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Enrichment characteristics, source identification, and health risk assessment of soil heavy metals in typical cultivated land in the mountainous area of southern Anhui Province |
YANG Yan( ), LIU Bin, XIA Fei-Qiang, CHEN Ping-Feng, ZHANG Xiang |
Anhui Institute of Geophysical and Geochemical Prospecting Techniques, Hefei 230022, China |
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Abstract This study aims to explore the enrichment characteristics and origin of soil heavy metals in typical cultivated land in the mountainous area of southern Anhui province. With Ningguo City in southeastern Anhui Province as the research object, this study collected 1399 topsoil samples in the cultivated land for determining the concentrations of As, Cd, Hg, Pb, Cr, Ni, Cu, and Zn. Furthermore, this study conducted a health risk assessment and source identification of heavy metals using the correlation analysis, the soil environmental quality - risk control standard for soil contamination of agricultural land, the geoaccumulation index, the health risk index, and the positive matrix factorization (PMF) model. The results are as follows: (1) The average concentrations of As, Cr, Hg, Pb, Cr, Ni, Cu, and Zn were 15.8×10-6, 0.41×10-6, 0.106×10-6, 31×10-6, 67×10-6, 29×10-6, 29×10-6, and 94×10-6, respectively, which were all higher than their background values in Anhui Province, except Ni. (2) The soil heavy metals generally exhibited low pollution risks, with the heavy metal concentrations of 866 soil samples lower than their risk screening values. (3) The cultivated soil was primarily polluted by Hg, Cd, and As, as indicated by the geoaccumulation index results. (4) Both non-carcinogenic and carcinogenic risk levels in adults in the study area were within the acceptable ranges, as revealed by the health risk assessment results. (5) Four sources of heavy metals in the study area were identified based on the PMF model: industrial and agricultural emissions associated with human activities, atmospheric deposition, soil parent materials related to soil types, and the geological background source.
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Received: 30 November 2022
Published: 26 February 2024
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Geographical location (a),soil type (b), and sampling point distribution(c) of the study area 1—Quaternary;2—Cretaceous;3—Jurassic;4—Permian;5—Carboniferous;6—Devonian;7—Silurian;8—Ordovician;9—Cambrian;10—Tanian;11—Nanhua system;12—Yanshanian monzonitic granite;13—Yanshanian monzonitic granite porphyry;14—granite porphyry;15—stratigraphic boundary;16—fault;17—soil sampling points
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元素/指标 | 分析方法 | 检出限/10-6 | 测定范围/10-6 | As | AFS | 0.2 | 0.2~500 | Cd | ICP-MS | 0.02 | 0.02~4.0 | Hg | AFS | 0.0005 | 0.0005~10 | Pb | ICP-MS | 2 | 2~2000 | Cr | ICP-AES | 3 | 3~3500 | Ni | ICP-AES | 0.05 | 0.05~2000 | Cu | ICP-AES | 1 | 1~2000 | Zn | ICP-AES | 2 | 2~3000 | pH | ISE | 0.1* | 0.1~14.0* |
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Analysis methods and detection limits for each element
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等级 | 1 | 2 | 3 | 4 | 5 | 6 | 7 | Igeo | ≤0 | >0~1 | >1~2 | >2~3 | >3~4 | >4~5 | ≥5 | 污染程度 | 无 | 无到中等 | 中等 | 中等到重度 | 重度 | 重度到极度 | 极度 |
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Classification standard of geoaccumulation index
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参数 | 含义 | 单位 | 成人 | 儿童 | | 土壤摄入量 | mg/d | 100 | 200 | EF | 暴露频率 | d/a | 350 | 350 | ED | 暴露期 | a | 24 | 6 | BW | 平均体重 | kg | 61.8 | 19.2 | AT | 平均作用时间 | d | 9125 | 2190 | SA | 可能接触土壤的皮肤面积 | cm2/d | 5700 | 2800 | AF | 皮肤对土壤的吸附系数 | mg/cm2 | 0.07 | 0.2 | ABS | 皮肤吸收率 | % | 0.1 | 0.1 | PEF | 土壤尘产生因子 | m3/kg | 1.36′109 | 1.36′109 | | 日空气吸入量 | m3/d | 14.5 | 7.5 |
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Health risk assessment model exposure parameters
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元素 | 参考计量RfD/mg·(kg·d)-1 | 致癌斜率SF/[mg/(kg·d)]-1 | 经口 | 皮肤 | 呼吸 | 经口 | 皮肤 | 呼吸 | As | 3.00×10-4 | 1.23′10-4 | 4.29′10-6 | 1.50 | 1.50 | 15.10 | Cd | 1.00×10-3 | 2.50′10-5 | 2.86′10-6 | | | 6.30 | Hg | 3.00×10-4 | 2.14′10-5 | | | | | Pb | 1.40×10-3 | 5.24′10-4 | | 8.50×10-3 | | 4.20×10-2 | Cr | 3.00×10-3 | 3.00′10-5 | 2.86′10-5 | 5.01×10-1 | 2.00′101 | 4.20′101 | Ni | 2.00×10-2 | 5.40′10-3 | 9.00′10-5 | 1.70 | 4.25′101 | 8.40×10-1 | Cu | 4.00×10-2 | 1.20′10-2 | | | | | Zn | 3.00×10-1 | 6.00′10-2 | | | | |
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RfD and SF of different heavy metal exposure pathways
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| 参数 | Cr | Cu | Ni | Zn | Cd | Pb | As | Hg | pH | 原始数据 | 最大值 | 326 | 95 | 94.48 | 451 | 16.06 | 225 | 292.5 | 0.650 | 8.3 | 最小值 | 10 | 7 | 4.49 | 39 | 0.03 | 4 | 1.3 | 0.030 | 4.3 | 中位数 | 68 | 27 | 28.20 | 91 | 0.21 | 30 | 10.6 | 0.100 | 5.4 | 算术平均值 | 67 | 29 | 29.00 | 94 | 0.41 | 31 | 15.8 | 0.106 | 5.5 | 标准离差 | 17.450 | 10.998 | 9.863 | 34.392 | 0.799 | 7.993 | 18.902 | 0.048 | 0.659 | 变异系数 | 0.26 | 0.38 | 0.34 | 0.37 | 1.97 | 0.26 | 1.20 | 0.46 | 0.12 | 迭代剔除后 | 算术平均值 | 67 | 29 | 28.57 | 91 | 0.27 | 30 | 11.4 | 0.098 | 5.4 | 标准离差 | 14.657 | 9.919 | 9.025 | 26.139 | 0.173 | 4.567 | 6.155 | 0.031 | 0.363 | 变异系数 | 0.22 | 0.35 | 0.32 | 0.29 | 0.64 | 0.15 | 0.54 | 0.32 | 0.07 | 样品数量 | 1374 | 1380 | 1383 | 1363 | 1288 | 1357 | 1276 | 1329 | 1290 | 安徽省[11] | 算术平均值 | 66.5 | 20.4 | 29.8 | 62 | 0.097 | 26.6 | 9.0 | 0.033 | 6.4 | 全国[17] | 算术平均值 | 66 | 25 | 27 | 71 | 0.205 | 30 | 10.3 | 0.076 | |
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Basic statistics of heavy metals in soil
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土壤污染 风险等级 | 样品数/件 | Cr | Cu | Ni | Zn | Cd | Pb | As | Hg | 综合 | 低风险 | 1398 | 1343 | 1393 | 1382 | 930 | 1396 | 1266 | 1397 | 866 | 风险可控 | 1 | 56 | 6 | 17 | 437 | 3 | 130 | 2 | 498 | 较高风险 | | | | | 32 | | 3 | | 35 |
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Statistical results of cultivated land soil pollution risk levels in the study area
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元素 | Igeo≤0 | 0<Igeo≤1 | 1<Igeo≤2 | 2<Igeo≤3 | 3<Igeo≤4 | 4<Igeo≤5 | Igeo>5 | 污染程度 | 无 | 无到中等 | 中等 | 中等到重度 | 重度 | 重度到极度 | 极度 | Cr | 99.0 | 0.9 | 0.1 | 0 | 0 | 0 | 0 | Cu | 62.1 | 36.9 | 1.0 | 0 | 0 | 0 | 0 | Ni | 95.4 | 4.4 | 0.1 | 0 | 0 | 0 | 0 | Zn | 53.4 | 44.8 | 1.6 | 0.1 | 0 | 0 | 0 | Cd | 20.7 | 42.8 | 20.6 | 11.8 | 2.7 | 0.8 | 0.6 | Pb | 93.9 | 6.0 | 0.1 | 0.1 | 0 | 0 | 0 | As | 65.0 | 24.2 | 7.0 | 3.1 | 0.6 | 0.1 | 0 | Hg | 3.4 | 51.5 | 41.0 | 4.0 | 0.1 | 0 | 0 |
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The proportion of heavy metals in different levels of geo-accumulation index
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元素 | Cr | Cu | Ni | Zn | Cd | Pb | As | Hg | Cr | 1.000 | | | | | | | | Cu | 0.613 | 1.000 | | | | | | | Ni | 0.743 | 0.872 | 1.000 | | | | | | Zn | 0.371 | 0.818 | 0.769 | 1.000 | | | | | Cd | 0.224 | 0.554 | 0.551 | 0.759 | 1.000 | | | | Pb | 0.181 | 0.401 | 0.290 | 0.444 | 0.256 | 1.000 | | | As | 0.273 | 0.379 | 0.348 | 0.269 | 0.170 | 0.225 | 1.000 | | Hg | 0.116 | 0.175 | 0.136 | 0.187 | 0.125 | 0.130 | -0.019 | 1.000 |
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Correlation analysis of heavy metal content in soil
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Source profiles and source contribution of soil heavy metals in the study area from PMF
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Factors profiles of heavy metals sources identified by PMF
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Space distribution of PMF-factors
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