Zhang Di, Ke Tiantian, Xiu Wei, Ren Cui, Chen Guangyu, Lloyd Jonathan R, Bassil Naji M, Richards Laura A, Polya David A, Wang Guangcai, Guo Huaming
State Key Laboratory of Biogeology and Environmental Geology and MOE Key Laboratory of Groundwater Circulation and Environmental Evolution, China University of Geosciences, Beijing 100083, PR China; School of Water Resources and Environment, China University of Geosciences (Beijing), Beijing 100083, PR China.
State Key Laboratory of Biogeology and Environmental Geology and MOE Key Laboratory of Groundwater Circulation and Environmental Evolution, 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, Department of Earth and Environmental Sciences, The University of Manchester, Manchester M13 9PL, United Kingdom.
Sci Total Environ. 2023 Feb 1;858(Pt 3):160066. doi: 10.1016/j.scitotenv.2022.160066. Epub 2022 Nov 8.
Sulfide-induced reduction (sulfidization) of arsenic (As)-bearing Fe(III) (oxyhydro)oxides may lead to As mobilization in aquifer systems. However, little is known about the relative contributions of sulfidization and non-sulfidization of Fe(III) (oxyhydro)oxides reduction to As mobilization. To address this issue, high As groundwater with low sulfide (LS) and high sulfide (HS) concentrations were pumped through As(V)-bearing ferrihydrite-coated sand columns (LS-column and HS-column, respectively) being settled within wells in the western Hetao Basin, China. Sulfidization of As(V)-bearing ferrihydrite was evidenced by the increase in dissolved Fe(II) and the presence of solid Fe(II) and elemental sulfur (S) in both the columns. A conceptual model was built using accumulated S and Fe(II) produced in the columns to calculate the proportions of sulfidization-induced Fe(III) (oxyhydro)oxide reduction and non-sulfidization-induced Fe(III) (oxyhydro)oxide reduction. Fe(III) reduction via sulfidization occurred preferentially in the inlet ends (LS-column, 31 %; HS-column, 86 %), while Fe(III) reduction via non-sulfidization processes predominated in the outlet ends (LS-column, 96 %; HS-column, 86 %), and was attributed to the metabolism of genera associated with Fe(III) reduction (including Shewanella, Ferribacterium, and Desulfuromonas). Arsenic was mobilized in the columns via sulfidization and non-sulfidization processes. More As was released from the solid of the HS-column than that of the LS-column due to the higher intensity of sulfidization in the presence of higher concentrations of dissolved S(-II). Overall, this study highlights the sulfidization of As-bearing Fe(III) (oxyhydro)oxides as an important As-mobilizing pathway in complex As-Fe-S bio-hydrogeochemical networks.
硫化物诱导的含砷铁(III)(羟基)氧化物的还原(硫化作用)可能导致含水层系统中砷的活化。然而,关于铁(III)(羟基)氧化物还原的硫化作用和非硫化作用对砷活化的相对贡献,人们知之甚少。为了解决这个问题,分别将低硫化物(LS)和高硫化物(HS)浓度的高砷地下水抽过中国河套盆地西部井中沉降的含砷(V)水铁矿涂层砂柱(分别为LS柱和HS柱)。含砷(V)水铁矿的硫化作用通过溶解态Fe(II)的增加以及两柱中固态Fe(II)和元素硫(S)的存在得到证实。利用柱中积累的S和Fe(II)建立了一个概念模型,以计算硫化作用诱导的铁(III)(羟基)氧化物还原和非硫化作用诱导的铁(III)(羟基)氧化物还原的比例。通过硫化作用的Fe(III)还原优先发生在入口端(LS柱为31%;HS柱为86%),而通过非硫化作用过程的Fe(III)还原在出口端占主导(LS柱为96%;HS柱为86%),这归因于与Fe(III)还原相关的属(包括希瓦氏菌属、铁杆菌属和脱硫单胞菌属)的代谢。砷通过硫化作用和非硫化作用过程在柱中被活化。由于在较高浓度溶解态S(-II)存在下硫化作用强度较高,HS柱固体释放的砷比LS柱更多。总体而言,本研究强调了含砷铁(III)(羟基)氧化物的硫化作用是复杂的砷 - 铁 - 硫生物地球化学网络中砷活化的重要途径。