土壤中砷对人类健康的风险:一个模型适合所有吗?

Dibyendu Sarkar, Rupali Datta
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引用次数: 13

摘要

由于缺乏砷生物可利用性的“土壤模型”,许多对砷富集地点进行基线风险评估的研究人员都假设土壤中存在的所有砷都是生物可利用性的。这一假设高估了实际的人体健康风险,因为各种地球化学形式的砷在人体消化液中是稳定的或不溶的。作者进行了一项实验室培养研究,分析了土壤中砷的体外生物利用度与土壤性质的关系。根据砷反应性的潜在差异,选择了4种不同的土壤类型。每个土壤都用亚砷酸钠进行了改良,其速率代表了在农业系统中1年常规施用砷农药的速率。土壤被孵育1年,之后,作者测量了土壤特异性总砷和生物可利用砷浓度。结果表明,土壤理化性质显著影响砷的生物利用度,从而影响癌症风险的估计,进而影响场地清理成本的预测。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Human health risks from arsenic in soils: does one model fit all?

In the absence of a "soil model" on arsenic bioavailability, many investigators conducting baseline risk assessments of arsenic-enriched sites have assumed that all arsenic present in the soil is bioavailable. This assumption overestimates actual human health risk because various geochemical forms of arsenic are stable, or insoluble, in human digestive juices. The authors conducted a laboratory incubation study to analyze the in vitro bioavailability of arsenic in soils as a function of soil properties. Four different soil types were selected on the basis of their potential differences with respect to arsenic reactivity. Each soil was amended with sodium arsenite at a rate representative of a routine 1-yr application of arsenical pesticide in an agricultural system. The soils were incubated for 1 yr, after which the authors measured soil-specific total and bioavailable arsenic concentrations. Results demonstrated that soil physicochemical properties significantly affect arsenic bioavailability, and hence estimates of cancer risk, which in turn affect site cleanup cost projections.

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