Arsenic contamination: a potential hazard to the affected areas of West Bengal, India

被引:0
作者
Sefaur Rahaman
A. C. Sinha
R. Pati
D. Mukhopadhyay
机构
[1] Uttar Banga Krishi Viswavidyalaya,Department of Agronomy, Faculty of Agriculture
[2] Uttar Banga Krishi Viswavidyalaya,Department of Soil Science and Agricultural Chemistry, Faculty of Agriculture
[3] Viswa Bharati University,undefined
来源
Environmental Geochemistry and Health | 2013年 / 35卷
关键词
Arsenic; Water; Soil; Rice; Mango; Vegetables; Pulses; Amaranth;
D O I
暂无
中图分类号
学科分类号
摘要
Arsenic contamination in groundwater is becoming more and more a worldwide problem. Nearing 50 million of people are at health risk from arsenic contamination at Ganga–Meghna–Bramhaputra basin. The experimental results of the five blocks under Malda district of West Bengal, India, showed that the arsenic concentration in groundwater (0.41–1.01 mg/l) was higher than the permissible limit for drinking water (0.01 mg/l) (WHO) and FAO (Food and Agriculture Organization) permissible limit for irrigation water (0.10 mg/l). The soil arsenic level (13.12 mg/kg) crossed the global average (10.0 mg/kg), but within the maximum acceptable limit for agricultural soil (20.0 mg/kg) recommended by the European Union. The total arsenic concentration on food crops varied from 0.000 to 1.464 mg/kg of dry weight. The highest mean arsenic concentration was found in potato (0.456 mg/kg), followed by rice grain (0.429 mg/kg). The total mean arsenic content (milligrams per kg dry weight) in cereals ranged from 0.121 to 0.429 mg/kg, in pulses and oilseeds ranged from 0.076 to 0.168 mg/kg, in tuber crops ranged from 0.243 to 0.456 mg/kg, in spices ranged from 0.031 to 0.175 mg/kg, in fruits ranged from 0.021 to 0.145 mg/kg and in vegetables ranged from 0.032 to 0.411 mg/kg, respectively. Hence, arsenic accumulation in cereals, pulses, oilseed, vegetables, spices, cole crop and fruits crop might not be safe in future without any sustainable mitigation strategies to avert the potential arsenic toxicity on the human health in the contaminated areas.
引用
收藏
页码:119 / 132
页数:13
相关论文
共 176 条
[11]  
Samanta G(2000)Mineral sources and transport pathways for arsenic release in a coastal watershed, USA International Journal of Epidemiology 29 1047-1052
[12]  
Mandal BK(2006)Arsenic in drinking water and the prevalence of respiratory effects in West Bengal, India Science of the Total Environment 368 531-541
[13]  
Chakraborti D(2004)Soil arsenic availability and the transfer of soil arsenic to crops in suburban areas in Fujian Province, southeast China Asian Journal of Plant Science 3 489-493
[14]  
Faruk I(1979)Assessment of arsenic in the water–soil–plant systems in gangetic flood plains of Bangladesh Soil Science Society of American Journal 43 304-308
[15]  
Chakraborty D(1992)Comparative effectiveness of fourteen solutions for extracting arsenic from four Western New York soils The Science of the Total Environment 126 263-275
[16]  
Rahman MM(2004)Atmospheric deposition of trace elements around point sources and human health risk assessment. II. Uptake of arsenic and chromium by vegetables grown near a wood preservation factory Journal of Experimental Botany 55 1707-1713
[17]  
Paul K(2009)Do iron plaque and genotypes affect arsenate uptake and translocation by rice seedlings ( Applied Environmental Microbiology 75 2558-2565
[18]  
Chowdhury UK(1996) L.) grown in solution culture Current Science 70 976-986
[19]  
Sengupta MK(2002)Microbial mineral weathering for nutrient acquisition releases arsenic Talanta 58 201-235
[20]  
Lodh D(2004)Arsenic in groundwater in seven districts of West Bengal, India: The biggest arsenic calamity in the world Environmental Pollution 132 21-27