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中国河北省农业平原的生态风险、输入通量和重金属来源。

Ecological Risk, Input Flux, and Source of Heavy Metals in the Agricultural Plain of Hebei Province, China.

机构信息

Institute of Geological Survey, Hebei GEO University, Shijiazhuang 050031, China.

Hebei Key Laboratory of Strategic Critical Mineral Resources, Hebei GEO University, Shijiazhuang 050031, China.

出版信息

Int J Environ Res Public Health. 2022 Feb 17;19(4):2288. doi: 10.3390/ijerph19042288.

Abstract

A large amount of heavy metal (HM) inputs exists in the farming areas of the Hebei plain of northern China. However, the potential ecological risk, source, and input flux of HMs in these areas have not been well-investigated. In this study, atmospheric deposition, fertilizer, irrigation water, and agricultural soil samples were collected from farming areas (~74,111 km) in Hebei Province, China. The HM index of geoaccumulation (I) and potential ecological risk index (RI) of soil was calculated for eight HMs. The source and input flux of each element were predicted using the input flux and principal component score-multiple linear regression (PCS-MLR) methods. The results showed that Cd and Hg increased I values, and the maximum levels of As (29.5 mg/kg), Cu (228.9 mg/kg), Cd (4.52 mg/kg), and Zn (879.0 mg/kg) were greater than the health risk screening values in the soil quality standard of China. The potential ecological risk factor (Er) of Cd demonstrated a moderately potential ecological risk, accounting for 67.72%. The distribution map showed that Cd was mainly concentrated in eastern area of Baoding (BD) in the study area. The result of the atmospheric dry and wet deposition contributed more to soil pollution than the usage of fertilizer or irrigation water by calculating the input flux. The order was Zn (94%) > Cu (92%) > Pb (89%) > Cr (86%) > Cd (72%) > Hg = Ni (71%) > As (59%). Principal component analysis (PCA) results showed that there were four sources of HMs in soil. Geological sources contribute to the accumulation of As, Cr, and Ni in soil. Cu and Pb in the soil were attributable to the input from vehicular emissions and irrigation water. Cd and Zn in the soil were attributable to the farming activity, whereas Hg originates from the combustion of coal. The results of PCS-MLR demonstrated that the contribution rate of As, Ni, and Cr in the study area was 30.06%, 71.86%, 57.71% for the first group (natural source); Cu, Pb and Zn were 71.78%, 63.59%, and 30.72% for the second group (vehicle emissions); Zn was 60.93% for the third group (fertilizer application and irrigation water); and Hg was 85.16%, for the fourth group (coal combustion). These factors provide a valuable reference for remediating HM pollution.

摘要

在中国河北省平原的农业区,存在大量的重金属(HM)输入。然而,这些地区的重金属潜在生态风险、来源和输入通量尚未得到充分研究。本研究采集了河北省农业区(约 74111km²)的大气沉降、肥料、灌溉水和农业土壤样品。采用地质累积指数(I)和土壤潜在生态风险指数(RI)对 8 种重金属进行了计算。利用输入通量和主成分得分-多元线性回归(PCS-MLR)方法预测了各元素的来源和输入通量。结果表明,Cd 和 Hg 增加了 I 值,土壤中 As(29.5mg/kg)、Cu(228.9mg/kg)、Cd(4.52mg/kg)和 Zn(879.0mg/kg)的最大含量均大于中国土壤质量标准中的健康风险筛选值。Cd 的潜在生态风险因子(Er)表现为中度潜在生态风险,占比 67.72%。分布图谱表明,Cd 主要集中在研究区保定东部地区。通过计算输入通量,大气干湿沉降对土壤污染的贡献大于肥料或灌溉水的使用。顺序为 Zn(94%)>Cu(92%)>Pb(89%)>Cr(86%)>Cd(72%)>Hg=Ni(71%)>As(59%)。主成分分析(PCA)结果表明,土壤中存在 4 种重金属来源。地质来源导致土壤中 As、Cr 和 Ni 的积累。土壤中 Cu 和 Pb 来自于机动车排放和灌溉水。土壤中 Cd 和 Zn 来自于农业活动,而 Hg 则来源于煤炭燃烧。PCS-MLR 结果表明,研究区 As、Ni 和 Cr 的贡献率为 30.06%、71.86%、57.71%,第一组为自然源;Cu、Pb 和 Zn 的贡献率为 71.78%、63.59%和 30.72%,第二组为机动车排放源;Zn 的贡献率为 60.93%,第三组为肥料应用和灌溉水源;Hg 的贡献率为 85.16%,第四组为煤炭燃烧源。这些因素为修复重金属污染提供了有价值的参考。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/fb5e/8872327/f1c096639679/ijerph-19-02288-g001.jpg

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