中国农业科技导报 ›› 2022, Vol. 24 ›› Issue (8): 144-153.DOI: 10.13304/j.nykjdb.2021.0890
• 生物制造 资源生态 • 上一篇
柴冠群1(), 刘桂华1, 周玮1, 张秀锦2, 李龙品3, 范成五1(
)
收稿日期:
2021-10-19
接受日期:
2022-03-03
出版日期:
2022-08-15
发布日期:
2022-08-22
通讯作者:
范成五
作者简介:
柴冠群 E-mail:chaiguanqun@163.com;
基金资助:
Guanqun CHAI1(), Guihua LIU1, Wei ZHOU1, Xiujin ZHANG2, Longpin LI3, Chengwu FAN1(
)
Received:
2021-10-19
Accepted:
2022-03-03
Online:
2022-08-15
Published:
2022-08-22
Contact:
Chengwu FAN
摘要:
为评价贵州乌蒙山区设施蔬菜基地土壤重金属污染程度和生态风险,选取研究区种植面积较大的4个设施蔬菜基地为研究对象,共采集144个大棚土样和68个露天土样,测定土壤pH及Cd、Hg、As、Pb、Cr、Cu、Zn和Ni含量,分析研究区设施菜地土壤重金属的污染程度和生态风险,并运用多元统计(简单相关分析和主成分分析)与剖面分异法综合分析研究区设施菜地耕层土壤重金属污染的主要来源。结果表明,研究区设施蔬菜种植会加速土壤酸化,与露天菜地土壤相比,设施菜地耕层土壤pH降低了0.24。研究区设施菜地与露天菜地耕作层土壤重度污染样点占比分别为53.57%与42.86%,中等以上生态风险样点占比分别为82.14%与57.14%,土壤Cd是研究区最主要的污染因子与生态风险因子。研究区设施菜地耕层土壤中As、Pb、Cr、Cu、Ni主要来源于成土母质风化,Cd、Hg、Zn主要来源于成土母质风化与农业投入品。综上所述,研究区设施菜地受重金属污染程度高于露天菜地,尤其应控制外源Cd、Hg、Zn的投入,并加强农产品重金属监测,为贵州乌蒙山区设施农产品安全生产提供了理论支撑。
中图分类号:
柴冠群, 刘桂华, 周玮, 张秀锦, 李龙品, 范成五. 贵州乌蒙山区设施土壤重金属污染风险评估与来源解析[J]. 中国农业科技导报, 2022, 24(8): 144-153.
Guanqun CHAI, Guihua LIU, Wei ZHOU, Xiujin ZHANG, Longpin LI, Chengwu FAN. Evaluation of Pollution Risk and Source Analysis of Heavy Metals in Greenhouse Soils in Wumeng Mountain Area, Guizhou Province[J]. Journal of Agricultural Science and Technology, 2022, 24(8): 144-153.
土地利用方式Land use type | 土层 Soil layer/cm | 统计项 Statistical item | pH | Cd/ (mg·kg-1) | Hg/ (mg·kg-1) | As/ (mg·kg-1) | Pb/ (mg·kg-1) | Cr/ (mg·kg-1) | Cu/ (mg·kg-1) | Zn/ (mg·kg-1) | Ni/ (mg·kg-1) |
---|---|---|---|---|---|---|---|---|---|---|---|
设施菜地 Green house | 0—20 | 平均 Mean | 5.92 | 0.94 | 0.23 | 25.88 | 119.15 | 189.16 | 121.52 | 542.41 | 85.08 |
标准差 Standard deviation | 0.64 | 0.61 | 0.12 | 17.03 | 103.54 | 51.75 | 74.46 | 558.78 | 26.64 | ||
最大值 Maximum | 7.43 | 2.28 | 0.73 | 64.10 | 431.85 | 279.60 | 261.95 | 1 941.35 | 126.75 | ||
最小值 Minimum | 5.44 | 0.21 | 0.13 | 2.97 | 28.55 | 119.55 | 32.60 | 136.05 | 42.80 | ||
20—40 | 平均 Mean | 6.35 | 0.85 | 0.25 | 26.09 | 118.72 | 185.24 | 118.08 | 490.88 | 85.04 | |
标准差 Standard deviation | 0.69 | 0.62 | 0.11 | 17.35 | 141.92 | 43.59 | 73.38 | 515.99 | 28.49 | ||
最大值 Maximum | 7.49 | 2.25 | 0.56 | 64.20 | 413.55 | 260.05 | 285.90 | 1 802.05 | 140.05 | ||
最小值 Minimum | 4.92 | 0.16 | 0.13 | 2.40 | 24.95 | 114.60 | 29.90 | 103.85 | 39.00 | ||
露天菜地 Open field | 0—20 | 平均 Mean | 6.16 | 0.81 | 0.22 | 21.51 | 142.83 | 200.04 | 108.58 | 551.76 | 87.54 |
标准差 Standard deviation | 0.92 | 0.71 | 0.11 | 20.89 | 187.45 | 47.11 | 76.57 | 679.14 | 31.13 | ||
最大值 Maximum | 7.45 | 1.84 | 0.36 | 53.00 | 472.20 | 265.65 | 254.10 | 1 728.90 | 127.10 | ||
最小值 Minimum | 5.19 | 0.17 | 0.10 | 3.23 | 28.80 | 134.05 | 34.95 | 110.00 | 43.95 | ||
20—40 | 平均 Mean | 6.37 | 0.80 | 0.30 | 28.06 | 158.06 | 186.22 | 112.34 | 589.97 | 84.32 | |
标准差 Standard deviation | 0.89 | 0.51 | 0.14 | 21.79 | 172.52 | 51.37 | 94.78 | 571.84 | 33.35 | ||
最大值 Maximum | 7.37 | 1.41 | 0.47 | 53.80 | 393.60 | 246.10 | 250.75 | 1 224.65 | 122.35 | ||
最小值 Minimum | 5.01 | 0.23 | 0.10 | 2.86 | 25.80 | 133.80 | 27.55 | 128.30 | 46.75 |
表1 土壤pH与重金属含量特征
Table 1 pH value and heavy metal concentration in soils
土地利用方式Land use type | 土层 Soil layer/cm | 统计项 Statistical item | pH | Cd/ (mg·kg-1) | Hg/ (mg·kg-1) | As/ (mg·kg-1) | Pb/ (mg·kg-1) | Cr/ (mg·kg-1) | Cu/ (mg·kg-1) | Zn/ (mg·kg-1) | Ni/ (mg·kg-1) |
---|---|---|---|---|---|---|---|---|---|---|---|
设施菜地 Green house | 0—20 | 平均 Mean | 5.92 | 0.94 | 0.23 | 25.88 | 119.15 | 189.16 | 121.52 | 542.41 | 85.08 |
标准差 Standard deviation | 0.64 | 0.61 | 0.12 | 17.03 | 103.54 | 51.75 | 74.46 | 558.78 | 26.64 | ||
最大值 Maximum | 7.43 | 2.28 | 0.73 | 64.10 | 431.85 | 279.60 | 261.95 | 1 941.35 | 126.75 | ||
最小值 Minimum | 5.44 | 0.21 | 0.13 | 2.97 | 28.55 | 119.55 | 32.60 | 136.05 | 42.80 | ||
20—40 | 平均 Mean | 6.35 | 0.85 | 0.25 | 26.09 | 118.72 | 185.24 | 118.08 | 490.88 | 85.04 | |
标准差 Standard deviation | 0.69 | 0.62 | 0.11 | 17.35 | 141.92 | 43.59 | 73.38 | 515.99 | 28.49 | ||
最大值 Maximum | 7.49 | 2.25 | 0.56 | 64.20 | 413.55 | 260.05 | 285.90 | 1 802.05 | 140.05 | ||
最小值 Minimum | 4.92 | 0.16 | 0.13 | 2.40 | 24.95 | 114.60 | 29.90 | 103.85 | 39.00 | ||
露天菜地 Open field | 0—20 | 平均 Mean | 6.16 | 0.81 | 0.22 | 21.51 | 142.83 | 200.04 | 108.58 | 551.76 | 87.54 |
标准差 Standard deviation | 0.92 | 0.71 | 0.11 | 20.89 | 187.45 | 47.11 | 76.57 | 679.14 | 31.13 | ||
最大值 Maximum | 7.45 | 1.84 | 0.36 | 53.00 | 472.20 | 265.65 | 254.10 | 1 728.90 | 127.10 | ||
最小值 Minimum | 5.19 | 0.17 | 0.10 | 3.23 | 28.80 | 134.05 | 34.95 | 110.00 | 43.95 | ||
20—40 | 平均 Mean | 6.37 | 0.80 | 0.30 | 28.06 | 158.06 | 186.22 | 112.34 | 589.97 | 84.32 | |
标准差 Standard deviation | 0.89 | 0.51 | 0.14 | 21.79 | 172.52 | 51.37 | 94.78 | 571.84 | 33.35 | ||
最大值 Maximum | 7.37 | 1.41 | 0.47 | 53.80 | 393.60 | 246.10 | 250.75 | 1 224.65 | 122.35 | ||
最小值 Minimum | 5.01 | 0.23 | 0.10 | 2.86 | 25.80 | 133.80 | 27.55 | 128.30 | 46.75 |
重金属 Heavy metal | 土地利用方式 Land use type | 占比Proportion/% | ||||
---|---|---|---|---|---|---|
清洁 Clean | 尚清洁 Approaching pollution | 轻度污染 Slight pollution | 中度污染 Medium pollution | 重度污染 Heavy pollution | ||
Cd | 设施菜地 Green house | 3.57 | 10.72 | 7.14 | 17.86 | 60.71 |
露天菜地Open field | 28.57 | 0.00 | 28.57 | 0.00 | 42.86 | |
Hg | 设施菜地 Green house | 28.57 | 28.57 | 32.14 | 3.58 | 7.14 |
露天菜地 Open field | 42.86 | 14.28 | 42.86 | 0.00 | 0.00 | |
As | 设施菜地 Green house | 46.43 | 3.57 | 46.43 | 3.57 | 0.00 |
露天菜地 Open field | 57.14 | 0.00 | 42.86 | 0.00 | 0.00 | |
Pb | 设施菜地 Green house | 28.57 | 42.86 | 0.00 | 0.00 | 28.57 |
露天菜地 Open field | 57.14 | 0.00 | 14.29 | 0.00 | 28.57 | |
Cr | 设施菜地 Green house | 0.00 | 35.71 | 64.29 | 0.00 | 0.00 |
露天菜地 Open field | 0.00 | 42.86 | 57.14 | 0.00 | 0.00 | |
Cu | 设施菜地 Green house | 7.14 | 35.72 | 17.86 | 28.57 | 10.71 |
露天菜地 Open field | 14.29 | 57.14 | 0.00 | 14.28 | 14.29 | |
Zn | 设施菜地 Green house | 25.00 | 17.86 | 28.57 | 0.00 | 28.57 |
露天菜地 Open field | 42.86 | 28.57 | 0.00 | 0.00 | 28.57 | |
Ni | 设施菜地 Green house | 0.00 | 0.00 | 57.15 | 35.71 | 7.14 |
露天菜地 Open field | 0.00 | 0.00 | 42.86 | 57.14 | 0.00 | |
N | 设施菜地 Green house | 0.00 | 0.00 | 21.43 | 25.00 | 53.57 |
露天菜地 Open field | 0.00 | 0.00 | 42.86 | 14.28 | 42.86 |
表2 不同污染级别样点占比
Table 2 Proportion of different pollution level samples
重金属 Heavy metal | 土地利用方式 Land use type | 占比Proportion/% | ||||
---|---|---|---|---|---|---|
清洁 Clean | 尚清洁 Approaching pollution | 轻度污染 Slight pollution | 中度污染 Medium pollution | 重度污染 Heavy pollution | ||
Cd | 设施菜地 Green house | 3.57 | 10.72 | 7.14 | 17.86 | 60.71 |
露天菜地Open field | 28.57 | 0.00 | 28.57 | 0.00 | 42.86 | |
Hg | 设施菜地 Green house | 28.57 | 28.57 | 32.14 | 3.58 | 7.14 |
露天菜地 Open field | 42.86 | 14.28 | 42.86 | 0.00 | 0.00 | |
As | 设施菜地 Green house | 46.43 | 3.57 | 46.43 | 3.57 | 0.00 |
露天菜地 Open field | 57.14 | 0.00 | 42.86 | 0.00 | 0.00 | |
Pb | 设施菜地 Green house | 28.57 | 42.86 | 0.00 | 0.00 | 28.57 |
露天菜地 Open field | 57.14 | 0.00 | 14.29 | 0.00 | 28.57 | |
Cr | 设施菜地 Green house | 0.00 | 35.71 | 64.29 | 0.00 | 0.00 |
露天菜地 Open field | 0.00 | 42.86 | 57.14 | 0.00 | 0.00 | |
Cu | 设施菜地 Green house | 7.14 | 35.72 | 17.86 | 28.57 | 10.71 |
露天菜地 Open field | 14.29 | 57.14 | 0.00 | 14.28 | 14.29 | |
Zn | 设施菜地 Green house | 25.00 | 17.86 | 28.57 | 0.00 | 28.57 |
露天菜地 Open field | 42.86 | 28.57 | 0.00 | 0.00 | 28.57 | |
Ni | 设施菜地 Green house | 0.00 | 0.00 | 57.15 | 35.71 | 7.14 |
露天菜地 Open field | 0.00 | 0.00 | 42.86 | 57.14 | 0.00 | |
N | 设施菜地 Green house | 0.00 | 0.00 | 21.43 | 25.00 | 53.57 |
露天菜地 Open field | 0.00 | 0.00 | 42.86 | 14.28 | 42.86 |
重金属 Heavy metal | 土地利用方式 Land use type | 占比Proportion/% | ||||
---|---|---|---|---|---|---|
轻微风险 Slight risk | 中等风险 Medium risk | 较强风险 Relatively strong risk | 很强风险 Strong risk | 极强风险 Extremely strong risk | ||
Cd | 设施菜地 Green house | 17.85 | 17.86 | 42.86 | 21.43 | 0.00 |
露天菜地 Open field | 57.14 | 0.00 | 28.57 | 14.29 | 0.00 | |
Hg | 设施菜地 Green house | 57.15 | 32.14 | 7.14 | 3.57 | 0.00 |
露天菜地 Open field | 57.14 | 42.86 | 0.00 | 0.00 | 0.00 | |
As | 设施菜地 Green house | 100.00 | 0.00 | 0.00 | 0.00 | 0.00 |
露天菜地 Open field | 100.00 | 0.00 | 0.00 | 0.00 | 0.00 | |
Pb | 设施菜地 Green house | 89.29 | 10.71 | 0.00 | 0.00 | 0.00 |
露天菜地 Open field | 85.71 | 14.29 | 0.00 | 0.00 | 0.00 | |
Cr | 设施菜地 Green house | 100.00 | 0.00 | 0.00 | 0.00 | 0.00 |
露天菜地 Open field | 100.00 | 0.00 | 0.00 | 0.00 | 0.00 | |
Cu | 设施菜地 Green house | 100.00 | 0.00 | 0.00 | 0.00 | 0.00 |
露天菜地 Open field | 100.00 | 0.00 | 0.00 | 0.00 | 0.00 | |
Zn | 设施菜地 Green house | 100.00 | 0.00 | 0.00 | 0.00 | 0.00 |
露天菜地 Open field | 100.00 | 0.00 | 0.00 | 0.00 | 0.00 | |
Ni | 设施菜地 Green house | 100.00 | 0.00 | 0.00 | 0.00 | 0.00 |
露天菜地 Open field | 100.00 | 0.00 | 0.00 | 0.00 | 0.00 | |
RI | 设施菜地 Green house | 17.86 | 50.00 | 32.14 | 0.00 | 0.00 |
露天菜地 Open field | 42.86 | 28.57 | 28.57 | 0.00 | 0.00 |
表3 不同生态风险级别样点占比
Table 3 Proportion of different ecological risk level samples
重金属 Heavy metal | 土地利用方式 Land use type | 占比Proportion/% | ||||
---|---|---|---|---|---|---|
轻微风险 Slight risk | 中等风险 Medium risk | 较强风险 Relatively strong risk | 很强风险 Strong risk | 极强风险 Extremely strong risk | ||
Cd | 设施菜地 Green house | 17.85 | 17.86 | 42.86 | 21.43 | 0.00 |
露天菜地 Open field | 57.14 | 0.00 | 28.57 | 14.29 | 0.00 | |
Hg | 设施菜地 Green house | 57.15 | 32.14 | 7.14 | 3.57 | 0.00 |
露天菜地 Open field | 57.14 | 42.86 | 0.00 | 0.00 | 0.00 | |
As | 设施菜地 Green house | 100.00 | 0.00 | 0.00 | 0.00 | 0.00 |
露天菜地 Open field | 100.00 | 0.00 | 0.00 | 0.00 | 0.00 | |
Pb | 设施菜地 Green house | 89.29 | 10.71 | 0.00 | 0.00 | 0.00 |
露天菜地 Open field | 85.71 | 14.29 | 0.00 | 0.00 | 0.00 | |
Cr | 设施菜地 Green house | 100.00 | 0.00 | 0.00 | 0.00 | 0.00 |
露天菜地 Open field | 100.00 | 0.00 | 0.00 | 0.00 | 0.00 | |
Cu | 设施菜地 Green house | 100.00 | 0.00 | 0.00 | 0.00 | 0.00 |
露天菜地 Open field | 100.00 | 0.00 | 0.00 | 0.00 | 0.00 | |
Zn | 设施菜地 Green house | 100.00 | 0.00 | 0.00 | 0.00 | 0.00 |
露天菜地 Open field | 100.00 | 0.00 | 0.00 | 0.00 | 0.00 | |
Ni | 设施菜地 Green house | 100.00 | 0.00 | 0.00 | 0.00 | 0.00 |
露天菜地 Open field | 100.00 | 0.00 | 0.00 | 0.00 | 0.00 | |
RI | 设施菜地 Green house | 17.86 | 50.00 | 32.14 | 0.00 | 0.00 |
露天菜地 Open field | 42.86 | 28.57 | 28.57 | 0.00 | 0.00 |
重金属 Heavy metal | 土地利用方式 Land use type | Pi | E | PN | RI |
---|---|---|---|---|---|
Cd | 设施菜地 Green house | 3.65±2.11 | 109.45±63.42 | 3.58±1.83 | 202.62±100.12 |
露天菜地 Open field | 2.64±2.24 | 79.34±67.12 | 3.25±2.07 | 155.62±104.36 | |
Hg | 设施菜地 Green house | 1.22±0.59 | 48.75±44.31 | ||
露天菜地 Open field | 0.82±0.41 | 32.87±16.31 | |||
As | 设施菜地 Green house | 0.91±0.59 | 9.07±5.88 | ||
露天菜地 Open field | 0.77±0.67 | 7.66±6.71 | |||
Pb | 设施菜地 Green house | 2.39±2.85 | 11.91±14.27 | ||
露天菜地 Open field | 2.86±3.47 | 14.28±17.35 | |||
Cr | 设施菜地 Green house | 1.12±0.32 | 2.25±0.64 | ||
露天菜地 Open field | 1.12±0.21 | 2.24±0.43 | |||
Cu | 设施菜地 Green house | 1.80±1.27 | 9.02±6.36 | ||
露天菜地 Open field | 1.42±0.94 | 7.12±4.71 | |||
Zn | 设施菜地 Green house | 2.61±2.84 | 2.61±2.84 | ||
露天菜地 Open field | 2.67±3.20 | 2.67±3.20 | |||
Ni | 设施菜地 Green house | 1.91±0.66 | 9.56±3.31 | ||
露天菜地 Open field | 1.98±0.54 | 9.43±2.68 |
表4 耕层土壤重金属污染程度与生态风险程度
Table 4 Heavy metal pollution degree and ecological risk degree of topsoil
重金属 Heavy metal | 土地利用方式 Land use type | Pi | E | PN | RI |
---|---|---|---|---|---|
Cd | 设施菜地 Green house | 3.65±2.11 | 109.45±63.42 | 3.58±1.83 | 202.62±100.12 |
露天菜地 Open field | 2.64±2.24 | 79.34±67.12 | 3.25±2.07 | 155.62±104.36 | |
Hg | 设施菜地 Green house | 1.22±0.59 | 48.75±44.31 | ||
露天菜地 Open field | 0.82±0.41 | 32.87±16.31 | |||
As | 设施菜地 Green house | 0.91±0.59 | 9.07±5.88 | ||
露天菜地 Open field | 0.77±0.67 | 7.66±6.71 | |||
Pb | 设施菜地 Green house | 2.39±2.85 | 11.91±14.27 | ||
露天菜地 Open field | 2.86±3.47 | 14.28±17.35 | |||
Cr | 设施菜地 Green house | 1.12±0.32 | 2.25±0.64 | ||
露天菜地 Open field | 1.12±0.21 | 2.24±0.43 | |||
Cu | 设施菜地 Green house | 1.80±1.27 | 9.02±6.36 | ||
露天菜地 Open field | 1.42±0.94 | 7.12±4.71 | |||
Zn | 设施菜地 Green house | 2.61±2.84 | 2.61±2.84 | ||
露天菜地 Open field | 2.67±3.20 | 2.67±3.20 | |||
Ni | 设施菜地 Green house | 1.91±0.66 | 9.56±3.31 | ||
露天菜地 Open field | 1.98±0.54 | 9.43±2.68 |
土壤 Soil | 指标 Index | 耕作层 Topsoil | 心土层 Subsoil | |||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Cd | Hg | As | Pb | Cr | Cu | Zn | Ni | Cd | Hg | As | Pb | Cr | Cu | Zn | ||
耕作层 Topsoil | Hg | 0.058 | ||||||||||||||
As | 0.752** | 0.098 | ||||||||||||||
Pb | 0.429* | 0.217 | 0.750** | |||||||||||||
Cr | -0.337 | 0.083 | -0.601** | -0.652** | ||||||||||||
Cu | 0.194 | -0.186 | -0.080 | -0.677** | 0.447* | |||||||||||
Zn | 0.523** | 0.233 | 0.832** | 0.972** | -0.607** | -0.527** | ||||||||||
Ni | -0.017 | -0.223 | -0.429* | -0.818** | 0.723** | 0.817** | -0.728** | |||||||||
心土层 Subsoil | Cd | 0.944** | 0.396* | 0.682** | 0.338 | -0.279 | 0.182 | 0.399* | 0.011 | |||||||
Hg | 0.632** | 0.908** | 0.781** | 0.762** | -0.469* | -0.297 | 0.845** | -0.536** | 0.480* | |||||||
As | 0.750** | 0.146 | 0.986** | 0.757** | -0.605** | -0.095 | 0.844** | -0.441* | 0.672** | 0.781** | ||||||
Pb | 0.424* | 0.195 | 0.726** | 0.988** | -0.670** | -0.690** | 0.946** | -0.836** | 0.347 | 0.746** | 0.731** | |||||
Cr | -0.392* | -0.049 | -0.745** | -0.715** | 0.920** | 0.369 | -0.709** | 0.700** | -0.342 | -0.559** | -0.755** | -0.708** | ||||
Cu | 0.222 | -0.227 | -0.088 | -0.683** | 0.442* | 0.971** | -0.541** | 0.787** | 0.228 | -0.286 | -0.107 | -0.686** | 0.409* | |||
Zn | 0.524** | 0.203 | 0.788** | 0.973** | -0.651** | -0.585** | 0.970** | -0.772** | 0.423* | 0.821** | 0.801** | 0.983** | -0.698** | -0.579** | ||
Ni | -0.025 | -0.315 | -0.493** | -0.811** | 0.702** | 0.716** | -0.755** | 0.903** | 0.026 | -0.526** | -0.509** | -0.801** | 0.771** | 0.769** | -0.747** |
表5 设施菜地耕作层和心土层土壤重金属相关性
Table 5 Correlation of heavy metals between topsoil and subsoil of greenhouse
土壤 Soil | 指标 Index | 耕作层 Topsoil | 心土层 Subsoil | |||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Cd | Hg | As | Pb | Cr | Cu | Zn | Ni | Cd | Hg | As | Pb | Cr | Cu | Zn | ||
耕作层 Topsoil | Hg | 0.058 | ||||||||||||||
As | 0.752** | 0.098 | ||||||||||||||
Pb | 0.429* | 0.217 | 0.750** | |||||||||||||
Cr | -0.337 | 0.083 | -0.601** | -0.652** | ||||||||||||
Cu | 0.194 | -0.186 | -0.080 | -0.677** | 0.447* | |||||||||||
Zn | 0.523** | 0.233 | 0.832** | 0.972** | -0.607** | -0.527** | ||||||||||
Ni | -0.017 | -0.223 | -0.429* | -0.818** | 0.723** | 0.817** | -0.728** | |||||||||
心土层 Subsoil | Cd | 0.944** | 0.396* | 0.682** | 0.338 | -0.279 | 0.182 | 0.399* | 0.011 | |||||||
Hg | 0.632** | 0.908** | 0.781** | 0.762** | -0.469* | -0.297 | 0.845** | -0.536** | 0.480* | |||||||
As | 0.750** | 0.146 | 0.986** | 0.757** | -0.605** | -0.095 | 0.844** | -0.441* | 0.672** | 0.781** | ||||||
Pb | 0.424* | 0.195 | 0.726** | 0.988** | -0.670** | -0.690** | 0.946** | -0.836** | 0.347 | 0.746** | 0.731** | |||||
Cr | -0.392* | -0.049 | -0.745** | -0.715** | 0.920** | 0.369 | -0.709** | 0.700** | -0.342 | -0.559** | -0.755** | -0.708** | ||||
Cu | 0.222 | -0.227 | -0.088 | -0.683** | 0.442* | 0.971** | -0.541** | 0.787** | 0.228 | -0.286 | -0.107 | -0.686** | 0.409* | |||
Zn | 0.524** | 0.203 | 0.788** | 0.973** | -0.651** | -0.585** | 0.970** | -0.772** | 0.423* | 0.821** | 0.801** | 0.983** | -0.698** | -0.579** | ||
Ni | -0.025 | -0.315 | -0.493** | -0.811** | 0.702** | 0.716** | -0.755** | 0.903** | 0.026 | -0.526** | -0.509** | -0.801** | 0.771** | 0.769** | -0.747** |
土壤 Soil | 重金属 Heavy metal | 第1主成分 Principal component 1 | 第2主成分 Principal component 2 |
---|---|---|---|
耕作层 Topsoil | Cd | 0.132 | 0.935 |
Hg | -0.311 | 0.709 | |
As | -0.320 | 0.900 | |
Pb | -0.808 | 0.543 | |
Cr | 0.689 | -0.380 | |
Cu | 0.920 | 0.145 | |
Zn | -0.668 | 0.697 | |
Ni | 0.941 | -0.167 | |
特征值 Characteristic value | 10.161 | 3.360 | |
方差贡献率 Variance contribution rate/% | 63.509 | 21.001 | |
累积贡献率 Accumulating contribution rate/% | 63.509 | 84.511 |
表6 设施菜地耕作层土壤重金属含量的主成分分析
Table 6 Principal component analysis of heavy metal content in soils of greenhouse
土壤 Soil | 重金属 Heavy metal | 第1主成分 Principal component 1 | 第2主成分 Principal component 2 |
---|---|---|---|
耕作层 Topsoil | Cd | 0.132 | 0.935 |
Hg | -0.311 | 0.709 | |
As | -0.320 | 0.900 | |
Pb | -0.808 | 0.543 | |
Cr | 0.689 | -0.380 | |
Cu | 0.920 | 0.145 | |
Zn | -0.668 | 0.697 | |
Ni | 0.941 | -0.167 | |
特征值 Characteristic value | 10.161 | 3.360 | |
方差贡献率 Variance contribution rate/% | 63.509 | 21.001 | |
累积贡献率 Accumulating contribution rate/% | 63.509 | 84.511 |
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