Hebei and China Geological Survey Key Laboratory of Groundwater Remediation, Institute of Hydrogeology and Environmental Geology, Chinese Academy of Geological Sciences, Shijiazhuang, 050061, China; Key Laboratory of Cenozoic Geology and Environment, Institute of Geology and Geophysics, Chinese Academy of Sciences, Beijing, 100029, China.
Hebei and China Geological Survey Key Laboratory of Groundwater Remediation, Institute of Hydrogeology and Environmental Geology, Chinese Academy of Geological Sciences, Shijiazhuang, 050061, China.
Environ Pollut. 2020 Oct;265(Pt B):115105. doi: 10.1016/j.envpol.2020.115105. Epub 2020 Jun 26.
Sulfate (SO) contamination in groundwater and surface water is an environmental problem of widespread concern. In this study, we combined stable isotope analyses of SO (δS and δO) and water (δH and δO) with a Bayesian mixing model (SIAR), for the first time, to identify sources and transformation of SO in an area of northern China with multiple potential sources of pollution. The overall values of δS and δO-SO ranged from 1.3‰ to 16.3‰ and -3.8‰-8.8‰ in groundwater, and from -1.1‰ to 9.3‰ and 2.7‰-9.2‰ in surface waters, respectively. Analyses of SO isotopes and water chemistry indicated that SO in groundwater and surface water mainly originated from mixing of oxidation of sulfate, sewage, chemical fertilizers, dissolution of evaporite and precipitation. There was no significant correlation between δS and δO and SO concentration in groundwater, indicating that bacterial sulfate reduction did not affect the SO isotopic composition. SIAR model showed the main sources of SO in groundwater and surface water comprised oxidation of sulfide minerals and sewage. In groundwater, oxidation of sulfide minerals and sewage accounted for 37.5-44.5% and 35.5-42.7% of SO, respectively. In regard to surface waters, the contribution of oxidation of sulfide minerals to SO was higher in the wet season (31.8 ± 9.9%) than in the intermediate (22.4 ± 7.8%) and dry (20.9 ± 8.2%) seasons, but the contribution proportion of sewage was slightly lower in the wet season (19.9 ± 8.5%) than in the intermediate (23.8 ± 8.7%) and dry (24.2 ± 8.5%) seasons. This study indicates that it is necessary for local government to improve the treatment infrastructure for domestic sewage and optimize methods of agricultural fertilization and irrigation to prevent SO contamination of groundwater and surface water.
硫酸盐(SO)在地下水和地表水的污染是一个普遍关注的环境问题。本研究首次结合稳定同位素分析(δS 和 δO)和水(δH 和 δO)与贝叶斯混合模型(SIAR),对中国北方一个具有多种潜在污染源的地区的 SO 来源和转化进行了研究。地下水和地表水的 δS 和 δO-SO 的总体值分别为 1.3‰至 16.3‰和-3.8‰至-8.8‰,-1.1‰至 9.3‰和 2.7‰至 9.2‰。SO 同位素和水化学分析表明,地下水和地表水的 SO 主要来源于硫酸盐氧化、污水、化肥、蒸发盐溶解和沉淀的混合。地下水的 δS 和 δO 与 SO 浓度之间没有显著相关性,这表明细菌硫酸盐还原作用没有影响 SO 的同位素组成。SIAR 模型表明,地下水和地表水的 SO 主要来源于硫化物矿物氧化和污水。在地下水中,硫化物矿物氧化和污水分别占 SO 的 37.5-44.5%和 35.5-42.7%。对于地表水,硫化物矿物氧化对 SO 的贡献在雨季(31.8±9.9%)高于中间季(22.4±7.8%)和旱季(20.9±8.2%),但污水的贡献比例在雨季(19.9±8.5%)略低于中间季(23.8±8.7%)和旱季(24.2±8.5%)。本研究表明,地方政府有必要改善生活污水的处理基础设施,优化农业施肥和灌溉方式,以防止地下水和地表水的 SO 污染。