Maataloustieteellinen A ikakauskirja Vol. 61: 61—66, 1989 Effect of cumulative fertilizer dressings on the phosphorus status of mineral soils II Comparison of two phosphorus testing methods HELINÄ HARTIKAINEN Department of Agricultural Chemistry, University of Helsinki, SF-00710 Helsinki, Finland Abstract. Soil samples collected from field plots before onset of fertilization trials and after seven years of cultivation with annual P additions of 0, 30 or 60 kg ha-1 , were analyzed for water-soluble P (P„) and acid NH 4-acetate-extractable P (P AAc ). I'l all soil samples, the P test values correlated closely (r =o.93***). However, they differed significantly in the clay soils where PAAc amounted to 59—96 Vo of P w . In the coarser soils, the acetate solution ex- tracted 70—365 Vo of the water-soluble P, but the difference between the methods remained insignificant. In both soil groups, the molar ratio of NH4F-P to oxalate-soluble Al explained 90 Vo or more of the variation in the P test values. The soil samples were divided into different P content classes according to the acetate test calibration scheme. In various P classes the test values tended to differ statistically signifi- cantly: in the lower classes acetate extracted P more and in the higher classes less than water did. Only in soils ranked as satisfactory in P the test values were about equal. When the rating scale limits given for the advisory soil testing were applied to the water extraction, in most soils the difference between the P testing methods was of one P class. The fertilization recom- mendations based on the acetate and water extraction tests were compared. Index words: P tests, water extraction, acid acetate extraction Introduction A great deal of fertilizer P is known to ac- cumulate in acid soils. In Finnish soils, the retention of superphosphate P by soil consti- tuents and the low solubility of rock phos- phate have been demonstrated in detail by Kaila (e.g. 1961, 1963, 1969). With time, the accumulation of P may alter the rate of fer- tilizer needed. Although newly added P is more readily available to plants than residual reserves, the yield response to freshly applied P decreases when the residual P level is high (Mattingly and Widdowson 1963). Long- term residual contributions of P fertilizer to crop yields and P uptake have been shown in numerous studies (e.g. Campbell 1965, Bailey et al. 1977, Halvorsson and Black 61 JOURNAL OF AGRICULTURAL SCIENCE IN FINLAND https://www.c-info.fi/en/info/?token=OZ-1CltvI0caoAba.u69j15X62talki5O6j4-Cw.ZcBY_UyinOQA-OwFCCEZvdJ1BB3xNjk-UVVcCXVn1bfLT7T3Soi2g-Z-rcrVYi-xKA0-hFDLbu8Tg9IY995bELgQ13LG1Vs0Q8Dg2h3VOH9MXOYsHwwElZ-KFK8xgBoPsAE6ePjIO5YIPwCRSMfBfaLBqh19ZTysD9Rk4AolXDX8KoC8Mw 1985). Thus, it is important that the P tests used as the basis for P fertilization recommen- dations are sensitive enough to describe the changes in P resources. A previous paper of Hartikainen (1989) reported changes in various inorganic P frac- tions in soil samples from a series of long-term field experiments as a result of different P fer- tilization regimens. In the present study, the same material was used to compare the P test values obtained by the water extraction and by the acid NH 4-acetate extraction applied in routine soil testing in Finland. The depend- ence of the P test values on inorganic P frac- tions was investigated statistically. Material and methods The soil samples were collected from 16 field trials consisting of plots cultivated for seven years without P addition or fertilized an- nually with superphosphate in quantities cor- responding to 30 or 60 kg of P ha '. The control samples were taken from the ex- perimental fields before onset of the trials. The characteristics of the experimental soils and the methods of soil analyses are given in the first part of this study (Hartikainen 1989). Acetate-soluble P ( =PAac) was extracted according to Vuorinen and Mäkitie (1955); the air-dried and 2 mm sieved soil samples were shaken in triplicate for 1 h with acid NH4OAc (0.5 M CH 3COOH, 0.5 M CHr COONH 4 , pH 4.65) at a soihsolution ratio of 1:10 (w/v). The extracts were analyzed for P by a molybdenum blue-stannous chloride method of Kaila (1955). Water-soluble P ( =P w ) was extracted by a modified van der Paauw and Sissingh method at a soihsolu- tion ratio of 1:60 (w/v) (Hartikainen 1982) and analyzed by a molybdenum blue-ascorbic acid method (Anon. 1969). Results The P test values in soil samples collected from the experimental field before onset of trials and from plots fertilized in total with 0, 210 or 420 kg of P ha 1 are listed in Table 1. In all soil samples, the acetate-soluble and water-soluble P were closely correlated (r = Table I. P test values (mg kg-1 ) (AAc = acid NH 4OAc test, W = water extraction test) in the soil samples before and after P fertilization trials. After total P addition (kg ha 1) of Soil Before trial 0 210 420 AAc W AAc W AAc W AAc W Clay soils 1 5.0 7.0 3.8 4.2 5.5 6.3 8.5 10.5 2 15.5 23.8 12.7 15.1 14.8 17.7 18.3 24.2 3 7.3 10.3 5.3 6.7 9.0 13.7 13.3 22.4 4 17.5 18.2 11.5 14.4 17.5 20.4 18.3 24.2 5 4.9 7.2 3.5 5.6 5.0 8.0 6.8 11.6 Coarser soils 6 12.4 9.5 10.3 9.0 11.7 10.3 12.7 10.2 7 4.5 6.4 3.0 3.3 5.0 6.3 7.0 9.4 8 16.8 19.3 10.8 13.2 16.5 21.7 24.5 32.3 9 29.8 32.0 26.0 31.1 34.0 41.3 36.9 45.5 10 5.8 2.6 5.0 2.3 7.3 3.1 8.5 3.8 11 9.3 4.1 8.8 3.8 11.3 5.5 13.8 7.4 12 10.8 6.9 8.8 6.7 10.5 8.8 10.0 7.4 13 9.5 9.3 7.5 6.3 9.3 7.4 13.2 12.9 14 4.3 3.0 4.3 1.9 6.0 2.7 7.4 3.1 15 7.8 3.3 8.4 2.3 10.4 3.0 10.8 3.5 16 10.0 13.0 10.2 9.8 14.8 14.9 17.3 19.6 62 63 o.93***, n = 64) and their mean values (11.4 and 11.7 mg kg ', respectively) were about equal. However, in various textural soil groups these methods seemed to extract P in- congruently: in the clay soils P AAc amounted to 59 —96 °/o of P w , whereas in the coarser soils the range was decisively wider, 70 — 365 %. The relationship between the P test values (mg kg~') conformed to the equa- tions: clay soils: P AAc = 0.09 + 0.74 P w R 2 = o.9o*** (n =20) coarser soils: P AAc =4.41 +0.69 Pw R 2 = o.92*** (n =44) Table 2. Rating scale for P (mg 1 ■') in soils of dif- ferent textures (Anon. 1986). Clay soils Coarser soils Poor 1.4 1.9 Rather poor 1.5—2.9 2.0—4.9 Fair 3.0 5.9 5.0 9.9 Satisfactory 6.0—11.9 10.0—19.9 Good 12.0—29.9 20.0—39.9 High 30.0—69.9 40.0—69.9 In fact, the paired t-statistics revealed that the estimates for soil P obtained by NH4OAc extraction and those by water extraction differed significantly in the clay soils, where- as in the coarser ones the differences remained statistically insignificant. The soil samples were classified as to their P content according to the advisory P test cal- ibration scheme given in Table 2 (except that the extractability was expressed in mg kg'). The rating in Table 3 reveals that a cumula- tive P addition of 210 kg ha^ 1 did not affect the PAAc concentration classes of the clay soils, but raised them in four coarser soils (7, 11, 14 and 15) that had initially been ranked as fair or rather poor in P. When the water extraction results were interpreted by using the P level limits given for the NH 4OAc extraction test, the P class was raised in five soils (3, 6,8, 9 and 11) that had originally been categorized as rather poor to good in P (Table 3). Very heavy P dressings (totally 420 kg ha~') were needed in five soils to upgrade the P class according to the NH 4 OAc extraction, and in one soil accord- Table 3. Rating of soil samples for P according to the acid NH 4OAc test (AAc) and the water extraction test (W) before and after P fertilization trials (1 = poor, 2 = rather poor, 3 = fair, 4 = satisfactory, 5 = good, 6 = high). After total P addition (kg ha-') of Soil Before trial 0 210 420 AAc w AAc W AAc W AAc W Clay soils 1 3 4 3 3 3 4 4 4 2 5 5 5 5 5 5 5 5 3 4 4 3 4 4 5 5 5 4 5 5 4 5 5 5 5 5 5 3 4 3 3 3 4 4 4 Coarser soils 6 4 3 4 3 4 4 4 4 2 3 2 2 3 3 3 3 8 4 4 4 4 4 5 5 5 9 5 5 5 5 5 6 5 6 10 3 2 3 2 3 2 3 2 11 3 2 3 2 4 3 4 3 '2 4 3 3 3 4 3 4 3 13 3 3 3 3 3 3 4 4 14 2 2 2 1 3 2 3 2 15 3 2 3 2 4 2 4 2 16 44 43 44 44 Table 4. Correlation coefficients for the relation between the P test values and inorganic P fraction characteristics. P extracted sequentially by Test Soil group NH 4F NaOH H :S0 4 NH 4F-P/A1 NaOH-P/Fe "aAI Clays o.9o*** o.9l*** 0.37 o.9s*** o.9s*** Coarser soils 0.18 0.19 0.47** o.9s*** 0.45** All soils 0.31* 0.28* 0.45** o.9s*** o.sl*** P, Clays o.Bs*** o.BB*** 0.38 o.9s*** o.B6*** Coarser soils 0.10 0.04 o.ss*** o.97*** 0.44** All soils 0.13 0.20 o.s2*** o.94*** o.s4*** ing to the water extraction. There were five soils (fair to good in P AAc or rather poor to good in P w) in which not even this dosage was enough to affect the rating. In order to compare the testing methods in more detail, the relation between Pw and P AAc was studied also within individual P classes. The correlation coefficients were: rather poor or fair soils r = 0.12 (n =27), satisfactory soils r = 0.58** (n = 24) and good soils r =o.9s*** (n= 13). The paired t-statistics revealed, how- ever, that the P test values did not differ in soils classified as satisfactory, whereas they differed significantly in soils of the other cat- egories: in the lower P classes acetate tended to extract more, and in the higher classes it extracted less than water did. Discussion The affinity of a given inorganic P frac- tion to desorb P into water has been found to be controlled by the quantity of the cor- responding sorption component (Hartikai- nen 1982). This seemed to hold true also for acid NH 4-acetate soluble P which was close- ly correlated with the molar ratio of NH 4F-P (“Al-P”) to oxalate-soluble Al. Furthermore, both P test values correlated with the ratio of NaOH-P (“Fe-P”) to oxalate-soluble Fe in the clay soils but not in the coarser soils, where the variation in the Fe content was very wide and, thus, despite the same “saturation de- gree” the soil samples might markedly differ in their content of free active sorption agents (cf. Hartikainen 1982). In the first part of this study (Hartikainen 1989) the H 2S0 4 - soluble fraction was found to be quite inac- tive, for which reason P was hardly desorbed from these reserves, at least in the water ex- traction. The correlation coefficients for the relation between the P test values and the inorganic P fractions investigated in the first part of this study (Hartikainen 1989) are presented in Table 4. In the clay soils, both P test values correlated closely with the P extracted by NH4F and NaOH, in the coarser soils with the P soluble in H2S0 4 . However, the molar ratio of NH 4F-P to oxalate-soluble Al was a factor that explained the variation in both test values to a marked degree, whereas the cor- responding molar ratio NaOH-P/Fe explained the variation only in the clay soils. Accord- ingly, the increases in the P test values seemed to be related to the increase in the NH 4F-P: in the clay soils the r values were 0.86** and 0.67* for P w and P AAc; the respective values in the coarser soils were 0.50* and o.7s***. The sorption of P is reversible with respect to changes in pH, and increases as the pH decreases (e.g. Muljadi et al. 1966). The differences in P quantities extracted by the methods compared may partly be attributable to the dissimilar pH of the contacting solu- tion. In the water extraction, thepH depends largely on the soil acidity. In the acetate meth- od, on the contrary, the extraction takes place in acid buffered (pH 4.65) conditions, which may enhance the resorption of dissolved P. In fact, in soils with pH>5.O, P w was higher than P AAc . 64 Both P test values were, on average, of the same magnitude. Average extraction results or regression equation may, however, give too approximate estimates of the equality of two methods in routine soil testing. From the prac- tical point of view, it is important to know how markedly the methods differ in individual soil samples. When the extraction results were interpreted by using the same scale of P classes, half of the control samples were iden- tically ranked by both P testing methods, three control samples were ranked higher and five soils were ranked lower by water than by NH 4OAc. A similar variation in the reactivi- ty of soil P with respect to these extractants can be seen in the data published by Sippola and Jaakkola (1980). The soil material was too limited to allow any far-reaching conclusions to be drawn, but the different fertilization backgrounds seemed to change Pw more than P AAc, and to alter the P classes more sensitively when the rating was based on P„ instead of on PAAc. This response is similar to that found by Prummel (1980) in a long-term fertilization study where the P-citr (1 % citric acid) and P-AL (ammonium lactate-acetic acid) in- creased less than P w . In the present study, the changes found in a given soil by the NH4OAc extraction test generally were not obtainable by the water extraction test, and vice versa. According to the NH 4OAc test, long-term cultivation without P fertilization lowered the P class in three soils (3, 4 and 12) which had originally been rich in secondary P and had been ranked as satisfactory or good. Water extraction revealed a reduction in five soils (1, 5,7, 11 and 16) the P status of which ranged from rather poor to satisfac- tory. References Anon. 1969. Juoma- ja talousveden tutkimusmenetel- mät. Elintarviketutkijain Seura. 169 p. Helsinki. Anon. 1986. Viljavuustutkimuksen tulkinta peltoviljelys- sä. Viljavuuspalvelu Oy. If the ranges used for the P rating scale are the same regardless of the P extraction meth- od, the rating for many samples differsby one class. This, in turn, means that fertilization recommendations based on the NH 4OAc ex- traction test are not necessarily valid in the sys- tem based on the water extraction test. For in- stance, if the data in Table 3 are employed for fertilization recommendations according to the advisory soil test calibration scheme (Anon. 1986), in the clay soil samples the P fertilizer requirement for grasses, cereals, leguminous or oil plants is, on average, 10 kg ha^ 1 lower in the Pw than in the PAAc system. In coarser soils, on the contrary, the rating system based on Pw more often increases the recommended P dosages. However, in two subsamples of soil 9 there would be no need for P addition. The most striking difference between the rating systems was found in soil 15; the water extraction ranked its P level as being rather poor irrespective of the fertilization history, whereas according to the NH 4OAc extraction test it was fair and further improved by fer- tilization. In practice, this means that the P fertilization recommendations for most crops would differ by 20 kg ha-1 . The superiority of NH 4OAc to water in extracting P from this soil and the differences found in the many other samples suggest that the extractability of P by the solutions compared are controlled by dissimilar factors. Acknowledgcmenl. The author wishes to thank Prof. Paavo Elonen and Dr, Into Saarela, Agricultural Research Centre, and the staff of the research stations for their help in collecting the soil samples. The financial support of the Academy of Finland is gratefully acknowledged. Bailey, L.D., Spratt, E.D., Read, D.W.L., Warder, F.G. & Ferguson, W.S. 1977. Residual effects of phosphorus fertilizer for wheat and flax grown on chernozemic soils in Manitoba. Can. J. Soil Sci. 57: 65 263—270. Campbell, R.E. 1965. Phosphorus fertilizer residual ef- fects on irrigated crops in rotation. Soil Sci. Soc. Amer. Proc. 29: 67—70. Halvorsson, A.D. & Black, A.L. 1985.Fertilizer phos- phorus recovery after seventeen years of dryland crop- ping. Soil Sei. Soc. Amer. J, 49: 933—937. Hartikainen, H. 1982. Water soluble phosphorus in Finnish mineral soils and its dependence on soil properties. J. Scient, Agric. Soc. Finl. 54: 89—98. Hartikainen, H. 1989. Effect of cumulative fertilizer dressings on the phosphorus status of mineral soils. 1 Changes in inorganic phosphorus fractions. J. Agric. Sci. Finl. 61: 55—59, Kaila, A. 1955. Studies on the colorimetric determina- tion of phosphorus in soil extracts. Acta Agr. Fenn. 83: 25—47. Kaila, A. 1961. Fertilizer phosphorus in some Finnish mineral soils. J. Scient. Agric. Soc. Finl. 33: 131—139. Kaila, A. 1963. Fertilizer phosphorus in various frac- tions of soil phosphorus. J. Scient. Agric. Soc. Finl. 35: 36—46. Kaila, A. 1969. Residual effect of rock phosphate and SELOSTUS Pitkäaikaisen superfosfaattilannoituksen vaikutus kivennäismaiden fosforililaan Il Kahden uuttotestin vertailu Helinä Hartikainen Helsingin yliopisto, Maanviljelyskemian laitos, 00710 Helsinki Tutkimuksessa vertailtiin vesiuutolla ja viljavuusana- lyysissä käytettävällä happamalla äsetaattiuutolla saatu- ja fosforin testiarvoja. Maanäytteet oli koottu Maatalou- den Tutkimuskeskuksen eri tutkimusasemilla olleesta 16 fosforilannoituskokeesta ruuduilta, joiden 7 vuoden aikana saama vuosittainen superfosfaattilannoitusoli 0, 30 ja 60 kg P:a ha-1 . Tutkimuksen ensimmäisessä vai- heessa oli selvitetty eri lannoituskäsittelyjenaiheuttamat muutokset epäorgaanissa fosforifraktiossa. Karkeista kivennäismaista asetaatti uutti fosforia kes- kimäärin yhtä paljon, mutta savimaista vähemmän kuin vesi. Savimaiden ryhmässä uuttomenetelmien välinen ero oli tilastollisesti merkitsevä. Kun maanäyteaineisto jaet- tiin viljavuusanalyysin tulkintaohjeiden mukaisiin vilja- vuusluokkiin, eri uuttomenetelmien todettiin antavan suunnilleen samansuuruisia tuloksia vain fosforitilaltaan superphosphate. J. Scient. Agric. Soc. Finl. 41: 82—88. Mattingly, G.E.G. & Widdowson, F.V. 1963. Residual value of superphosphate and rock phosphate on an acid soil. I. Yields and phosphorusuptake in the field. J. Agric. Sci. 60: 394—407. Muljadi, D., Posner, A.M. & Quirk, J.P. 1966. The mechanism of phosphate adsorption by kaolinite, gibbsite and pseudoboehmite. I The isotherms and ef- fect of pH on adsorption. J. Soil Sci. 17: 212—228. Prummel, J. 1980. Fertilizer regime and changes in the phosphate and potash status of a silty marine clay soil during 25 years. Fertilizer Research 1: 95—101. Sippola, J. & Jaakkola, A. 1980. Maasta eri menetelmil- lä määritetyt typpi, fosfori ja kalium lannoitustarpeen osoittajina astia- ja kenttäkokeissa. Maatalouden Tut- kimuskeskus. Maanviljelyskemian ja -fysiikan laitos. Tiedote n:o 13. Vuorinen, J. & Mäkitie, O. 1955. The method of soil testing in use in Finland. Agrogeol. Pubi. 63: 1—44. Ms received July 25, 88 tyydyttäviksi luokitelluissa maissa. Alemmissa viljavuus- luokissa asetaatti pyrki uuttamaan fosforia tehokkaam- min ja ylemmässä luokassa huonommin kuin vesi. Fosforin väheneminen tai kertyminen näytti kuitenkin vaikuttavan suhteellisen vähän viljavuustutkimuksen mu- kaiseen fosforiluokitukseen; lannoittamattomissa koejä- senissä viljavuusluokka laski kahden savimaan ja vain yhden karkean maan kohdalla. Kohtalainen lannoitus (30 kg P) ei vaikuttanut savimaiden luokitukseen lainkaan, mutta karkeiden maiden ryhmässä nosti sitä neljässä ta- pauksessa. Kun vesi- ja asetaattiuuton tuloksia tulkittiin käyttämällä samoja luokitusrajoja, uuttotestien antama käsitys maan fosforitilasta poikkesi usein yhdellä fosfo- riluokalla. Useimpien viljelykasvien kohdalla eron aiheut- tama muutos lannoitussuosituksessa olisi 10 kg P ha-1 . 66