School of Environmental Studies, Jadavpur University, Kolkata 700032, West Bengal, India.
Int J Hyg Environ Health. 2010 Nov;213(6):414-27. doi: 10.1016/j.ijheh.2010.09.003. Epub 2010 Oct 16.
A somewhat detailed study was carried out in Gaighata, one of the 107 arsenic-affected blocks in West Bengal, India, to determine the degree of groundwater contamination with arsenic, its depth wise distribution, correlation with iron, arsenical health effects to the inhabitants and the factors responsible for arsenic poisoning. Groundwater in all the 107 mouzas over 13 gram-panchayets in Gaighata block contains arsenic above 0.01mgl(-1) and in 91 mouzas, arsenic concentration has been found above 0.05mgl(-1). About 59.2 and 40.3% of the tubewell water samples contain arsenic above 0.01 and 0.05mgl(-1), respectively. The approximate population drinking arsenic-contaminated water above 0.01 and 0.05mgl(-1) are 106,560 and 72,540, respectively. The tubewells that were installed within the depth range of 15.4-30.3m are mostly arsenic-contaminated. Even the shallow groundwater level (7.87-15.1m) is arsenic-contaminated. Both arsenic and iron concentrations in groundwater gradually increase from lower depth to higher depth up to 39.4m, and then decrease with increasing depth. About 58% of the deep tubewell water samples (depth range 122-182m, n=31) contain arsenic ≥0.05mgl(-1). About 72% of the arsenic-contaminated deep tubewells (n=18) were safe when surveyed first time. But within a span of 2-5 years, they became contaminated with arsenic. The linear regression shows direct correlation between arsenic and iron concentrations in groundwater (r(2)=0.8114, p<0.0001, n=912). Intakes of inorganic arsenic from water by an adult male and female in the surveyed areas are 11.7 and 13.1μg/kg body wt./day, respectively and these values are higher than the WHO recommended PTDI value of inorganic arsenic (2.1μg/kg body wt./day). Mean arsenic concentrations in urine, hair and nail samples, collected from the inhabitants of Gutri mouza are higher than their normal level and the values are 292μgl(-1) (range: 8.35-1024μg l(-1), n=193), 2.50mgkg(-1) (range: 0.17-5.99mgkg(-1), n=132), and 6.05mgkg(-1) (range: 0.55-16.7mgkg(-1), n=116), respectively. About 83% and 68% of the urine samples (n=250) contain arsenic above 100 and 200μgl(-1), respectively. Linear regressions show very good correlations between arsenic concentrations in water vs. urine, hair and nail samples from the inhabitants (n=103) of Gutri mouza. About 18.3% of the population (n=930) were registered with arsenical skin lesions.
在印度西孟加拉邦的 Gaighata 进行了一项较为详细的研究,以确定地下水砷污染的程度、其深度分布、与铁的相关性、对居民的砷健康影响以及导致砷中毒的因素。Gaighata 区块 13 个 Gram-Panchayets 中 107 个砷污染区块的所有 107 个 mouzas 中的地下水均含有超过 0.01mg/L 的砷,在 91 个 mouzas 中,砷浓度超过 0.05mg/L。约 59.2%和 40.3%的管井水样中,砷含量分别超过 0.01 和 0.05mg/L。分别约有 106560 人和 72540 人饮用砷含量超过 0.01 和 0.05mg/L 的受污染水。安装在 15.4-30.3m 深度范围内的管井大多受到污染。即使浅层地下水(7.87-15.1m)也受到污染。地下水的砷和铁浓度从较低深度到较高深度逐渐增加,最高可达 39.4m,然后随深度增加而降低。约 58%(n=31)的深管井水样(深度范围为 122-182m)中,砷含量≥0.05mg/L。第一次调查时,约 72%(n=18)的受砷污染的深井是安全的。但在 2-5 年内,它们受到了砷的污染。线性回归显示地下水砷和铁浓度之间存在直接相关性(r(2)=0.8114,p<0.0001,n=912)。在所调查地区,成年男性和女性从水中摄入的无机砷分别为 11.7 和 13.1μg/kg 体重/天,高于世界卫生组织推荐的无机砷暂定每日耐受摄入量(2.1μg/kg 体重/天)。从 Gutri mouza 居民采集的尿液、头发和指甲样本中的砷浓度高于正常水平,分别为 292μgl(-1)(范围:8.35-1024μg l(-1),n=193)、2.50mgkg(-1)(范围:0.17-5.99mgkg(-1),n=132)和 6.05mgkg(-1)(范围:0.55-16.7mgkg(-1),n=116)。约 83%(n=250)和 68%(n=250)的尿液样本中,砷含量分别超过 100μgl(-1)和 200μgl(-1)。线性回归显示 Gutri mouza 居民(n=103)的水中砷浓度与尿液、头发和指甲样本中的砷浓度之间存在很好的相关性。约 18.3%(n=930)的人口登记有砷性皮肤损伤。