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西藏年楚河流域农用地土壤重金属分布与生态风险评价

杜梅 张强英 任培 高爽 布多

杜梅,张强英,任培,等.西藏年楚河流域农用地土壤重金属分布与生态风险评价[J].环境工程技术学报,2022,12(5):1618-1625 doi: 10.12153/j.issn.1674-991X.20210381
引用本文: 杜梅,张强英,任培,等.西藏年楚河流域农用地土壤重金属分布与生态风险评价[J].环境工程技术学报,2022,12(5):1618-1625 doi: 10.12153/j.issn.1674-991X.20210381
DU M,ZHANG Q Y,REN P,et al.Distribution of soil heavy metals and ecological risk assessment of agricultural land in Nianchu River basin, Tibet[J].Journal of Environmental Engineering Technology,2022,12(5):1618-1625 doi: 10.12153/j.issn.1674-991X.20210381
Citation: DU M,ZHANG Q Y,REN P,et al.Distribution of soil heavy metals and ecological risk assessment of agricultural land in Nianchu River basin, Tibet[J].Journal of Environmental Engineering Technology,2022,12(5):1618-1625 doi: 10.12153/j.issn.1674-991X.20210381

西藏年楚河流域农用地土壤重金属分布与生态风险评价

doi: 10.12153/j.issn.1674-991X.20210381
基金项目: 第二次青藏高原综合科学考察研究项目(2019QZKK0603);国家重点研发计划项目(2019YFC1904103);西藏自治区自然科学基金项目(XZ2019ZRG-02(Z));中央支持地方高校改革发展专项资金(藏财预指[2020]1号、[2021]1号)
详细信息
    作者简介:

    杜梅(1996—),女,硕士研究生,主要研究方向为固体废物资源化过程环境风险管控,dumeicl@163.com

    通讯作者:

    布多(1972—),男,教授,主要研究方向为环境化学与环境监测,phudor@vip.163.com

  • 中图分类号: X522

Distribution of soil heavy metals and ecological risk assessment of agricultural land in Nianchu River basin, Tibet

  • 摘要:

    以西藏年楚河流域江孜县、白朗县农用地土壤为研究对象,对Hg、As、Pb、Cd、Cr、Cu、Mn、Zn和Ni 9种重金属进行调查;采用单因子指数法、内梅罗综合污染指数法等方法,结合空间插值法评价年楚河流域农用地土壤重金属污染状况,同时运用相关性和主成分分析探究土壤重金属来源。结果表明:1)农用地土壤中Hg、Cu、Mn和Ni浓度与西藏土壤环境背景值相比,均表现为不同程度的累积,与GB 15618—2018《土壤环境质量 农用地土壤污染风险管控标准(试行)》比较,As元素超标率最大;从江孜县到白朗县,农用地土壤重金属综合生态风险指数逐步增大;2)研究区的区域污染负荷指数为1.45,属低污染等级,重度污染集中在白朗县;3)主成分分析表明,9种重金属的来源可分为自然与人为源复合因子、矿山开采因子、农业因子、土壤母质因子和大气传输因子。

     

  • 图  1  年楚河流域行政区划及采样点分布

    Figure  1.  Administrative divisions and distribution of sampling points in Nianchu River basin

    图  2  采样点农用地土壤PN空间分布

    Figure  2.  PN spatial distribution of soil in agricultural land at each sampling point

    图  3  各采样点农用地土壤中9种重金属Igeo统计

    Figure  3.  Igeo distribution of 9 heavy metals in soils of agricultural land at sampling sites

    图  4  各采样点农用地土壤中9种重金属Er统计

    Figure  4.  Er distribution of 9 heavy metals in soils of agricultural land at sampling sites

    图  5  各采样点农用地土壤中Hg、Cd和Ni的Er空间分布

    Figure  5.  Er spatial distribution of Hg, Cd and Ni in soils of agricultural land at sampling points

    图  6  研究区农用地土壤RI空间分布

    Figure  6.  RI spatial distribution in soils of agricultural land in the study area

    图  7  农用地土壤9种重金属主成分载荷

    Figure  7.  Principal component loading of nine heavy metals in soils of agricultural land

    表  1  单因子指数法与内梅罗指数法评价标准

    Table  1.   Evaluation criteria of single-factor index method and Nemerow index method

    PiPN
    数值污染等级数值污染等级
    <1清洁<0.7清洁
    1~2轻度0.7~1警戒
    2~3中度1~2轻度
    ≥3重度2~3中度
    ≥3重度
    下载: 导出CSV

    表  2  潜在生态风险指数法评价标准

    Table  2.   Evaluation standard of potential ecological risk index method

    ErRI 风险等级
    <40<150 低风险
    40~80150~300 中等风险
    80~160300~600 重度风险
    160~320≥600 较重度风险
    ≥320 严重风险
    下载: 导出CSV

    表  3  农用地采样点土壤中重金属浓度统计结果

    Table  3.   Statistical results of heavy metal concentrations in the soil of sampling sites in agricultural land

    重金属浓度/(mg/kg)变异系数西藏土壤环境背景值[18]/(mg/kg)超标采样点数量占比/%
    最大值最小值平均值
    Hg0.160.030.060.540.026100
    As34.108.0920.960.3818.7068.8
    Pb30.9014.5022.840.2328.9012.5
    Cd0.180.080.120.200.08100
    Cr516.0069.20161.630.8677.4087.5
    Cu52.1029.5039.180.1621.9093.8
    Mn1 287.88666.67903.880.19626.0093.8
    Zn148.0067.7093.220.2073.7087.5
    Ni583.3338.89117.691.4332.1093.8
    下载: 导出CSV

    表  4  农用地土壤各采样点Igeo和PLI统计结果

    Table  4.   Statistical results of Igeo and PLI at each sampling point of agricultural land soil

    样点编号 Igeo PLI
    Hg As Pb Cd Cr Cu Mn Zn Ni
    1 0.65 −1.61 −1.58 −0.58 −0.10 −0.04 −0.05 −0.13 −0.17 1.14
    2 0.11 −1.79 −1.46 0.12 0.69 0.32 −0.05 0.42 0.39 1.36
    3 1.20 −0.23 −0.49 0.32 −0.06 0.67 −0.17 −0.09 −0.05 1.63
    4 0.14 −0.14 −0.73 0.12 −0.40 0.28 −0.49 −0.39 −0.31 1.29
    5 0.56 −0.84 −0.82 0.12 −0.20 0.62 −0.17 −0.13 0.00 1.40
    6 0.79 0.09 −0.61 0.58 −0.10 0.34 −0.17 −0.16 −0.07 1.58
    7 0.05 0.20 −0.88 0.00 −0.34 0.12 −0.40 −0.39 −0.25 1.30
    8 −0.28 0.03 −0.79 0.00 −0.45 0.23 −0.05 −0.35 −0.20 1.30
    9 −0.35 −0.47 −0.53 0.32 −0.75 0.27 0.37 −0.14 −0.28 1.33
    10 0.47 0.28 −0.63 0.12 −0.46 0.10 0.46 −0.21 −0.14 1.50
    11 0.27 −1.50 −1.39 −0.26 0.92 0.29 −0.05 −0.52 1.62 1.43
    12 0.59 −0.55 −1.05 0.12 −0.36 0.03 −0.35 −0.36 −0.07 1.29
    13 2.05 −0.16 −0.89 0.00 −0.38 0.10 −0.17 −0.07 0.41 1.60
    14 −0.17 −0.53 −1.08 −0.13 0.39 0.42 −0.17 −0.55 0.95 1.40
    15 0.80 −0.56 −1.17 −0.55 2.07 −0.16 0.18 −0.71 3.60 1.96
    16 0.28 −0.85 −1.25 0.00 2.15 0.24 0.07 −0.53 3.37 1.96
    下载: 导出CSV

    表  5  研究区农用地土壤中重金属元素之间相关系数

    Table  5.   Correlation coefficients of heavy metal elements in the soil of agricultural land in the study area

    重金属HgAsPbCdCrCuMnZnNi
    Hg1
    As0.1251
    Pb0.1030.750**1
    Cd0.0220.4530.745**1
    Cr−0.61−0.357−0.480−0.4141
    Cu−0.67−0.0570.4060.519*−0.2421
    Mn−0.1420.0180.125−0.0570.235−0.2291
    Zn0.174−0.2260.0200.364−0.3800.2680.0341
    Ni−0.002−0.243−0.384−0.4370.976**−0.3260.276−0.4801
    注:*表示在0.05水平上显著相关;**表示在0.01水平上显著相关。
    下载: 导出CSV
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