Indian Journal of Agricultural Research

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Indian Journal of Agricultural Research, volume 55 issue 3 (june 2021) : 257-264

Effect of Soil Nutrient Management on P transformation under Protected Cultivation

Arindam Kumar Dutta1,*, Danish Tamuly1
1Department of Soil Science, Assam Agricultural University, Jorhat-785 001, Assam India.
Cite article:- Dutta Kumar Arindam, Tamuly Danish (2020). Effect of Soil Nutrient Management on P transformation under Protected Cultivation . Indian Journal of Agricultural Research. 55(3): 257-264. doi: 10.18805/IJARe.A-5448.
Background: Phosphorus, an essential element, plays a central role in cell metabolism and reproduction. It is a structural component of energy transferring molecules (ATP, ADP and AMP), nucleic acids, coenzymes, phosphor-proteins, phospholipids and sugar phosphates. In soils, the P does not occur abundantly as nitrogen or potassium. Despite its importance, only a proportion (~ 0.1-1.0 %) of it is available for use by plants and microorganisms because phosphorous has poor solubility and gets fixed in soil. Many studies had been done regarding nutrient management of soil in various parts of the world, but limited study was done in India and in North-East India, it is relatively unexplored. Thus, the main aim of this experiment was to find out how nutrient management influencing P fractions under protected cultivation.

Methods: The investigation area from which soil samples were collected i.e., Horticultural Farm, Assam Agricultural University, Jorhat-13, Assam. The study was carried out under protected poly house condition in the year 2017-18. The test crop was Capsicum (Capsicum annum var. Swarna). The design of the experiment was Split-Split plot technique. Random soil samples were collected from different treatments under protected cultivation at a depth of 0-15 cm. The soil samples were collected at two different stages of the crop viz., flowering and fruiting stages at 45 and 115 days after planting respectively.

Result: The present study revealed that single factor effect of nitrogen (N), phosphorus (P) and potassium (K) had a significant effect on different forms of P The readily available P forms tend to increase in the fruiting stage while the iron bound phosphates registered a decrease. This implies that iron bound phosphate form predominantly controlled available P in acid soils under protected cultivation. The study indicates that iron bound P may be considered as slowly available labile P for fertilizer scheduling under protected cultivation. The present study also revealed that single factor effect of nitrogen(N) and phosphorus(P) had a significant effect on yield of capsicum. Among the various P fractions, Pi-water and Pi-Fe contribute more towards yield of capsicum.
Phosphorus, an essential element, plays a central role in cell metabolism and reproduction. It is a structural component of energy transferring molecules (ATP, ADP and AMP), nucleic acids, coenzymes, phosphor-proteins, phospholipids and sugar phosphates. In soils, the P does not occur abundantly as nitrogen or potassium. But only a proportion (~ 0.1-1.0%) of it is available for use by plants and microorganisms because phosphorous has poor solubility and gets fixed in soil (Bednarek, 1992).
       
Phosphorus exists in soil in various forms. These may be categorized into four groups (Barber 1984), namely, (i) P in ions and compound in the soil solution (solution P); (ii) P adsorbed on the surface of inorganic soil constituents; (iii) P minerals, both crystalline and amorphous; and (iv) P as a compounds of organic matter. Solution P is a form that occurs in minimal quantity yet directly affects the P availability to plants in the forms of dihydrogen orthophosphate (H2PO4-) and mono hydrogen orthophosphate (HPO4-2).
       
Various P phases and fractions can be transformed to other fractions under certain conditions and have remarkable differences in mobility, bioavailability and chemical behaviors (Sharpley et al., 2000). Sequential extraction technique is used to define P fractions in soils qualitatively and quantitatively. Such information is useful for predicting P bioavailability, movement and transformations in agricultural soils. Thus, the main aim of this experiment were to find out how nutrient management influencing P fractions under protected cultivation.
The investigation area from which soil samples were collected i.e., Horticultural Farm, Assam Agricultural University, Jorhat-13, Assam is a part of old flood plain of the Brahmaputra river and located in between 26°44'N latitude and 94°12'S longitude and at an elevation of 91.0 m above mean sea level. The study was carried out under protected poly house condition in the year 2017-18. The test crop was Capsicum (Capsicum annum var. Swarna). The design of the experiment was Split-Split plot technique. The land was thoroughly prepared and divided into 3 blocks with 27 treatment plots per blocks Details of all the treatments are furnished in Table 1. Random soil samples were collected from different treatments under protected cultivation at a depth of 0-15 cm. The soil samples were collected at two different stages of the crop viz., flowering and fruiting stages at 45 and 115 DAP respectively. The soil were air dried, grounded and passed through a 2 mm sieve and analysed for different physico-chemical properties (soil texture (International pipette method), bulk density (Core method), particle density (Keen rackzowski box) along with Organic carbon (Walkey and Black (1934) method), Cation Exchange Capacity (NH4OAc Method) and Initial N (Alkaline potassium permanganate method), P (Bray’s-I method (1945) and K (Neutral normal ammonium acetate method) content and details flourished in Table 2.
 

Table 1: Treatment details and Allocation of treatments.


 

Table 2: Methods for determination of various parameters.


       
Fractionation of phosphorus was done by extracting the soil with different extracting agent. Various fraction of inorganic P (Pi) was sequentially extracted and the concentration of Pi in the extract was immediately determined by the phosphomolybdate colorimetric method of Murphy and Riley (1962) as described by Kuo (1996).
 
Statistical analysis
 
Data were subjected to analysis of variance using statistical package ‘MSTAT-C’ package (Freed, 2006). Whenever the F-test was significant (at 5% level) multiple comparison among the treatments were done with Duncan’s Multiple Range test (DMRT).
The results of the experiment that was carried out shows variations in the various P fractions upon nutrient management.
 
Loosely bound Phosphate (Pi-water)
 
During flowering stage of the crop, single factor effect of different level of nitrogen, phosphorus and potassium on loosely bound phosphate (Pi-water) was significant (Table 2a). The loosely bound phosphate (Pi-water) was significant with the interaction effect of NK (Table 4). The values varied between 1.821 and 2.900 mg kg-1 and the highest value was measures under N100K60. Moreover, interaction effect of PK (Table 5) with loosely bound phosphate (Pi-water) was also found to be significant and the highest value (3.124 mg kg-1) was found in the treatment P80K40. Loosely bound phosphate (Pi-water) was found to differ significantly with the interaction effect of NPK (Table 6) and the values varied from 1.336 (N80P60K80) to 3.682 mg kg-1 (N120P80K60). During fruiting stage of the crop, single factor effect of different level of nitrogen, phosphorus and potassium on loosely bound phosphate (Pi-water) was also significant (Table 2). Besides, loosely bound phosphate (Pi-water) was significant with the interaction effect of NK (Table 4). The values varied between 3.637 and 4.553mg kg-1 and the highest value was noted under N100K80. The interaction effect of PK with loosely bound phosphate (Pi-water) was also found to be significant and the highest value (4.728 mg kg-1) was registered under P80K80. Loosely bound phosphate (Pi-water) differed significantly with the interaction effect of NPK (Table 6) and the values varied from 2.719 mg kg-1 (N100P80K40) to 5.766 mg kg-1 (N100P80K80).
 

Table 2a: Single factor effect of N, P and K levels on various P fractions.


       
Loosely bound phosphate (Pi-water) significantly differed with the application of different levels of N, P and K fertilizers and their interaction. The easily soluble phosphate forms, increased with the application of higher dose of nutrients, although their concentration was low as compared to other labile and non-labile fractions. Thus mineral fertilization significantly affected the easily soluble phosphate fraction in soil. However, this P fraction relatively prone to migrate to the 20-40 cm soil layer under the influence of acid rain (Bednarek, Kaczor 1994) but it is relatively easily taken up by plants. The loosely bound phosphate or the Resin-Pi increased during fruiting stage. This may be due to transformation of relatively unavailable forms of P into available forms. Similar results were also reported by Chmielews et al., (1980). This increase in the fractions followed by decrease in the other fraction (NaOH-Pi, Ca-Pi) confirms the occurrence of P transformation in soil.

Aluminum phosphate (Pi-Al)
 
During flowering stage of the crop, single factor effect of different level of nitrogen, phosphorus and potassium on aluminum phosphate (Pi-Al) was significant (Table 2). NP interaction was also significant with the aluminum phosphate (Pi-Al) and the values varied from 2.637 to 9.174 mg kg-1 (Table 3). The highest value was noticed under N120P80. Besides, aluminum phosphate (Pi-Al) was also significant under interaction NK. The lowest (3.598 mg kg-1) and the highest (6.258 mg kg-1) values were obtained in the treatments N120K80 and N80K40 respectively. Additionally, interaction of PK with the aluminum phosphate (Pi-Al) was significant and the highest value (7.357 mg kg-1) was recorded in the treatment P60K40 (Table 5). During fruiting stage of the crop, single factor effect of different level of nitrogen, phosphorus and potassium was found to be significant (Table 2) with the aluminum phosphate (Pi-Al). NP interaction was also significant with the aluminum phosphate (Pi-Al) and the values varied from 5.933 to 13.62 mg kg-1 (Table 3). Aluminum phosphate (Pi-Al) was also significant under interaction of NK. Interaction PK with the aluminum phosphate (Pi-Al) was found to be significant. Aluminum phosphate (Pi-Al) also differed significantly under interaction of NPK (Table 6) and the values ranged between 2.954 mg kg-1 (N80P40K60) and 14.94 mg kg-1 (N100P80K40).
 

Table 3: Interaction effect of NP levels on various P fractions.


       
Aluminum phosphate (Pi-Al) also differed significantly under interaction of NPK and the values ranged between 1.135 (N80P40K40) and 11.79 mg kg-1 (N120P80K60). The aluminum phosphate (Pi-Al) also significantly differed with the different levels of NPK applied.The Pi-Al fraction increased with the increase in  level of nutrients. Similar results were also found by Chmielewska et al., (1980) and Bednarek (2011). At the same time, this fraction had a relatively high proportion in available phosphorus, as determined by different methods (Alexander and Robertson 1968). The Pi-Al content was ranged from 1.135-11.97 mg kg-1 in the flowering stage to 2.94-14.94 mg kg-1 of soil in the fruiting stage. The increase in the concentration of Pi-Al may be attributed to transformation of unavailable form into available form (Larsen S 1967).
 
Iron phosphate (Pi-Fe)
 
Data indicates that during flowering stage of the crop, single factor effect of nitrogen, phosphorus and potassium on Iron phosphate (Pi-Fe) was significant (Table 2). Interaction effect of NP on iron phosphate (Pi-Fe) was also significant and the highest value (90.89 mg kg-1) was recorded under N80P80 (Table 3). Iron phosphate (Pi-Fe) was also significant under interaction of NK and the highest value (84.19 mg kg-1) was recorded under N80K80. Besides, interaction effect of PK was also significant with the iron phosphate (Pi-Fe) and the values ranged between 70.40 and 87.81 mg kg-1 (Table 5). The highest value was obtained in the treatment receiving the highest level of phosphorus. Iron phosphate (Pi-Fe) was also differed significantly under interaction of NPK (Table 6) and the highest value (102.9 mg kg-1) was obtained in the treatment N80P80K80. Data showed that during fruiting stage of the crop, single factor effect of nitrogen was significant (Table 2) with the iron phosphate (Pi-Fe) and the values ranged from 55.84 to 64.28 mg kg-1. Further, different level of phosphorus and potassium on iron phosphate (Pi-Fe) was also significant. Interaction effect of NP on iron phosphate (Pi-Fe) was also significant and the highest value (71.51 mg kg-1) was found in the treatment N80P80. Beside this, iron phosphate (Pi-Fe) was also significant with the interaction effect of NK and the highest value (66.56 mg kg-1) was recorded under N80K80 (Table 4). Moreover, interaction of PK was also significant with the iron phosphate (Pi-Fe). The highest value was obtained in the treatment receiving the highest level of phosphorus and lowest dose of potassium (P80K40). Iron phosphate (Pi-Fe) was also differed significantly with the interaction of NPK (Table 6) and the highest value (73.61 mg kg-1) was obtained in the treatment N80P60K40.
 

Table 4: Interaction effect of NK levels on various P fractions.


 

Table 5: Interaction effect of PK levels on various P fractions.


 

Table 6: Interaction effect of NPK levels on various P fractions.


       
The iron phosphate (Pi-Fe) also differed significantly with the nutrient management and these fractions constitute a larger pool of P as compared to labile forms of phosphate (Resin-Pi and NaHCO3-Pi). The soils of Assam contain high amount of exchangeable Al3(Sahu et al., 2001). The acidity of the soils of north eastern region was attributed to the presence of Al3+ in clay complex. This explains the dominance of either Pi-Al or Pi-Fe fraction in acid soils of Assam (Halder et al., 1981). This pool is considered to be important to plant P nutrition and important in P transformation (Kumoyo et al., 2005). The iron phosphate fraction decreased at fruiting stage and this may be because of transformation of iron bound phosphate to more labile forms of phosphate and thereby increasing the availability of labile P fractions (Chao et al., 2015). In this way, hydroxide or acid extractable Pi (NaOH-Pi or HCl-P) may act as the quantity factor that buffers the more labile P forms.
 
Calcium phosphate (Pi-Ca)
 
Data revealed that during flowering stage of the crop, single factor effect of different levels of nitrogen, phosphorus and potassium on calcium phosphate (Pi-Ca) was significant (Table 2). Interaction effect of NP on calcium phosphate (Pi-Ca) was also significant (Table 3) and the values varied between 9.992 and 15.76 mg kg-1and the highest value was obtained under N120P40. Calcium phosphate (Pi-Ca) also differed significantly under interaction of NK and PK. Calcium phosphate (Pi-Ca) differed significantly under interaction of NPK (Table 6). The lowest value (5.098 mg kg-1) and the highest value (21.50 mg kg-1) were recorded under N80P60K60 and N80P80K80 respectively. Data revealed that during fruiting stage of the crop, single factor effect of different levels of nitrogen, phosphorus and potassium was significant (Table 2) with calcium phosphate (Pi-Ca). Interaction of different levels of NP on calcium phosphate (Pi-Ca) was also significant and the values varied between 9.23 and 17.07 mg kg-1 and the highest value was obtained under N120P40. Besides, calcium phosphate (Pi-Ca) was also significant under interaction effect of NK (Table 4). Interaction of PK was also significant under calcium phosphate (Pi-Ca) and the values ranged from 10.24 mg kg-1 (P40K80) to 17.79 mg kg-1 (P40K60).  Calcium phosphate (Pi-Ca) was differed significantly under the interaction of NPK (Table 6). The lowest value (3.928 mg kg-1) and the highest value (22.45 mg kg-1) were recorded under N80P60K60 and N80P80K80 respectively.
       
Apatite phosphate (Pi-Ca) differed significantly with the different levels of NPK and the values ranged between 5.09-21.50 mg kg-1 at the flowering stage and 3.928-22.45 g kg-1 at fruiting stage. This fraction also constitutes a small proportion as compared to the total Pi fraction in soil. This is because as the soil is acidic, they do not contains much calcium as most of the cations are leached down due to rainfall or application of irrigation (Kumoyo et al., 2005). Talashikar et al., (2006) in some lateritic soils of Konkan region of Maharashtra found that Total-P, Ca-P and Occluded-P increased with the increased in acidity.
 
Residual phosphate (Residual-Pi)
 
Data indicated that during flowering stage of the crop, the single factor effect of different level of nitrogen on residual phosphate (Residual-Pi) was non-significant (Table 2). The effect of levels of phosphorus and potassium on residual phosphate (Residual-Pi) was also non-significant.  Interaction effect of NP with the residual phosphate (Residual-Pi) was also non-significant (Table 3). Besides, residual fraction of P was also non-significant with the interaction of NK. Moreover, interaction of PK and NPK was also non-significant with the residual phosphate (Residual-Pi).
       
Residual phosphate (Residual-Pi) was non-significant with the interaction effect of NPK. The concentrated H2SO4 digested P (Residual P) is the P which is not readily removed by 0.5 M NaHCO3, 0.1M NaOH or 1M HCl extracting solution and is considered to be a recalcitrant P form of very low solubility and availability, with the residual P as the most resistant fraction (Tiessen and Moir, 1993). It was found that residual P was very high indicating that most of the soil P was found in residual form. The nutrient management on residual-P was non-significant as it has very low solubility and do not had any effect on application of different levels of fertilizers (O’Halloran, 1993; Richards et al., 1995; Tran and N’dayegamiye, 1995; Zhang and MacKenzie, 1997a, 1997b).
 
Effect of nutrient management on yield and yield prediction by various P fractions
 
Data indicated that nutrient management does influence the yield of capsicum. Single factor effect of different nitrogen levels on yield was significant (Table 7) and the highest value obtained at N120 (4288 g/plant). Phosphorus also significantly influence the yield of capsicum and the highest value was recorded on P80 (3577 g/plant). Different levels of potassium were not significantly influence the yield of capsicum.
 

Table 7: Single factor effect of N, P and K levels on Yield.


       
Using Artificial Neural Networking method (Fig 1), we tried to find out which P fraction is able to contribute more to the yield of capsicum and we found that Pi-water and Pi-Fe have an impact on yield of capsicum indicating that these two fractions contribute more to the yield of capsicum as compared to other P fractions.
 

Fig 1: Artificial neural network showing the influence of P fraction in predicting the yield of capsicum.

The various fractions of P in the plow layer (0-15 cm) of acidic soil under 27 different treatments of nutrient management were evaluated using a sequential extraction method. Results revealed that, different soil nutrient management has a significant influence on various P fractions viz., Pi-water, Al-P, Fe-P, Ca-P, except for residual-P fractions. Soil nutrient management also influences the transformation of P. The availability of readily available P tends to increase in the fruiting stage as compared to the flowering stage of the crop which may be due to transformation of P from unavailable form to available form, which in turn helps in growth and development of the plant. Resin-Pi and NaOH-Pi contribute more to the yield attributes as compared to the other P fractions.

  1. Alexander, T.G., Robertson J.A., (1968). Inorganic phosphorus forms in some Alberta soils as related to soil development, parent material and available phosphorus. Canad. J. Soil Sci. 48: 289-295.

  2. Barber, S.A. (1984). Soil nutrient bioavailability: A mechanistic approach. Wiley. New York.

  3. Bednarek, W. (1992). Phosphorus Uptake by Cultivable Plants From the Soil Fertilized by Means of Unconventional Fertilizers. Part I (in Polish). Phosphorus Forms in the Soil. Ann. UMCS, sec. E. 47: 85-98.

  4. Bednarek W., (201)1. Mineral fertilization effect on timothy-grass yield (in Polish). Acta Agroph. 17 (2): 267-275.

  5. Blake, G.R. and Hartge, K.H. (1986). Bulk density. In [A. Klute (ed.)]. Methods of Soil Analysis, part1. Agronomy 9, ASA, Madison, WI p.363-375.

  6. Bray, R.H. and Kurtz, L.T. (1945). Determination of Total Organic and Available Forms of Phosphorus in Soils. Soil Science. 59: 39-45.

  7. Chao, A., Chiu, C.-H., Hsieh, T., Davis, T., Nipperess, D.A. and Faith, D.P. (2015). Rarefaction and extrapolation of phylogenetic diversity. 6: 380-388.

  8. Chmielewska, B., Myszka, A., Kupisz, E. (1980). The influence of once-applicable, differentiated doses of phosphorus on the contents of its both various mineral fractions and the available P in brown loess soil (in Polish). Prace nauk. AE we Wroc³awiu, Chemia. 159: 191-202.

  9. Freed, R. (2006). MSTAT-C version 7. Department of crop and Soil Science. Michigan State University.

  10. Halder, B.R. (1979). Studies on the reduction of native and applied sulphate under waterlogged condition in some soils of Assam. M.Sc (Agri) thesis, Assam Agricultural University, Jorhat-13.

  11. Kumoyo, K., Yerokun, O.A., Damaseke, M.I. (2005) Changes in organic phosphorus following incubation of some Zambian soils. S Afr J Plant Soil. 22: 149-53

  12. Kuo, S. (1996). Phosphorus. In: Methods of soil analysis, [ed. D. L. Sparks.] : ASA-SSSA. Madison, Wisc. 

  13. Larsen, S. (1967) Soil phosphorus. Adv Agron. 19: 151-210.

  14. Murphy, J. and Riley, J.P. (1962). A modified single solution method for the determination of phosphate in natural waters. Analytica Chimica Acta. 27: 31-36.

  15. O’Halloran, I.P. (1993). Effect of tillage and fertilizer on the inorganic and organic phosphorus. Can. J. Soil Sci. 73: 359-369.

  16. Piper, C.S. (1966) Soil and Plant Analysis. Hans Publisher. Bombay.

  17. Richards, J.E., Bates, T.E. and Sheppard, S.C. (1995). Change in the forms and distribution of soil phosphorus due to long-term corn production. Can. J. Soil Sci. 75: 311-318.

  18. Sahu, G.C., Mishra, K.N., Parida, R., Nayak, R.K. (2001) Characterization and classification of some Vertisols of western zone in Orissa. Agro-pedology. 11: 78-82.

  19. Sharpley, A.N., Foy, B. and Withers, P.J. (2000). Practical and innovative measures for the control of agricultural phosphorus losses to water and phosphorus availability and transformation as affected by repeated phosphorus additions in an Ultisol: An overview. Journal of Environment Quality. 29: 1-9.

  20. Subbiah, B.V. and Asija, G.L. (1956). A rapid procedure for the estimation of available nitrogen in soils. Current Sci. 25: 259 

  21. Talashilkar, S.C. Mehta, V.B. Dosani, A.A. Dhopavkar, R.V. and Dhekale, J.S. (2006). Influence of soil reaction on soil acidity parameters and fractions of organic matter, nitrogen, phosphorus and potassium in lateritic soils of konkan. J. Indian Soc. Soil Sci. 54(2): 174-178

  22. Walkley, A. and Black, I.A. (1934). An examination of the Degtjareff method for determining soil organic matter and a proposed modification of the chromic acid titration method. Soil Science. 37: 29-38.

  23. Zhang, T.Q. and MacKenzie, A.F. (1997a). Changes of soil phosphorus fractions under longterm corn monoculture. Soil Sci. Soc. Am. J. 61: 485-493.

  24. Zhang, T.Q. and Mackenzie, A.F. (1997c). Changes of phosphorous fractions under continuous corn production in a temperate clay soil. Plant Soil. 192: 133-139.

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