Eawag, Swiss Federal Institute of Aquatic Science and Technology, Department Water Resources and Drinking Water, 8600 Dübendorf, Switzerland.
Key Laboratory of Analytical Technology for Environmental Quality and Food Safety Control (KLATEFOS), VNU University of Science, Vietnam National University, Hanoi, Vietnam.
Sci Total Environ. 2020 May 15;717:137143. doi: 10.1016/j.scitotenv.2020.137143. Epub 2020 Feb 5.
Geogenic arsenic (As) contamination of groundwater poses a major threat to global health, particularly in Asia. To mitigate this exposure, groundwater is increasingly extracted from low-As Pleistocene aquifers. This, however, disturbs groundwater flow and potentially draws high-As groundwater into low-As aquifers. Here we report a detailed characterisation of the Van Phuc aquifer in the Red River Delta region, Vietnam, where high-As groundwater from a Holocene aquifer is being drawn into a low-As Pleistocene aquifer. This study includes data from eight years (2010-2017) of groundwater observations to develop an understanding of the spatial and temporal evolution of the redox status and groundwater hydrochemistry. Arsenic concentrations were highly variable (0.5-510 μg/L) over spatial scales of <200 m. Five hydro(geo)chemical zones (indicated as A to E) were identified in the aquifer, each associated with specific As mobilisation and retardation processes. At the riverbank (zone A), As is mobilised from freshly deposited sediments where Fe(III)-reducing conditions occur. Arsenic is then transported across the Holocene aquifer (zone B), where the vertical intrusion of evaporative water, likely enriched in dissolved organic matter, promotes methanogenic conditions and further release of As (zone C). In the redox transition zone at the boundary of the two aquifers (zone D), groundwater arsenic concentrations decrease by sorption and incorporations onto Fe(II) carbonates and Fe(II)/Fe(III) (oxyhydr)oxides under reducing conditions. The sorption/incorporation of As onto Fe(III) minerals at the redox transition and in the Mn(IV)-reducing Pleistocene aquifer (zone E) has consistently kept As concentrations below 10 μg/L for the studied period of 2010-2017, and the location of the redox transition zone does not appear to have propagated significantly. Yet, the largest temporal hydrochemical changes were found in the Pleistocene aquifer caused by groundwater advection from the Holocene aquifer. This is critical and calls for detailed investigations.
地下水的地质成因砷(As)污染对全球健康构成了重大威胁,尤其是在亚洲。为了减轻这种暴露,人们越来越多地从低砷更新世含水层中提取地下水。然而,这会干扰地下水流动,并可能将高砷地下水吸入低砷含水层。在这里,我们报告了越南红河三角洲范府含水层的详细特征,在那里,来自全新世含水层的高砷地下水被吸入低砷更新世含水层。本研究包括 2010 年至 2017 年八年的地下水观测数据,以了解氧化还原状态和地下水水化学的时空演变。砷浓度在<200 m 的空间尺度上高度可变(0.5-510μg/L)。在含水层中确定了五个水文(地质)化学带(表示为 A 至 E),每个带都与特定的砷释放和阻滞过程相关。在河岸(A 区),砷从新沉积的沉积物中释放出来,在那里发生铁(III)还原条件。砷然后穿过全新世含水层(B 区)运输,在那里,蒸发水的垂直侵入,可能富含溶解有机质,促进产甲烷条件和进一步释放砷(C 区)。在两个含水层边界的氧化还原过渡带(D 区),在还原条件下,砷通过吸附和并入 Fe(II)碳酸盐和 Fe(II)/Fe(III)(氧氢)氧化物而减少地下水砷浓度。在氧化还原过渡带和 Mn(IV)还原更新世含水层(E 区)中,As 吸附/并入 Fe(III)矿物一直将 As 浓度保持在 10μg/L 以下,在 2010-2017 年的研究期间,氧化还原过渡带的位置似乎没有显著变化。然而,在全新世含水层中发现的最大的时间水文化学变化是由地下水从全新世含水层的对流引起的。这是至关重要的,需要进行详细的调查。