air dried and extracted according to the scheme in fig. 2. shortly, in the first step, biomass was extracted with 2 cm3 0.1 mmol/dm3 dithizone for 1 h at 25 °c, in the next step biomass was extracted with chloroform solution of 1 mm dithizone, and in the last step with 0.1 mol/dm3 hcl. after each extraction the extract was removed, samples of wet biomass were weighted and retained volume of extractants was calculated by subtraction of dry biomass used in experiments. concentration ratio of zn and cd species was calculated from the radioactivity of extracts and remaining biomass by gamma-spectrometry. 2.6 radiometric analysis for determination of 65zn and 109cd gamma-spectrometric scintillation detectors 54bp54/2-x and 76bp76/3 with well type crystal na(tl) (scionix, nl) and data processing software scintivission-32 (ortec, usa) were used. a library of radionuclides was built by selecting characteristic γ-ray peaks (88.04 kev for 109cd and 1115.52 kev for 65zn) for energy and efficiency calibration. standardized solution of 65zncl2 (4.90 mbq/cm 3; 0.05 g/dm3 zncl2 in 3 g/dm 3 hcl) and 109cdcl2 (3.94 mbq/cm3; 0.05 g/dm3 cdcl2 in 3 g/dm 3 hcl) was provided from the czech metrological institute (prague, cr). bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 16:05 utc 42 micháleková richveisová, b. et al. 3. results and discussion giant reed (a. donax) was grown in liquid nutrient media spiked with 65zn and 109cd at subtoxic concentrations 11.0 μmol/dm3 zncl2 and 11.0 μmol/dm 3 cdcl2. it was found that zinc and cadmium were distributed between roots and shoots in the ratio 6.6:1 for cd and 5.4:1 for zn. the ratio of specific radioactivity (bq/g, d.w.) of root biomass to specific radioactivity of shoots biomass calculated from 20 plants of a. donax was 33.7:1 for cd and 11.9:1 for zn. this phenomenon can be explained by higher mobility of zinc as microelement comparing with mobility of phytotoxic cadmium, which is retained in root biomass with higher efficiency. speciation of zinc and cadmium in plants speciation of heavy metals entering the plant tissues plays decisive role in the both long distance and short distance transport of these metals in plant and is responsible for phytotoxic behaviour of heavy metals and participation in metabolic processes. for solving these problems in our experiments we combined sequential extraction procedures and derivatization of plant zinc and cadmium by complexing ligands (fig. 1). 2 + m2+ fig.1. reaction of dithizone (i) with bivalent metals m2+resulting in metal dithizonates formation (ii). dithizone is able to react with free zn2+ and cd2+ ions and also with zinc and cadmium bound in complexes with many organic and inorganic compounds bearing anionic groups such as carboxylic acids, amino acids, inorganic and organic phosphates. concentration equilibrium of this substitution reaction depends on log k values of stability constants of corresponding metal ligands. stability constants of synthetic complexing ligands such as edta, nta and dithizone are higher within orders than stability constants for components of plant tissues (table 1). synthetic complexing ligand could therefore serve as an efficient tool for speciation analysis of microelements and toxic metals entering plant tissues. the main advantage of dithizone comparing with edta is high solubility of zn and cd dithizonate in organic solvents e.g. in chloroform and it can be quantitatively separated from reaction mixture and at utilization of radiotracer methods determined by common radioanalytical equipments. i k ii bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 16:05 utc nova biotechnologica et chimica 13-1 (2014) 43 . table 1. stability constants log k of naturally occurring and synthetic metal-ligand complexes. log k ligand zn2+ cd2+ naturally occurring acetic acid 1.59 c 1.7 c glutamic acid 5.45 a 4.78 b histidine 6.6 c 5.65 b cysteine 9.8 c 10.30 a adp 4.28 c znh3phytate 7.81 d triphosphates 9.7 c synthetic nta 10.45 c 9.8 b edta 16.5 b 16.5 b other organic ligands 0.8-21.9 e 0.9-23.3 e a bottari and festa (1997); b christensen and izatt (1983); c martell (1964); d crea et al. (2008); e solovjev et al. (2012) fig. 2. sequential extraction of dried a. donax biomass (~ 110 mg, d.w.) combined with zn and cd complexation with dithizone in situ without removal of lipid fraction. plants grown in mineral medium (mm) at c0 = 11 μmol/dm3 zncl2 and 11 μmol/dm3 cdcl2. in our experiments (fig. 2), dried plant biomass was treated with 0.1 and 1.0 mmol/dm3 dithizone in chloroform at 20 °c. this procedure leads to conversion of zn bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 16:05 utc 44 micháleková richveisová, b. et al. and cd species to corresponding dithizonates and their extraction to chloroform phase. gamma-spectrometry showed, that in root biomass after double extraction was 78 % zn and 76 % cd in non-ion-exchangeable form, which was soluble in 0.1 mol/dm3 hcl. similar ratios were obtained in shoot biomass, where after double extraction was in non-ion-exchangeable form 66 % zn and 57 % cd. residual proportion in biomass after extraction with 0.1 mol/dm3 hcl represented ≤3%, which defines metal binding to metalloproteins or other biomass compartments, which can be for example for steric reasons unavailable in reaction with such effective ligand as hcl. the data are presented in table 2. table 2. ion-exchangeable (dithizonate) and non-ion-exchangeable (non dithizonate) forms of zn and cd in a. donax estimated by in situ conversion of metals to corresponding metal-dithizone complexes with the following extraction into chloroform. a sum of the data of the subsequent reaction with 0.1 mmol/dm3 and 1 mmol/dm3 dithizone in chloroform. fig. 3. sequential extraction of dried a. donax biomass (~ 110 mg d.w.) combined with zn and cd complexation with dithizone in situ after removal of lipid fraction by folch reagents. root (%) shoot (%) fraction zn cd zn cd total biomass 100 100 100 100 dithizonate (a) 22 24 34 43 non dithizonate 78 76 66 57 hcl soluble 75 74.5 66 54 hcl insoluble 3 1.5 0 3 bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 16:05 utc nova biotechnologica et chimica 13-1 (2014) 45 after removal of lipid fraction from biomass (fig. 3) we found, that zn entering the plant via root of a. donax l. from very diluted solutions (11 μmol/dm3 zncl2 and 11 μmol/dm3 cdcl2) was not distributed in root and shoot lipid fraction, or only in small quantities. zn was localized in non-lipid fraction, in forms which are not available for reaction with dithizone in non-polar organic solvent immiscible with water, or is bound to a chemical forms in ion non-exchangeable form (e.g. proteins, nucleic acid…). cadmium is bound in high quantities in root lipid fraction (48 %) and shoot lipid fraction (18 %). derivatization of dried root and shoot lipid fraction by dithizone showed that two third of cd in root and practically all cd in shoot lipid fraction could be transformed to cd-dithizonate. in shoot lipid fraction, substantial part of cadmium is in ion-exchangeable form (16 % total). in root, the proportion of metal in non-ionexchangeable form is higher (15 %). in shoot non lipid fraction, cd in ionexchangeable form is practically in comparable amount as zn (cd 41 % and zn 38 %), but in root non-lipid fraction is higher (zn 8 % and cd 18 %). prevailing part of the zinc in root (up to 92 % of the total) and cadmium (up to 34 % of total) remaining in non-lipid fraction was not convertible to dithizonate. similarly, high proportion of zinc and cadmium remained in non-lipid fraction of shoots (62 % of total zinc and 41 % of total cadmium). all data are presented in table 3. table 3. ion-exchangeable and non-ion-exchangeable forms of zn and cd in lipid and non-lipid fraction of root and shoot tissues of a. donax. see table 2 for details. many papers confirmed (see e.g. hiroshi et al., 1994) that both zn and cd dithizonate in chloroform extract can be completely converted to water soluble form by re-extraction with edta solution what gives the next opportunity of speciation analysis of microelements and toxic metals entering the plant tissues via root and foliar uptake as well as for speciation analysis of metal ions sorbed on sorbents with many different metal binding active centres. 4. conclusions experiments with giant reed (a. donax) plants grown in the presence of non-phytotoxic concentration of 65zncl2 and 109cdcl2 in nutrient media showed that metals are transported from roots to shoots reaching root-to-shoot ratio 6.6:1 and 5.4: 1 for cadmium and zinc, respectively. treatment of dried plant biomass with dithizone showed that up to 24 % of cd and 22 % of zn incorporated in root and up to 43% of cd and 34% of zn incorporated in shoot can be transformed to dithizonate complexes. root (%) shoot (%) fraction zn cd zn cd total biomass 100 100 100 100 lipid fraction 0 48 0 18 dithizonate 0 33 0 16 non dithizonate 0 15 0 2 non lipid fraction dithizonate 8 18 38 41 non dithizonate 92 34 62 41 bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 16:05 utc 46 micháleková richveisová, b. et al. sequential extraction of plants biomass, treatment of extracts and solids by complexing ligands provide metal-ligand complexes of various stabilities. radiotracer methods can be a powerful tool for the study of long distance transport and speciation analysis of bivalent metals entering the plant tissues via root system. acknowledgement: this work was supported by project of the cross-border co-operation programme and co-financed with european regional development fund (erdf) with the grant number husk/1101/1.2.1/0148. also authors want to thank to msc. m. gubišová, the center for research of plant production, piešťany, slovak republic for plant materials obtained by tissue culture cultivation. references babel, s., dacera, d.d.m.: heavy metal removal from contaminated sludge for land application. j. waste manag., 26, 2006, 988-1004. bonanno, g.: arundo donax as a potential biomonitor of trace element contamination in water and sediment. ecotoxicol. environ. saf., 80, 2012, 20-27. bottari, e., festa, m.r.: on the behavior of cysteine as ligand of cadmium (ii). talanta, 44, 1997, 1705-1718. bracklow, u., drews, a., vocks, m., kraume, m.: comparison of nutrients degradation in small-scale mbr fed with synthetic/domestic wastewater. j. hazard. mater., 144, 2007, 620-626. crea, f.: formation and stability of phytate complexes in solutions. coord. chem. rev., 252, 2008, 1108-1120. dürešová, z., horník, m., gubišová, m., gubiš, j.: phytofiltration potential of arundo donax in cd removing from contaminated wastewater. chem. pap., 2014 (accepted). dürešová, z., šuňovská, a., horník, m., pipíška, m., gubišová, m, gubiš, j., augustín, j.: phytofiltration of cd and zn by root system of energy plants. proceedings of the international conference of applied natural sciences. nový smokovec, slovakia, october 2-4, 2013, 26. folch, j., lees, m., sloane stanley, g.h.: a simple method for the isolation and purification of total lipides from animal tissues. j. biol. chem., 226, 1957, 497-509. frišták, v., valovčiaková, m., pipíška, m., augustín, j.: simultaneous and sequential extraction protocols as tools for determination of zinc bioavailability in dried anaerobic sludge. nova biotechnol. chim., 11, 2012, 167175. han, z., hu z.: tolerance of arundo donax to heavy metals. chin. j. appl. ecol., 16, 2005, 161-165. hiroshi, k., hideyuki, i., tomoyuki, o.: mutual separation of metal ions by dithizone extraction-isotachophoresis on the basis of hsab principle. analyst, 9, 1994, 723-726. hoagland, d.r.: optimum nutrient solutions for plants. science, 52, 1920, 562564. horník, m., šuňovská, a., pipíška, m., gubišová, m., gubiš, j., augustín, j.: phytofiltration of cd and zn by roots of vascular plants: effect of bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 16:05 utc nova biotechnologica et chimica 13-1 (2014) 47 metals speciation. proceedings of international conference of applied natural sciences 2011, faculty of natural sciences ucm, trnava 2011, 210-214. christensen, j.j, izatt m.r.: handbook of metal-ligand heats and related thermodynamic quantities. marcel dekker, new york, 1983, 783 pp. lindsay, w.l., w.a. norvell, w.a.: development of a dtpa soil test for zinc, iron, manganese, and copper. soil sci. soc. amer. j., 42, 1978, 421-428. martell, a.e.: stability constants of metal-ion complexes. the chemical society, london, 1964, 754 pp. mavrogianopoulos, g., vogli v., kyrisis, s.: use of wastewater as a nutrient solution in a closed gravel hydroponic culture of giant reed (arundo donax). bioresour. technol., 82, 2002, 103-107. mehlich, a.: mehlich-3 soil test extractant: a modification of mehlich-2 extractant. commn. soil sci. plant anal., 15, 1984, 1409–1416. mehlich, a.: determination of p, ca, mg, k, na and nh4. north carolina soil test division, raleig. 1953. no 1-53. murashige, t., skoog, f.: a revised media for rapid growth and bio assay with tobacco tissue cultures. physiol. plant., 15, 1962, 473-479. pilu, r., bucci, a., badone, f.c., landoni, m.: giant reed (arundo donax l.): a weed plant or a promising energy crop? afr. j. biotechnol., 11, 2012, 91639174. solov´ev, v., sukhno, i., buzko, v., polushin, a., marcou, g., tsivadze, a., varnek, a.: stability constants of complexes of zn2+, cd2+ and hg2+ with organic ligands: qspr consensus modeling and design of new metal binders. j. incl. phenom. macrocycl. chem., 72, 2012, 309-321. takahashi, w., takamizo, t., kobayahi, m., ebina, m.: plant regeneration from calli in giant reed (arundo donax, l). grassland sci., 4, 2010, 56224–56229. tessier, a., campbell, p.g.c., bisson, m.: sequential extraction procedure for the speciation of particulate trace metals. j. anal. chem., 51, 1979, 844-851. ure, a.m., quevauviller, p., muntau, h., griepink, b.: speciation of heavy metals in soils and sediments. an account of the improvement and harmonization of extraction techniques undertaken under the auspices of the bcr of the commission of the european communities. int. j. environ. anal. chem., 51, 1993, 1-4. van hullebusch, e.d., utomo, s., zandvoort, m.h., lens, p.n.l.: comparison of three sequential extraction procedures to describe metal fractionation in anaerobic granular sludges. talanta, 65, 2005, 549-558. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 16:05 utc nova biotechnol chim (2023) 22(1): e1384 doi: 10.34135/nbc.1384 1 nova biotechnologica et chimica control of magnetic susceptibility of probiotic strain lactobacillus rhamnosus gg svitlana gorobets1, oksana gorobets2, liubov kuzminykh1 1department of bioenergy, bioinformatics and environmental biotechnology, faculty of biotechnology and biotech engineering, national technical university of ukraine "igor sikorsky kyiv polytechnic institute", pr. peremohy 37, kyiv 03056, ukraine 2faculty of physics and mathematics, national technical university of ukraine "igor sikorsky kyiv polytechnic institute", pr. peremohy 37, kyiv 03056, ukraine  corresponding author: l.kuzminykh-2022@kpi.ua article info article history: received: 14th october 2021 accepted: 20th october 2022 keywords: iron chelate lactobacillus rhamnosus gg magnetic susceptibility magnetically-guided vector permanent magnetic field targeted drug delivery abstract the paper investigates the increase in the natural magnetically controlled properties of probiotic microorganisms lactobacillus rhamnosus gg (lgg) and their ability to form magnetically sensitive inclusions (msi). the magnetic susceptibility of lgg was increased by modifying the nutrient medium composition and by cultivating the probiotic culture in a constant magnetic field. therefore, this study can be useful for their further use as magnetically controlled vectors since it is being extensively researched for their use in targeted drug delivery in cancer treatment, for the prevention of chemotherapy complications, etc. the results of this study indicate that growing microorganisms with natural magnetically-guided properties in a modified medium with iron chelate and in an external magnetic field leads to an increase in the magnetic susceptibility of lgg by 1.8 and 2.6 times, respectively, compared with the control. the best magnetic susceptibility was recorded for lgg suspensions, which were grown in a constant magnetic field and cultured in modified medium with iron chelate. the lgg suspension, grown both in a constant magnetic field and on a modified medium with iron chelate, had the highest magnetic susceptibility, and it was 4.8 times larger than the magnetic susceptibility in the control. © university of ss. cyril and methodius in trnava introduction probiotics are used for treating and preventing diseases of the gastrointestinal tract (parian et al. 2018), strengthening the immune system (mendi et al. 2016), overcoming the effects of antibiotic therapy (saarela et al. 2000), for the prevention and treatment of tumor diseases (bedada et al. 2020; lamichhane et al. 2020), as vectors for targeted drug delivery (duong et al. 2019). in particular, studies show a number of advantages while using probiotic microorganisms as vectors comparing to other microorganisms that can have toxic effects on the body (zhou et al. 2018; laliani et al. 2020). the strain of lactic acid bacteria lactobacillus rhamnosus gg or l. rhamnosus atcc 53103 (lgg) is the most studied strains of probiotics due to its valuable properties. the microorganism colonises the gastrointestinal tract and thus protects against pathogens and increases the body's resistance to infections (capurso 2019). it is known that lgg is used as a vector in targeted drug mailto:l.kuzminykh-2022@kpi.ua nova biotechnol chim (2023) 22(1): e1384 2 delivery in the treatment of pathologies and tumors (tangney 2010; bedada et al. 2020). the use of probiotics as vectors for targeted drug delivery has a number of advantages, in particular, the noninvasiveness of probiotic cultures and the affinity for tumor tissue of some probiotic microorganisms (bedada et al. 2020). probiotic microorganisms can specifically target a tumor, causing intra-tissue regression (tangney 2010). in the last few years, the field of biotechnology and medicine has been intensively developing to create minimally invasive systems for the targeted delivery of drugs and genes using biohybrid microrobots – conjugates of bacteria, magnetic nanoparticles, and the target cargo (liposomes, etc.). such microrobots should possess highthroughput fabrication, efficient motility, tissue penetration, multifunctional operation, and external stimuli-responsive control (including control and trigger-triggered cargo release). magnetic nanoparticles in the composition of microrobots are used to provide the possibility of remote control by means of magnetic field application and, accordingly, targeted delivery to the target organ. many bacterial biohybrid microrobots suffer from low to moderate conjugation yields, with only a small fraction of cells carrying artificial cargo. in particular, since bacteria have a short doubling time (e.g., 20 min for wild-type e. coli under optimal conditions), some of the payload will be lost during the growth phase, which results in a loss of payload efficiency and weakens magnetic controllability over long periods of time. thus, for effective magnetic control in medical applications, a highperformance conjugation process and stability of the properties of microrobots for a long time are required. in addition to throughput, the conjugation approach should not adversely affect either the bacteria or the functional properties of the artificial media. in addition, as a result of conjugation, the large size of the microrobot can seriously hinder its mobility and thus affect the performance of the bacterial microrobot. the problem of increasing the motility of the bacterial microrobot is related to the difficulty of penetration of the bacterial vector through an environment with high density and hierarchical structure in real tumors (akolpoglu et al. 2022). a significant part of the biohybrid designs of microrobots reported in the literature have insufficient characteristics of mobility, stability, and controllability. in this regard, further investigation of the mechanical motility of bacteria in confined spaces is needed, together with the possibilities of artificial taxis, such as magnetophoresis, which may create more opportunities for effective penetration and transport of anticancer agents into solid tumors. microorganisms that synthesize biogenic magnetic nanoparticles (bmns) or magnetosomes can be used as magnetically-guided vectors to transfer a large number of therapeutic substances (kuzajewska et al. 2020). these microorganisms lack the disadvantages of bacterial biohybrids as their large size, insufficient stability, and loss of magnetic controllability over time. magnetotactic bacteria are the best-known producers of biogenic magnetic nanoparticles. the genetic apparatus of bmns biosynthesis is unique in all kingdoms of living organisms, as shown by genetic analysis (gorobets et al. 2014a). however, magnetotactic bacteria (mtb) are used with caution as bacterial vectors for drug delivery because their effect on living organisms is not fully studied and because of the lack of clinical trials and regulatory documentation (mathuriya 2015). also, mtb is difficult to cultivate and maintain viability since their habitat is significantly different from the internal environment of a human or animal organism (müller et al. 2020). bmns of nonmagnetotactic microorganisms have been studied in comparison with bmns of mtb (vainshtein et al. 2002 and 2014; gorobets 2012). bmns of nonmagnetotactic microorganisms are perspective as bacterial magnetically guided vectors because they manifest magnetophoresis in gradient magnetic fields (vainshtein et al. 2002 and 2014; gorobets and koralewski 2017). a number of probiotic and non-magnetotactic microorganisms can produce bmns, as summarized in the review of the experimental data (gorobets et al. 2014b). as a result, the use of probiotics that produce bmns and magnetically sensitive inclusions (msi) is a promising solution for this class of problems (vainshtein et al. 2002 and 2014). bacteria from the genus lactobacillus synthesize msi when grown on special media with the addition of ferric ions (ariskina 2003). also, magnetically-guided vectors based on lgg can have additional nova biotechnol chim (2023) 22(1): e1384 3 advantages, as they can control their velocity to the tumor site and are well concentrated in the desired area (mokriani et al. 2021). it is known that tumors can produce an increased amount of bmns compared to healthy tissues (brem et al. 2006; chekchun et al. 2011; gorobets 2017). magnetically-guided vectors are more efficiently attached to tumor cells and accumulate in the target area due to both aerotaxis to hypoxic regions of the tumor and magnetic dipole-dipole interactions of bacterial bmn and bmn of the tumor (mikeshyna et al. 2018; gorobets et al. 2022). magneticallyguided vectors in the tumor area can serve as a magnetic material for therapeutic magnetic hyperthermia, which together with the therapeutic effect of the delivered drugs, can increase the effectiveness of treatment several times (gorobets et al. 2013; felfoul et al. 2016). based on the above issues, the purpose of this work is as follows: the approach is developed increasing the magnetic susceptibility of bacterial vectors not due to loading (conjugation) with artificial magnetic nanoparticles but due to, firstly, the selection of bioinformatics methods of bacterial strains that have genetic mechanism of biomineralization of biogenic magnetic nanoparticles (bmn) and, secondly, due to the modification of the environment for growing bacteria (adding iron salts to the medium during cultivation) and growing conditions (applying an external magnetic field during cultivation) to activate the biomineralization mechanism of bmn. thus, the study of ways to control the magnetic susceptibility of lgg is relevant for the creation of magnetically-guided vectors based on the natural magnetically-guided properties of lgg. experimental physical methods and software the physical methods of the research were optic microscopy, magnetophoresis, and methods of magnetostatics. the scipy package of python programming language was used for the numeric simulation of magnetophoresis in bacterial agglomerates. cultivation of microorganisms the probiotic lyophilized drug acidolac® (1 sachet of the drug contains 4×109 cfu lactobacillus rhamnosus gg) was used for the study. pure cultures of microorganisms were isolated and cultured on lactobacilli-mrs agar medium. the microorganisms were cultured on the standard agar medium and modified medium with the addition of iron chelate for 48 h at a temperature of 36 ± 1 oc. lgg was grown on mrs medium prepared according to a standard recipe. the modified medium was prepared to enhance the natural magnetically-guided properties with the addition of iron chelate at a concentration of 64 mg.l-1. the media were prepared according to the recipe and sterilized by pressure in a steam sterilizer at 121 oc for 15 –20 min. the control group of microorganisms (lgg contr.) was grown on a standard medium under standard conditions. lgg was grown to enhance the natural magneticallyguided properties with modification of the cultivation conditions: grown on а standard medium in a constant magnetic field (lgg + m), grown on a modified medium with the addition of iron chelate (lgg + fe), grown on a modified medium with the addition of iron chelate in a constant magnetic field (lgg + fe + m). the purity of the lgg culture was checked by microscopic examination. research of microorganisms with a two-magnet system the magnetic susceptibility of the lgg suspension was investigated using a system of two magnets according to the method already described (wosik et al. 2018). a drop of suspension with a culture of microorganisms is applied to the glass located on the contact surface of the system of two permanent magnets. the system of two permanent magnets is created so that the highest gradient of the magnetic field is created in the area of their joint. the magnetic particles in the suspension move to the contact line of the magnets, forming a strip. magnetic susceptibility was studied in two ways: concentrating the bacterial suspension on the contact line to determine the width of the formed band and determining the velocity of cell agglomerates to the contact line of the system of two permanent magnets. nova biotechnol chim (2023) 22(1): e1384 2 bandwidth measurements of an lgg cell suspension formed at the contact surface of a system of 2 permanent magnets an aqueous suspension of probiotic strain lgg was applied to a 0.13 mm thick cover slide, placed on a two-magnet system until the liquid was completely dry to measure the width of the strip formed. after drying the product, the bandwidth of the suspension was evaluated using a digital microscope and a microline. series of digital microscope images were taken, and the average width of the formed strip was determined using the irfanview software. determination of the velocity and the average magnetic susceptibility of particles of the lgg suspension a drop of lgg suspension was applied to a glass placed on the contact surface of the system of two permanent magnets. the movement of conglomerates of lgg suspension was recorded on video using a digital microscope. the video was filmed in several repetitions to ensure the reliability of the results. microorganisms were taken from different parts of the petri dish, a suspension was prepared, and individual videos were made moving to the line of contact of the system of two permanent magnets. the experiment was repeated several times with separate generations of lgg cultures to obtain reliable results. an average of 15 videos were made for each type of microorganism cultivation. particles with similar sizes were selected, the motion of which was clearly visible in the video, for the experiments. the number of particles examined was: lgg contr. 57 particles, lgg + m 78 particles, lgg + fe 83 particles, lgg + fe + m 139 particles. particles were selected that were clearly visible, 40-110 μm in size, the average particle size was approx. 70 μm. the magnetic susceptibility of the lgg suspension was determined using python and the formulas in the section results and discussion. the program irfanview has been used to determine the particle movement (µm) to the contact line of the magnets and the particle diameter (µm). the time (s) of movement of the particle was determined by dividing the video into frames by the free video to jpg converter software. the average velocity (µm.s-1) of the particles was determined by dividing the path (µm) by the time (s) of movement of the particles to the contact line of the magnets. table 1 presents the physical parameters taken to determine the magnetic susceptibility of the lgg suspensions. table 1. physical parameters of the system that were used to calculate the average magnetic susceptibility of suspensions in the study with a system of two magnets. parameter dimension value, units saturation magnetization of magnets in a system of two permanent magnets ms 1600 g a dynamic viscosity of water η 0.01 g/(cm·s) magnet length a 0.65, cm glass thickness h 0.13, mm note: a the unit is part of the gaussian system of units or cgs-emu, 1 g = 10−4 tesla (si system). results and discussion determination of bandwidth and velocity of suspension particles lgg the microscopy of the studied of probiotic strain lgg is shown in fig. 1. the video files are linked to fig. 1: 1) the video file “l.rhamnosus gg contr”: the control group of microorganisms (lgg contr.) was grown on a standard medium under the standard conditions; 2) the video file “l.rhamnosus gg + fe”: lgg was grown to enhance the natural magneticallyguided properties with modification of the cultivation conditions grown on a modified medium with the addition of iron chelate (lgg + fe); 3) the video file “l.rhamnosus gg + m”: lgg was grown to enhance the natural magneticallyguided properties with modification of the cultivation conditions: grown on а standard 4 nova biotechnol chim (2023) 22(1): e1384 3 medium in a constant magnetic field (lgg + m); 4) the video file “l.rhamnosus +fe +m”: lgg was grown to enhance the natural magneticallyguided properties with modification of the cultivation conditions: grown on a modified medium with the addition of iron chelate in a constant magnetic field (lgg + fe + m). the cover glass with the bacterial culture was manually shifted several times during the video capture with the purpose to show magnetophoretic movement of bacterial agglomerates to the contact line of two magnets at several typical microscope fields. the method of video capture was the same as for video capture of the magnetophoretic movement of bacterial agglomerates in the reference (gorobets et al. 2023). a b fig. 1. probiotic bacteria l. rhamnosus gg, cultured from acidolac® on mrs medium (a). digital microscope examination of the magnetophoretic mobility of l. rhamnosus gg: a system of two permanent magnets is presented, where a cover glass with a culture concentrating on the contact line is located on top (b). fig. 2 shows a preparation from a suspension of lgg, placed over a system with two magnets. the images show the conglomerates of bacterial cells located along the contact line of the magnetic system. a b c d fig. 2. stripes from a suspension of probiotic strain l. rhamnosus gg, which formed above the contact line of the system of two magnets: lgg contr. (a), lgg +m (b), lgg + fe (c), lgg + fe + m (d). 5 nova biotechnol chim (2023) 22(1): e1384 3 wider and less branched strips form above the contact line when the natural magnetically-guided properties of the lgg culture are enhanced by iron ions and a constant magnetic field. the strip that is formed after cultivation under standard conditions (lgg contr.) is thin, indistinct, with gaps and branches, many particles are not on the line of contact and do not move towards the line. the strip, formed by cultivation in a constant magnetic field (lgg + m) is distinct along its entire length but rather branched; a certain number of suspension particles do not move towards the contact line. the strip that is formed after cultivation on a modified medium with iron chelate (lgg + fe) is somewhat narrower compared to the strip formed by lgg + m. the strip formed for lgg + fe on the contact line of two magnets is distinct, rather uniform, the particles are concentrated on the line, therefore, they form a denser strip with few branches; there are few particles that remain outside the strip and do not move towards the contact line. the strip for lgg + fe is narrower than the strip for lgg + m due to the fact that the particles are more densely concentrated on the contact line. the strip formed during cultivation on a modified medium with the addition of iron chelate and in a constant magnetic field (lgg + fe + m) is the widest strip compared to the strips formed for other cultivation conditions. a distinct, wide strip is formed for lgg + fe + m rather homogeneous and has few branches; few particles remain outside the strip and do not move towards the contact line. fig. 3 shows the results of the average velocity of particles at the line of contact of the system of two magnets. the average velocity (µm.s-1) of the particles was obtained by dividing the path of the particle by time. fig. 3. dependence of the average velocity of the particles in the suspension of l. rhamnosus gg depending on the cultivation conditions. the statistical significance of the results is 0.95. the results in this paper show that the speed of the suspension particles in the two-magnet system increased as the growing conditions changed, and the culture medium was modified. calculation of the magnetic susceptibility of the suspension lgg the main idea of modifying the magnetic properties of bacteria with natural magnetically guided properties is to grow these bacteria under special conditions, namely with the addition of iron chelates to the environment and under the application of an external constant magnetic field during cultivation. this idea is based on experimental data on the influence of cultivation conditions on the amount of bmns in magnetotactic bacteria. the bmns of magnetotactic bacteria increase up to several times due to an increase in the concentration of iron ions in the cultivation medium and the application of an external magnetic field with an induction of about 0.1 t during cultivation. the magnetic susceptibility of the biomass of magnetotactic 6 nova biotechnol chim (2023) 22(1): e1384 2 bacteria also increases (wang et al. 2009). according to gorobets et al. (2014b) and mokriani et al. (2021), it can be assumed that the same influencing factors that regulate the amount of bmns in magnetotactic bacteria will similarly affect the number of bmns and the magnetic susceptibility of non-magnetotactic bacteria with natural magnetically-guided properties. in addition, the novelty of this work is the choice of nonmagnetotactic bacteria with natural magneticallyguided properties that are used as vectors for drug delivery (zhou et al. 2018; bedada et al. 2020). in recent years, methods for creating strong magnetic fields have been intensively developed using systems of highly anisotropic permanent magnets connected in such a way that the directions of the magnetization vectors of these magnets are different at the boundary between them. in this case, strong magnetostatic fields are created at the "sharp angles" of each of the magnets, having a logarithmic divergence at certain points in space. this divergence is not distorted due to the bending of the magnetization vector, if the material from which the magnet is made has a large magnetic anisotropy. akhiezer et al. (1968) and samofalov et al. (2004; 2013) calculated the divergence of the tangential component of the magnetic field outside a uniformly magnetized rectangular parallelepiped. the magnetostatic field increases logarithmically when approaching the edges of the parallelepiped and can exceed the value that is the limiting value for permanent magnets of traditional designs. fig. 4 presents an option of implementation of this idea. the combination of several highly anisotropic ferromagnets of various shapes with different directions of magnetization in one magnet to create strong magnetic fields near their common "sharp angle". fig. 4 presents a magnet where two ferromagnets are connected in such a way that one of them is magnetized along the axis and the other one in the opposite direction. the expression for the tangential component of the magnetostatic field for the kittel’s domain structure of two magnets has the form (eq. 1) (akhiezer et al. 1968; samofalov et al. 2004 and 2013): (1) where contains a logarithmic divergence at z = 0 and . a b fig. 4. scheme of kittel's open domain structure of two magnets (a). schematic representation of magnetic poles of the kittel's open domain structure of two magnets (b): red – south pole, blue – north pole. therefore, a magnet of this shape, made of highly anisotropic material, can be used to create strong magnetic fields in localized volumes of space. the normal component of the magnetostatic field for the kittel’s domain structure of two magnets has the form (eq. 2) (samofalov et al. 2004 and 2013): (2) analysis of the existing theories of particle deposition in a gradient magnetic field has revealed that the theory of magnetophoresis of paraand diamagnetic particles in high-gradient fields has been quite fundamentally developed. the choice of a model to describe the efficiency of the magnetic separator depends on the size of the particles that must be isolated from the working medium. there are two approaches which depend on particle size (more or less some critical size), the particle approach and the continuous medium approach. the continuous medium approach is used to model 7 nova biotechnol chim (2023) 22(1): e1384 3 the separation of particles, usually less than one micron in size. the statistical method is used when it is impossible to estimate the spontaneous brownian motion of each particle and the suspension is considered as a continuous medium. the particle approach gives good results for particles of sufficient size to be neglected in brownian motion. the model using the particle approach was first developed in (friedlander et al. 1981; plyavin’ and blum 1983; vincent-viry et al. 2000; gorobets and mikhailenko 2014). this model takes into account only the gradient magnetic force and the force of hydrodynamic resistance . the force of inertia is neglected, and the balance of forces is written in the following form (eq. 3 and 4): (3) (4) – the strength of the magnetic in the working volume of the magnetic separator, – effective magnetic susceptibility, which is equal to the difference between the susceptibilities of the liquid and the particle , the volume of the particle. the gradient of the magnetic force is directly proportional to the gradient of the magnetic energy density. thus, if the field is locally homogeneous, it means that no force acts on the particles. a nonzero gradient magnetic force exists in an inhomogeneous magnetic field. if the motion can be characterized by small reynolds numbers, the stokes force acting on a spherical particle has the form (eq. 5): (5) assuming that the shape of a particle trapped in an inhomogeneous magnetic field is a sphere of radius which is moving in a liquid with dynamic viscosity , the velocity difference between liquid and particle in a stationary medium. b is the radius of bacterial cell agglomerates in magnetophoretic experiments, in the case of b about 3 microns, the estimated value of the ratio b/a is about 0.001. however, the numeric simulation of mag/netophoresis of the agglomerates of bacterial cells was carried out not for the estimated value of b/a but for an exact one based on the measurement of the radius of every bacterial cell agglomerate using video recording of optic microscopy of magnetophoretic movement of bacterial agglomerates. the capture process is determined as a result of the competition between the magnetic force and the stokes force (friedlander et al. 1981). the magnetic field strength is described by expressions (eq. 1), eq. 2 in the case when an inhomogeneous magnetic field is created by a system of two magnets shown in fig. 4. we assume that a thin layer of liquid on the surface of the system of magnets is stationary, then the velocity of spherical particles in the liquid on the surface of the system of magnets along the axis, and the characteristic radius of the particle. eq. 3 can be converted to the next dimensionless form (eq. 6): (6) where dimensionless coordinates , , and and notation are introduced (eq. 7): (7) as a result of integrating eq. 7, we find the dimensionless time required for the particle to move in the magnetic field of the magnet system from a point with dimensionless coordinate to the line of contact of two magnets with dimensionless coordinate, as a function of dimensionless particle coordinates : (8) the suspension of particles sedimented in the gravitational field before being introduced into the magnetic field, therefore the dimensionless 8 nova biotechnol chim (2023) 22(1): e1384 2 coordinate of the particle was chosen for the calculation, where h is the thickness of the glass on the surface of the system of two magnets. this means that the center of the spherical particle is at a height above the surface of the magnet system equal to the radius of the particle with the addition of the thickness of the glass. it can be assumed with great accuracy that if . (9) calculation of the average dimensionless velocity of the particle along the axis in the region based on expression (eq. 10): (10) the dependence of average dimensionless velocity on x when z=0 is presented in fig. 5. fig. 5. dependence of the average dimensionless velocity of the particle on x at z=0.001 and at calculated by eq. 10. the average velocity of a particle measured in seconds is determined through the dimensionless average velocity by the formula (eq. 11): (11) the effective magnetic susceptibility of a particle moving in a liquid on glass on the surface of a system of two magnets can be determined from the last expression (eq. 12): (12) the dimensionless coordinate of the particle is chosen for calculation, as already mentioned: . the results of the calculation of the average effective magnetic susceptibility of particles depending on the cultivation conditions by formula (eq. 12) are presented in fig. 6. fig. 6. the average effective magnetic susceptibility of the particles of the l. rhamnosus gg suspension depending on the cultivation conditions according to formula eq. 12. the error was determined using the sdm. the statistical significance of the results is 0.95. the approach of increasing of magnetic susceptibility of bacteria for drug delivery applications proposed in this work has the following advantages compared to methods based on conjugation: • in this approach, the rapid division of bacteria does not lead to the loss of increased magnetic susceptibility by daughter cells, so a homogeneous and stable process of distribution 9 nova biotechnol chim (2023) 22(1): e1384 3 of magnetic susceptibility in the bacterial culture occurs. • the size of the bacteria in this approach does not change, so the mobility of the bacterial vector is not reduced, which will facilitate the penetration of the bacterial vector through the environment with high density and hierarchical structure in real tumors. • the proposed approach is also promising as the first stage of creating a bacterial vector with increased magnetic susceptibility, with the aim of further using the method of conjugation with magnetic nanoparticles or magnetoliposomes. in this case, the magnetodipole interaction between the bmn of the bacterial vector and artificial magnetic nanoparticles will create additional magnetic forces that bind this nanocomposite. conclusion the results show that the speed of the suspension particles in the two-magnet system increased as the growing conditions changed and the culture medium was modified. the effective magnetic susceptibility for the lgg control sample is (0.25 ± 0.03) × 10-7. the magnetic susceptibility of the lgg bacterial culture growing in a constant magnetic field was 1.8 times greater in comparison with the magnetic susceptibility for the control sample. the magnetic susceptibility of the lgg bacterial culture growing at the medium modified with iron chelate was 2.6 times greater in comparison with the magnetic susceptibility for the control sample. the magnetic susceptibility of the lgg bacterial culture growing at the medium modified with iron chelate in a constant magnetic field was 4.8 times greater in comparison with the magnetic susceptibility for the control sample. thus, modification of the growth medium with iron chelate and/or cultivation in a constant magnetic field improves the ferrimagnetic properties of the bacterial culture lgg, which can be useful in creating vectors of magnetically-guided delivery. a significant increase in the magnetic susceptibility of lgg bacterial culture was observed when both methods are used together i.e., modification of the medium with iron chelate and cultivation in a constant magnetic field. conflict of interest the authors declare that they have no conflict of interest. references akhiezer ai, barʹyakhtar vg, peletminskii sv (1968) spin waves. amsterdam, north-holland pub. co. akolpoglu mb, alapan y, dogan no, baltaci sf, yasa o, tural ga, sitti m 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133 comparison of ten biochemical laboratory tests before and after treatment by statins tatiana ďurčeková1, ján mocák1*, ján balla2, gabriela gromanová2, katarína boronová1 1department of chemistry, university of ss. cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic (tatiana.durcekova@ucm.sk) 2analytical-diagnostic laboratory, kováčska 15, prešov, sk-080 01, slovak republic (jan.balla@mail.t-com.sk) abstract: results of 10 biochemical tests of 172 patient data (among them 84 men data and 88 women data, resp.) before and after administration of statins were thoroughly studied. all monitored patients are characterized by disorders of lipoprotein metabolism or other kind of dislipidaemia. the calculations were performed using four chemometrical methods facilitating quantification and visualization of the statin effect upon most important biochemical parameters, mainly lipid markers, and allowing classification of the patient blood samples taking into account whether the patient has been or has not been medicated by a statin drug. key words: cardiovascular risk, lipid markers, statins, roc curves, anova, knn classification. 1. introduction at the present state of medicine the patients with coronary heart disease (chd) may require intensive drug therapy usually realized by hypolipidemic drugs like statins. the number of individuals who are candidates for lipid-lowering therapy by statins has continued to increase. statins are chemically and pharmacologically diverse class of drugs that lower cholesterol levels in people with or at risk of cardiovascular disease by inhibiting the enzyme hmg-coa reductase, which is the rate-limiting enzyme of the cholesterol synthesis (wierbzbicki et al., 2003; laws et al., 2004; kinlay et al., 2005; deambrosis et al., 2009). statins, the most widely prescribed medications in patients with hyperlipidaemia and coronary heart disease, have a number of pleiotropic actions beyond cholesterol lowering. they improve endothelial function, they have antioxidant and anti-inflammatory effects, they regulate neovascularization and have immunomodulatory activities (kwak et al., 2003; tousoulis et al., 2007; blum et al., 2009). the first part of the results dealing with most important and frequent biochemical tests of 172 patients (among them 84 men and 88 women, respectively) before and after administration of statins and processed by basic chemometrical procedures were given in our previous paper (durcekova et al., 2009). in this work, further techniques of laboratory data processing were applied to inspect a diverse influence of the statin administration upon blood serum levels of the selected biochemical parameters. several statistical/chemometrical tools have been here newly applied: (a) 134 ďurčeková, t. et al. the box-plot representation of the statin drug effect, (b) the comparison of efficiency of the selected variables (biochemical tests plus patient’s age) by means of receiver operating characteristic curves (roc) analysis and gini indices, (c) one-way analysis of variance (anova) demonstrating whether the selected variable is significantly changed with the statin administration, (d) the k-th nearest neighbour (knn) pattern recognition technique used for classification of the patient samples before and after statin administration. this, rather complex approach allows investigate the statin effects on the patient’s status from a different point of view. 2. material and methods 2.1 description of the analyzed biochemical data serum level of the selected biochemical tests was analytically determined for 172 probands (individuals) who were characterized by failure of their lipoprotein metabolism or another kind of lipidaemia. two data matrices were investigated containing the test results for: (1) 84 men samples, and (2) 88 women samples, which represent the rows of the investigated data matrix. its columns contained 12 monitored variables, namely 5 lipid parameters total cholesterol (tchol), high density lipoprotein cholesterol (hdlc), low density lipoprotein cholesterol (ldlc), triacylglycerols (tg), aterogenity index (ai) – obtained by the following calculation: (tchol – hdlc)/hdlc, 6 standard biochemical parameters creatinine (crea), aspartate aminotransferase (ast), alanine aminotransferase (alt), alkaline phosphatase (alp), creatinine kinase (ck), and gamma-glutamyl transferase (ggt), and, finally, the age of the patient as the last variable. all mentioned variables were measured before statin administration and one year after it. 2.2 multidimensional data analysis multidimensional data analysis was performed using three software packages: (1) minitab 15 was utilized to perform box-plots, (2) spss 15.0 was used to perform roc analysis and anova and (3) knn was carried out using software package sas enterprise guide 3.0. 3. results and discussion 3.1 comparison of selected biochemical parameters using box-plots box-plots (or box-and-whisker plots) are useful for the comparison of different groups of one-dimensional data. its construction allows a visual representation of the data (massart et al., 1997). the box itself covers inner 50 % of all data values, starting from the lower quartile (25 % of the ordered data) and ending by the upper quartile (75 % of the ordered data); the whiskers, represented by the abcisses, cover the lowest and highest part of the data representing the given variable. the line across the box represents the median. based on known categorization of probands, divided into two categories before and after administration of statins, a comparison of the blood serum levels of the nova biotechnologica 9-2 (2009) 135 studied variable before and after administration of statins was visualized using boxand-whisker plots and demonstrated for all studied variables. in addition, some multicomponent variables, namely pc1 (the first principal component), df1 (the first discriminate function) and logit (the dependent variable in logistic regression) are also shown and compared to individual biochemical tests. the mentioned multicomponent variables were calculated by linear combinations of all original variables by principal component analysis, discriminant analysis and logistic regression (durcekova et al., 2009). further details of these multivariate techniques can be found in khattree et al., 2000; jolliffe et al., 2002; kleinbaum et al., 2005. it is demonstrated in fig. 1 that the selected two categories of probands are relatively well separated in case of variables ldlc, tchol and ai for the men samples and ldlc and tchol for the women samples. nevertheless, it is evident that the best separation of two categories is achieved when using multicomponent variables df1 and logit for the men samples and df1, logit and pc1 for the women samples. the effective utilization of the multicomponent variables in prediction and/or confirmation of clinical diagnosis was discovered in our previous works (balla et al., 2004; mrazova et al., 2009). a minor difference of hdl cholesterol between treated and untreated patients were expected. the change in box-plots of six standard biochemical parameters with the statin treatment was not significant. 3.2 roc analysis the predictive value of an assay can be displayed in the form of a plot of sensitivity against (1 specificity), where sensitivity and specificity are defined in the way common in clinical chemistry (mocak et al., 2003). the area under the corresponding curve, a, is defined between 0.5 (the diagonal line on the roc diagram represents an assay with a zero predictive value and corresponds to 50 % of the total area) and 1.0 (absolutely successful laboratory test corresponds to the total area) (massart et al., 1997; balla et al., 2004). in the roc analysis, the original laboratory variables as well as the multicomponent variables pc1, df1 and logit were used. the variables with the largest roc curve area are shown in fig. 2, which demonstrates that the areas belonging to logit and df1 are clearly larger compared to the best original variables (tchol, ldlc, ai). among the original variables, the most significant statin effect exhibit tchol, ldlc, ai, tg and hdlc for the men samples and tchol, ldlc, ai and tg for the women samples with the roc area greater that 0.6. the observed independence of six standard biochemical parameters characterizing liver and/or renal function upon statin treatment was anticipated and confirmed. an alternative, new-fashioned comparison of the statin effect upon 11 investigated variables is surveyed in table 1 containing gini coefficients, g, defined by means of the roc curve area, a, in the more convenient interval (0, 1): g = 2 a – 1 (1) it is worth noting that negative values of gini coefficients are insignificant since they were caused by calculation errors and denote in fact zero. 136 ďurčeková, t. et al. fig. 1. comparison of the box-and-whisker plots for the best laboratory tests and multicomponent variables df1, pc1 and logit by box-and-whisker plots constructed using 10%, 25%, 50%, 75% and 90% percentiles of the ranked variable. b − blood serum samples before statin uptake, a − after the uptake. men samples are located in the left frame, women samples are in the right frame. software minitab 15.1.0.0. ab 1 .6 1 .2 0 .8 h d l ab 2 .4 1 .6 0 .8 h d l ab 6 4 2 a i ab 5 3 1 a i ab 6 4 2 l d l ab 6 4 2 l d l ab 4 0 -4 p c 1 ab 4 0 -4 p c 1 ab 1 0 0 -1 0 l o g it ab 1 0 0 -1 0 l o g it ab 2 0 -2 d f 1 ab 4 0 -4 d f 1 nova biotechnologica 9-2 (2009) 137 fig. 2. roc curves for the best biochemical parameters tchol, ldlc, ai and tg, and multicomponent variables df1, logit and pc1 selected by the largest area under the curve. 88 women samples. software spss 15.0. table 1. effect of statin administration on all investigated variables (laboratory as well as multicomponent ones) expressed by gini coefficients. men women variable a g variable a g df1 0.949 0.898 logit 0.973 0.946 logit 0.935 0.870 df1 0.968 0.936 tchol 0.931 0.862 tchol 0.940 0.880 ldlc 0.921 0.842 ldlc 0.880 0.760 pc1 0.892 0.784 ai 0.748 0.496 ai 0.798 0.596 pc1 0.710 0.420 tg 0.713 0.426 tg 0.676 0.352 hdlc 0.629 0.258 hdlc 0.562 0.124 crea 0.529 0.058 alt 0.598 0.196 alt 0.512 0.024 alp 0.533 0.066 ast 0.509 0.018 gmt 0.517 0.034 alp 0.501 0.002 ast 0.512 0.024 gmt 0.490 -0.020 crea 0.509 0.018 ck 0.446 -0.108 ck 0.443 -0.114 3.3 analysis of variance the goal of analysis of variance, anova, is to divide the total variance of the given variable into their appropriate components in order to discover whether the variable is significantly affected by the selected factor, which represents the outcome of the investigated problem (massart et al., 1997). this factor is represented by a categorical variable, named here as statmw and indicating whether the treatment by statins was carried out (after drug administration) or not (before) and if the patient is a 138 ďurčeková, t. et al. man or a woman: 1 – men before drug administration, 2 – men after the drug treatment, 3 – women before the treatment, 4 – women after the treatment. two posthoc anova tests were applied: the least significant difference (lsd) test found out the variables tchol, ldlc, tg and ai capable to separate the categories 1 from 2 and 3 from 4 (which is the main goal), eventually also 1 from 4 and 3 from 2; bonferroni test provided the same results. the selection of the most important anova outputs is summarized in table 2 where only the significant categories combinations are included. table 2. anova outputs showing only those variables and categories i and j, which are significantly influenced by the statin treatment (with the significance p-value less than 0.05). multiple comparison 95% confidence interval dependent variables (i) (j) mean difference (i-j) stand. error sig. lower bound upper bound tchol 1 2 1.567 0.172 0.000 1.228 1.905 1 4 1.746 0.170 0.000 1.411 2.081 3 2 1.489 0.170 0.000 1.154 1.824 3 4 1.668 0.168 0.000 1.337 1.999 ldlc 1 2 1.243 0.156 0.000 0.936 1.550 1 4 1.431 0.154 0.000 1.128 1.735 3 2 1.061 0.154 0.000 0.758 1.365 3 4 1.250 0.152 0.000 0.950 1.550 tg 1 2 0.555 0.169 0.001 0.226 0.888 1 3 0.478 0.167 0.005 0.150 0.807 1 4 0.879 0.167 0.000 0.551 1.208 3 1 -0.478 0.167 0.005 -0.817 -0.150 3 4 0.401 0.165 0.016 0.076 0.726 ai 1 2 0.908 0.179 0.000 0.555 1.260 1 3 0.916 0.177 0.000 0.567 1.265 1 4 1.657 0.177 0.000 1.308 2.006 3 1 -0.916 0.177 0.000 -1.265 -0.567 3 4 0.741 0.175 0.000 0.396 1.086 significance level is expressed by p-values rounded to 3 decimal figures; the mean difference is considered significant when p < 0.050. categories: 1 – men before drug administration, 2 – men after drug administration, 3 – women before drug administration, 4 – women after drug administration. software spss 15.0. 3.4 knn classification k-th nearest neighbour, knn, is a non parametric discrimination technique (khattree and naik, 2000) very useful for classification purposes, which does not need any assumption on the distribution of errors. the main variant of this technique is based on the majority vote rule, which means that k neighbour objects, nearest to the classified object, are searched and then the classification of the given object is made according to which class the neighbour objects are predominantly classified. nova biotechnologica 9-2 (2009) 139 knn results were evaluated by the successful classification in % for (a) the training set, from which the classification model is calculated, and for (b) the samples leaved out from the training set by leave-one-out method, which is most important for prediction purposes. it is shown in table 3 that the best classification performance was achieved when using seven nearest neighbours (k = 7) for the men samples and eleven for the woman samples. table 3. classification results by knn method; k = 5 – 11. k results model leave-1-out true/all 69/84 64/84 5 % true 82.1 76.2 true/all 69/84 66/84 7 % true 82.1 78.6 true/all 70/84 64/84 9 % true 83.3 76.2 true/all 69/84 63/84 m 11 % true 82.1 75 true/all 76/88 70/88 5 % true 86.4 79.5 true/all 75/88 73/88 7 % true 85.2 82.9 true/all 76/88 73/88 9 % true 86.4 82.9 true/all 76/88 75/88 w 11 % true 86.4 85.2 m – men samples, w – women samples 4. conclusions positive changes in lipid metabolism after statin treatment of the patients with cardiovascular risk can be unambiguously discovered and monitored by means of statistical and chemometrical techniques, which provide qualitative as well as quantitative judgment, which laboratory parameters are mostly affected by the administration of statin drugs. in this work, box-and-whisker plots and roc curves allowed visualization of the statin effects. knn classification method allowed a clear discrimination of the patients’ samples into two categories – before and after statin treatment. analysis of variance revealed that four variables are capable to differentiate the statin treatment with regard to the patient gender: aterogenity index, low density lipoprotein cholesterol, total cholesterol and triacylglycerols. high density lipoprotein cholesterol as well as all further investigated biochemical parameters were not efficient in differentiating neither men nor women groups before and after statin treatment. a special feature of the achieved results is a very high diagnostic effectiveness of the multicomponent variables composed by linear combination of individual laboratory assays, which predestinates their further utilization in cardiovascular risk confirmation and prediction. there may be considered two potentially serious side effects of statins of which patients need to be aware. occasionally, statin use cause an increase in liver enzymes. if the increase is severe, the patient may need to stop taking the drug, which usually 140 ďurčeková, t. et al. reverses the problem. if there is no increase or it is only mild, one can continue to take the drug. in general, our study has not proved a significant change in the level of liver enzymes with the statin uptake. such an effect should be individually assessed and perhaps further investigation should be made aimed to evaluating the mentioned side effects. acknowledgement: the support of this work by the grants vega 1/1005/09, vega 1/0066/09 and vvce-0004-07 is acknowledged. references balla b., mocak j., pivovarnikova h., balla j.: comparative study of cardiovascular markers data by various techniques of multivariate analysis. chemom. intell. lab. sys., 72, 2004, 259-267. blum a., shamburek r.: the pleiotropic effect of statins on endothelial function, vascular inflammation, immunomodulation and thrombogenesis. atherosclerosis, 203, 2009, 325-330. deambrosis p., terrazzani g., walley t., bader g., giusti p., debetto p., chinellato a.: benefit of statins in daily practise? a six-year retrospective. pharmacol. res., 2009 (in press). durcekova t., mocak j., balla j., gromanova g., boronova k.: relationship between administration of statins and blood serum levels of selected biochemical parameters. nova biotechnol., 9, 2009, 83-90. laws p.e., spark j.i., cowled p.a., fitridge r.a.: the role of statins in vascular disease. eur. j. vasc. endovasc. surg., 27, 2004, 6-16. jolliffe i.t.: principal component analysis, springer-verlag, new york, 2002, 487 pp. kinlay s.: potential vascular benefits of statins. am. j. med., 118, 2005, 625-675. kleinbaum d.g., klein m., pryor e.r.: logistic regression, springer, heidelberg, 2005, 282 pp. khattree r., naik d.n.: multivariate data reduction and discrimination. sas institute, cary, north carolina, 2000, 558 pp. kwak b., mulhaupt f., mach f.: atherosclerosis: anti-inflammatory and immunomodulatory activities of statins. autoimmun. rev., 2, 2003, 332-338. massart, d.l., vandeginste, b., buydens, l., de jong, s., lewi, p., smeyers-verbeke, j.: handbook of chemometrics and qualimetrics, part a, elsevier, amsterdam, 1997, 886 pp. mocak j., balla b., bobrowski a., blazicek p.: proper ways of comparison of two laboratory methods. chem. pap., 57, 2003, 143-146. mrazova v., mocak j., varmusova e., kavkova d., bednarova a.: use of multidimensional data analysis for prediction of lung malignity. j. pharm. biomed. anal., 50, 2009, 210-215. tousoulis d., charakida m., stefanadi e., siasos g., latsios g., stefanadis c.: statins in heart failure. beyond the lipid lowering effect. int. j. cardiol., 115, 2007, 144-150. wierzbicki a.s., poston r., ferro a.: the lipid and non-lipid effects of statins. pharmacol. therapeut., 99, 2003, 95-112. nova biotechnologica et chimica 11-2 (2012) 147 doi 10.2478/v10296-012-0017-9 © university of ss. cyril and methodius in trnava the possibilities of application of bacterial leaching in retrieval of valuable metals from mining waste peter fečko1, vojtěch zechner1, michal guziurek1, barbora lyčková2, eva pertile2 1všb-tu ostrava, institute of clean technologies for extraction and utilization of energy resources, 17.listopadu street 15, 708 33 ostrava, czech republic, (vojtech.zechner@vsb.cz) 2všb-tu ostrava, institute of environmental engineering, 17.listopadu street 15, 708 33 ostrava, czech republic abstract: the paper deals with an application of bacterial leaching on two selected samples from old ecological loads situated in the karlovy vary region. to be specific, they are heaps in prebuz and kraslice. bacterial leaching was applied making use of acidithiobacillus ferrooxidans bacteria and lasted 28 days. the results imply that the given method is suitable for the retrieval of valuable metals from waste and may help to deal with the issue of old heaps and dumps. keywords: bacterial leaching, acidithiobacillus ferrooxidans, mining waste heaps 1. introduction mining of mineral resources and utilization of lithospheric sources always represent a substantial interference with the geological conditions in any territory. mining endangers both the deposits and the natural environment. it causes decreases in the land resources, destruction of the vegetation cover, damage to the agricultural, forest and water management, destruction of settlements, worse environmental conditions and results in the anthropogenic georelief (bosecker, 1997; závada and bouchal, 2010). the major manifestations of the influence on the geomorphology by mining are anthropogenic movements caused by undermining, changes in the georelief (miming forms), influence of mining and waste on the landscape (removal of overburden, heaps, preparation tailings), pollution by preparation processes, collapse of quarry slopes and induced bursts (brombacher et al., 1997; fečko et al., 2004). the remediated anthropogenic forms of landscape georelief may have various functions: protected natural phenomenon, non-toxic waste disposal site, agriculturally cultivated fields, recreation-sports facilities (playgrounds, swimming) or may be used as car parks, etc (ledin and padersen, 1995). a collected evaluation of the environmental impacts of abandoned mine workings (predominantly for mining of building materials, ores, coal and uranium) in the cr showed that out of 2,000 mine workings in the cr 79 % of them do not influence the environment in any way, more than 20 % only marginally and with no long-term consequences. mere 0.5 % of mine workings are critical, with hazardous wastes, slag, contaminants, etc. it is surprising that only mining causes 1/3 of the unfavorable influence on the natural environment. the prevailing part is of a different bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 13:12 utc 148 fečko, p. et al. origin (unauthorized waste disposal sites, etc.). the consequences of mining are effaced by the auto-regulative powers of the nature with no human intervention only in a low extent. from this point of view, it is necessary to project the environmental settlement for using lithospheric sources into the gross domestic product calculation system. as mentioned above, any extraction of mineral resources produces waste along with the major component. this waste is usually called mining waste. for example, it is waste rock, spoil, preparation tailings, etc. this waste is usually disposed of on heaps and dumps. however, it is often the case that the waste may be rich some elements, e.g. copper, gold. in the past, the elements remained unused because of economic intensity of their retrieval, but at present various methods tend to be applied to retrieve the valuable elements. recently, one of the most effective methods has been bacterial leaching (torma, 1997; maršálek, 1979; borovec, 1989; crundwell et al., 2000; boom, 2001; kraus, 2006; fečko et al., 2008). the objective of the work is to identify what elements in which quantities are to be found in the samples from the above mentioned heaps related to extraction of copper and tin in the karlovy vary region and how to extract them by means of bacterial leaching. 2. materials and methods 2.1. characteristic of the locality prebuz and kraslice in the work two samples are described, namely from the locality of prebuz and the locality of kraslice. fig. 1 shows the geological characteristic of the locality of prebuz and kraslice. fig. 1. locality of prebuz and kraslice. prebuz is found in the district of sokolov, in the karlovy vary region. the mining locality is 1 km southwestwards from prebuz at the foot of the hartelsberg hill. there is the most important tin district in the region. there are remnants of extensive mining and preparation activities from the 16th – 20th century, e.g. shaft otto, the main shaft with a shaft frame construction in good repair (technical monument), 45 rows of cave-ins – surface depressions, drift entrance, heaps of as-mined ore and waste rock, ore preparation plant frame, sludge ponds, tin placers and a lade. on the heaps there are granites in the karlovy bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 13:12 utc nova biotechnologica et chimica 11-2 (2012) 149 vary pluton (earlier intruded complex), ore mineralization (sn-greisens and several generation veins with ore mineralization of sn, as, w, fe, mn, u, etc. rare minerals can be found there (topaz, opal, secondary minerals of as, cu, bi, u, etc.). it is a locality of supraregional importance to do research in the genesis of tin deposits of the greisens type. from the regional zoning point of view, it is the bohemian massif, crystalline complex and prevariscan paleozoic – saxothuringicum, ore mountains pluton. as for stratigraphy, they are igneous rocks of a hercynian age. figures 2 shows the character of the drawn samples from both the localities. fig. 2. character of the sample after its drawing from the locality of kraslice (a) and prebuz (b). 2.2. mineralogical characteristics of the samples the mineralogical analyses were implemented using an x-ray analyzer in the laboratories of the institute of geological engineering of vsb-tu ostrava. the results imply that the kraslice sample contains barite, cerussite, galena and quartz. the prebuz sample contains muscovite and chlorite. tables 1 and 2 state the percentages of the individual minerals in the tested samples. table 1. mineralogical composition of the kraslice sample. composition ratio (%) barite 56.4 ± 3.0 cerussite 2.4 ± 1.1 galena 2.9 ± 0.7 quartz 38.3 ± 3.0 table 2. mineralogical composition of the prebuz sample. composition ratio (%) chlorite llb-2 20.2 ± 9.6 muscovite_2m1 79.8 ± 9.6 2.3. methodology of bacterial leaching samples of 100 % grain-size below 0.071 mm were prepared for bacterial leaching. a pure bacterial culture of acidithiobacillus ferrooxidans was applied, coming from the czech collection of microorganisms in brno. a 5-litre bioreactor was used, into which 500 ml of the bacterial culture were poured, followed by the tested samples and then bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 13:12 utc 150 fečko, p. et al. silverman medium 9k was added. stirring in the bioreactor was ensured by means of aquarium pumps. the ph value of the solution was maintained at the range from 1.8 to 2.0 by means of 1m sulfuric acid during the overall experiment. bacterial leaching was conducted at the laboratory temperature of 20 °c. the time of the experiment was 28 days and having finished the experiment, the samples were analyzed on an x-ray fluorescence analyzer. 3. results and discussion the evaluated test results are summarized in tables 3 and 4. the stated results revealed that the highest recovery of cu and pb, over 40 %, was obtained in the sample from kraslice. from the presented results it is clear that the recovery with bacterial leaching depends on the primary concentration of an element in the waste rock. of toxic elements, as exhibited variable behavior during leaching by acidithiobacillus ferrooxidans; the ability of the element to be released is probably connected with the original concentration of the element in the waste rock (fig. 3). table 3. results of bacterial leaching of the kraslice sample. element prior to leaching (ppm) post leaching (ppm) recovery (%) ca 3686 3572 3.1 ti 116102 112663 2.7 cr 3342 2944 11.9 mn 1653 1085 34.4 fe 7148 5383 24.7 ba 414756 330033 20.4 cu 5332 3040 43.0 zn 1545 1338 13.4 as 2752 2456 10.8 pb 87988 48557 44.8 sr 3099 2834 8.6 sn 738 0.001 99.9 v 18849 17908 5.0 table 4. results of bacterial leaching of the prebuz sample. element prior to leaching (ppm) post leaching (ppm) recovery (%) ca 17801 15164 14.8 ti 9637 1774 81.6 cr 680 0.001 99.9 mn 1680 1300 22.6 fe 234998 148019 37.0 ba 7947 0.001 99.9 cu 2447 0.001 99.9 zn 3606 300 91.7 as 207 74 64.3 pb 1669 0.001 99.9 sr 89 18 79.8 sn 2988 0.001 99.9 the dependence of the concentration of elements in the waste rock on the recovery with bacterial leaching shows a power trend with a high value of the correlation bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 13:12 utc nova biotechnologica et chimica 11-2 (2012) 151 coefficient, i.e. > 0.98. the activity of the bacteria may be affected by a relatively high concentration of toxic as in the environment of the bioreactor (stolz et al., 2006). in the case of the přebuz sample, better results were obtained; the concentration of metals in the waste rock was very low. the recovery was high, almost 100% in the majority of the elements, except for fe and mn. fig. 3. relationship between recovery of elements (as, cu) during bacterial leaching and concentration of elements in waste rock. 4. conclusion the objective of the work was to test bacterial leaching using waste material samples from the localities of kraslice and prebuz applying the bacteria of acidithiobacillus ferrooxidans. the obtained results imply that the given technology is suitable for the waste material drawn from the locality of prebuz. in case of the slag material from the locality of kraslice, it would be advisable to prolong the time of leaching. it is apparent from the above mentioned that applying an ecological technology it is possible to retrieve valuable metals from old heaps. acknowledgments: article has been done in connection with project institute of clean technologies for mining and utilization of raw materials for energy use, reg. no. cz.1.05/2.1.00/03.0082 supported by research and development for innovations operational programme financed by structural founds of europe union and from the means of state budget of the czech republic. references boom, m.: the mechanism of direct and indirect bacterial oxidation of sulfide minerals. hydrometallurgy, 62, 2001, 67-70. borovec, z.: mikrobiologická oxidace sulfidických rud. rudy, 37, 1989, 261-268. bosecker, k.: bioleaching: metal solubilization by microorganisms. fems microbiol. rev., 20, 1997, 591-604. brombacher, c., bachofen, r., brandl, a.: biohydrometallurgical processing of solids: a patent review. appl. microbiol. biotechnol., 48, 1997, 577-587. crundwell, f. k., holmes, p. r., fowler, t. a.: how do bacteria interact with minerals. j. s. afr. inst. min. metall., 100, 2000, 399-401. fečko, p.; kušnierová, m.; čablík, v.; pečtová, i.: environmentální biotechnologie, všb – tuo, ostrava, 2004, 180 pp. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 13:12 utc 152 fečko, p. et al. fečko, p.; kušnierová, m.; sochorková, a.; praščáková, m.; ovčaří, p.; mucha, n.; janáková, i.: biotechnólogie v úprave uhlia, všb – tuo, ostrava, 2008, 156 pp. kraus, s.: metale pretioase-vol ii. matrix rom, bucuresti, romania, 2006. ledin, m., pedersen, k.: the environmental impact of mine wastes role of microorganisms and their significance in treatment of mine wastes survey. göteborg university, lundeberg institute, 1995, 104 pp. maršálek, j.: thiobacillus ferrooxidans a jeho kultivace v procesu biologického loužení rud. sntl nakl. technické literatury, praha, 1979, 143 pp. stolz, j. f.; basu p.; santini, j. m.; oremland, r. s.: arsenic and selenium in microbial metabolism. ann. rev. microbiol., 60, 2006, 107–130. torma, a. e. the role of thiobacillus ferrooxidans in hydrometallurgical processes. in: ghose, t.k. and fiechter, a. and blakebrough, n. (eds.) advances in biochemical engineering. springer berlin heidelberg, berlin, 1977, 1-37. závada, j., bouchal, t.: chemické metody zpracování nerostných surovin a odpadů, všb – tuo, ostrava, 2010, 99 pp. presented at the 2nd international conference “biotechnology and metals 2011”, september 22–23, 2011, košice, slovak republic. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 13:12 utc nova biotechnologica et chimica 11-2 (2012) 125 doi 10.2478/v10296-012-0014-z © university of ss. cyril and methodius in trnava biosorption of copper, zinc and nickel from multi-ion solutions jana kaduková, hedviga horváthová technical university in košice, faculty of metallurgy, department of material science, letná 9, košice, 040 00, slovak republic (jana.kadukova@tuke.sk) abstract: the biosorption of cu(ii), zn(ii) and ni(ii) by microscopic green algae chlorella kessleri was investigated using batch experiments. biosorption studies with single and multi ion solutions were carried out to study the effect of several ions on the biosorption of selected metal. the influence of zinc and nickel on copper biosorption, copper and nickel on zinc biosorption and zinc and copper on nickel biosorption were investigated. the langmuir and freundlich model were used to describe the adsorption equilibrium of studied metals on chlorella kessleri biomass. based on the experimental results it was found that the presence of copper increased the biosorption capacity of zinc from 48.6 mg/g to 96.8 mg/g and nickel from 29.3 mg/g to 62.7 mg/g, respectively. however, the presence of nickel decreased the biosorption capacity of zinc from 48.6 mg/g to 31.7 mg/g. key words: adsorption isotherms, biosorption, chlorella kessleri, heavy metals, bioavailability 1. introduction environmental pollution is a very serious problem in the present time. the main sources of heavy metals contamination in wastewater derived from electroplating, metal finishing and metallurgical industry. metals like copper, zinc and nickel are present in almost all types of wastewaters. these metals are toxic even at low concentrations (kaduková and virčíková, 2003). several studies reported the biosorption of these metals from solution using different types of biosorbents. filamentous fungus rhizopus arrhizus have been used for effective biosorption of copper and nickel from single ion solutions (sag and arda, 2000). peanut shell biomass also showed good biosorption capacity for copper (anna and roman, 2011). phaseolus vulgaris immobilized in silica-gel had good biosorption capacity for nickel (akar and zerrin, 2009). zinc can be effectively removed by activated sludge or by penicillium simplicissimum biomass (chunping and min, 2010). bacterial strains bacillus cereus and pseudomonas sp. showed promising biosorption capacity for nickel and zinc (wei – chen and chieh – chen, 2008). the major problem in wastewater treatment is that it usually contains more than one metal. the presence of several metals in solution may have a synergistic or conversely antagonistic effect on their biosorption, which depends on many factors, such as the quantity of metal ions competing for the same binding sites, the concentration of metal ions, the nature and concentration of biosorbent (wang and yong, 2005; horváthová, kaduková, 2008; marešová et al., 2011). due to this fact it is very important to study the influence of several metals on their biosorption as well as to study the biosorption process itself. in terms of metal biosorption from multi ion solution systems several experimental studies have been reported up to now. due to the relatively small amount of information on the interaction among non-ferrous metal bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 12:59 utc 126 kaduková, j. et al. ions during biosorption process on green algae biomass the effect of copper, zinc and nickel on their biosorption from multi ion solutions was experimentally studied in this work. 2. materials and methods 2.1 biosorbent and model solutions preparation chlorella kessleri, an unicellular green alga, obtained from the institute of botany of slovak academy of sciences was used in this study. it was grown at 25°c, aerated and lighted by 4×40 w fluorescent tubes in liquid medium milieu bristol. the ph of the media was adjusted to 7.0 with 10% naoh. in the log phase of the growth, chlorella kessleri cells were cooled, centrifuged at 3000 rpm for 5 min, washed twice in distilled water and then dried at 100°c for 3 h. algal cells in the form of powder were used as a biosorbent. solutions of copper, zinc and nickel used for experiments were prepared by dissolving cuso4.5h2o, znso4.7h2o and niso4.7h2o in distilled water. solutions ph was adjusted using 10% h2so4 and 10% naoh. 2.2 metal biosorption experiments powdered algae were used for the biosorption experiments at the concentration 2 g/l. initial concentrations of copper, zinc and nickel in studied solutions ranged from 0 – 1000 mg/l. experiments were carried out according to the protocol for adsorption isotherms experiments (kaduková and virčíková, 2003). the ph value of used solutions was 5.0. these solutions were agitated on a shaker during 24 hours. after this time solution samples were withdrawn for metal analysis. the concentration of metal ions was measured by atomic absorption spectroscopy (varian aa20+). the metal uptake q was calculated from the mass balance equation as follows: m ccv q e )( 0 −= (1) where q the quantity of metal uptake by biomass [mg/g], c0 the initial metal concentration [mg/l], ce final (after sorption at equilibrium) metal concentration [mg/l], v the volume of solution [l] and m dry weight of the biomass added [g]. 2.3 biosorption isotherm modeling the modeling of the biosorption process by using chlorella kessleri was obtained by using different adsorption isotherms. in order to clarify the adsorption isotherms, langmuir and freundlich equations were chosen. the langmuir equation can be expressed as: e e e bc bcq q + = 1 max (2) bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 12:59 utc nova biotechnologica et chimica 11-2 (2012) 127 where qe is the amount of metal ion sorbed on the biosorbent (mg/g) at equilibrium time, qm is monolayer capacity of the biosorbent (mg/g), b is the biosorption constant (l/mg), and ce is equilibrium concentration of metal ion in solution (mg/l). the freundlich equation can be expressed as: n efe ckq /1= (3) where kf and n are empirical freundlich constants and indicative of adsorption capacity and adsorption intensity, respectively, qe and ce are like the langmuir equation described above. the value of n is generally between 2 to 10. langmuir mathematical model for binary system solutions can be expressed as: ( )2211111max1 1/ eee cbcbcbqq ++= (4) ( )2211222max2 1/ eee cbcbcbqq ++= (5) 3. results and discussion 3.1. influence of zn2+ and ni2+ on copper biosorption the influence of zinc and nickel on copper biosorption is shown in the fig. 1. the presence of zn had a positive effect on the copper biosorption, the biosorption capacity of copper increased two times in the solution cu – zn in comparison with the biosorption capacity from the single copper solution. fig. 1. comparison of biosorption capacity of copper from one, two and three ion solutions using langmuir model. the positive effect of zn on cu biosorption was observed at higher equilibrium concentrations (above 70 mg/l). it is possible that at higher concentrations copper is bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 12:59 utc 128 kaduková, j. et al. forced to bind to various types of binding sites resulting in the increase of the biosorption capacity. on the contrary al-rub et al. (2004) observed 10% decrease of the copper biosorption capacity by alga chlorella vulgaris in system cu zn. synergic effect was reported by tien (2002) during cu2+ biosorption from the three-ion solution cu-cd-pb by alga eudorina elegans. the influence of nickel was negligible. in our case slight decrease of the biosorption capacity was observed for the three ion system cu-zn-ni. 3.2. influence of cu2+ and ni2+ on zinc biosorption significant, almost double, increase of the biosorption capacity was also observed in the presence of copper during zn biosorption (fig. 2). similarly as in the case of copper the increase was observed at higher equilibrium concentrations (above 290 mg/l). the influence of copper on zinc biosorption was negative at lower concentrations. the synergic effect of metal ions during biosorption is very rarely mentioned in literature so the detail explanation of that phenomenon is missing. probably after the easily available binding sites are occupied the metal ions are forced to bind on less available sites which would not be occupied in more favorable situation. the presence of nickel or nickel and copper significantly decreased the zinc biosorption capacity. in this case metal ions are probably competing for binding sites (fan et al., 2008). fig. 2. comparison of biosorption capacity of zinc from one, two and three ion solutions using langmuir model. significant inhibition of zinc biosorption by copper presence was found when cork biomass was used as biosorbent (chubar et al., 2004) as well as when the biomass of fucus spiralis (romera et al., 2008) or cyanobacteria oscillatoria angustissima (mohapatra and gupta, 2005) were used. similarly pipíška et al. (2010) found that zn and cd compete for the same binding sites on the rhytidiadelphus bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 12:59 utc nova biotechnologica et chimica 11-2 (2012) 129 squarrosus biomass surface resulting in equal biosorption efficiency. negative effect on zinc biosorption was found also for other ions such as cd2+ (remenárová et al., 2012). 3.3. influence of zn2+ and cu2+ on nickel biosorption the presence of copper had very positive effect also on the nickel biosorption (fig. 3). nickel biosorption capacity increased more than twice. presence of zinc slightly increases the biosorption capacity of nickel in the range of low concentration. on the other hand in the highest concentration range the effect of zinc on nickel biosorption is negligible. fig. 3. comparison of biosorption capacity of nickel from one, two and three ion solutions using langmuir model. mutual influence of metals on their biosorption probably depends on the biosorbent type, too. villaescusa et al. (2004) observed negative effect of copper (20% decrease of the capacity) on nickel biosorption when grape waste was used as the biosorbent. 3.4 equilibrium modeling of process biosorption the highest value of maximum biosorption capacity from single ion solutions was found for zinc, which is consistent with experimental results. based on the obtained experimental results the affinity constant bl was calculated using langmuir mathematical model. the experimental results showed that zinc had the highest affinity for the green alga chlorella kessleri. using the freundlich model similar results were obtained. obviously algae had the highest adsorption capacity for zinc from single ion solutions. study of the biosorption from multiple ion solutions is much more complicated than from single ion solutions because it is always necessary to include the influence bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 12:59 utc 130 kaduková, j. et al. of other ions present in the solution. in the case of copper – zinc solution maximum biosorption capacity was higher for copper. on the other hand, in the solution containing zinc and nickel, the maximum biosorption capacity was higher for zinc. the values of parameters calculated from the langmuir model for single and multiple ion solutions are shown in table 1 and 2. table 1. model constants for single solution of metals. isotherms model constants cu zn ni qmax [mg/g] 44.0 48.6 29.3 b [l/mg] 0.052 0.070 0.007 langmuir r2 0.976 0.971 0.921 kf [l/g] 10.1 12.9 2.21 1/n 0.230 0.213 0.363 freundlich r2 0.940 0.866 0.916 table 2. model constants for binary system solutions. langmuir qmax [mg/g] b1 [l/mg] b2 [l/mg] r 2 cu 90.3 0.0007 0.9887 cu + zn zn 96.8 0.0036 0.9898 cu 57.3 0.0007 0.9951 cu + ni ni 62.7 0.0063 0.9849 zn 31.7 -0.019 0.9959 zn + ni ni 28.5 0.0349 0.9785 maximum biosorption capacity for zinc from the system cu-zn is slightly higher than that of copper. zinc in zn + ni system has a slightly higher biosorption capacity in comparison with nickel. in the cu + ni solution system maximum biosorption capacities for studied metals were very similar. from the comparison of affinity constants for cu + zn solution it is obvious that the algae have higher affinity to zinc. surprisingly, algae have higher affinity to nickel in the other two studied systems. as in the previous cases, in the study of the mutual influence of three ions cu2+, zn2+ and ni2+ in multiple solution systems the adsorption isotherms was calculated. biosorption capacity of studied metals decreased in the order: cu > zn > ni. at the present time well known mathematical models do not reliably calculate the necessary parameters. therefore the modeling of three-and multi-ionic solutions still requires further study. 4. conclusions wastewater treatment is very important issue of today because of the increase of pollutant amount released into surface water followed by the pollution of groundwater. many studies are dedicated to the developing new wastewater treatment methods. among the suitable methods biological methods represents good alternative for wastewater treatment. copper, zinc and nickel present in the solution can influence their mutual biosorption significantly. interestingly the presence of copper had positive bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 12:59 utc nova biotechnologica et chimica 11-2 (2012) 131 effect on zinc and nickel biosorption capacity at higher equilibrium concentrations. also zinc increased the biosorption capacity of copper. more study would be necessary to explain the phenomenon because in general metal ions should compete for binding sites on the biosorbent surface resulting in the decrease of the biosorption capacity. the decrease was observed only in some of two-ion solutions but in three ion solution the decrease of the biosorption capacity was reported for all three ions. understanding of mutual influence of metals on their biosorption could significantly contribute to broader biosorption application in wastewater treatment. acknowledgement: authors thanks to ing. vladimír pencák for his help with the article preparation. this work was supported by vega 1/0235/12. references abu al-rub, f.a., el-naas, m.h., benyahia, f., ashour i.: biosorption of nickel on blank alginate beads, free and immobilized algal cells. process biochem., 39, 2004, 1767-1773. akar, t., zerrin, k.: enhanced biosorption of nickel (ii) ions by silica-gelimmobilized waste biomass: biosorption characteristics in batch and dynamic flow mode. j. hazard. mater., 163, 2009, 1134–1141. anna, w., roman, g.: biosorption of heavy metals from aqueous solutions onto peanut shell as a low-cost biosorbent. desalination, 265, 2011, 126–134. chubar, n., carvalho, j.r., correia m.j.n.: cork biomass as biosorbent for cu(ii), zn(ii) and ni(ii). colloid surface physicochem. eng. aspects 230, 2004, 57–65. chunping, y., min, l.: biosorption of zinc(ii) from aqueous solution by dried activated sludge. j. environ. sci., 22, 2010, 675–680. fan, h.j., yang, h.s., tsai, y.s., furuya, e.: prediction of individual freundlich isotherms from binary and ternary phenolic compounds mixtures. chemosphere 71, 2008, 886-893. horváthová, h., kaduková, j.: effect of nickel on copper and zinc biosorption. acta metallurg. slovaca, 14, 2008, 78–82. kaduková, j., virčíková, e.: mineral biotechnology iii, biosorption of metals from solution, 1st edition, všb-tu, ostrava, 2003. isbn 80-248-0244-9. marešová, j., pipíška, m., rozložník, m., horník, m., remenárová, l., augustín, j.: cobalt and strontium sorption by moss biosorbent: modeling of single and bingy metal systems. desalination, 266, 2011, 134–141. mohapatra, h., gupta, r.: concurrent sorption of zn(ii), cu(ii) and co(ii) by oscillatoria angustissima as a function of ph in binary and ternary metal solutions. bioresour. technol., 96, 2005, 1387–1398. pipíška, m., horník, m., remenárová, l. augustín, j., lesný, j: biosorption of cadmium, cobalt and zinc by moss rhytidiadelphus squarrosus in the single and binary component systems. acta chim. slov., 57, 2010, 163–172. remenárová, l., pipíška, m., horník, m., rozložník, m., augustín, j., lesný, j.: biosorption of cadmium and zinc by activated sludge from single bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 12:59 utc 132 kaduková, j. et al. and binary solutions: mechanism, equilibrium and experimental design study, j. taiwan inst. chem. eng., 43, 2012, 433–443. romera, e., gonzález, f., ballester, f., a., blázquez, m.l., muoz, j.a.: biosorption of heavy metals by fucus spiralis. bioresour. technol., 99, 2008, 4684-4693. sag, y., arda, y.: mono and multi-component biosorption of heavy metal ions on rhizopus arrhizus in a cfst. process biochem., 35, 2000, 787–799. tien, c.j.: biosorption of metal ions by freshwater algae with different surface characteristics. process biochem., 38, 2002, 605-613. villaescusa, i., fiol, n., martinez, m., miralles, n. et al.: removal of copper and nickel ions from aqueous solutions by grape stalks wastes. water res., 38, 2004, 992–10. wang, x., yong, q.: equilibrium sorption isotherms for cu2+ on rice bran. process biochem., 40, 2005, 677–680. wei – chen, k., chieh – chen, h.: biosorption of nickel, chromium and zinc by merpexpressing recombinant escherichia coli. j. hazard. mater., 158, 2008, 100 – 106. presented at the 2nd international conference “biotechnology and metals 2011”, september 22–23, 2011, košice, slovak republic. bereitgestellt von slovenská poľnohospodárska knižnica | heruntergeladen 16.01.20 12:59 utc microsoft word apv-pipiska fulltext.doc nova biotechnologica vii-i (2007) 23 sorption of cobalt and zinc from single and binary metal solutions by evernia prunastri martin pipíška, miroslav horník, ľuboš vrtoch, soňa šnircová, jozef augustín department of biotechnology, university of ss. cyril and methodius, j. herdu 2, trnava, sk-917 01, slovak republic (pipiskam@ucm.sk) non-living lichen evernia prunastri was studied as biosorbent material for zinc and cobalt removal from single and binary metal solutions. sorption equilibrium of zn2+ and co2+ ions was reached within 1 hour. both cobalt and zinc biosorption was not ph dependent within the range ph 4-6 and negligible at ph 2. the experimental results were fitted to the langmuir, freundlich, redlich-peterson and langmuir-freundlich adsorption isotherms to obtain the characteristic parameters of each model. the langmuir, redlich-peterson and langmuir-freundlich isotherms were found to well represent the measured sorption data. according to the evaluation using the langmuir equation, the maximum sorption capacities of metal ions onto lichen biomass were 112 μmol/g zn and 97.2 μmol/g co from single metal solutions. e. prunastri exhibited preferential uptake of zinc from equimolar binary zn2+ co2+ mixtures within the range 50 – 4000 μm. even thought mutual interference was seen in all co-zn binary systems. to evaluate the two-metal sorption system, simple curves had to be replaced by three-dimensional sorption surface. these results can be used to elucidate the behavior of lichens as bioindicators of cobalt and zinc pollution in water and terrestrial ecosystems. key words: zinc, cobalt, evernia prunastri, sorption, equilibrium, isotherms 1. introduction sorption processes represent one of the possible mechanisms of interaction of toxic metals in contaminated aquatic systems. bioremoval of single species of metal ions is affected by several factors such as the specific surface properties of biosorbent, temperature, ph, initial metal ion concentration and biomass concentration. when several metals are present, many other parameters affect the sorption process. simple sorption isotherms are usually constructed as a result of studying equilibrium batch sorption behavior of different biosorbent materials. these curves enable quantitative evaluation of biosorption performance of these materials for only one metal (hammaini et al., 2003; aksu and dőnmez, 2006) when more than one metal at a time is present in a sorption system, evaluation, interpretation, and representation of biosorption results become much more complicated. the aim of this study was to investigate the ability of the lichen e. prunastri growing in slovak territory to sorb co2+ and zn2+ from single and binary metal solutions. co-zn system was chosen as representative of bivalent metals found in industrial effluents. a range of equilibrium adsorption isotherms were obtained to quantitatively describe cobalt and zinc uptake. 24 pipíška, m. et al. 2. materials and methods 2.1 biomass biomass of fruticose lichen e. prunastri were taken from the spruces (picea abis) grown in the forest of high tatras, slovak republic. the lichen was washed twice in deionized water and oven-dried at 45°c for 72 h. cut thallus sections of diameter 3-4 mm were used in experiments. 2.2 sorption studies sorption experiments were carried out in 10 ml solutions ranged from 50 to 4000 μm of zn2+, co2+ and zn2+-co2+, spiked with 65zn or 60co. the ph value was adjusted to 4.0. biomass (50 mg, d.w.) was added, and the content in flasks was agitated on a reciprocal shaker (120 rpm) for 4 h at 20°c. at the end of the experiments radioactivity of both lichen and liquid samples was measured. all experiments were carried out four times. if not otherwise stated, presented data are arithmetic mean values. to calculate the qmax values and the corresponding parameters of adsorption isotherms (tab. 1) non-linear regression analysis was performed by the nlreg® software (statistical analysis program, version 6.3 created by p.h. sherrod) and origin 7.0 professional (originlab corporation, northampton, usa). the 3-d sorption surfaces were obtained by plotting the experimental zn and co equilibrium concentrations ceq on the x and y axes, against the co, zn and total metal uptake qeq on the z axis. the statistica 7.0 (statsoft, inc., tulsa, usa) and nlreg® software were used for this purpose. table 1. adsorption isotherm models used in this work. isotherm equation equation no. adjustable parameters langmuir eq eq eq bc cbq q + = 1 max 1 qmax, b freundlich qeq= k ceq (1/n) 2 b, n redlich – peterson g eq eq eq cb ac q )(1+ = 3 a, b, g langmuir – freundlich ( ) n eq n eq eq bc bcq q /1 /1 max )(1+ = 4 qmax, b, n binary langmuir 2211 1max1 1 1 eqeq eq eq cbcb cqb q ++ = 5 qmax, b1,b2 2.3 speciation modeling prediction of the speciation of co and zn in the aqueous systems was performed using the visualminteq (version 2.52) program. this speciation model allows the calculation of the composition of solutions for specified conditions. nova biotechnologica vii-i (2007) 25 2.4 radiometric analysis for radiometric determination of 60co and 65zn in liquid samples and lichen biomass, gamma spectrometric scintillation detector 54bp54/2-x with well type crystal nai(tl) (scionix, netherlands) and data processing software scintivision32 (ortec, usa) were used. standardized 60cocl2 solution (5.181 mbq.ml -1, cocl2 20 mg.l-1 in 3 g.l-1 hcl) and 65zncl2 (0.8767 mbq.ml -1, zncl2 50 mg.l -1 in 3 g.l-1 hcl) obtained from alldeco inc., slovakia were used in all experiments. 3. results and discussion 3.1 metal uptake metals speciation in solution is important in sorption studies since the metal uptake depends on the solution ph. as can be calculated by visualminteq speciation program, cobalt and zinc in the single and binary solutions at ph 4 occur practically as free cations (>99,5 % co2+, >98 % zn2+) (data not shown). the time-course studies on the biosorption of cobalt and zinc ions were performed by contacting co and zn solutions with lichen biomass at ph 4.0 and 20 °c. biosorption of co2+ and zn2+ ions by e. prunastri shown in fig. 1 is a rapid process. maximum uptakes (approximately 90%) were reached within 1 hour and practically did not change during the next 24 hours. 0 5 10 15 20 25 0 20 40 60 80 100 b io so rp tio n [% ] t [h] zn2+ co2+ fig. 1. biosorption kinetics of co2+ (100 µmol/l, 60cocl2 89 kbq/l) and zn2+ (100 µmol/l, 65zncl2 70 kbq/l) by e. prunastri (5 g /l, d.w.) from single metal solutions at 20°c. initial ph 4.0; ph 4.2 after 24 hours. error bars represent standard deviation of the mean (n = 4). similar adsorption kinetics of cd2+, zn2+, pb2+ and cu2+ by lichen e. prunastri was observed by antonelli et al., (1998), where equilibrium was reached within a few minutes. the above mentioned results indicate that biosorption of the aforementioned cations was not dependent on metabolic activity. the biosorption process can be attributed to interactions of cations with anionic functional groups on the thallus surface. the thallus surface was supposed to contain ionogenic groups that generate a negative net charge (garty, 2001). 26 pipíška, m. et al. 3.2 sorption equilibrium in single metal solution analysis of equilibrium data on a specific mathematical equation is of significance for comparing different sorbents under different experimental conditions. four well known adsorption isotherm models: langmuir, freundlich, redlich-peterson and langmuir-freundlich (see equations in table 1) were applied for the analysis of the experimental data. these models use parameters that reflect the nature of the sorbent and can be used to compare biosorption performance. qmax represents the maximum sorption capacity, b is a constant related to the energy of adsorption. k and 1/n values are the freundlich constants referring to adsorption capacity and intensity of adsorption, respectively. a, b and g (0