School of Environmental Studies, State Key Laboratory of Biogeology and Environmental Geology, China University of Geosciences, Wuhan, 430071, China; State Key Laboratory of Environmental Geochemistry, Institute of Geochemistry, Chinese Academy of Sciences, Guiyang, 550002, China.
School of Environmental Studies, State Key Laboratory of Biogeology and Environmental Geology, China University of Geosciences, Wuhan, 430071, China.
Environ Pollut. 2018 Jun;237:28-38. doi: 10.1016/j.envpol.2018.01.092. Epub 2018 Feb 20.
High arsenic groundwater generally coexists with elevated Fe concentrations (mg L levels) under reducing conditions, but an explanation for the extremely high arsenic (up to ∼2690) concentrations at very low Fe (i.e., μg L levels) in groundwater of Datong Basin remains elusive. Field groundwater investigation and laboratory microcosm experiments were implemented in this study. The field groundwater was characterized by weakly alkaline (pH 7.69 to 8.34) and reducing conditions (Eh -221.7 to -31.9 mV) and arsenic concentration averages at 697 μg L. Acinetobacter (5.9-51.3%), Desulfosporosinus (4.6-30.2%), Brevundimonas (3.9-19%) and Pseudomonas (3.2-14.6%) were identified as the dominant genera in the bacterial communities. Bacterially mediated arsenate reduction, Fe(III) reduction, and sulfate reduction are processes occurring (or having previously occurred) in the groundwater. Results from incubation experiment (27 d) revealed that nitrate, arsenate, and Fe(III)/sulfate reduced sequentially with time under anoxic conditions, while Fe(III) and sulfate reduction processes had no obvious differences, occurring almost simultaneously. Moreover, low Fe concentrations were attributed to initially high pH conditions, which relatively retarded Fe(III) reduction. In addition, arsenic behavior in relation to groundwater redox conditions, matrices, and solution chemistry were elaborated. Bacterial arsenate reduction process proceeded before Fe(III) and sulfate reduction in the incubation experiment, and the total arsenic concentration (dominated by arsenite) gradually increased from ∼7 to 115 μg L as arsenate was reduced. Accordingly, bacterially mediated reductive desorption of arsenate is identified as the main process controlling arsenic mobility, while Fe(III) reduction coupled with sulfate reduction are secondary processes that have also contributed to arsenic enrichment in the study site. Overall, this study provide important insights into the mechanism controlling arsenic mobility under weakly alkaline and reducing conditions, and furnishes that arsenate reduction by bacteria play a major role leading to high accumulation of desorbed arsenite in groundwater.
高砷地下水通常与还原条件下的高 Fe 浓度(mg/L 级)共存,但大同盆地地下水 Fe 浓度极低(μg/L 级)而砷浓度极高(高达约 2690)的原因仍不清楚。本研究进行了野外地下水调查和实验室微宇宙实验。野外地下水具有弱碱性(pH 值为 7.69 到 8.34)和还原条件(Eh 值为-221.7 到-31.9 mV),砷浓度平均值为 697μg/L。在细菌群落中,优势菌属为不动杆菌(5.9-51.3%)、脱硫螺旋菌(4.6-30.2%)、短小杆菌(3.9-19%)和假单胞菌(3.2-14.6%)。研究表明,砷酸盐还原、Fe(III)还原和硫酸盐还原等细菌介导的反应在地下水中发生(或曾发生过)。27 天的培养实验结果表明,在缺氧条件下,硝酸盐、砷酸盐和 Fe(III)/硫酸盐依次随时间发生还原反应,而 Fe(III)和硫酸盐还原过程没有明显差异,几乎同时发生。此外,低 Fe 浓度归因于初始高 pH 值条件,这相对减缓了 Fe(III)的还原。此外,还详细阐述了砷在地下水氧化还原条件、基质和溶液化学方面的行为。在培养实验中,细菌砷酸盐还原过程先于 Fe(III)和硫酸盐还原进行,随着砷酸盐的还原,总砷浓度(主要以亚砷酸盐为主)逐渐从约 7 增加到 115μg/L。因此,细菌介导的砷酸盐还原的还原解吸被认为是控制砷迁移性的主要过程,而 Fe(III)还原与硫酸盐还原是次要过程,它们也导致了研究区的砷富集。总的来说,本研究深入了解了弱碱性和还原条件下控制砷迁移性的机制,并表明细菌还原砷酸盐在导致地下水中亚砷酸盐大量解吸方面起着主要作用。