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含砷针铁矿中有机质对微生物介导的砷和铁还原及迁移的影响。

Impact of Organic Matter on Microbially-Mediated Reduction and Mobilization of Arsenic and Iron in Arsenic(V)-Bearing Ferrihydrite.

机构信息

College of Resources and Environment, University of Chinese Academy of Sciences, Beijing 101408, People's Republic of China.

Soil Chemistry Group, Institute of Biogeochemistry and Pollutant Dynamics, Department of Environmental Systems Science, ETH Zurich, Universitätstrasse 16, CHN, CH-8092 Zurich, Switzerland.

出版信息

Environ Sci Technol. 2021 Jan 19;55(2):1319-1328. doi: 10.1021/acs.est.0c05329. Epub 2020 Dec 30.

DOI:10.1021/acs.est.0c05329
PMID:33377766
Abstract

Under anoxic conditions, the interactions between As-bearing ferrihydrite (Fh) and As(V)-reducing bacteria are known to cause Fh transformations and As mobilization. However, the impact of different types of organic matter (OM) on microbial As/Fe transformation in As-bearing Fh-organic associations remains unclear. In our study, we therefore exposed arsenate-adsorbed ferrihydrite, ferrihydrite-PGA (polygalacturonic acid), and ferrihydrite-HA (humic acid) complexes to two typical Fe(III)- and As(V)-reducing bacteria, and followed the fate of Fe and As in the solid and aqueous phases. Results show that PGA and HA promoted the reductive dissolution of Fh, resulting in 0.7-1.6 and 0.8-1.9 times more As release than in the OM-free Fh, respectively. This was achieved by higher cell numbers in the presence of PGA, and through Fe-reduction via electron-shuttling facilitated by HA. Arsenic-XAS results showed that the solid-phase arsenite fraction in Fh-PGA and Fh-HA was 15-19% and 27-28% higher than in pure Fh, respectively. The solid-associated arsenite fraction likely increased because PGA promoted cell growth and As(V) reduction, while HA provided electron shuttling compounds for direct microbial As(V)-reduction. Collectively, our findings demonstrate that As speciation and partitioning during microbial reduction of Fh-organic associations are strongly influenced by PGA and HA, as well as the strains' abilities to utilize electron-shuttling compounds.

摘要

在缺氧条件下,含砷的水铁矿(Fh)与砷还原菌之间的相互作用会导致 Fh 转化和砷释放。然而,不同类型的有机物(OM)对含砷 Fh-有机物联合体中微生物砷/铁转化的影响尚不清楚。因此,在我们的研究中,我们将砷酸盐吸附的水铁矿、水铁矿-PGA(多聚半乳糖醛酸)和水铁矿-HA(腐殖酸)复合物暴露于两种典型的 Fe(III)和 As(V)还原菌,并跟踪固相与水相中的 Fe 和 As 命运。结果表明,PGA 和 HA 促进了 Fh 的还原溶解,导致 As 的释放量分别比无 OM 的 Fh 多 0.7-1.6 倍和 0.8-1.9 倍。这是通过 PGA 存在时细胞数量的增加,以及通过 HA 促进电子穿梭的 Fe 还原来实现的。砷 XAS 结果表明,Fh-PGA 和 Fh-HA 中固相亚砷酸盐分数分别比纯 Fh 高 15-19%和 27-28%。固相结合的亚砷酸盐分数可能会增加,因为 PGA 促进了细胞生长和 As(V)还原,而 HA 提供了电子穿梭化合物,用于直接微生物 As(V)-还原。总之,我们的研究结果表明,PGA 和 HA 以及菌株利用电子穿梭化合物的能力强烈影响 Fh-有机物联合体中微生物还原过程中的砷形态和分配。

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