Sources and enrichment processes of groundwater arsenite and arsenate in fissured bedrock aquifers in the Xunhua-Hualong basin, China

IF 3.1 3区 地球科学 Q1 GEOCHEMISTRY & GEOPHYSICS Applied Geochemistry Pub Date : 2023-08-01 DOI:10.1016/j.apgeochem.2023.105708
Shiping Xing , Huaming Guo , Xueda Hu
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Abstract

Although high arsenic (As) groundwater has been widely observed in sedimentary aquifers, arsenite (As(III)) and arsenate (As(V)) mobilization in fissured bedrock aquifers are less documented, and different mobilization behaviors of As(III) and As(V) in groundwater from those aquifers are little known. Thus, geochemical and isotopic characteristics of high As groundwater in fissured bedrock aquifers in the Xunhua-Hualong basin were investigated. Results showed that fissured bedrock aquifer hosted high As groundwater. Total As concentrations in spring waters were up to 628 μg/L being dominated by As(V) with high ORP values (from 87.2 to 212 mV). As(III) dominated dissolved As in deep groundwater (up to 22.5 μg/L) with low ORP values (−217 and −288 mV). The positive correlation between As concentration and δ18O in spring water revealed that oxidation of As-bearing pyritic minerals in the fissured bedrock aquifers released As into groundwater. In deep groundwater under anoxic conditions recharged by shallow aquifers, high As groundwater usually had high concentrations of dissolved Fe, suggesting that reductive dissolution of Fe (oxyhydr)oxide minerals mobilized As into groundwater. Elevated concentrations of PO43− in high As spring water and deep groundwater indicated the competition adsorption between PO43− and As(V) (and As(III)). Insignificant correlations were observed between As(V) and pH, HCO3, and Na+/Ca2+ in spring water, revealing that desorption induced by pH and HCO3 and cation exchange between Ca2+ and Na + had negligible effects on As(V) mobilization. However, alkaline pH caused the desorption of As(III), and the presence of HCO3 was conducive to As(III) desorption in deep groundwater. A conceptual model was established to explain As distribution in fissured bedrock aquifers, emphasizing contributions of mineral dissolution, desorption, and hydrogeological conditions to As mobilization. This paper highlights different mobilization behaviors of As(III) and As(V) in groundwater from fissured bedrock aquifers, requiring the different strategies to ensure the safety of drinking water in those areas.

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循化-化龙盆地基岩裂隙含水层地下水亚砷酸盐和砷酸盐的来源及富集过程
虽然高砷(As)地下水在沉积含水层中已被广泛观察到,但亚砷酸盐(As(III))和砷酸盐(As(V))在裂隙基岩含水层中的运移研究较少,且对裂隙基岩含水层中As(III)和As(V)的不同运移行为知之甚少。为此,对循化—华龙盆地裂隙基岩含水层中高砷地下水的地球化学特征和同位素特征进行了研究。结果表明,裂隙基岩含水层含高砷地下水。泉水中总As浓度高达628 μg/L,以高ORP值(87.2 ~ 212 mV)的As(V)为主。深层地下水中溶解As以As(III)为主(最高达22.5 μg/L), ORP值较低(−217和−288 mV)。泉水中As浓度与δ18O呈正相关,表明裂隙基岩含水层含As黄铁矿氧化释放As进入地下水。在浅层含水层补给缺氧条件下的深层地下水中,高砷地下水通常具有高浓度的溶解铁,表明铁(氧合)氧化物矿物的还原性溶解将砷运移到地下水中。高砷泉水和深层地下水中PO43−浓度的升高表明PO43−与As(V)(和As(III))之间存在竞争吸附。泉水中As(V)与pH、HCO3−和Na+/Ca2+之间的相关性不显著,表明pH和HCO3−诱导的解吸以及Ca2+和Na+之间的阳离子交换对As(V)的动员影响可以忽略不计。而碱性pH引起As(III)的解吸,HCO3−的存在有利于深层地下水As(III)的解吸。建立了裂隙基岩含水层As分布的概念模型,强调矿物溶解、解吸和水文地质条件对As运移的贡献。本文重点分析了裂隙基岩含水层中As(III)和As(V)在地下水中的不同动员行为,并提出了保证裂隙基岩含水层饮用水安全的不同策略。
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来源期刊
Applied Geochemistry
Applied Geochemistry 地学-地球化学与地球物理
CiteScore
6.10
自引率
8.80%
发文量
272
审稿时长
65 days
期刊介绍: Applied Geochemistry is an international journal devoted to publication of original research papers, rapid research communications and selected review papers in geochemistry and urban geochemistry which have some practical application to an aspect of human endeavour, such as the preservation of the environment, health, waste disposal and the search for resources. Papers on applications of inorganic, organic and isotope geochemistry and geochemical processes are therefore welcome provided they meet the main criterion. Spatial and temporal monitoring case studies are only of interest to our international readership if they present new ideas of broad application. Topics covered include: (1) Environmental geochemistry (including natural and anthropogenic aspects, and protection and remediation strategies); (2) Hydrogeochemistry (surface and groundwater); (3) Medical (urban) geochemistry; (4) The search for energy resources (in particular unconventional oil and gas or emerging metal resources); (5) Energy exploitation (in particular geothermal energy and CCS); (6) Upgrading of energy and mineral resources where there is a direct geochemical application; and (7) Waste disposal, including nuclear waste disposal.
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