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[Ecological Risk Assessment of Heavy Metals at Township Scale in the High Background of Heavy Metals, Southwestern, China].
Huan Jing Ke Xue. 2020 Sep 08; 41(9):4197-4209.HJ

Abstract

Heavy metals (HMs) are naturally occurring elements that have high natural background levels in the environment. Therefore, it is important to conduct ecological risk assessment and identify potential sources of HMs. In the past, studies were conducted at the regional scale. The accuracy of those studies could not meet the needs of spatial planning and natural resource management. Therefore, it is necessary to conduct ecological risk assessment at the township scale. In this study, 1092 soil samples (from 0-20 cm depth) were collected in the town of Reshui, an area with high background levels of soil HMs with the parent material of carbonatite, which is commonly found in Southwest China. The town of Reshui is a multi-ecological risk superimposed area where the ecological risk is high. In this study, concentrations of HMs (Cd, Cr, As, Hg, Pb, Cu, Zn, and Ni) in the topsoil were analyzed, and statistical analysis (SA), geographic information system (GIS) modeling, and positive matrix factorization (PMF) analysis were performed. The geoaccumulation index (Igeo) and potential ecological risk index (PERI) were applied for the ecological risk assessment and quantification of the sources of the soil HMs. The mean values of HM concentrations in the topsoil were 18.1, 1.18, 174.1, 202.2, 0.09, 71.1, 34.9, and 167.2 mg ·kg-1for As, Cd, Cr, Cu, Hg, Ni, Pb, and Zn, respectively, which were considerably higher than the average background value (ABV) in soils in Yunnan Province except for As and Pb. The average concentrations of Cd, Cr, Cu, and Ni exceeded the screening values specified in the soil contamination risk in agricultural land (GB 15618-2018) by 5.82, 1.16, 4.04, and 1.02 times, respectively. The Igeo value shows that the major pollutant is Cu in the surface soil of the study area, followed by Cr, and Cd. Speciation analysis of HMs indicates that HMs (Cr, As, Pb, Cu, Zn, and Ni) mainly exist in the residual form, mostly from the geological background with low bioavailability. The potential effective components of Hg have higher levels, but the total amount of Hg and its pollution risk are lower. Cd has a high bioavailability ratio, is easy to enter the soil solution and be absorbed by crops, and is the HM with the highest pollution risk in the study area. The PERI shows that the proportions of low ecological risk, moderate risk, and high risk soil samples are 44.23%, 54.40%, and 1.37% of the total number of samples, respectively. Hg and Cd were the major sources of risk because of their high toxicity coefficient. The PMF analysis indicates that there are four major sources of HMs in the study area: human activity, natural sources, coal mining and traffic emissions, and agricultural sources with the risk contribution ratios of 9.29%, 53.67%, 11.23%, and 25.81%, respectively. The PMF analysis effectively quantified the ecological risk from these sources, providing a reference for further pollution control and prevention measures.

Authors+Show Affiliations

Research Center of Geochemical Survey and Assessment on Land Quality, China Geological Survey, Langfang 065000, China. Institute of Geophysical and Geochemical Exploration, Chinese Academy of Geological Sciences, Langfang, 065000, China. Key Laboratory of Geochemical Cycling of Carbon and Mercury in the Earth's Critical Zone, China Geological Survey, Langfang 065000, China. College of Earth Sciences, Chengdu University of Technology, Chengdu 610059, China.Research Center of Geochemical Survey and Assessment on Land Quality, China Geological Survey, Langfang 065000, China. Institute of Geophysical and Geochemical Exploration, Chinese Academy of Geological Sciences, Langfang, 065000, China. Key Laboratory of Geochemical Cycling of Carbon and Mercury in the Earth's Critical Zone, China Geological Survey, Langfang 065000, China.Research Center of Geochemical Survey and Assessment on Land Quality, China Geological Survey, Langfang 065000, China. Institute of Geophysical and Geochemical Exploration, Chinese Academy of Geological Sciences, Langfang, 065000, China. Key Laboratory of Geochemical Cycling of Carbon and Mercury in the Earth's Critical Zone, China Geological Survey, Langfang 065000, China.Research Center of Geochemical Survey and Assessment on Land Quality, China Geological Survey, Langfang 065000, China. Institute of Geophysical and Geochemical Exploration, Chinese Academy of Geological Sciences, Langfang, 065000, China. Key Laboratory of Geochemical Cycling of Carbon and Mercury in the Earth's Critical Zone, China Geological Survey, Langfang 065000, China.Research Center of Geochemical Survey and Assessment on Land Quality, China Geological Survey, Langfang 065000, China. Institute of Geophysical and Geochemical Exploration, Chinese Academy of Geological Sciences, Langfang, 065000, China. Key Laboratory of Geochemical Cycling of Carbon and Mercury in the Earth's Critical Zone, China Geological Survey, Langfang 065000, China.Research Center of Geochemical Survey and Assessment on Land Quality, China Geological Survey, Langfang 065000, China. Institute of Geophysical and Geochemical Exploration, Chinese Academy of Geological Sciences, Langfang, 065000, China. Key Laboratory of Geochemical Cycling of Carbon and Mercury in the Earth's Critical Zone, China Geological Survey, Langfang 065000, China.Yunnan Institute of Geological Survey, Kunming 650216, China.College of Earth Sciences, Chengdu University of Technology, Chengdu 610059, China. Yunnan Institute of Geological Survey, Kunming 650216, China.Research Center of Geochemical Survey and Assessment on Land Quality, China Geological Survey, Langfang 065000, China. Institute of Geophysical and Geochemical Exploration, Chinese Academy of Geological Sciences, Langfang, 065000, China. Key Laboratory of Geochemical Cycling of Carbon and Mercury in the Earth's Critical Zone, China Geological Survey, Langfang 065000, China.Research Center of Geochemical Survey and Assessment on Land Quality, China Geological Survey, Langfang 065000, China. Institute of Geophysical and Geochemical Exploration, Chinese Academy of Geological Sciences, Langfang, 065000, China. Key Laboratory of Geochemical Cycling of Carbon and Mercury in the Earth's Critical Zone, China Geological Survey, Langfang 065000, China.

Pub Type(s)

Journal Article

Language

chi

PubMed ID

33124301

Citation

Zhang, Fu-Gui, et al. "[Ecological Risk Assessment of Heavy Metals at Township Scale in the High Background of Heavy Metals, Southwestern, China]." Huan Jing Ke Xue= Huanjing Kexue, vol. 41, no. 9, 2020, pp. 4197-4209.
Zhang FG, Peng M, Wang HY, et al. [Ecological Risk Assessment of Heavy Metals at Township Scale in the High Background of Heavy Metals, Southwestern, China]. Huan Jing Ke Xue. 2020;41(9):4197-4209.
Zhang, F. G., Peng, M., Wang, H. Y., Ma, H. H., Xu, R. T., Cheng, X. M., Hou, Z. L., Chen, Z. W., Li, K., & Cheng, H. X. (2020). [Ecological Risk Assessment of Heavy Metals at Township Scale in the High Background of Heavy Metals, Southwestern, China]. Huan Jing Ke Xue= Huanjing Kexue, 41(9), 4197-4209. https://doi.org/10.13227/j.hjkx.201912241
Zhang FG, et al. [Ecological Risk Assessment of Heavy Metals at Township Scale in the High Background of Heavy Metals, Southwestern, China]. Huan Jing Ke Xue. 2020 Sep 8;41(9):4197-4209. PubMed PMID: 33124301.
* Article titles in AMA citation format should be in sentence-case
TY - JOUR T1 - [Ecological Risk Assessment of Heavy Metals at Township Scale in the High Background of Heavy Metals, Southwestern, China]. AU - Zhang,Fu-Gui, AU - Peng,Min, AU - Wang,Hui-Yan, AU - Ma,Hong-Hong, AU - Xu,Ren-Ting, AU - Cheng,Xiao-Meng, AU - Hou,Zhao-Lei, AU - Chen,Zi-Wan, AU - Li,Kuo, AU - Cheng,Hang-Xin, PY - 2020/10/30/entrez PY - 2020/10/31/pubmed PY - 2020/11/5/medline KW - ecological risk assessment KW - high background area KW - positive matrix factorization KW - soil heavy metal KW - source apportionment SP - 4197 EP - 4209 JF - Huan jing ke xue= Huanjing kexue JO - Huan Jing Ke Xue VL - 41 IS - 9 N2 - Heavy metals (HMs) are naturally occurring elements that have high natural background levels in the environment. Therefore, it is important to conduct ecological risk assessment and identify potential sources of HMs. In the past, studies were conducted at the regional scale. The accuracy of those studies could not meet the needs of spatial planning and natural resource management. Therefore, it is necessary to conduct ecological risk assessment at the township scale. In this study, 1092 soil samples (from 0-20 cm depth) were collected in the town of Reshui, an area with high background levels of soil HMs with the parent material of carbonatite, which is commonly found in Southwest China. The town of Reshui is a multi-ecological risk superimposed area where the ecological risk is high. In this study, concentrations of HMs (Cd, Cr, As, Hg, Pb, Cu, Zn, and Ni) in the topsoil were analyzed, and statistical analysis (SA), geographic information system (GIS) modeling, and positive matrix factorization (PMF) analysis were performed. The geoaccumulation index (Igeo) and potential ecological risk index (PERI) were applied for the ecological risk assessment and quantification of the sources of the soil HMs. The mean values of HM concentrations in the topsoil were 18.1, 1.18, 174.1, 202.2, 0.09, 71.1, 34.9, and 167.2 mg ·kg-1for As, Cd, Cr, Cu, Hg, Ni, Pb, and Zn, respectively, which were considerably higher than the average background value (ABV) in soils in Yunnan Province except for As and Pb. The average concentrations of Cd, Cr, Cu, and Ni exceeded the screening values specified in the soil contamination risk in agricultural land (GB 15618-2018) by 5.82, 1.16, 4.04, and 1.02 times, respectively. The Igeo value shows that the major pollutant is Cu in the surface soil of the study area, followed by Cr, and Cd. Speciation analysis of HMs indicates that HMs (Cr, As, Pb, Cu, Zn, and Ni) mainly exist in the residual form, mostly from the geological background with low bioavailability. The potential effective components of Hg have higher levels, but the total amount of Hg and its pollution risk are lower. Cd has a high bioavailability ratio, is easy to enter the soil solution and be absorbed by crops, and is the HM with the highest pollution risk in the study area. The PERI shows that the proportions of low ecological risk, moderate risk, and high risk soil samples are 44.23%, 54.40%, and 1.37% of the total number of samples, respectively. Hg and Cd were the major sources of risk because of their high toxicity coefficient. The PMF analysis indicates that there are four major sources of HMs in the study area: human activity, natural sources, coal mining and traffic emissions, and agricultural sources with the risk contribution ratios of 9.29%, 53.67%, 11.23%, and 25.81%, respectively. The PMF analysis effectively quantified the ecological risk from these sources, providing a reference for further pollution control and prevention measures. SN - 0250-3301 UR - https://www.unboundmedicine.com/medline/citation/33124301/[Ecological_Risk_Assessment_of_Heavy_Metals_at_Township_Scale_in_the_High_Background_of_Heavy_Metals_Southwestern_China]_ DB - PRIME DP - Unbound Medicine ER -