Ecology and Environment ›› 2024, Vol. 33 ›› Issue (9): 1451-1459.DOI: 10.16258/j.cnki.1674-5906.2024.09.012
• Research Article [Environmental Science] • Previous Articles Next Articles
CONG Xin1(), ZHANG Huaidi1,2, ZHANG Rong2, ZHAO Cen2, CHEN Kun2, LIU Hanbing2,*(
)
Received:
2024-05-08
Online:
2024-09-18
Published:
2024-10-18
Contact:
LIU Hanbing
丛鑫1(), 张怀迪1,2, 张荣2, 赵琛2, 陈坤2, 刘寒冰2,*(
)
通讯作者:
刘寒冰
作者简介:
丛鑫(1976年生),女,教授,博士,研究方向为土壤环境化学和生态修复。E-mail: congxin1800@163.com
基金资助:
CLC Number:
CONG Xin, ZHANG Huaidi, ZHANG Rong, ZHAO Cen, CHEN Kun, LIU Hanbing. Pollution Characteristics and Risk Analysis of Heavy Metal in Farmland Soils of China in Recent 10 Years Based on Meta Analysis[J]. Ecology and Environment, 2024, 33(9): 1451-1459.
丛鑫, 张怀迪, 张荣, 赵琛, 陈坤, 刘寒冰. 基于Meta分析的近10年中国农田土壤重金属污染特征与风险解析[J]. 生态环境学报, 2024, 33(9): 1451-1459.
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URL: https://www.jeesci.com/EN/10.16258/j.cnki.1674-5906.2024.09.012
地区 | As | Cd | Cr | Cu | Hg | Ni | Pb | Zn | 文献 |
---|---|---|---|---|---|---|---|---|---|
北京 | 9.70 | 0.074 | 68.1 | 25.4 | 0.069 | 29.0 | 25.4 | 103 | 杨雳等, |
天津 | 9.60 | 0.090 | 84.2 | 21.0 | 0.084 | 33.3 | 21.0 | 79.3 | 杨雳等, |
河北 | 13.6 | 0.094 | 68.3 | 21.5 | 0.036 | 30.8 | 21.5 | 78.4 | 杨雳等, |
山西 | 9.80 | 0.128 | 61.8 | 15.8 | 0.027 | 32.0 | 15.8 | 75.5 | 杨雳等, |
辽宁 | 8.80 | 0.108 | 57.9 | 21.4 | 0.037 | 25.6 | 21.4 | 63.5 | 杨雳等, |
吉林 | 8.00 | 0.099 | 46.7 | 28.8 | 0.037 | 21.4 | 28.8 | 80.4 | 杨雳等, |
黑龙江 | 7.30 | 0.086 | 58.6 | 24.2 | 0.037 | 22.8 | 24.2 | 70.7 | 杨雳等, |
上海 | 9.19 | 0.138 | 70.2 | 25.0 | 0.095 | 29.9 | 25.0 | 81.3 | 杨雳等, |
江苏 | 11.0 | 0.126 | 77.8 | 26.2 | 0.289 | 26.7 | 26.2 | 62.6 | 杨雳等, |
浙江 | 9.20 | 0.070 | 52.9 | 23.7 | 0.086 | 24.6 | 23.7 | 70.6 | 杨雳等, |
安徽 | 9.99 | 0.097 | 66.5 | 26.6 | 0.033 | 29.8 | 26.6 | 62.0 | 杨雳等, |
福建 | 5.78 | 0.054 | 41.3 | 34.9 | 0.081 | 18.2 | 34.9 | 82.7 | 杨雳等, |
江西 | 14.9 | 0.108 | 45.9 | 32.3 | 0.084 | 18.9 | 32.3 | 69.4 | 杨雳等, |
山东 | 9.30 | 0.084 | 66.0 | 25.8 | 0.019 | 25.8 | 25.8 | 63.5 | 杨雳等, |
河南 | 11.4 | 0.074 | 63.8 | 19.6 | 0.034 | 26.7 | 19.6 | 60.1 | 杨雳等, |
湖北 | 12.3 | 0.172 | 86.0 | 26.7 | 0.080 | 37.3 | 26.7 | 83.6 | 杨雳等, |
湖南 | 15.7 | 0.126 | 71.4 | 29.7 | 0.116 | 31.9 | 29.7 | 94.4 | 杨雳等, |
广东 | 8.99 | 0.056 | 50.5 | 36.0 | 0.078 | 14.4 | 36.0 | 47.3 | 杨雳等, |
广西 | 20.5 | 0.267 | 82.1 | 24.0 | 0.152 | 26.6 | 24.0 | 75.6 | 杨雳等, |
四川 | 10.4 | 0.079 | 79.0 | 30.9 | 0.061 | 32.6 | 30.9 | 86.5 | 杨雳等, |
贵州 | 20.0 | 0.659 | 95.9 | 35.2 | 0.110 | 39.1 | 35.2 | 99.5 | 杨雳等, |
云南 | 18.4 | 0.218 | 65.2 | 40.6 | 0.058 | 42.5 | 40.6 | 89.7 | 杨雳等, |
西藏 | 16.2 | 0.074 | 68.0 | 19.4 | 0.021 | 32.1 | 27.6 | 70.7 | 杨雳等, |
陕西 | 11.1 | 0.094 | 62.5 | 21.4 | 0.030 | 28.8 | 21.4 | 69.4 | 杨雳等, |
甘肃 | 12.6 | 0.116 | 70.2 | 18.8 | 0.020 | 35.2 | 18.8 | 68.5 | 杨雳等, |
宁夏 | 11.9 | 0.112 | 60 | 20.9 | 0.021 | 36.5 | 20.9 | 58.8 | 杨雳等, |
新疆 | 11.2 | 0.120 | 49.3 | 19.4 | 0.017 | 26.6 | 19.4 | 68.8 | 杨雳等, |
重庆 | 5.82 | 0.133 | 76.1 | 23.8 | 0.053 | 30.6 | 25.5 | 75.8 | 杨雳等, |
内蒙古 | 6.12 | 0.050 | 39.8 | 13.9 | 0.030 | 18.6 | 16.8 | 56.6 | 高红霞等, |
海南 | 1.14 | 0.050 | 15.2 | 4.95 | 0.030 | 4.12 | 22.3 | 35.1 | 谭凌智等, |
Table 1 Background values of heavy metals in soils of survey regions mg·kg?1
地区 | As | Cd | Cr | Cu | Hg | Ni | Pb | Zn | 文献 |
---|---|---|---|---|---|---|---|---|---|
北京 | 9.70 | 0.074 | 68.1 | 25.4 | 0.069 | 29.0 | 25.4 | 103 | 杨雳等, |
天津 | 9.60 | 0.090 | 84.2 | 21.0 | 0.084 | 33.3 | 21.0 | 79.3 | 杨雳等, |
河北 | 13.6 | 0.094 | 68.3 | 21.5 | 0.036 | 30.8 | 21.5 | 78.4 | 杨雳等, |
山西 | 9.80 | 0.128 | 61.8 | 15.8 | 0.027 | 32.0 | 15.8 | 75.5 | 杨雳等, |
辽宁 | 8.80 | 0.108 | 57.9 | 21.4 | 0.037 | 25.6 | 21.4 | 63.5 | 杨雳等, |
吉林 | 8.00 | 0.099 | 46.7 | 28.8 | 0.037 | 21.4 | 28.8 | 80.4 | 杨雳等, |
黑龙江 | 7.30 | 0.086 | 58.6 | 24.2 | 0.037 | 22.8 | 24.2 | 70.7 | 杨雳等, |
上海 | 9.19 | 0.138 | 70.2 | 25.0 | 0.095 | 29.9 | 25.0 | 81.3 | 杨雳等, |
江苏 | 11.0 | 0.126 | 77.8 | 26.2 | 0.289 | 26.7 | 26.2 | 62.6 | 杨雳等, |
浙江 | 9.20 | 0.070 | 52.9 | 23.7 | 0.086 | 24.6 | 23.7 | 70.6 | 杨雳等, |
安徽 | 9.99 | 0.097 | 66.5 | 26.6 | 0.033 | 29.8 | 26.6 | 62.0 | 杨雳等, |
福建 | 5.78 | 0.054 | 41.3 | 34.9 | 0.081 | 18.2 | 34.9 | 82.7 | 杨雳等, |
江西 | 14.9 | 0.108 | 45.9 | 32.3 | 0.084 | 18.9 | 32.3 | 69.4 | 杨雳等, |
山东 | 9.30 | 0.084 | 66.0 | 25.8 | 0.019 | 25.8 | 25.8 | 63.5 | 杨雳等, |
河南 | 11.4 | 0.074 | 63.8 | 19.6 | 0.034 | 26.7 | 19.6 | 60.1 | 杨雳等, |
湖北 | 12.3 | 0.172 | 86.0 | 26.7 | 0.080 | 37.3 | 26.7 | 83.6 | 杨雳等, |
湖南 | 15.7 | 0.126 | 71.4 | 29.7 | 0.116 | 31.9 | 29.7 | 94.4 | 杨雳等, |
广东 | 8.99 | 0.056 | 50.5 | 36.0 | 0.078 | 14.4 | 36.0 | 47.3 | 杨雳等, |
广西 | 20.5 | 0.267 | 82.1 | 24.0 | 0.152 | 26.6 | 24.0 | 75.6 | 杨雳等, |
四川 | 10.4 | 0.079 | 79.0 | 30.9 | 0.061 | 32.6 | 30.9 | 86.5 | 杨雳等, |
贵州 | 20.0 | 0.659 | 95.9 | 35.2 | 0.110 | 39.1 | 35.2 | 99.5 | 杨雳等, |
云南 | 18.4 | 0.218 | 65.2 | 40.6 | 0.058 | 42.5 | 40.6 | 89.7 | 杨雳等, |
西藏 | 16.2 | 0.074 | 68.0 | 19.4 | 0.021 | 32.1 | 27.6 | 70.7 | 杨雳等, |
陕西 | 11.1 | 0.094 | 62.5 | 21.4 | 0.030 | 28.8 | 21.4 | 69.4 | 杨雳等, |
甘肃 | 12.6 | 0.116 | 70.2 | 18.8 | 0.020 | 35.2 | 18.8 | 68.5 | 杨雳等, |
宁夏 | 11.9 | 0.112 | 60 | 20.9 | 0.021 | 36.5 | 20.9 | 58.8 | 杨雳等, |
新疆 | 11.2 | 0.120 | 49.3 | 19.4 | 0.017 | 26.6 | 19.4 | 68.8 | 杨雳等, |
重庆 | 5.82 | 0.133 | 76.1 | 23.8 | 0.053 | 30.6 | 25.5 | 75.8 | 杨雳等, |
内蒙古 | 6.12 | 0.050 | 39.8 | 13.9 | 0.030 | 18.6 | 16.8 | 56.6 | 高红霞等, |
海南 | 1.14 | 0.050 | 15.2 | 4.95 | 0.030 | 4.12 | 22.3 | 35.1 | 谭凌智等, |
项目 | 地积累指数污染程度等级 | ||||
---|---|---|---|---|---|
Igeo | 3<Igeo | 2<Igeo≤3 | 1<Igeo≤2 | 0<Igeo≤1 | Igeo≤0 |
分级 | 4 | 3 | 2 | 1 | 0 |
污染程度 | 严重污染 | 重度污染 | 中度污染 | 轻度污染 | 无污染 |
Table 2 Pollution classification standard of ground accumulation index
项目 | 地积累指数污染程度等级 | ||||
---|---|---|---|---|---|
Igeo | 3<Igeo | 2<Igeo≤3 | 1<Igeo≤2 | 0<Igeo≤1 | Igeo≤0 |
分级 | 4 | 3 | 2 | 1 | 0 |
污染程度 | 严重污染 | 重度污染 | 中度污染 | 轻度污染 | 无污染 |
项目 | 潜在生态风险等级 | ||||
---|---|---|---|---|---|
潜在风险 | 轻微风险 | 中等风险 | 较强风险 | 很强风险 | 极强风险 |
Ir, i | Ir, i ≤40 | 40<Ir, i≤80 | 80<Ir, i≤160 | 160<Ir, i≤320 | Ir,i>320 |
Ir | Ir≤150 | 150<Ir≤300 | 300<Ir≤600 | 600<Ir≤1200 | Ir>1200 |
Table 3 Grading standards of potential ecological hazard index
项目 | 潜在生态风险等级 | ||||
---|---|---|---|---|---|
潜在风险 | 轻微风险 | 中等风险 | 较强风险 | 很强风险 | 极强风险 |
Ir, i | Ir, i ≤40 | 40<Ir, i≤80 | 80<Ir, i≤160 | 160<Ir, i≤320 | Ir,i>320 |
Ir | Ir≤150 | 150<Ir≤300 | 300<Ir≤600 | 600<Ir≤1200 | Ir>1200 |
元素 | As | Cd | Cr | Cu | Hg | Ni | Pb | Zn |
---|---|---|---|---|---|---|---|---|
最大值 | 34.63 | 3.915 | 149.6 | 167.6 | 20.90 | 96.11 | 141.3 | 333.5 |
最小值 | 2.420 | 0.043 | 9.710 | 0.350 | 0.003 | 5.600 | 10.04 | 31.65 |
中位数 | 8.368 | 0.250 | 56.33 | 25.62 | 0.285 | 26.24 | 28.16 | 70.55 |
算数平均值 | 10.93 | 0.391 | 60.96 | 29.59 | 0.495 | 25.06 | 34.20 | 85.47 |
几何平均值 | 7.399 | 0.309 | 38.06 | 22.86 | 0.321 | 21.61 | 25.71 | 59.46 |
标准差 | 5.960 | 0.596 | 24.75 | 23.09 | 1.249 | 14.72 | 17.53 | 55.93 |
变异系数/% | 54.53 | 152.4 | 40.60 | 78.05 | 252.3 | 58.74 | 51.25 | 65.44 |
超背景值占比/% | 43.53 | 84.09 | 38.20 | 55.29 | 80.49 | 43.04 | 65.93 | 60.49 |
Table 4 Statistical results of heavy metal content in farmland soils in study areas from 2014 to 2023 mg·kg?1
元素 | As | Cd | Cr | Cu | Hg | Ni | Pb | Zn |
---|---|---|---|---|---|---|---|---|
最大值 | 34.63 | 3.915 | 149.6 | 167.6 | 20.90 | 96.11 | 141.3 | 333.5 |
最小值 | 2.420 | 0.043 | 9.710 | 0.350 | 0.003 | 5.600 | 10.04 | 31.65 |
中位数 | 8.368 | 0.250 | 56.33 | 25.62 | 0.285 | 26.24 | 28.16 | 70.55 |
算数平均值 | 10.93 | 0.391 | 60.96 | 29.59 | 0.495 | 25.06 | 34.20 | 85.47 |
几何平均值 | 7.399 | 0.309 | 38.06 | 22.86 | 0.321 | 21.61 | 25.71 | 59.46 |
标准差 | 5.960 | 0.596 | 24.75 | 23.09 | 1.249 | 14.72 | 17.53 | 55.93 |
变异系数/% | 54.53 | 152.4 | 40.60 | 78.05 | 252.3 | 58.74 | 51.25 | 65.44 |
超背景值占比/% | 43.53 | 84.09 | 38.20 | 55.29 | 80.49 | 43.04 | 65.93 | 60.49 |
成分 | 初始特征值 | 提取平方和载入 | 旋转平方和载入 | ||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
总计 | 方差/ % | 累计/ % | 总计 | 方差/ % | 累计/ % | 总计 | 方差/ % | 累计/ % | |||
1 | 2.80 | 35.0 | 35.0 | 2.80 | 35.0 | 35.0 | 2.58 | 32.28 | 32.3 | ||
2 | 1.76 | 22.0 | 57.0 | 1.76 | 22.0 | 57.0 | 1.97 | 24.6 | 56.9 | ||
3 | 1.23 | 15.3 | 72.30 | 1.23 | 15.3 | 72.3 | 1.23 | 15.4 | 72.3 | ||
4 | 0.784 | 9.80 | 82.1 | ||||||||
5 | 0.566 | 7.08 | 89.2 | ||||||||
6 | 0.337 | 4.21 | 93.4 | ||||||||
7 | 0.311 | 3.89 | 97.3 | ||||||||
8 | 0.219 | 2.74 | 100 |
Table 5 Interpretation of total variance of principal components in study areas
成分 | 初始特征值 | 提取平方和载入 | 旋转平方和载入 | ||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
总计 | 方差/ % | 累计/ % | 总计 | 方差/ % | 累计/ % | 总计 | 方差/ % | 累计/ % | |||
1 | 2.80 | 35.0 | 35.0 | 2.80 | 35.0 | 35.0 | 2.58 | 32.28 | 32.3 | ||
2 | 1.76 | 22.0 | 57.0 | 1.76 | 22.0 | 57.0 | 1.97 | 24.6 | 56.9 | ||
3 | 1.23 | 15.3 | 72.30 | 1.23 | 15.3 | 72.3 | 1.23 | 15.4 | 72.3 | ||
4 | 0.784 | 9.80 | 82.1 | ||||||||
5 | 0.566 | 7.08 | 89.2 | ||||||||
6 | 0.337 | 4.21 | 93.4 | ||||||||
7 | 0.311 | 3.89 | 97.3 | ||||||||
8 | 0.219 | 2.74 | 100 |
主成分 | As | Cd | Cr | Cu | Hg | Ni | Pb | Zn |
---|---|---|---|---|---|---|---|---|
1 | 0.061 | 0.805 | 0.442 | 0.692 | 0.041 | 0.418 | 0.772 | 0.836 |
2 | −0.178 | −0.325 | 0.720 | 0.295 | −0.360 | 0.791 | −0.426 | −0.283 |
3 | −0.755 | −0.130 | 0.141 | −0.168 | 0.750 | 0.123 | 0.083 | 0.071 |
Table 6 Principal component analysis of heavy metals in farmland soils in study areas
主成分 | As | Cd | Cr | Cu | Hg | Ni | Pb | Zn |
---|---|---|---|---|---|---|---|---|
1 | 0.061 | 0.805 | 0.442 | 0.692 | 0.041 | 0.418 | 0.772 | 0.836 |
2 | −0.178 | −0.325 | 0.720 | 0.295 | −0.360 | 0.791 | −0.426 | −0.283 |
3 | −0.755 | −0.130 | 0.141 | −0.168 | 0.750 | 0.123 | 0.083 | 0.071 |
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