Key Laboratory for Environmental Factors Control of Agro-Product Quality Safety, Ministry of Agriculture and Rural Affairs, Tianjin, 300191, PR China; Agro-Environmental Protection Institute, Ministry of Agriculture and Rural Affairs, Tianjin 300191, PR China; College of Natural Resources and Environment, South China Agricultural University, Guangzhou, 510642, PR China.
Center for Environmental Remediation, Institute of Geographic Sciences and Natural Resources Research, Chinese Academy of Sciences, Beijing, 100101, PR China.
Chemosphere. 2019 Jul;227:614-623. doi: 10.1016/j.chemosphere.2019.04.030. Epub 2019 Apr 6.
The mining and smelting of lead-zinc (Pb-Zn) ores cause widespread As contamination. The fractions and colloidal distribution of As associated with Fe oxide minerals in Pb-Zn mine-contaminated soils have not been well understood. In this study, As fractions associated with Fe oxide minerals in Pb-Zn tailings- and smelter-contaminated soils were compared using sequential extraction techniques. Kinetic experiments were conducted to characterize the reactivity of Fe oxide minerals. The distribution of As and Fe oxide minerals in soil colloids were analyzed. The results show that in mining-contaminated soils (both tailings and smelter) the relatively active fraction (amorphous hydrous oxide-bound As, As) has a strong relationship with easily reducible Fe (Fe). In smelter-contaminated soils, relatively stable fractions (crystalline hydrous oxide-bound As, As) were closely associated with reducible Fe (Fe). Although the average proportions of specifically-bound As (As) and As in contaminated soils were similar, high As release in tailings-contaminated soils was observed because of the high reactivity of Fe oxide minerals in those soils compared with that in smelter-contaminated soils. Some slightly polluted soils with high pH and TOC concentrations formed As-bearing colloidal suspensions. Especially in smelter-contaminated soils, many small-sized soil colloids could facilitate As migration with surface runoff or vertical transport.
铅锌矿(Pb-Zn)的开采和冶炼会导致广泛的砷污染。与 Pb-Zn 矿区污染土壤中的氧化铁矿物结合的砷的形态和胶体分布尚未得到很好的理解。在本研究中,使用顺序提取技术比较了 Pb-Zn 尾矿和冶炼厂污染土壤中氧化铁矿物结合的砷形态。进行动力学实验以表征氧化铁矿物的反应性。分析了土壤胶体中砷和氧化铁矿物的分布。结果表明,在矿区污染土壤(尾矿和冶炼厂)中,相对活跃的形态(无定形水合氧化物结合态砷,As)与易还原的铁(Fe)有很强的关系。在冶炼厂污染土壤中,相对稳定的形态(结晶水合氧化物结合态砷,As)与可还原铁(Fe)密切相关。尽管污染土壤中特定结合态砷(As)和 As 的平均比例相似,但由于这些土壤中的氧化铁矿物的高反应性,在尾矿污染土壤中观察到了高砷释放。一些 pH 值和 TOC 浓度较高的轻度污染土壤形成了含砷胶体悬浮液。特别是在冶炼厂污染的土壤中,许多小尺寸的土壤胶体可以通过地表径流或垂直迁移促进砷的迁移。