State Key Laboratory of Biogeology and Environmental Geology, China University of Geosciences, Beijing 100083, PR China; Institute of Earth Sciences, China University of Geosciences (Beijing), Beijing 100083, PR China; School of Water Resources and Environment, China University of Geosciences (Beijing), Beijing 100083, PR China.
Williamson Research Centre for Molecular Environmental Science, School of Earth and Environmental Sciences, the University of Manchester, Manchester, United Kingdom.
Environ Int. 2020 Mar;136:105489. doi: 10.1016/j.envint.2020.105489. Epub 2020 Jan 25.
Various functional groups of microorganisms and related biogeochemical processes are likely to control arsenic (As) mobilization in groundwater systems. However, spatially-dependent correlations between microbial community composition and geochemical zonation along groundwater flow paths are not fully understood, especially with respect to arsenic mobility. The western Hetao Basin was selected as the study area to address this limitation, where groundwater flows from a proximal fan (geochemical-group I: low As, oxidizing), through a transition area (geochemical-group II: moderate As, moderately-reducing) and then to a flat plain (geochemical-group III: high As, reducing). High-throughput Illumina 16S rRNA gene sequencing showed that the microbial community structure in the proximal fan included bacteria affiliated with organic carbon degradation and nitrate-reduction or even nitrate-dependant Fe(II)-oxidation, mainly resulting in As immobilization. In contrast, for the flat plain, high As groundwater contained Fe(III)- and As(V)-reducing bacteria, consistent with current models on As mobilization driven via reductive dissolution of Fe(III)/As(V) mineral assemblages. However, Spearman correlations between hydrogeochemical data and microbial community compositions indicated that ammonium as a possible electron donor induced reduction of Fe oxide minerals, suggesting a wider range of metabolic pathways (including ammonium oxidation coupled with Fe(III) reduction) driving As mobilization in high As groundwater systems.
各种功能微生物群和相关的生物地球化学过程可能控制地下水系统中砷(As)的迁移。然而,微生物群落组成与地下水流动路径上的地球化学分带之间的空间相关关系尚不完全清楚,特别是在砷迁移方面。河套西部盆地被选为研究区,以解决这一限制,地下水从近端扇(地球化学组 I:低砷,氧化),通过过渡区(地球化学组 II:中砷,中度还原),然后到平原(地球化学组 III:高砷,还原)。高通量 Illumina 16S rRNA 基因测序表明,近端扇区的微生物群落结构包括与有机碳降解和硝酸盐还原相关的细菌,甚至与硝酸盐依赖的 Fe(II)-氧化相关的细菌,主要导致砷固定。相比之下,对于平原,高砷地下水含有 Fe(III)-和 As(V)-还原细菌,与当前关于通过 Fe(III)/As(V)矿物组合的还原溶解驱动砷迁移的模型一致。然而,水地球化学数据和微生物群落组成之间的 Spearman 相关性表明,铵作为一种可能的电子供体诱导了 Fe 氧化物矿物的还原,这表明更广泛的代谢途径(包括与 Fe(III)还原偶联的铵氧化)驱动高砷地下水系统中砷的迁移。