Fungi isolated in school buildings ELŻBIETA EJDYS Department of Mycology, University of Warmia and Mazury in Olsztyn Oczapowskiego 1A, PL-10-719 Olsztyn-Kortowo, elzbieta.ejdys@uwm.edu.pl E j d y s E.: Fungi isolated in school buildings. Acta Mycol. 42 (2):245-254, 2007. The aim of the study was to determine the species composition of fungi occurring on wall surfaces and in the air in school buildings. Fungi isolated from the air using the sedimentation method and from the walls using the surface swab technique constituted the study material. Types of finish materials on wall surfaces were identified and used in the analysis. Samples were collected in selected areas in two schools: classrooms, corridors, men’s toilets and women’s toilets, cloakrooms, sports changing rooms and shower. Examinations were conducted in May 2005 after the heating season was over. Fungi were incubated on Czapek-Dox medium at three parallel temperatures: 25, 37 and 40°C, for at least three weeks. A total of 379 isolates of fungi belonging to 32 genera of moulds, yeasts and yeast-like fungi were obtained from 321 samples in the school environment. The following genera were isolated most frequently: Aspergillus, Penicillium and Cladosporoium. Of the 72 determined species, Cladosporium herbarum, Aspergillus fumigatus and Penicillium chrysogenum occurred most frequently in the school buildings. Wall surfaces were characterised by an increased prevalence of mycobiota in comparison with the air in the buildings, with a slightly greater species diversity. A certain species specificity for rough and smooth wall surfaces was demonstrated. Fungi of the genera Cladosporium and Emericella with large spores adhered better to smooth surfaces while those of the genus Aspergillus with smaller conidia adhered better to rough surfaces. The application of three incubation temperatures helped provide a fuller picture of the mycobiota in the school environment. Key words: fungi, school, walls, indoor air INTRODUCTION Schools belong to a specific category of public buildings were factors that increase the expansion of fungi belonging to different systematic and ecological groups accu- mulate. The technical condition of a school building which results from the construc- tion technology, finish materials and its use significantly influences the occurrence of conditions favourable for a temporary or permanent occurrence of fungi (B o g a c k a 1997). School occupants constitute further sources or transmission vectors of fungi ACTA MYCOLOGICA Vol. 42 (2): 245-254 2007 Dedicated to Professor Alina Skirgiełło on the occasion of her ninety-fifth birthday 246 E. Ejdys into and within a school building. The present author’s previous studies show that fungi are isolated in over 1/3 of school children (E j d y s 2003). The bioaerosol in school buildings also consists of secondary metabolites pro- duced by the mycobiota occurring in building partitions. Possible toxins penetrat- ing the bodies of the children and school employees may cause various toxicoses (B u d a k 1998). On the other hand, antibiotics produced in low concentrations may induce resistance of the bacterial flora of school occupants (M a r k i e w i c z , K w i a t k o w s k i 2001). As literature data on the diversity range of fungi in schools are greatly divergent (L e v e t i n at al. 1995; M e k l i n at al. 2002; D a c a r r o et al. 2003), the species composition of fungi occurring on wall surfaces and in the air in school buildings was analysed. MATERIAL AND METHODS Fungi isolated from the air using the sedimentation method and from the walls using the surface swab technique were the study material. Types of finish materi- als on wall surfaces were identified and used in the analysis. Surfaces finished with acrylic or emulsion paint were defined as rough while the walls covered with gloss paint or tiled were defined as smooth. Macroscopic changes indicating the develop- ment of the mycelium were not found on the walls. Samples were collected in se- lected areas in two schools: classrooms, corridors, men’s toilets and women’s toilets, cloakrooms, sports changing rooms and shower (only school I). A total of 312 sam- ples were collected in 13 enclosed spaces within the school buildings. Studies were conducted in May 2005 after the heating season was over. Indoor temperature and air humidity were measured during sampling. Fungi were incubated on Czapek-Dox medium at three parallel temperatures: 25, 37 and 40°C, for at least three weeks. Cultured colonies of moulds were described macroscopically. Slides stained with cotton blue in lactophenol according to G e r l a c h (1972) were made to identify mi- croscopic features. Biochemical properties were assessed using methods commonly accepted in mycological laboratories. The obtained isolates of yeast-like fungi and yeasts were incubated on Sabouraud medium without antibiotics. Media containing antibiotics that could affect typical fungal features were not used (D y n o w s k a 1991/1992). The isolates were incubat- ed at 37°C for 48 hours. After fungal growth was obtained, the material was passed twice or three times onto fresh Sabouraud medium to eliminate bacteria which rela- tively often accompanied fungi in the first culture. After pure bacteria-free strains were obtained, microcultures on Nickerson agar were established. Fungi were inoculated on glass slides, covered with a thin layer of the medium (ca. 2 mm), and 2-3 drops of broth and serum in a ration of 1:1 were added onto the inoculation site. Microcultures were incubated at 37°C for 48 up to 72 hours. Macroscopic features (size, colour, shape, texture, smell of the colony) and micro- scopic features (shape and size of budding cells, blastospores and chlamydospores, the diameter of pseudohyphae and hyphae) as well as biochemical features obtained on bio–Mérieux API-tests (API 20C, API 20C AUX) were used for identification. CHROMagar (bio–Mérieux) was used to differentiate individual species of the Fungi in school buildings 247 genus Candida. It was treated as an auxiliary test as it does not yield accurate results in mixed-species isolations (B o u c h a r a et al. 1996). Photographic documentation was made throughout the process. Yeast-like fungi and yeasts were determined using the following keys: K r e g e r - v a n R i j (1984); B a r n e t t , P a y n and Ya r r o w (1990), and a study by -K u r n a - t o w s k a (1995). Fungi of the genera Aspergillus and Penicillium were identified up to the level of species using the following keys: R a p e r and F e n n e l l (1965) and R a p e r , T h o m and F e n n e l l (1945). Other species were determined using the atlas of clinical fungi (d e H o o g et al. 2000). RESULTS A total of 379 fungal isolates were obtained from 312 samples. 213 isolates were recorded in 7 study areas in school I and 166 isolates in school II. 32 genera of moulds, yeasts and yeast-like fungi were identified in the study material. Fungi of the genera Aspergillus, Penicillium and Cladosporium were isolated most frequently. Fungi belonging to 27 and 21 genera were recorded in school I and II, respectively; 16 genera occurred in the study areas in both buildings while the others were iso- lated only from one school and were usually sporadic isolates. 9 fungi of the genus Chaetomium and 4 of the genus Hormographiella were exceptionally recorded in school I (Fig. 1). Of the 72 fungal species identified in the samples, 33 species were isolated at least twice. A group of predominant species with a similar occurrence frequency can be distinguished. These are: Cladosporium herbarum (43 isolates– 11.3%), Aspergillus fumigatus (39-10.3%) and P. chrysogenum (37-9.8%) as well as P. citrinum (32-8.4%) (Tab. 1). P. chrysogenum (13.1%), P. citrinum (11.7%) and Cl. herbarum (10.3%) were isolated most frequently in school I. A. fumigatus occurred almost twice less frequently (6.6%). It was, however, one of the species predominant in the mycobiota in school II, and its frequency of occurrence was 15.1%. Cl. her- barum, whose prevalence was 12.7%, was the second dominant. P. chrysogenum and P. citrinum, on the other hand, occurred with the frequency lower than 4.5%. The differences in the species range in both buildings could also be noticed in the greater number of species belonging to the genus Aspergillus recorded in building I (18) than in building II (6). Fig.1. Occurrence of fungal genera in the school buildings. 248 E. Ejdys 235 fungal isolates were obtained from the swabs and 144 isolates were obtained using the sedimentation method. 26 and 22 genera were recorded on wall surfaces and in the air, respectively; 16 genera were isolated in both sample types (Fig. 2). Only 6 genera were characteristic of the air. These were: Bipolaris, Bjerkandera, Chrysosporium, Corynespora, Madurella and Phoma. Fungi of the genera Penicillium (32 isolates), Cladosporium (26) and Aspergillus (22) were recorded most frequently in this medium. The same genera also dominated on wall surfaces although their stratification was slightly different. The genus Aspergillus unquestionably dominat- ed (75 isolates). Yeast-like fungi, mostly of the genera Candida, Rhodotorula and Geotrichum, were frequently recorded in both sample types: 11.3%. Significantly greater differences were recorded in the species range in the wall samples and the air samples. Twice as many species (65) were identified on the walls as in the air (32). However, the structure of the domination in both sample types was the same. 23 species common for both the walls and the air were recorded. Of the 32 species that occurred only on the surfaces in the school buildings, 16 species represented the genus Aspergillus. Only one isolate of the genus Candida, C. datilla, was determined from the air. The prevalence of yeast-like fungi in the air did not differ significantly from that on the wall surfaces and was 10.4% and 11.9%, respectively. Fungi of the order Mucorales which occurred sporadically in the school buildings did not occur in the air at all. A slightly smaller number of isolates was recorded on smooth walls (106) than on rough walls (129). Rough surfaces were characterised by a slightly greater species range (43 species) and a greater number of fungi belonging to the genus Aspergil- lus (15) than smooth walls (39 and 12 species, respectively). These differences were accompanied by an increased number of isolates of fungi of this genus: 45 on rough walls and 30 on smooth walls. The fungus Emericella quadrilineata was identified on the smooth wall in the sports shower, and its asexual stage, Aspergillus quadrilineatus, on the rough surface. However, a greater number of Cladosporium species were re- corded on smooth surfaces. Apart from Cl. herbarum, Cl. cladosporoides, Cl. oxyspo- rum and Cl. sphaerospermum also occurred. Significant differences in the species range and prevalence of fungi belonging to the genus Penicillium on both surfaces studied were not recorded. Fig. 2. Occurrence of fungal genera on the walls and in the air in the school buildings. Fungi in school buildings 249 Ta b l e 1 Fungi isolated from the walls and the air in the school buildings No Fungal species Number of isolates to ta l ro ug h w al l sm oo th w al l ai r sc ho ol I sc ho ol I I 1 Acremonium alabamense Morgan-Jones 1 1 0 0 1 0 2 Ac. hyalinulum (Sacc.) W. Gams 1 0 1 0 1 0 3 Ac. kiliense Grütz 1 0 1 0 0 1 4 Ac. roseogriseum (S.B. Saksena) W. Gams 1 0 0 1 1 0 5 Acremonium sp. 1 0 0 1 0 1 6 Alternaria alternata (Fr.) Keissl. 2 1 0 1 0 2 7 A. infectoria Simmons 1 0 1 0 1 0 8 Alternaria sp. 2 2 0 0 0 2 9 Artrographis kalrae (Tewari&Macpherson) Singler & Carmichael 1 0 1 0 1 0 10 Aspergillus allahabadi Mehrotra & Agnihotri 1 1 0 0 0 1 11 A. aureolus Fennell & Raper 1 0 1 0 1 0 12 A. auricomus (Gueguen) Saito 1 0 1 0 1 0 13 A. caesiellus Saito 5 3 2 0 1 4 14 A. candidus Link 3 1 1 1 1 2 15 A. crystallinus Kwon & Fennel 1 1 0 0 1 0 16 A. flavus Link 12 7 5 0 7 5 17 A. fumigatus Fresenius 39 13 8 18 14 25 18 A. glaucus Link 1 1 0 0 1 0 19 A. granulosus Raper & Thom 1 1 0 0 1 0 20 A. janus Raper & Thom 4 3 1 0 3 1 21 A. longobasidia (Bain.) Moseray 1 0 1 0 1 0 22 A. malodoratus Kwon & Fennell 1 1 0 0 1 0 23 A. nidulans (Eidam) Wint 1 0 1 0 1 0 24 A. niger Van Tieghem 4 2 1 1 4 0 25 A. ochraceus Wilhelm 1 1 0 0 1 0 26 A. quadrilineatus Thom & Raper 1 1 0 0 1 0 27 A. sydowi (Bain.& Sart.) Thom & Church 3 0 3 0 3 0 28 A. versicolor Tiraboschi 12 6 4 2 6 6 29 Aspergillus sp. 4 3 1 0 1 3 30 Bipolaris spicifera (Bain.) Subram. 2 0 0 2 2 0 31 Bjerkandera sp. 4 0 0 4 2 2 32 Botrytis cinerea Pers. ex Pers. 2 0 2 0 0 2 33 Candida albicans (Robin) Berkhout 1 1 0 0 0 1 34 C. datila (Kluyver) S.A. Meyer & Yarrow 1 0 0 1 0 1 35 C. globosa Yarrow & S.A. Meyer 5 0 5 0 2 3 36 C. guilliermondii (Castellani) Berkhout 1 1 0 0 0 1 37 C. krusei (Castellani) Berkhout 1 1 0 0 0 1 38 C. versatilis (Etchells & T.A. Bell) S.A.Meyer & Yarrow 2 0 2 0 2 0 250 E. Ejdys 39 Chaetomium atrobruneum Ames 9 3 5 1 9 0 40 Chrysosporium queenslandicum Apinis & Rees 1 0 0 1 1 0 41 Cladosporium cladosporoides (Fres.) de Vries 3 2 0 1 3 0 42 Cl. herbarum (Pers.) Link: Fr. 43 13 10 20 22 21 43 Cl. oxysporum Berk. & Curt. 3 1 0 2 0 3 44 Cl. sphaerospermum Penz. 4 1 0 3 1 3 45 Corynespora cassiicola (Berk. & Curt.) Wei 1 0 0 1 0 1 46 Emericella quadrilineata (Thom & Raper) C.R. Benjamin 1 0 1 0 1 0 47 Emonsia crescens Emmons & Jellison 1 1 0 0 1 0 48 Epidermophyton floccosum (Harz) Langer. & Milochevitch 3 1 1 1 1 2 49 Fusarium incarnatum (Rob.) Sacc. 3 1 1 1 1 2 50 Geotrichum candidum Link: Fr. 9 2 4 3 3 6 51 G. clavatum de Hoog et al. 4 0 1 3 4 0 52 Gymnoascus dancaliensis (Castell.) v. Arx 2 1 0 1 2 0 53 Hormographiella aspregillata Guarro et al. 2 1 0 1 2 0 54 H. verticillata Guarro et al. 2 2 0 0 2 0 55 Madurella grisea MacKinnon et al. 1 0 0 1 0 1 56 Microsporum fulvum Uriburu 1 1 0 0 1 0 57 Mucor amphibiorum Schipper 1 0 1 0 0 1 58 Mucor ramosissimus Samutsevich 1 0 1 0 1 0 59 Penicillium camamberti Thom 1 0 1 0 0 1 60 P. chrysogenum Thom 37 12 10 15 28 9 61 P. citrinum Thom 32 11 8 13 25 7 62 P. claviforme Bainier 1 0 1 0 0 1 63 P. notatum Westling 6 3 1 2 3 3 64 P. purpurrescens (Scopp) n. comb. 1 1 0 0 1 0 65 P. steckii Zaleski 4 0 2 2 0 4 66 Phialophora pubakii (Laxa) Schol-Schwarz 1 1 0 0 1 0 67 Phoma cruris-hominis Punithalingam 1 0 0 1 1 0 68 Rhizopus sp. 1 1 0 0 0 1 69 Rhodotorula glutinis (Fresenius) F.C. Harrison 12 3 2 7 8 4 70 Rhodotorula sp. 5 3 2 7 4 1 71 Scopulariopsis brevicaulis (Sacc.) Bain. 1 1 0 0 0 1 72 S. brumptii Salvanet-Duval 3 0 1 2 1 2 73 S. flava (Sopp) Morton & G. Smith 2 1 1 0 2 0 74 Scopulariopsis sp. 1 1 0 0 1 0 75 Saccharomyces cerevisiae Meyen ex E.C. Hansen 5 2 1 2 2 3 76 Saccharomycopsis capsularis Schiönning 2 2 0 0 1 1 77 Scytalidum lignicola Pesante 1 0 1 0 0 1 78 Trichphyton tonsurans Malmsten 1 0 0 1 1 0 79 T.verrucosum Bodin 1 0 0 1 0 1 80 Trichophyton sp. 4 0 4 0 4 0 81 Unidentified isolates 34 5 4 25 12 22 Total 379 129 106 144 213 166 Tab. 1 cont. Fungi in school buildings 251 Humidity ranged between 43 and 49% in school I and between 48 and 52% in school II. These values correspond to the PN-ISO 8756: 2000 standard on the air quality. The temperature was quite low in school II and ranged from 17.0 to 18.6 C°. It was warmer in school I, where the temperature ranged from 19.8 to 23.5 C°. DISCUSSION The composition of indoor mycobiota may differ significantly due to the nature and physicochemical properties of specific indoor environments, their use and the number of occupants, also not excluding the time of exposure to fungi. Results of most mycological analyses show that so-called indoor fungi of the genera Aspergillus and Penicillium as well outdoor fungi, or “field fungi”, such as Alternaria or Cladosporium, are recorded most frequently inside buildings (L e v e t i n at al. 1995; G u t a r o w s k a et al. 2004). In his analysis of the species range of indoor air in 19 groups of building facilities used for different purposes, Z y s k a (2001) demonstrated 14 recurring spe- cies of the 227 identified fungi. In the present study, the occurrence of 7 species was confirmed: Alternaria alternata, Aspergillus flavus, A. fumigatus, A.niger, A.versicolor, Cladosporium herbarum, Penicillium chrysogenum. They include species dominant in the school buildings studied. The range of fungal species that characterises indoor environment constitutes contamination of the pool of indoor fungi and species diffused with the air from outdoor environment (B o g a c k a 1997). It is best visible in spring when after a long heating season increased ventilation begins without the need to prevent heat losses. Indoor temperature similar to that outdoors may also cause temporary enrichment of the mycobiota in buildings although there are usually fewer spores in the air in spring than in summer or autumn (S h e l t o n et al. 2002; To p b a s et al. 2006). Thus, the great number of species isolated in the present study may indicate temporary contamination of the buildings by fungi from outside while those isolated only in the air may indicate incoming species. The greater taxonomic differentiation of the my- cobiota in school I may result from its location in a park, with many trees and shrubs, some fountains, incorrectly performed drainage and, consequently, prolonged sta- gnation of rain waters. The latter may be of great importance in the context of the increase in air humidity which is one of the basic factors limiting the occurrence of moulds. The age of the buildings is also an important factor encouraging contamination by fungi. Both schools are less than 30 years old and were constructed with prefab- ricated concrete. This should also be seen as one of the reasons for the high preva- lence of fungi belonging to the genus Cladosporium which readily colonise cement surfaces (E z e o n u et al. 1994; Tr e a u , F e r n a n d e s - C a l d a s 1994). Apart from the genus Cladosporium, fungi of the genera Penicillium, Aspergillus and Alternaria are often recorded in residential buildings (G u t a r o w s k i et al. 2004). The latter was rarely recorded in the present study. This may be related to the fact that spores of this fungus are isolated from the atmospheric air, and its occurrence indoors is connected with inappropriately used mineral wool in building insulation (E z e o n u et al. 1994), the insulation method used in the schools studied. Features that allow fungi to adhere quickly to the substrate or to occur in aerosols determine colonisation of indoor air or the retention of fungi in the air. This explains 252 E. Ejdys the significant species difference between the walls and the air reported in the litera- ture (G u t a r o w s k a et al. 2004) and observed in the present study. The discrepancy is related more to the formation of the surface of the spores than to their size. Ac- cording to K r z y s z t o f i k (1992), particles whose diameter ranges between 3 and 10 microns may remain in the air for long periods of time, even at very low upward air currents. The occurrence of large and smooth ascospores of Emericella quadrilineata on a smooth surface and only slightly smaller and rough conidia of its anamorph on a rough surface confirms these adaptations. A relatively permanent occurrence frequency of yeast-like fungi accompanied the great differences in the prevalence of moulds in the wall samples and in the air samples. It seems that while species predominant in indoor environment are mostly correlated with the properties of the building itself, the presence of yeasts and yeast- like fungi is correlated more with living organisms occupying it. This is shown by a great species correspondence of fungi isolated across the four seasons of the year from buildings and their occupants, recorded by M a c u r a and G n i a d e k (2003). Indoor prevalence of yeasts and yeast-like fungi shown by these authors (10.7%) strictly corresponds to the present results. The occurrence of Saccharomycopsis cap- sularis, a fungus recorded only since the late 1990s in the respiratory system in adults (D y n o w s k a , B i e d u n k i e w i c z 1999) and children (E j d y s 2003) in north-east- ern Poland, was recorded in the school buildings studied. The presence of yeast-like fungi is also affected by indoor humidity. Their oc- currence is reported in the second place after that of the genus Penicillium in damp schools. Additionally, indicator fungi of water-damaged buildings were isolated in such places: Stachybotrys, Trichoderma and A.versicolor (M e k l i n at al. 2002). This tendency was confirmed in the present study. Only 10% prevalence of yeast-like fungi and 3% prevalence of A.versicolor were recorded at low air humidity in the schools. The richness of indoor mycobiota also results from the parallel sample incuba- tion at different temperatures. It was accepted that while the temperature range of fungi is very broad it consists of narrow ranges of individual species. Aspergillus fumigatus, a thermophilous fungus, with slow initial growth, may be an example. Al- though it can grow at room temperature, it may lose competition with other, more rapid-growing species characteristic of this temperature. The results of the present author’s studies clearly show this. The domination of the genus Aspergillus similar to that observed in the school buildings was recorded in a significantly warmer cli- mate in student halls in Egypt ( M a g h a z y , S h a a b a n , E l - K a t a t n y 1 9 9 6 ) ; it was, however, isolated rarely (K r a w c z y k , K o w a l s k i , O c h ę c k a - S z y m a ń s k a 1999) or was not isolated at all (G u t a r o w s k a at al. 2004) in flats in Poland, which is another argument in favour of the expansion of the range of incubation tempera- tures to achieve greater knowledge of the mycobiota of various buildings. Fungi in school buildings 253 CONCLUSIONS 1. A total of 379 fungal isolates belonging to 32 genera of moulds, yeasts and yeast-like fungi were obtained in the school environment. The following genera dominated: Aspergillus, Penicillium and Cladosporium. 2. Of the 72 fungal species determined, Cladosporium herbarum, Aspergillus fu- migatus and Penicillium chrysogenum occurred most frequently in the school build- ings. 3. Wall surfaces were characterised by an increased prevalence of mycobiota in comparison with the air in these buildings, with only slightly greater species diver- sity. 4. A certain species specificity for rough and smooth wall surfaces was shown. Fungi with large spores of the genera Cladosporium and Emericella adhered better to smooth surfaces while fungi with smaller conidia of the genus Aspergillus – to rough surfaces. 5. The application of three incubation temperatures helped determine a fuller range of fungi colonising the school buildings. REFERENCES B a r n e t t J. A., P a y n e R., Ya r r o w D. 1990. Yeasts: Characteristics and identification. Cambridge Univ. Press. B o g a c k a E . 1997. Choroba budynków. Mikol. Lek. 4 (4): 233–237. B o u c h a r a J.P., D e c l e r c k P., C i m o n B., P l a n c h e n a u l t C., d e G e n t i l e L., C h a b a s s e D . 1996. Routine use of CHROM agar Candida medium for presumptive identification of Candida yeast species and detection of mixed fungal populations. Clin Microbiol. Infect. 2 (3):202–208. B u d a k A . 1998. Mikotoksyny. (In:) E. B a r a n (ed.) Zarys mikologii lekarskiej. Volumed, Wrocław. D a c a r r o C., P i c c o A.M., G r i s o l i P., R o d o l f i M . 2003. Determination of aerial microbiological contamination in scholastic sports environments. J. App. Microbiol. 95: 904–912. D e H o o g G. S., G u a r r o J., G e n e J., F i g u e r a s M. J. 2000. Atlas of Clinical Fungi. Ed.2. Centraal- bureall voor Schiielcultures/ Universitat Rovira i Virgili. D y n o w s k a M. 1991/1992. The influence of antibiotics on the morphology of Candida albicans and Candida stellatoidea. Acta Mycol. 27 (1): 205–211. D y n o w s k a M. 1995. Drożdże i grzyby drożdżopodobne jako czynniki patogenne oraz bioindykatory ekosystemów wodnych. Rozpr. hab. Studia i Materiały WSP 77, Olsztyn: 1–83. D y n o w s k a M., B i e d u n k i e w i c z A . 1999. Presence of Saccharomycopsis capsularis in the human respiratory system. Acta Mycol. 38 (1/2): 71–87. E j d y s E. 2003. Fungal infection risk groups among school children. Acta Mycol. 34 (2): 281–287. E j d y s E. 2003. Bioróżnorodność mikocenoz jamy ustnej, gardła i nosa dzieci w wieku 6-15 lat. Wiad. Parazyt. 49 (4): 363–374. E z e o n u I.M., P r i c e D.L., S i m m o n s R.B., C r o w S.A., A h e a r n D.G. 1994. Fungal production of volatiles during growth on fibreglass. Appl. Environ. Microbiol., 60: 4172–4173. G e r l a c h D . 1972. Zarys mikrotechniki botanicznej. PWRiL, Warszawa. G u t a r o w s k a B., P i o t r o w s k a M., Ż a k o w s k a Z., W i s z n i e w s k a M., P a ł c z y ń s k i C. 2004. Zanieczyszczenie grzybami strzępkowymi pomieszczeń mieszkalnych w Łodzi i ich wpływ na zdrowie użytkowników – badania wstępne. Mikotoksyny i patogenne pleśnie w środowisku. VII Międzynarodowa Konferencja Naukowa, Bydgoszcz: 214–220. K r a w c z y k P., K o w a l s k i M.L., O c h ę c k a - S z y m a ń s k a A. 1999. Stężenie zarodników grzybów alergogennych w powietrzu mieszkań w Łodzi. Wiad. Parazyt. 45 (2): 255–262. K r e g e r - v a n R i j N.J.W. 1984. The yeasts: a taxonomic study. Third revision and enlarged edition. Els Sci. Publ. B. V., Amsterdam. 254 E. Ejdys K u r n a t o w s k a A . 1995. Wybrane zagadnienia mikologii medycznej. Promedi, Łódź. K r z y s z t o f i k B . 1992. Mikrobiologia powietrza. Wydawnictwo Politechniki Warszawskiej, Warszawa. L e v e t i n E., S h a u g h n e s s y R., F i s h e r E., L i g m a n B., H a r r i s o n J., B r e n n a n T. 1995. Indoor air quality in schools: exposure to fungal allergens. Aerobiologia 11: 27–34. M a c u r a A.B., G n i a d e k A . 2003. Flora mikologiczna w środowisku Domu Pomocy społecznej im. Helclów w Krakowie w różnych porach roku. Mikol. Lek. 10 (3): 179–185. M a g h a z y S.N., S h a a b a n G.M., E l - K a t a t n y M.S. 1996. Study of the dermatophytes in the stu- dents houses of Minia Universyty, Egipt. Acta Mycol. 31 (2): 191–197. Markiewicz Z., Kwiatkowski Z.A. 2001. Bakterie, antybiotyki, lekooporność. Wydawnictwo Naukowe PWN, Warszawa. M e k l i n T., H u s m a n T., Ve p s � l � i n e n A., Va h t e r i s t o M., K o i v i s t o J., H a l l a - A h o J., -T., H u s m a n T., Ve p s � l � i n e n A., Va h t e r i s t o M., K o i v i s t o J., H a l l a - A h o J., - H u s m a n T., Ve p s � l � i n e n A., Va h t e r i s t o M., K o i v i s t o J., H a l l a - A h o J., -T., Ve p s � l � i n e n A., Va h t e r i s t o M., K o i v i s t o J., H a l l a - A h o J., - Ve p s � l � i n e n A., Va h t e r i s t o M., K o i v i s t o J., H a l l a - A h o J., -A., Va h t e r i s t o M., K o i v i s t o J., H a l l a - A h o J., - Va h t e r i s t o M., K o i v i s t o J., H a l l a - A h o J., -M., K o i v i s t o J., H a l l a - A h o J., - K o i v i s t o J., H a l l a - A h o J., -J., H a l l a - A h o J., - H a l l a - A h o J., -J., - H y - v � r i n e n A., M o s c h a n d e r a s D., N e v a l a i n e n A . 2002. Indoor air microbes and respiratory symptoms of children in moisture damaged and reference schools. Inoor Air 12:175–183. R a p e r K.B., F e n n e l l D.I. 1965. The genus Aspergillus. Wilians, Wilkins, Baltimore. R a p e r K.B., T h o m C., F e n n e l l D.I. 1949. A manual of the Penicillia. Wilians, Wilkins, Baltimore. S h e l t o n B.G., K i r k l a n d K.H., F l a n d e r s W.D., M o r r i s G.K. 2002. Profiles of airborne fungi in buildings and outdoor environments in the United States. Appl. Environ. Microbiol. 68 (4): 1743– 1753. To p b a s M., To s u n I., C a n G., K a k l i k k a y a N., A y d i n F. 2006. Identification and seasonal distribution of airborne fungi in urban outdoor air in an eastern Black Sea Turkish town. Turk. J. Med. Sci. 36:31–36. Tr u d e a u W., F e r n a n d e s - C a l d a s E. 1994. Identifying and measuring indoor air biologic agents. J. Allergy Clin. Immunol. 94 (2): 393–400. Z y s k a B . 2001. Grzyby powietrza wewnętrznego w krajach europejskich. Mikol. Lek. 8 (3/4): 127–140. Grzyby izolowane z pomieszczeń szkolnych S t r e s z c z e n i e Celem badań było określenie składu gatunkowego grzybów występujących na powierzch- niach ścian i w powietrzu budynków szkolnych. Materiałem do badań były grzyby uzyska- ne z powietrza metodą sedymentacji i ze ścian techniką wymazu powierzchniowego, biorąc pod uwagę różne materiały wykończeniowe ścian. Próby pobierano z wybranych pomieszczeń dwóch szkół: sali lekcyjnej, korytarza, toalet damskiej i męskiej, szatni ogólnej, szatni sporto- wej oraz prysznica. Badanie przeprowadzono w maju 2005r., po zakończonym okresie grzew- czym. Grzyby hodowano na podłożu Chapek-Doxa równolegle w trzech temperaturach: 25, 37 i 40°C, przez co najmniej trzy tygodnie. W środowisku szkolnym z 321 prób uzyskano 379 izolatów grzybów z 32 rodzajów grzybów pleśniowych, drożdży i grzybów drożdżopodobnych. Najczęściej izolowano rodzaje: Aspergil- lus, Penicillium i Cladosporium. Z oznaczonych 72 gatunków grzybów najczęściej w pomiesz- czeniach szkolnych występował: Cladosporium herbarum, Aspergillus fumigatus i Penicillium chrysogenum. Powierzchnie ścian charakteryzowały się zwiększoną prewalencją mikobioty w stosunku do powietrza tych pomieszczeń, przy nieco większej różnorodności gatunkowej. Wykazano pewną specyficzność gatunkową grzybów dla szorstkich i gładkich powierzchni ścian. Do powierzchni gładkich lepiej przylegały grzyby o dużych zarodnikach z rodzaju Cla- dosporium i Emericella, natomiast do szorstkich o mniejszych konidiach, z rodzaju Aspergillus. Zastosowanie trzech temperatur inkubacji pozwoliło na nakreślenie pełniejszego obrazu mi- kobioty środowiska szkolnego. 2014-01-01T11:46:35+0100 Polish Botanical Society