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Research Detail

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M.A. Rauf
Soil Resources Development Institute, Krishi Khamar Sarak, Farmgate Dhaka- 1215, Bangladesh

M. A. Hakim
Institute of Tropical Agriculture, Unversiti Putra Malaysia, 43400 UPM Serdang, Selangor DE, Malaysia

M. M. Hanafi
Institute of Tropical Agriculture, Unversiti Putra Malaysia, 43400 UPM Serdang, Selangor DE, Malaysia

M.M. Islam
Dept. of Forest Management, Faculty of Forestry, Universiti Putra Malaysia, 43400 UPM Serdang, Selangor, Malaysia.

G.K.M.M. Rahman
Dept. Soil Science, Bangabandhu Sheikh Mujibur Rahman Agricultural University, Gazipur, Bangladesh

G.M. Panaullah
Bangladesh Rice Research Institute, Gazipur, Bangladesh

Arsenic (As) pollution in soil and water has aroused a considerable attention. Inorganic forms of arsenic are associated with various cancers and cause major health problems. An experiment was conducted to investigate the effect of soil arsenic (As) concentration on arsenic and phosphorous accumulation in root, straw, husk and grain of rice (Oryza sativa). BRRI dhan33 and BR11 rice varieties were planted on six levels of As-contaminated growth media (T1=3.2, T2=11.6, T3=18.7, T4=38.6, T5=57.8 and T6=80.3 ppm) in a Completely Randomized Design (CRD) with six replications. Accumulation of arsenic in root, straw, husk and rice grain significantly increased when As dose increased in soil media. It was observed that As was highly concentrated in the roots, whereas phosphorous was highest in the grain. The T6 treatment (80.3 ppm) showed the highest As accumulation in different plant tissues. Arsenic contents in grain and husk of BR 11 were found higher than those of grain and husk of BRRI dhan33. The straw and root of BRRI dhan33 showed higher concentration of As than straw and root of BR 11. Phosphorous concentration of straw, husk and grain were also increased in higher As concentrations. In this study, rice plant showed high bioconcentration factor (BCF) and low translocation factor (TF), whereas As content in grains did not exceed the maximum permissible limit of 1 mg As kg-1, but straw As is highly risky for animal health as well as human food-chain. It could be concluded that BRRI dhan 33 can be cultivated instead of BR11 in As contaminated soil.

  Soil, BRRI dhan 33, BR11, Arsenic accumulation, Bioconcentration, Translocation
  Net house, Bangabandhu Sheikh Mujibur Rahman Agricultural University (BSMRAU), Gazipur
  
  
  Crop-Soil-Water Management
  Arsenic

1. To evaluate As absorption and translocation in Oryza sativa plant parts,

2. To compare the As concentrations in rice plant parts between the two economically important verities and

3. To establish the relationship between As and P accumulation in rice plant parts in different levels of As in soil.

Experimental site - The pot experiment was conducted at net house, Bangabandhu Sheikh Mujibur Rahman Agricultural University (BSMRAU), Gazipur. The net house area belongs to the Madhupur Tract (AEZ 28) having 24º 02´ 131" N latitude and 90º 23´ 810" E latitude, 8.4 m AMSL. It is sub-tropical humid climate and is characterized by high temperature accompanied by moderately high rainfall during kharif (April to September) season and low temperature in rabi (October to March) season. Experimental materials and treatments - The growth media prepared with soils contaminated with different levels of As which were: T1 (3.2 ppm), T2 (11.6 ppm), T3 (18.7 ppm), T4 (38.6 ppm), T5 (57.8 ppm) and T6 (80.3 ppm). Among them four elevated arsenic contaminated soils T3 (18.7 ppm), T4 (38.6 ppm), T5 (57.8 ppm) and T6 (80.3 ppm) were collected from STW irrigated area and one background soil (11.6 ppm As) collected from non-irrigated area of Komorpur, Faridpur Sadar Upazila. Another check soil (historically non-contaminated area), having soil As concentration of 3.2 mg kg-1, was collected from BSMRAU campus, Gazipur. The soil was high to medium high land of Tejgaon series in Madhupur Tract. The treatments were arranged in a completely randomized design (CRD) with 6 replications. Plant materials, Planting / sowing and fertilization - Two rice cultivars, BRRI dhan33 and BR11, having the cropping periods of 118 and 145 days, respectively were planted in 'Aman' season. Two healthy and vigor seedlings were transplanted per hill. Accordingly, two hills were received in each pot of 30 cm deep and 12.5 cm diameter plastic pot, containing 15 kg air dried soil. Water requirement was monitored visually. Pre-tested As free (below detection limit) irrigation water was applied in each pot of the experiment almost every day as recommended. The fertilizer doses were followed AEZ 12 as per fertilizer recommendation guide. Therefore, N, P, K, S and Zn were applied at the rate of 66, 6, 12, 7 and 1 kg ha-1 (1.08, 0.23, 0.18, 0.29 and 0.021 g pot-1) from urea, TSP, MP, gypsum and zinc sulphate fertilizer, respectively. Weeding was done manually by hand, when required. Diseases and pest infestations were monitored and necessary steps taken during the total growing period. Arsenic and P accumulation in straw, husk, and grain of Transplant Aman were recorded properly. Plant and soil sampling and chemical analysis - Plant samples collected after harvest and soil samples were collected before and after harvest and analyzed following standard laboratory methods. Mechanical analysis was done by hydrometer method. The pH was determined by the Metrohm 691 digital pH meter. Organic carbon was determined by Leco apparatus. Kjeldahl method was followed for the determination of total nitrogen. Available P of Faridpur soil was extracted with 0.5 M NaHCO3 extracting solution  since pH value of the soil was greater than 6.5 (pH>6.5) but the Gazipur soil was extracted with 0.03M NH4F-0.025M HCl since it was below 6.5. The ammonium acetate extraction method was followed for available potassium determination. The contents of K in the soil were directly measured by the Flame Emission Spectrophotometer  Available S content was determined by extracting the soil with CaCl2 (0.15%) solution. Available Zn, Cu, Fe, and Mn contents in soil were determined by DTPA extraction method as described by Hunter. The DTPA extractable elements were measured by Atomic Absorption Spectrometer (AAS) using air-acetylene flame and matrix matched standards. The total arsenic content was determined by flow-injection hydride-generation atomic absorption spectroscopy (FI-HG-AAS), using a Perkin Elmer Analyst 200, digestion made by HNO3.H2O2. Plant samples were also digested with conc. HNO3 and 30% H2O2 and determined total As and P in straw, husk and grain as above methods. Bioconcentration factor (BCF) and translocation factor (TF) - The plant’s ability to accumulate metals from soils and their translocation ability from roots to shoots can be estimated using the bioconcentration factor (BCF) and translocation factor (TF), respectively. Statistical Analysis - Statistical analysis was done following MSTAT-C program to find out the effect of each treatment on As and P accumulation in straw, husk and grain and to compare the parameters between the treatments. The means of each treatment was compared by DMRT. Computation and preparation of graphs were done using Microsoft EXCEL 2003 program.

  AJCS 5(12):1678-1684(2011); ISSN:1835-2707
  
Funding Source:
1.   Budget:  
  

Elevated soil arsenic (As) influenced the As and P accumulation in rice. Arsenic contents in grain and husk of BR11 were found higher than those of grain and husk of BRRI dhan33. The straw and root of BRRI dhan33 showed higher concentration of As than straw and root of BR11. The decreasing trend of As concentration was found as staw> husk> grain at both varieties. Phosphorous concentration was decreased in the order of grain > husk ≥ straw. Arsenic in root, straw, husk and grain of BRRI dhan33 and BR11 showed positive relationship with soil As concentrations. Arsenic concentration in root, straw, husk and grain increased significantly in higher soil As concentrations, which can be threat for animal and human health. If the soil is contaminated with As then BRRI dhan33 might be recommended for rice grain production. Further studies need to be carried out for remediation of polluted soil by phytoremediation techniques.

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