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Research Detail

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M. A. Saleque
Senior Scientific Officer
Soil Science Division, BRRI Gazipur

U.A. Naher
Scientific Officer
Soil Science Division, BRRI Gazipur

A.B.M.B.U. Pathan
Scientific Officer
Soil Science Division, BRRI Gazipur

A. T. M. S. Hossain
Scientific Officer
Soil Science Division, BRRI Gazipur

Aminul Islam
Scientific Officer
Soil Science Division, BRRI Gazipur

The changes in inorganic P (Pi) and organic P (Po) pools of lowland rice soils receiving no P fertilizer (control), the application of chemical P fertilizer alone (NPK) or in combination with cow dung (NPK + CD) for eight years were determined. The NPK plots received 192 kg P ha-1 as triple super phosphate (TSP) and the NPK + CD treatment received 392 kg P ha-1 in eight years. During the eight years, the total P uptake by rice from the control plot was 127 kg ha-1, from NPK plot it was about 207 kg ha-1 and from NPK + CD plot it was about 203 kg ha-1. Simple arithmetic calculations indicated that about 127 kg P ha-1 was mined from the control plots, the NPK plot depleted only about 15 kg P ha-1 and there was an accumulation of about 189 kg P ha-1 in the NPK + CD plots. After eight years of experimentation, the surface (0-15 cm) and subsurface (15-30 cm) soils of the control plots and NPK plots had similar solution-P concentration. The NaHCO3—-P, NaOH-Pi, acid-P and residual-P in the control plots were much lower than that of NPK plots. Compared with NPK treatment, there was an accumulation of solution-P, NaHCO3—-P, NaOH-Pi, acid-P and residual-P fractions in the soils of NPK + CD treatment. The concentrations of NaHCO3—-P, NaOH-Pi, acid-P and residual-P were lower in surface than in subsurface soils in the control plots, but these fractions of P were higher in surface than in the subsurface soils of the NPK + CD plots.

  Phosphorus fractions, Lowland rice and Fertilizer
  Bangladesh Rice Research Institute (BRRI) farm and Soil Science Lab, BRRI, Gazipur
  01-01-1999
  31-12-1999
  Crop-Soil-Water Management
  Soil fertility

          To compare changes in the inorganic and organic fractions of phosphorus (P) due to continuous application of cowdung (CD) and TSP to soil for eight years.

Soils of the study obtained from surface (0-15 cm) and sub-surface (15-30 cm) of the plots of three treatments- control, NPK and NPK + CD of the long-term integrated nutrient management experimental field at BRRI farm, Gazipur. During the last eight years (1990-1997) control plot received no fertilizer, NPK plot received 192 kg P ha-1 as triple super phosphate (TSP) and NPK + CD plot received 392 kg P ha-1 (192 kg as TSP and 200 kg as CD), respectively. The soil samples were air-dried, crushed, and passed through 2-mm sieve and stored in polyethylene bags at room temperature.

Fraction of inorganic and organic P was performed on each soil by a modified P fractionation scheme of Saleque and Kirk (1995). The following soil P fractions were measured in sequence:

(1) Solution P, by shaking 1 g soil in 30 ml of 0.05MCaCl2 for 16 h, centrifuging, filtering, and measuring P in the filtrate.

(2) NaHCO3–P, by shaking the residue from (1) in 30 ml of 0.5 M NaHCO3 for 16 h, centrifuging, filtering, and measuring P in the filtrate.

(3) NaOH-Pi–P, by shaking the residue from (2) in 30 ml of 0.1 M NaOH, centrifuging, filtering, and measuring P in the filtrate.

(4) NaOH-P0–P, by digesting 5 ml of the filtrate from (2) in 6 ml of concentrated H2SO4 for 1 h, cooling, adding 5 ml of H2O2, and re-heating until the residue became white, determining P in the digest, and subtracting NaOH-Pi–P from it.

(5) Acid P, by shaking the residue from (3) in 30 ml of 1:1 mixture of 1 M HCl/1 M H2SO4, centrifuging, filtering, and measuring P in the filtrate.

(6) Residual P, by refluxing the soil residue from (5) in 6 ml of a 5:2 mixture of concentrated HNO3 and HClO4, and determining P from the digest.

All P was determined colorimetrically (Murphy and Riley, 1962) after neutralization when necessary with dilute HCl and NaOH and the neutral pH indicated by the light yellow color of the solution in the presence of P-nitrophenol indicator.

  Bangladesh J. Agril. Sci. 29 (2):259-265, July, 2002.
  
Funding Source:
1.  Government Budget:  
  

Solution P: Control plots contained 0.14 mg P kg-1 in the surface soil and that in the NPK treated plots was 0.12 mg kg-1. Application of CD along with NPK increased solution P to 0.27 mg kg-1. Concentration of solution P in the surface soil was consistently lower than in the subsurface soil in all the three treatments. NaHCO3—-P: Concentration of NaHCO3—-P of control plot was 5.3 mg kg-1 in surface and 7.6 mg kg-1 in the subsurface soil. The NPK treated plot contained 13.4 mg kg-1 in the surface while subsurface soil contained 11.5 mg P kg-1. Application of CD increased P content to 38.2 mg kg-1 in the surface and 25.9 mg kg-1 in the subsurface soil. NaOH-Pi: Control plot had only 23,8 mg kg-1 P in the surface soil but 40.0 mg kg-1 P in the subsurface soil. Subsurface soil of NPK treated plot contained similar concentration of NaOH-Pi as in control plot but the surface soil of former contained about double amount of NaOH-Pi tan that of latter . There was about 2-folds increase in NaOH-Pi in the surface and subsurface soil of the NPK + CD treated plots compared to that of NPK. NaOH-Po: The NaOH-Po pool constituted the largest fraction of P in the studied soils. The surface and subsurface soil of the control plots showed 725 and 835 mg P kg-1 soil, respectively. In NPK plots, they were 825 and 851 mg kg-1 and in NPK + CD plots they were 923 and 889 mg kg-1, respectively. The differences in this fraction of P among three treatments were not significant. Acid-P: The magnitude of acid-P in the surface and subsurface of control plots were 49 and 54 mg kg-1, respectively. Application of inorganic P fertilizer increased acid P content in the both surface and subsurface soils of NPK plots to 61 and 62 mg kg-1, respectively. It was further increased due to CD addition to 77 mg kg-1 in the surface and 70 mg kg-1 in the subsurface soil. Residual-P: Amount of residual P fraction in the surface soil of the control plots was 81 mg kg-1 and in NPK and in NPK + CD plots this fraction was 101 and 151 mg kg-1, respectively.  However, the effect of neither the NPK nor CD on P accumulation was outspread to the subsurface soil.

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