基于PMF模型和Pb同位素示踪的土壤重金属污染现状分析及源解析

    Analysis and source analysis of soil heavy metal pollution based on PMF model and Pb isotope tracing

    • 摘要:
      研究目的 为精准识别城市土壤重金属混合污染来源并验证模型解析结果的可靠性,以黑龙江省哈尔滨市土壤为研究对象,通过多维度数据融合与Pb同位素指纹技术,系统揭示土壤重金属分布特征与来源贡献,以期为城市土壤污染防控提供科学依据。
      研究方法 在研究区采集60个土壤样品,测定土壤Pb同位素、重金属Cr、Mn、Co、Ni、Cu、Zn、Cd、As、Pb元素总量及表层土壤形态总量。通过重金属的空间分布特征、多元统计分析和同位素示踪等,分析该区域重金属污染程度和污染来源。
      研究结果 研究区土壤重金属Cr、Mn、Co、Ni、Cu、Zn、Cd、As、Pb元素平均含量分别为55.2 mg/kg、651 mg/kg、9.63 mg/kg、23.7 mg/kg、31.0 mg/kg、119 mg/kg、16.1 mg/kg、0.35 mg/kg、45.6 mg/kg,Mn、Zn、Cd的酸可提取态占总量相对较高,表明这3种元素活性最强,对环境的影响最大。在空间分布上,Cu、Zn、Cd和Pb元素在生活区含量最高,且具有相似的高值分布点,Cr、Mn、Co和Ni元素在空间分布上相对均匀。
      结论 通过PMF受体模型发现,研究区35%的Mn、35%的As、33%的Pb来自煤炭燃烧;45%的Zn、32%的Cd来自交通排放;73%的Cu、43%的Zn、35%的Pb来自工业生产;55%的Ni、48%的Co、47%的Cr、41%的As来自成土母质。土壤中Pb同位素比值结果表明,土壤中Pb人为来源可能主要来自工业排放(包括燃煤排放和矿石冶炼)。

       

      Abstract:
      Objective To accurately identify mixed sources of heavy metal pollution in urban soils and verify the reliability of source apportionment models, this study focused on the soil in Harbin City. By integrating multi−dimensional data and Pb isotopic fingerprinting, we systematically revealed the distribution characteristics and source contributions of heavy metals, aiming to provide a scientific basis for urban soil pollution control.
      Methods Sixty soil samples were collected in the study area, and the total amount of soil Pb isotopes, heavy metals Cr, Mn, Co, Ni, Cu, Zn, Cd, As and Pb elements and the total surface soil morphology were determined. Through the spatial distribution characteristics of heavy metals, multivariate statistical analysis and isotope tracing, the degree of heavy metal pollution and the source of heavy metal pollution in this region were analyzed.
      Results The average contents of heavy metals Cr, Mn, Co, Ni, Cu, Zn, Cd, As and Pb in the study area were 55.2 mg/kg, 651 mg/kg, 9.63 mg/kg, 23.7 mg/kg, 31.0 mg/kg, 119 mg/kg, 16.1 mg/kg, 0.35 mg/kg and 45.6 mg/kg, respectively. In terms of spatial distribution, Cu, Zn, Cd and Pb elements had the highest content in the living area, and had similar high−value distribution points, while Cr, Mn, Co and Ni elements were relatively uniformly distributed spatially.
      Conclusions The PMF receptor model showed that 35% of Mn, 35% Of As and 33% of Pb in the study area came from coal combustion. 45% of Zn and 32% of Cd come from traffic emissions; 73% of Cu, 43% of Zn, and 35% of Pb come from industrial production; 55% of Ni, 48% of Co, 47% of Cr, and 41% of As come from the soil−forming parent material. The results of the Pb isotope ratio in soil indicate that the anthropogenic sources of Pb in soil may be mainly from industrial emissions (including coal burning emissions and ore smelting).

       

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