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评估控制砷在黑脚病流行地区砷污染浅层冲积含水层中迁移的机制。

Assessing the mechanisms controlling the mobilization of arsenic in the arsenic contaminated shallow alluvial aquifer in the blackfoot disease endemic area.

机构信息

Department of Bioenvironmental Systems Engineering, National Taiwan University, Taipei, Taiwan.

出版信息

J Hazard Mater. 2011 Dec 15;197:397-403. doi: 10.1016/j.jhazmat.2011.09.099. Epub 2011 Oct 5.

Abstract

High levels of arsenic in groundwater and drinking water represent a major health problem worldwide. Drinking arsenic-contaminated groundwater is a likely cause of blackfoot disease (BFD) in Taiwan, but mechanisms controlling the mobilization of arsenic present at elevated concentrations within aquifers remain understudied. Microcosm experiments using sediments from arsenic contaminated shallow alluvial aquifers in the blackfoot disease endemic area showed simultaneous microbial reduction of Fe(III) and As(V). Significant soluble Fe(II) (0.23±0.03 mM) in pore waters and mobilization of As(III) (206.7±21.2 nM) occurred during the first week. Aqueous Fe(II) and As(III) respectively reached concentrations of 0.27±0.01 mM and 571.4±63.3 nM after 8 weeks. We also showed that the addition of acetate caused a further increase in aqueous Fe(II) but the dissolved arsenic did not increase. We further isolated an As(V)-reducing bacterium native to aquifer sediments which showed that the direct enzymatic reduction of As(V) to the potentially more-soluble As(III) in pore water is possible in this aquifer. Our results provide evidence that microorganisms can mediate the release of sedimentary arsenic to groundwater in this region and the capacity for arsenic release was not limited by the availability of electron donors in the sediments.

摘要

地下水和饮用水中砷含量过高是全球主要的健康问题。饮用受砷污染的地下水是导致台湾黑脚病(BFD)的一个可能原因,但对于控制含水层中高浓度砷的迁移机制仍研究不足。在黑脚病流行地区受砷污染的浅层冲积含水层中进行的微生物培养实验表明,Fe(III)和 As(V)同时被微生物还原。在第一周内,孔隙水中出现了大量的可溶性 Fe(II)(0.23±0.03 mM),并使 As(III)(206.7±21.2 nM)发生迁移。8 周后,水溶液中的 Fe(II)和 As(III)分别达到 0.27±0.01 mM 和 571.4±63.3 nM 的浓度。我们还表明,添加乙酸盐会进一步增加水溶液中的 Fe(II),但溶解的砷没有增加。我们进一步分离出一种天然存在于含水层沉积物中的 As(V)-还原细菌,表明在这种含水层中,孔隙水中的酶促直接将 As(V)还原为潜在更易溶的 As(III)是可能的。我们的研究结果提供了证据表明,微生物可以介导该地区沉积物中砷释放到地下水中,并且砷的释放能力不受沉积物中电子供体的可用性限制。

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