The leaching behavior of heavy metal from contaminated mining soil: The effect of rainfall conditions and the impact on surrounding agricultural lands

被引:11
|
作者
Wang, Fei [1 ]
Li, Wei [1 ]
Wang, Hao [1 ]
Hu, Yuanan [1 ]
Cheng, Hefa [2 ]
机构
[1] China Univ Geosci Beijing, Sch Water Resources & Environm, MOE Lab Groundwater Circulat & Evolut, Beijing 100083, Peoples R China
[2] Peking Univ, Coll Urban & Environm Sci, MOE Key Lab Earth Surface Proc, Beijing 100871, Peoples R China
关键词
Mining soils; Heavy metals; Leaching behavior; Chemical fractions; Ecological risk; ECOLOGICAL RISK-ASSESSMENT; POLYMETALLIC MINE; SURFACE RUNOFF; POLLUTION; TAILINGS; RIVER; AREA; BCR; PB; CD;
D O I
10.1016/j.scitotenv.2024.169877
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Contaminated mining soils could lead to heavy metal pollution of surrounding farmlands under rainfall conditions. With the aids of sequential extraction, batch leaching, and dynamic leaching experiments, this study was carried out to investigate the characteristics of heavy metals in contaminated mining soils, understand their leaching behavior under different rainfall conditions, and evaluate the potential effects on surrounding farmlands. The results indicated that the concentrations of heavy metals (Cr, Ni, Cu, Zn, As, Cd, and Pb) in the contaminated mining soils were several or even twenty times higher than their corresponding background values, and Cd, Zn, Cu and Pb had considerable proportions (>50 %) in mobile forms. The leaching amounts of heavy metals from the contaminated mining soils had positive correlation with their contents in acid soluble form, and showed strong dependence on rainfall pH conditions. Acid rainfalls (pH = 4.32) can greatly increase the average annual release of Cd, Zn, Cu and Pb from mine soils in the study area, with increments ranging from 72.4 % (Pb) to 85.9 % (Cd) compared to those under alkaline conditions (pH = 7.42). The leaching of heavy metals was well fitted by two-constant, pseudo second-order and parabolic equations, indicating that their multilayer sorption/desorption behavior on soil surface was dominated by chemical processes and their release was controlled by the diffusion within the soil pore channels. The two-column leaching experiment showed that the
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页数:11
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