Heavy metal accumulation in the surrounding areas affected by mining in China: Spatial distribution patterns, risk assessment, and influencing factors

土壤水分 环境科学 污染 空间分布 环境化学 中国 降水 重金属 分布(数学) 风险评估 共同空间格局 自然地理学 土壤科学 生态学 地理 化学 生物 数学 气象学 数学分析 考古 遥感 计算机科学 计算机安全
作者
Hongbo Liu,Mingkai Qu,Chen Jian,Xu Guang,Jianlin Zhang,Maosheng Liu,Junfeng Kang,Yongcun Zhao,Biao Huang
出处
期刊:Science of The Total Environment [Elsevier]
卷期号:825: 154004-154004 被引量:83
标识
DOI:10.1016/j.scitotenv.2022.154004
摘要

Previous studies about heavy metal (HM) accumulation in the surrounding areas affected by mining mainly focused on a single or just a few mining areas. However, these studies could not provide adequate information supporting HM controls in soils at the national scale. This study first conducted a literature investigation and collected HM data in mining areas in China from 263 pieces of published literature. Then, geo-accumulation index (Igeo), ecological risk index (ER), and health risk assessment model were adopted to evaluate their HM pollution, ecological risks, and health risks, respectively. Finally, Geodetector and Pearson correlation coefficients were used to explore the relationships between the spatial distribution patterns of HMs in soils and their influencing factors. Results showed that: (i) the average concentrations of Cd, Hg, Pb, Zn, Cu, As, Ni, and Cr were 5.4, 1.2, 335.3, 496.1, 105.8, 55.0, 42.6, and 72.4 mg kg-1, respectively, in the surrounding areas affected by mining in China; Cd pollution in soils (Igeo = 2.9) was most severe; Cd (ERCd > 320) and Hg (ERHg > 320) were the main ecological risk factors; (ii) among the selected factors, mine types, clay content, soil organic carbon, and precipitation with the highest relative importance for the spatial distribution patterns of the HMs; (iii) HM accumulation were inversely proportional to soil pH, and were proportional to clay content, precipitation, and temperature; (iv) As, Cd, Hg, Pb, and Ni should be selected as the HMs to be controlled preferentially; (v) priority attention should be given to mining areas in Central South China, Southwest China, Liaoning province, and Zhejiang province; (vi) special attention should be given to mining areas of antimony, tin, tungsten, molybdenum, manganese, and lead‑zinc. The above results provided crucial information for HM control in the areas affected by mining at the national scale.
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