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Research Detail

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Aminul Islam
Scientific Officer
Soil Science Division, BRRI Gazipur

A. J. M. S. Karim
Professor
Department of Soil Science, Bangabandhu Sheikh Mujibur Rahman Agricultural University, Gazipur

H. M. Khaled
Analyst
Soil Science Division, BRRI Gazipur

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

M. A. M. MIAH
Chief Scientific Officer and Head
Soil Science Division, BRRI Gazipur

A study was conducted with four surface (0-15 cm) soils collected from different levels of As contaminated area where As contaminated irrigation water from shallow tube well was used for rice cultivation to determine the maximum adsorption capacity, energy of adsorption and buffering capacity of As. Arsenic was determined by a Perkin-Elmer Analysts 100 AAS equipped with a FIAS-100 flow injection hydride generation system. Conventional adsorption equations- Langmuir, Freundlich and Temkin equations were used to describe As sorption characteristics of soils. Test soils showed a large capacity of As adsorption. The application of As progressively increased the equilibrium solution concentration of As. At the lower levels equilibrium concentration, the adsorption of As linearly increased, but at greater levels equilibrium solution concentration the rate of As adsorption. All soils were found to fit well in all the equations (R2 = 0.9052 to 0.9974). The highest and the lowest adsorption maxima were observed 2000 mg/kg in soil 2 and 3 and 1111 mg/kg in soil 4, respectively. The highest and the lowest As buffering capacity were observed 405 in soil 2 and 185 in soil 4, respectively. The highest energy of adsorption obtained for the soil 4, which showed the lowest As adsorption maxima and the lowest energy of adsorption obtained with soil 2 followed by soil 3, which showed the highest As adsorption maxima. Arsenic buffering capacity was positively correlated with maximum adsorption capacity of the soils (r = 0.99). The As sorption parameters were highly correlated with clay content, FeO and MnO content of the soils and not with the total As content of the soils.

  Arsenic, Adsorption, Soil
  BRRI Soil Science Lab
  01-04-2002
  30-06-2003
  Crop-Soil-Water Management
  Contamination of soil

To determine the maximum arsenic (As) adsorption capacity, energy of As adsorption and As buffering capacity As contaminated agricultural soils.

Four agricultural soils (0-15 cm) from different levels of As contaminated area, which received As contaminated irrigation water for several years were collected. The soils are designated as soil 1, soil 2, soil 3 and soil 4 for convenience. Soil samples were air-dried, ground and passed through 2 mm sieve and stones, roots and plant debris were removed before the soils were air dried at 300C. The bulk soils samples were mixed thoroughly by hand stored for analysis. Soils’ physical and chemical properties were determined using standard laboratory procedure. Total As content of the soil 1, soil 2, soil 3 and soil 4 were 20.3, 26.3, 14.1 and 24.3 mg/kg, respectively. Clay content of soil 1, soil 2, soil 3 and soil 4 were 22.2%, 28.9%, 30.5% and 18.5%, respectively. To study the adsorption characteristics of the soils, one equilibration time was used: the adsorption isotherm was calculated after 48 hours of adding sorption solution. For equilibration, 20 ml solution of 0-250 µg As/ml as Na2HAsO4.7H2O was added to 1 g of soils in 50 ml centrifuge tubes at room temperature (20 0C). The solution was shaken for 48 hours by an end to end shaker. After equilibration the suspension was centrifuged at 10,000 rpm for 10 min and the supernatant solution was filtered through Whatman No. 42 filter paper. The filtrates were analyzed for As using a FI-HG-AAS using matix-matched standards. Arsenic that had been lost from solution was considered to be sorbed. The As adsorption 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 As concentration (mg/L), x/m is the mg As 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 As adsorbed per kg soil, C is the equilibrium As 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 As adsorbed on unit mass of adsorbent (mg/kg), C is the equilibrium As 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 As buffering capacity.

  Asian Journal of Plant Sciences 2 (17-24): 1149-1152, 2003
  
Funding Source:
1.   Budget:  
  

A study was conducted at Soil Science Lab, BRRI, with four surface (0-15 cm) soils collected from different levels of As contaminated area where As contaminated irrigation water from shallow tube well was used for rice cultivation to determine the maximum adsorption capacity, energy of adsorption and buffering capacity of As. Application of chemical As increased solution As quadratically in all tested soils. Increase of As adsorption followed the same pattern with increase of As addition. The relationship between equilibrium solution As concentration and adsorbed As was quadratic in nature. The relationships between equilibrium solution As and adsorbed As were tested to fit the Langmuir, Freundlich and Temkin adsorption isotherm to calculate adsorption maxima (b), energy of adsorption (k) and As buffering  capacities of studied soils. All three adsorption isotherms were found to fit well in all soils. The highest As adsorption maxima (b) was observed in soil 2 and 3 (2000 mg/kg for both), and the lowest (1111 mg/kg) was found in soil 4 and for soil 1 it was 1429 mg/kg. The highest energy of adsorption (k) (0.042 g/ml) was found in soil 4 and the lowest (0.018 g/ml) in soil 2. There was a negative relationship between As adsorption maxima and energy of adsorption.  It was also observed that there was an apparent negative relationship (r = -0.95) between energy of adsorption and As buffering capacity of all studied soils. It was also observed that there was an apparent positive relationship (r = 0.99) between As adsorption maxima and As buffering capacity of all studied soils. The highest As buffering capacity of 408 was observed in soil 2 and the lowest (185) was in soil 4.

  Journal
  


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