Environmental Health and Ecological Risk Assessment of Soil Heavy Metal Pollution in the Coastal Cities of Estuarine Bay—A Case Study of Hangzhou Bay, China

Shanghai is the major city on the north shore of Hangzhou Bay, and the administrative regions adjacent to Hangzhou Bay are the Jinshan district, Fengxian district, and Pudong new area (Nanhui district), which are the main intersection areas of manufacturing, transportation, and agriculture in Shangh...

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Main Authors: Rongxi Li, Yuan Yuan, Chengwei Li, Wei Sun, Meng Yang, Xiangrong Wang
Format: Article
Language:English
Published: MDPI AG 2020-09-01
Series:Toxics
Subjects:
Online Access:https://www.mdpi.com/2305-6304/8/3/75
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author Rongxi Li
Yuan Yuan
Chengwei Li
Wei Sun
Meng Yang
Xiangrong Wang
author_facet Rongxi Li
Yuan Yuan
Chengwei Li
Wei Sun
Meng Yang
Xiangrong Wang
author_sort Rongxi Li
collection DOAJ
description Shanghai is the major city on the north shore of Hangzhou Bay, and the administrative regions adjacent to Hangzhou Bay are the Jinshan district, Fengxian district, and Pudong new area (Nanhui district), which are the main intersection areas of manufacturing, transportation, and agriculture in Shanghai. In this paper, we collected a total of 75 topsoil samples from six different functional areas (agricultural areas (19), roadside areas (10), industrial areas (19), residential areas (14), education areas (6), and woodland areas (7)) in these three administrative regions, and the presence of 10 heavy metals (manganese(Mn), zinc(Zn), chromium(Cr), nickel(Ni), lead(Pb), cobalt(Co), cadmium(Cd), mercury(Hg), copper(Cu), and arsenic(As)) was investigated in each sample. The Nemerow pollution index (NPI), pollution load index (PLI), and potential ecological risk index (PERI) were calculated to assess the soil pollution levels. The hazard quotient (HQ) and carcinogenic risk (CR) assessment models were used to assess the human health risks posed by the concentrations of the heavy metals. The CR and HQ for adults and children in different functional areas descended in the following order: industrial areas > roadside areas > woodland areas > residential areas > education areas > agricultural areas. The HQ of Mn for children in industrial areas was higher than 1, and the risk was within the acceptable range.
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spelling doaj.art-d4261177d7f8485d9552f7a55e0ccefd2023-11-20T14:39:30ZengMDPI AGToxics2305-63042020-09-01837510.3390/toxics8030075Environmental Health and Ecological Risk Assessment of Soil Heavy Metal Pollution in the Coastal Cities of Estuarine Bay—A Case Study of Hangzhou Bay, ChinaRongxi Li0Yuan Yuan1Chengwei Li2Wei Sun3Meng Yang4Xiangrong Wang5Department of Environmental Science and Engineering, Fudan University, Shanghai 200438, ChinaDepartment of Environmental Science and Engineering, Fudan University, Shanghai 200438, ChinaDepartment of Environmental Science and Engineering, Fudan University, Shanghai 200438, ChinaDepartment of Environmental Science and Engineering, Fudan University, Shanghai 200438, ChinaDepartment of Environmental Science and Engineering, Fudan University, Shanghai 200438, ChinaDepartment of Environmental Science and Engineering, Fudan University, Shanghai 200438, ChinaShanghai is the major city on the north shore of Hangzhou Bay, and the administrative regions adjacent to Hangzhou Bay are the Jinshan district, Fengxian district, and Pudong new area (Nanhui district), which are the main intersection areas of manufacturing, transportation, and agriculture in Shanghai. In this paper, we collected a total of 75 topsoil samples from six different functional areas (agricultural areas (19), roadside areas (10), industrial areas (19), residential areas (14), education areas (6), and woodland areas (7)) in these three administrative regions, and the presence of 10 heavy metals (manganese(Mn), zinc(Zn), chromium(Cr), nickel(Ni), lead(Pb), cobalt(Co), cadmium(Cd), mercury(Hg), copper(Cu), and arsenic(As)) was investigated in each sample. The Nemerow pollution index (NPI), pollution load index (PLI), and potential ecological risk index (PERI) were calculated to assess the soil pollution levels. The hazard quotient (HQ) and carcinogenic risk (CR) assessment models were used to assess the human health risks posed by the concentrations of the heavy metals. The CR and HQ for adults and children in different functional areas descended in the following order: industrial areas > roadside areas > woodland areas > residential areas > education areas > agricultural areas. The HQ of Mn for children in industrial areas was higher than 1, and the risk was within the acceptable range.https://www.mdpi.com/2305-6304/8/3/75risk assessmentenvironmental healthsoilheavy metalsHangzhou Bay
spellingShingle Rongxi Li
Yuan Yuan
Chengwei Li
Wei Sun
Meng Yang
Xiangrong Wang
Environmental Health and Ecological Risk Assessment of Soil Heavy Metal Pollution in the Coastal Cities of Estuarine Bay—A Case Study of Hangzhou Bay, China
Toxics
risk assessment
environmental health
soil
heavy metals
Hangzhou Bay
title Environmental Health and Ecological Risk Assessment of Soil Heavy Metal Pollution in the Coastal Cities of Estuarine Bay—A Case Study of Hangzhou Bay, China
title_full Environmental Health and Ecological Risk Assessment of Soil Heavy Metal Pollution in the Coastal Cities of Estuarine Bay—A Case Study of Hangzhou Bay, China
title_fullStr Environmental Health and Ecological Risk Assessment of Soil Heavy Metal Pollution in the Coastal Cities of Estuarine Bay—A Case Study of Hangzhou Bay, China
title_full_unstemmed Environmental Health and Ecological Risk Assessment of Soil Heavy Metal Pollution in the Coastal Cities of Estuarine Bay—A Case Study of Hangzhou Bay, China
title_short Environmental Health and Ecological Risk Assessment of Soil Heavy Metal Pollution in the Coastal Cities of Estuarine Bay—A Case Study of Hangzhou Bay, China
title_sort environmental health and ecological risk assessment of soil heavy metal pollution in the coastal cities of estuarine bay a case study of hangzhou bay china
topic risk assessment
environmental health
soil
heavy metals
Hangzhou Bay
url https://www.mdpi.com/2305-6304/8/3/75
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