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Research Detail

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Aminul Islam
Scientific Officer
Soil Science Division, BRRI Gazipur-1701

U.A. Naher
Scientific Officer
Soil Science Division, BRRI Gazipur-1701

A. T. M. S. Hossain
Scientific Officer
Soil Science Division, BRRI Gazipur-1701

B. K. Mitra
Scientific Officer
Soil Science Division, BRRI Gazipur-1701

M. A. Saleque
Senior Scientific officer
Soil Science Division, BRRI Gazipur-1701

A laboratory study was conducted to understand the effect of organic and inorganic amendment on phosphorus sorption characteristics of lowland rice soil. Soil samples (0-15 cm) were collected from a long-term integrated nutrient management experimental plots (three treatments- control, NPKS and NPKS + cow dung and ash) receiving different treatments over eight years. Collected soil samples were shaken with 0.01M CaCl2 solution containing P from 0 to 60 mg/ml for 24 hours at room temperature (28°C, soil to solution ratio 1:10). The phosphorus isotherm data for all the soils at equilibrium P concentration were found to fit well to Langmuir, Freundlich and Temkin equation (r2=0.8851 to 0.9896). The application of inorganic fertilizer increased P buffering capacity and maximum adsorption capacity compared to control and organic amendment. Energy of P adsorption was the highest with control followed by organic amendment and inorganic amendment.

  Phosphorus sorption, Organic, inorganic, Lowland rice and Fertilizer
  Bangladesh Rice Research Institute (BRRI) farm and Soil Science Lab, BRRI, Gazipur
  01-01-2000
  31-12-2000
  Crop-Soil-Water Management
  Soil fertility

                    To evaluate the effect of organic (cow dung and ash) and inorganic (NPKS) amendments on phosphorus (P) sorption characteristics of lowland rice soils.

Soil samples (0-15 cm) were collected from a long-term experimental field located at the Bangladesh Rice Research Institute farm. The soil is Aerie Haplaquept. The treatments of long-term experiment were: absolute control (T1), NPKS = 40-8-12-5 kg/ha (T2), NPKS = 80-16-24-10 kg/ha (T3), NPKS = 120-24-36-15 kg/ha (T4), T2 + cow dung (5 t/ha) and rice husk ash (2.5 t/ha) (T5), T3 + cow dung and ash (T6). The experiment was continued for eight years. The initial soil characteristics were clay loam in texture, pH 6.4, organic carbon content 0.13%, total nitrogen content 0.08%, 9 ppm Olsen P, exchangeable K 0.2meq/100g, available S 14 ppm and available Zn 1.0 ppm. Soil samples for the present study were collected from the T1, T3 and T6 treated plots after eight years of cropping and the soil samples were labeled as T1, T2, and T3 respectively. The soil samples were then air dried, passed through 2 mm mesh sieve and stored in plastic bags prior to use. Phosphate adsorption was studied for the collected samples by shaking 2 g of soil in 20 ml of 0.01M CaCl2 solutions containing each of 0, 15, 30, 45 and 60 mg P/ml as KH2PO4 in 50 ml centrifuge tubes for 24 hours at room temperature (28°C). After shaking, the tubes were centrifuged at 10,000 rpm for 5 minutes and P in the supernatant was estimated following Murphy and Riley (1962) method. The adsorbed P was calculated from the difference between initial and final concentration of P in the solution. The equilibrium P concentration data were interpreted from Langmuir, Freundlich and Temkin equations as described below:

Langmuir equation:

C/(x/m)= 1/kb + C/b ……………. (1)

 Where, C is the equilibrium P concentration (mg/L), x/m is the mg P sorbed per kg soil, b is the adsorption maxima (the maximum adsorption capacity) and k is a constant related to the bonding energy of adsorption. A plot of C (x/m) versus C gives a straight line. The constant b and k were obtained from the slope and intercept.

Freundlich equation:

x/m = aCb ………………………(2)

By rearranging,

Log(x/m) = log a +b log C ……(3)

Where, x/m is mg P adsorbed per kg soil, C is the equilibrium P concentration (mg/L) and a and b are constants. A linear plot of Log x/m versus Log C leads to a and b from the intercepts and slope respectively.

Temkin equation:

 x/m = a + blnC…………………..(4)

Where, x/m is the amount of P adsorbed on unit mass of adsorbent (mg/kg), C is the equilibrium P concentration (mg/L) and a and b are constants. A plot of x/m against lnC gives a straight line. The constant a and b are obtained from intercept and slope. The b of the equation (4) is considered as the P buffering capacity.

  Bangladesh J. Agril. Res. 29 (3):459-465, September, 2004.
  
Funding Source:
1.  Government Budget:  
  

Addition of P increased solution P concentration dramatically but cow dung and ash application in the field did not bring any significant change in the solution P concentration. The amount of P adsorbed by the soils increased progressively with increasing level of added phosphorus. However, the percentage of added phosphate adsorbed by the soils decreased with the increased level of P addition. These results indicated that the increase in the amount of P adsorbed in soils were not in proportion to the increasing levels of P addition. The fit of P adsorption data to Langmuir, Freundlich and Temkin equations indicated that all the three equations were quite good to fit the data. However, Langmuir and Freundlich equations gave a relatively superior fit as compared to Temkin equation. Line drawn using different sorption equations (1, 2 and 3) for T1, T2 and T3 soils clearly show that the adsorption behavior of the soils was almost similar. The maximum adsorption capacity (b) was the highest (555.56) in T2 and the lowest (526.32) in T1 and T3. In contrast to b, the bonding energy (k) values of Langmuir adsorption equation were the minimum in T2 (0.86) and maximum in T1 (1.06). In fact there was apparently a negative correlation between K and b values. From Temkin equation, the buffering capacity (b value) of the soil seems to be the lowest in T1 for both surface and sub-surface soils.

  Journal
  


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