CAS Key Laboratory of Soil Environment and Pollution Remediation, Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China.
State Environmental Protection Key Laboratory of Soil Environmental Management and Pollution Control, Nanjing Institute of Environmental Sciences, Ministry of Ecology and Environment of China, Nanjing 210042, China.
Sci Total Environ. 2022 May 1;819:153078. doi: 10.1016/j.scitotenv.2022.153078. Epub 2022 Jan 14.
Soil environmental capacity (EC) of heavy metals (HMs) can be used as an index to evaluate the pollution status of HMs and to provide basic data for HM remediation. However, the commonly used soil EC for HMs usually are prone to bias due to the lack of local background values (BVs) and the consideration of the contribution from various HM sources. Here, a modified method was proposed to estimate the soil EC by integrating the establishment of local BVs and the quantitative evaluation of contributions from HM sources in an intensive agricultural area of Shouguang city, China. The local BVs of HMs were established using the relative cumulative frequency distribution method. The source-specific EC was quantified based on the local BVs and the contributions of HM sources identified by receptor model and variable importance analysis. Results showed that the average BV values of As, Cd, Cr, Cu, Hg, Ni, Pb, and Zn were 7.67, 0.10, 62.84, 21.17, 0.031, 28.38, 19.25, and 59.60 mg kg, respectively, in the study area. The source-specific EC of Cd, Cu, Hg, and Zn were higher than their current EC, indicating an underestimation of soil capacity of HMs by the traditional method. The EC of HMs in these soils was generally medium indicated by their comprehensive EC index (PI) (PI >0.7), suggesting a low risk level of the targeted HMs. According to indexes such as the individual metal index (Pi) and enrichment factor (EF), special attention should be paid to Cd and Zn due to their low capacity (Pi <0.7) and high accumulation (EF > 2) in some points across this area. Altogether, our findings suggested that the modified method had a better capability for evaluating and predicting the enrichment status of soil HMs, which can be helpful for formulating the targeted measures to control HM pollution in such intensive agricultural areas.
土壤重金属环境容量(EC)可用于评估重金属污染状况,并为重金属修复提供基础数据。然而,常用的土壤重金属 EC 通常由于缺乏本地背景值(BV)和考虑各种重金属源的贡献而存在偏差。本研究提出了一种改进的方法,通过在山东省寿光市一个集约化农业区建立本地背景值和定量评估重金属源的贡献,来估算土壤 EC。利用相对累积频率分布法建立了重金属的本地背景值。基于本地背景值和受体模型和变量重要性分析确定的重金属源贡献,量化了特定源的 EC。结果表明,研究区 As、Cd、Cr、Cu、Hg、Ni、Pb 和 Zn 的平均 BV 值分别为 7.67、0.10、62.84、21.17、0.031、28.38、19.25 和 59.60mgkg-1。Cd、Cu、Hg 和 Zn 的特定源 EC 高于其当前 EC,表明传统方法低估了土壤重金属的容量。根据综合 EC 指数(PI)等指标(PI >0.7),这些土壤中重金属的 EC 普遍较高,表明目标重金属的风险水平较低。根据个别金属指数(Pi)和富集因子(EF)等指标,由于某些点的容量(Pi <0.7)和积累(EF >2)较低,应特别注意 Cd 和 Zn。总之,本研究结果表明,改进的方法在评估和预测土壤重金属的富集状况方面具有更好的能力,有助于制定针对这种集约化农业区重金属污染的控制措施。