高级检索

基于PMF模型的石煤矿周边农田土壤重金属源解析与环境风险评价

Source apportionment and environmental risk assessment of heavy metals in farmland soils surrounding stone coal mines based on the PMF Model

  • 摘要: 本研究以我国南方典型石煤矿区周边小流域为研究对象,基于1 823个农用地土壤样点的Cd、Pb、As、Hg、Cr、Cu、Zn和Ni等8种重金属含量数据,综合采用地累积指数法、污染指数法、潜在生态风险指数法和正定矩阵因子分解(PMF)模型,系统分析土壤重金属污染特征、来源贡献及生态风险,构建污染来源与风险贡献之间的定量关联。结果表明,研究区土壤重金属污染以Cd最为突出,其地累积指数和污染指数平均值分别为1.85和1.59,达到中度累积和中度污染水平,超过风险筛选值的样点比例达到45%;Hg表现出较高生态风险,潜在生态风险指数平均值为80.55;其余元素整体污染水平较低。PMF模型识别出4类主要污染来源,分别为地质背景与农业生产复合源(48.20%)、燃料燃烧与交通运输混合源(35.87%)、采选冶工业污染源(7.83%)以及采选冶炼与养殖农业混合源(8.11%)。研究区综合潜在生态风险指数(RI)平均值为353.03,整体处于较强生态风险水平,其中Cd和Hg是主要风险贡献元素。进一步分析发现,不同污染来源的质量贡献与生态风险贡献存在明显偏离,采选冶工业源虽然仅贡献7.83%的重金属质量负荷,但其生态风险贡献达到57.67%,表现出典型的“低质量贡献-高风险贡献”特征,是研究区风险精准管控的优先对象。本研究构建的“源-风险”关联分析框架,可为石煤矿区周边农田土壤重金属污染精准溯源、风险识别和分区管控提供科学依据。

     

    Abstract: This study investigated a typical small watershed surrounding a stone coal mining area in southern China. Based on concentrations of eight heavy metals (Cd, Pb, As, Hg, Cr, Cu, Zn, and Ni) from 1,823 agricultural soil sampling sites, the geo-accumulation index, pollution index, potential ecological risk index, and positive matrix factorization (PMF) model were integrated to systematically characterize heavy metal pollution, quantify source contributions, evaluate ecological risks, and establish a quantitative linkage between pollution sources and ecological risk contributions. The results showed that Cd was the most prominent contaminant in the study area. The mean geo-accumulation index and pollution index of Cd were 1.85 and 1.59, respectively, indicating moderate accumulation and moderate pollution levels, with 45% of sampling sites exceeding the risk screening value. Hg exhibited a relatively high ecological risk, with a mean potential ecological risk index of 80.55, whereas the remaining elements showed relatively low pollution levels. The PMF model identified four major pollution sources: composite sources of geological background and agricultural activities (48.20%), mixed sources of fuel combustion and transportation (35.87%), industrial sources associated with mining, beneficiation, and smelting activities (7.83%), and mixed sources of mining and smelting industries and livestock farming (8.11%). The mean comprehensive potential ecological risk index (RI) was 353.03, indicating a considerable ecological risk level, with Cd and Hg identified as the dominant risk contributors. Further analysis revealed a significant discrepancy between the mass loading contribution and ecological risk contribution of different pollution sources. Although the industrial source associated with mining and smelting activities contributed only 7.83% of the heavy metal mass loading, it accounted for 57.67% of the total ecological risk, showing a typical pattern of “low mass contribution but high risk contribution”. Therefore, this source should be prioritized for risk management and control. The source-risk linkage framework established in this study provides a scientific basis for precise source identification, risk assessment, and zonal management of heavy metal pollution in farmland soils surrounding stone coal mining areas.

     

/

返回文章
返回