College of Resources and Environment, University of Chinese Academy of Sciences , Beijing 100049, People's Republic of China.
State Key Laboratory of Urban and Regional Ecology, Research Center for Eco-Environment Sciences, Chinese Academy of Sciences , Beijing 100085, People's Republic of China.
Environ Sci Technol. 2015 Sep 1;49(17):10675-81. doi: 10.1021/acs.est.5b03046. Epub 2015 Aug 13.
Arsenic (As) speciation and distribution are two important factors in assessing human health risk from As-contaminated soil. In this study, we used the combination of physiologically based extraction test (PBET) and Simulator of Human Intestinal Microbial Ecosystem (SHIME) to determine soil As metabolism by human gut microbiota. The results showed that the percentage of soil arsenate [As(V)] transformation reached 22.1-38.2%, while that of arsenite [As(III)] attained 66.5-92.0%; 30.1-56.4% of As(V) transformed was attached to the soil solid phase. In comparison to sequential extraction results, almost all amorphous Fe/Al-oxide-bound As was liberated in the colon phase. An X-ray absorption near-edge structure (XANES) showed that the As(III) percentage in the soil solid phase reached 16.6-26.9% and reached 73.4% (soil 1) in the colon phase. Additionally, plenty of As(III) and different extents of methylation were also observed in colon extraction solution. As bioaccessibility in the colon phase was 1.8-2.8 times that in the small intestinal phase. Our results indicated that human gut microbiota increased As bioaccessibility, and large amounts of As(III) were adsorbed onto the soil solid phase as a result of microbial reduction. Determining As speciation and distribution in extraction solution and soil solid phases will allow for an accurate assessment of the risk to human health upon soil As exposure.
砷(As)形态和分布是评估受污染土壤中砷对人体健康风险的两个重要因素。在这项研究中,我们使用基于生理学的提取测试(PBET)和人类肠道微生物生态系统模拟器(SHIME)的组合来确定人类肠道微生物对土壤砷代谢的作用。结果表明,土壤砷酸盐[As(V)]转化的百分比达到 22.1-38.2%,而亚砷酸盐[As(III)]则达到 66.5-92.0%;30.1-56.4%的 As(V)转化与土壤固相结合。与顺序提取结果相比,几乎所有无定形铁/铝氧化物结合的砷都在结肠相中释放出来。X 射线吸收近边缘结构(XANES)表明,土壤固相中的 As(III)百分比达到 16.6-26.9%,在结肠相中达到 73.4%(土壤 1)。此外,在结肠提取液中还观察到大量的 As(III)和不同程度的甲基化。在结肠相中,As 的生物可利用性是小肠相中的 1.8-2.8 倍。我们的结果表明,人类肠道微生物群增加了 As 的生物可利用性,并且由于微生物还原,大量的 As(III)被吸附到土壤固相上。确定提取液和土壤固相中的 As 形态和分布将有助于准确评估土壤 As 暴露对人体健康的风险。