吕留彦,陈祥娥,陈武,等. 黔西北土法炼锌集聚区重金属污染评价及范围界定[J]. 农业工程学报,2024,40(18):228-239. DOI: 10.11975/j.issn.1002-6819.202403002
    引用本文: 吕留彦,陈祥娥,陈武,等. 黔西北土法炼锌集聚区重金属污染评价及范围界定[J]. 农业工程学报,2024,40(18):228-239. DOI: 10.11975/j.issn.1002-6819.202403002
    LYU Liuyan, CHEN Xiang´e, CHEN Wu, et al. Assessment of heavy metal pollution and scope definition in the Indigenous Zinc Smelting agglomeration areas of northwest Guizhou Province of China[J]. Transactions of the Chinese Society of Agricultural Engineering (Transactions of the CSAE), 2024, 40(18): 228-239. DOI: 10.11975/j.issn.1002-6819.202403002
    Citation: LYU Liuyan, CHEN Xiang´e, CHEN Wu, et al. Assessment of heavy metal pollution and scope definition in the Indigenous Zinc Smelting agglomeration areas of northwest Guizhou Province of China[J]. Transactions of the Chinese Society of Agricultural Engineering (Transactions of the CSAE), 2024, 40(18): 228-239. DOI: 10.11975/j.issn.1002-6819.202403002

    黔西北土法炼锌集聚区重金属污染评价及范围界定

    Assessment of heavy metal pollution and scope definition in the Indigenous Zinc Smelting agglomeration areas of northwest Guizhou Province of China

    • 摘要: 研究黔西北土法炼锌矿渣集聚区土壤、水系沉积物和水体重金属污染状况以及潜在生态危害,是保护土地和水资源的重要基础,对维护当地粮食安全和人民身体健康具有重要意义。该研究系统采集不同介质样品,测定其8种重金属含量及pH值,分析重金属在不同介质中的空间分布和来源,确定影响区域,对其进行污染和潜在生态危害评价,圈定重金属污染范围及强生态风险区域。结果表明,研究区表层土壤中除Hg和pH值外其他元素含量均高于毕节地区表层土壤背景值;As、Cd、Pb和Zn在空间分布上极不均匀,主要集中于表层土壤中,深部则主要受地质背景和原生土壤控制;约12.5%的研究区存在强或极强潜在生态风险,主要位于土法炼锌矿渣周边。土法炼锌矿渣集中的小流域2500 m内水体为重度污染,在矿渣集中分布区下游Cr、Cu、Ni、Pb和Zn含量存在叠加现象,As和Cd受集中连片矿渣影响最为明显;水系沉积物中As、Cd、Cu、Pb和Zn在矿渣集中区为重度污染,在下游2500 m外As、Pb和Zn未污染,Cd和Cu受地质背景影响为轻度污染。在高地质背景下,土法炼锌矿渣重污染区域主要分布于集中堆存区周边,受地形地貌及水文地质制约其影响范围较为有限。

       

      Abstract: Heavy metal pollution has been a serious risk in the Indigenous Zinc Smelting in Northwest Guizhou, China. Long-term open-air stacking of waste slag has also led to a great increase in the heavy metal reactivity under suitable environmental conditions after leaching, thus continuously migrating to the surrounding groundwater, surface water, and soil. A substantial amount of mining slag has been left behind, due to outdated technology and extensive production. Therefore, it is very urgent to clarify the contamination status of heavy metals in the soil, water bodies, and sediments in the areas, particularly with the concentrated distribution of Indigenous Zinc Smelting slag and their potential ecological risks, in order to protect the local land and water resources for the food safety and public health. This study focused on an 8 km2 area with a relatively wide distribution of Indigenous Zinc Smelting slag from traditional smelting areas. Human pollution sources were avoided to collect the surface soil samples within a grid of 1/9 km2. The background levels of heavy metals in surface soils were established over the region. Some samples were collected from the smaller watersheds, including surface soil, sediment from water systems, leachate, mine slag, and water bodies, according to the hydrogeological and topographical conditions. Additionally, the samples of deep soil profile were gathered from the site, where the largest amount of mine slag was stored for the longest time. The content of heavy metals and pH value were measured in various samples using the single-factor pollution index, Nemerow comprehensive pollution index, and potential ecological risk index. The spatial distribution and pollution status of heavy metals were analyzed in different media. The results show that the surface soil in the study area was mainly acidic, where the average contents of As, Cd, Cr, Cu, Hg, Ni, Pb, and Zn were 23.54, 3.20, 208.78, 193.02, 0.07, 91.41, 315.80, and 479.13 mg/kg, respectively. Except for Hg and pH, the contents of the rest elements were higher than the background value of surface soil in the Bijie region. The contents of As, Cd, Cr, Cu, Ni, Pb, and Zn exceeded the national environmental background values of surface soil. The overall slag was neutral with the average contents of As, Cd, Cu, Hg, Pb, and Zn higher than the average value of surface soil in the study area. Especially Pb, the raw materials used in local traditional zinc smelting were imported the lead-zinc ores. The soil profile samples show that the heavy metals were mainly concentrated in the surface soil of 0-20cm, whereas, the heavy metals in deep soil were mainly controlled by geological background and primary soil. The highest contents of As, Cd, Cu, Pb, and Zn in small watershed sediments were 274, 11.90, 488, 2340, and 2580 mg/kg, respectively, all of which were located in the central area of traditional zinc smelting slag. The highest contents of Cr, Cu, Ni, Pb, and Zn in the surface water of a small watershed were distributed downstream of the slag concentrated distribution area, which were 43.60, 64.90, 15.70, 226.00, and 223.00 mg/L, respectively. Only Ni was slightly higher than the content of slag leachate in groundwater. The contents of the rest elements were lower than those in the leachate. Single-factor evaluation was performed on the pollution of heavy metals in the surface soil. The Cd and Cu shared the highest proportion of pollution, with the Cd in the widest range of pollution. The Nemerow comprehensive pollution index for heavy metals in small watershed sediments was heavily polluted by As, Cd, Cu, Pb, and Zn. The very strong potential ecological risk was only found in the central part of the traditional Indigenous Zinc Smelting slag distribution area. The Nemerow comprehensive pollution index of heavy metals in small watershed water bodies was severely polluted; The medium to very strong potential ecological risk areas were concentrated in the traditional zinc smelting slag distribution areas. There was an extremely uneven distribution of As, Cd, Pb, and Zn in the surface soil with the coefficients of variation exceeding 1.5, indicating the strong human factors. About 12.5% of the study area shared a strong ecological risk, which was mainly distributed around the waste dump site of the Indigenous Zinc Smelting plant. As such, the Indigenous Zinc Smelting slag posed a significant impact on the surrounding ecology. The pollution range of heavy metals was concentrated mainly within 2500 m in the water sediments in the small watershed; The impact of slag on groundwater was less than that on surface water, due to the restriction from the hydrogeological conditions. Overall, the pollution areas of the zinc smelting slag in the study area were mainly distributed around the centralized storage area of the slag, with a relatively limited range of impacts.

       

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