Yuan Xiaofang, Deng Yamin, Gao Jie, Zheng Tianliang, Xu Yuxiao, Wang Yanxin
Key Laboratory of Groundwater Quality and Health (China University of Geosciences), Ministry of Education, Wuhan 430078, China; Geological Survey, China University of Geosciences, Wuhan 430074, China.
Key Laboratory of Groundwater Quality and Health (China University of Geosciences), Ministry of Education, Wuhan 430078, China; School of Environmental Studies, China University of Geosciences, Wuhan 430078, China.
Water Res. 2025 Sep 1;283:123864. doi: 10.1016/j.watres.2025.123864. Epub 2025 May 19.
Arsenic (As) methylation is a crucial process within the geochemical cycle of arsenic in groundwater systems. The transformation of inorganic arsenic into less toxic monomethylarsenate (MMA) and demethylarsenate (DMA) holds the potential to partially mitigate the environmental risk of arsenic, thereby offering a promising strategy for regulating arsenic contamination in groundwater. Sulfate-reducing bacteria (SRB) have demonstrated the ability for As methylation under various environmental conditions. However, the capacity of SRB to methylate As specially in groundwater remains unverified. In this study, the predominant biogeochemical processes contribute to the enrichment of methylated arsenic (MeAs) in alluvial-lacustrine aquifers have been investigated through a combination of hydrogeochemical monitoring and incubation experiments. Field investigations in the Jianghan Plain demonstrated that MeAs concentrations in groundwater ranged from 0.34 to 444 μg/L, which are significantly higher than those reported in other region globally. The results suggested that a strongly reducing and neutral environment with elevated level of As(III) and dissolved organic carbon (DOC) facilitated the accumulation of MeAs in groundwaters. Sulfate reduction emerged as an important promoter of As methylation in groundwater, with Desulfovibrio potentially identified as the key SRB genus through high-throughput sequencing of dsrB gene. Moreover, the incubation experiments showed the As methylation efficiency was up to 22.8 % with As(III) being a critical substrate in the aquifer systems from the Jianghan Plain, while such a lower efficiency compared with paddy soil environments likely attributable to the limited available organic matter and the distinct microbial communities. This study provides novel insights on As methylation mechanisms and theoretical support for in-situ remediation of As-contaminated aquifers.
砷(As)甲基化是地下水系统中砷地球化学循环的关键过程。无机砷转化为毒性较低的一甲基砷酸盐(MMA)和去甲基砷酸盐(DMA)有可能部分降低砷的环境风险,从而为控制地下水中的砷污染提供了一个有前景的策略。硫酸盐还原菌(SRB)已被证明在各种环境条件下都具有砷甲基化能力。然而,SRB在地下水中进行砷甲基化的能力尚未得到验证。在本研究中,通过水文地球化学监测和培养实验相结合的方法,研究了冲积-湖相含水层中导致甲基化砷(MeAs)富集的主要生物地球化学过程。江汉平原的现场调查表明,地下水中MeAs浓度范围为0.34至444μg/L,显著高于全球其他地区报道的浓度。结果表明,具有较高As(III)和溶解有机碳(DOC)水平的强还原和中性环境促进了地下水中MeAs的积累。硫酸盐还原是地下水中砷甲基化的重要促进因素,通过对dsrB基因的高通量测序,潜在地确定脱硫弧菌为关键的SRB属。此外,培养实验表明,在江汉平原的含水层系统中,以As(III)作为关键底物时,砷甲基化效率高达22.8%,而与稻田土壤环境相比,这种效率较低可能归因于可用有机物有限和微生物群落不同。本研究为砷甲基化机制提供了新的见解,并为原位修复受砷污染的含水层提供了理论支持。