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Frontiers of Environmental Science & Engineering

ISSN 2095-2201

ISSN 2095-221X(Online)

CN 10-1013/X

邮发代号 80-973

2018 Impact Factor: 3.883

Frontiers of Environmental Science & Engineering  2023, Vol. 17 Issue (11): 142   https://doi.org/10.1007/s11783-023-1742-9
  本期目录
Multimedia distribution and health risk assessment of typical organic pollutants in a retired industrial park
Shijin Wu1, Zijing Xiang1, Daohui Lin1,2, Lizhong Zhu1,2()
1. Zhejiang Provincial Key Laboratory of Organic Pollution Process and Control, Department of Environmental Science, Zhejiang University, Hangzhou 310058, China
2. Zhejiang Ecological Civilization Academy, Anji 313300, China
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Abstract

● A fine portrayal of organic pollutants in a retired industrial park is provided.

● Key factors affecting the spatial distribution of organic pollutants are unrevaled.

● Risk classification, grading, and management are reached based on risk assessment.

The overall cross-media risk evaluation of organic pollutants in retired industrial parks is insufficiently recognized. In this study, 11 semi-volatile organic compounds (SVOCs) and 27 volatile organic compounds (VOCs) were measured in 531 soil and groundwater samples taken from a retired industrial park by coast in Zhejiang Province, China. Total petroleum hydrocarbons (TPHs), Di (2-ethylhexyl) phthalate (DEHP), benzene, and ethylbenzene were identified as the critical pollutants in the soil, while TPHs, 1,2-dichloropropane (1,2-DCP), toluene, benzo[a]anthracene (BaA), and benzo[b]fluoranthene (BbF) were identified as critical pollutants in the groundwater for exceeding China national standards. The spatial correlation between the concentrations of organic pollutants in soil and groundwater was explored by employing the Geodetector model. Based on the results of spatial interpolation, high-risk hotspots regarding soil and groundwater pollution were identified. Moreover, the possible harm to human health of the critical pollutants were also under evaluation. Among various critical pollutants, benzene, ethylbenzene, and DEHP in soil, and 1,2-DCP in groundwater, were the main contributors to the overall health risk of multimedia pollution. This study developed a comprehensive approach to assess the risks posed by specific organic toxicants in various environmental media. The findings of this work can serve as a valuable reference for future management strategies in retired industrial parks.

Key wordsOrganic pollutants    Retired industrial park    Spatial correlation    Health risk assessment
收稿日期: 2023-03-14      出版日期: 2023-11-15
Corresponding Author(s): Lizhong Zhu   
 引用本文:   
. [J]. Frontiers of Environmental Science & Engineering, 2023, 17(11): 142.
Shijin Wu, Zijing Xiang, Daohui Lin, Lizhong Zhu. Multimedia distribution and health risk assessment of typical organic pollutants in a retired industrial park. Front. Environ. Sci. Eng., 2023, 17(11): 142.
 链接本文:  
https://academic.hep.com.cn/fese/CN/10.1007/s11783-023-1742-9
https://academic.hep.com.cn/fese/CN/Y2023/V17/I11/142
Fig.1  
Critical pollutants Detection frequency (%) Max (mg/kg) Min (mg/kg) Screening value (mg/kg) Over-standard rate (%) Maximum exceedance multiple
Soil TPHs 62.0 9980 ND 826 2.1 12.1
DEHP 24.1 92.2 ND 42 0.19 2.20
Benzene 2.82 3.04 ND 1 0.19 3.04
Ethylbenzene 2.64 20.8 ND 7.2 0.19 2.89
Groundwater TPHs 100 7.40E + 00 0.01 6.00E–01b) 19.4 12.3
BbF 75.8 3.44E–02 ND 8.00E–03 a) 23.2 3.30
BaA 53.2 1.11E–02 ND 3.80E–03 a) 43.6 2.31
Toluene 3.23 1.56E + 00 ND 1.40E + 00 a) 1.61 1.11
1,2-DCP 1.61 7.98E–01 ND 6.00E–02 a) 1.61 13.3
Tab.1  
Fig.2  
Fig.3  
Fig.4  
Scenarios Site Pollutants Soil   Groundwater   CRT
CRois CRdcs CRpis CRiiv1   CRiiv2  
Sensitive scenario S21 Benzene       3.47E−06        
Ethylbenzene       3.07E−06        
1,2-DCP       3.34E−08        
BaA 3.84E−08 1.59E−08 2.73E−10        
BbF 7.67E−08 3.19E−08 5.46E−10        
DEHP 7.16E−09 2.29E−09 1.46E−11        
Sum 1.22E−07 5.01E−08 8.33E−10 6.57E− 06       6.74E−06
S41(W21 ) Ethylbenzene         1.07E−08    
1,2-DCP         2.87E−06    
BbF         5.51E−14    
DEHP 5.01E−08 1.60E−08 1.02E−10 3.44E−15        
Sum 5.01E−08 1.60E−08 1.02E−10 3.44E−15   2.88E−06   3.01E−06
S81(W41) BaA         3.19E−13    
BbF         3.48E−14    
DEHP 1.65E−06 5.28E−07 3.35E−09        
Sum 1.65E−06 5.28E−07 3.35E−09   3.53E−13   2.18E−06
Non-sensitive scenario S21 Benzene       8.01E−07        
Ethylbenzene       7.09E−07        
1,2-DCP       7.71E−09        
BaA 1.09E−08 8.60E−09 1.43E−10        
BbF 2.19E−08 1.72E−08 2.87E−10        
DEHP 2.04E−09 1.23E−09 7.64E−12        
Sum 3.49E−08 2.70E−08 4.38E−10 1.52E−06       1.58E−06
Tab.2  
Site Pollutants Soil Groundwater HI
HQois HQdcs HQpis HQiiv1 HQiiv2
S21 Benzene 1.67E−01
Ethylbenzene 1.57E−03
1,2-DCP 1.38E−02
DEHP 4.00E−04 1.14E−04
Sum 4.00E−04 1.14E−04 1.85E−01 1.86E−01
S41(W21 ) Ethylbenzene 8.46E−04
1,2-DCP 4.84E−05
BbF 2.18E−01
DEHP 2.80E−03 7.97E−04
Sum 2.80E−03 7.97E−04 2.19E−01 2.23E−01
S81(W41) DEHP 9.21E−02 2.62E−02
Sum 9.21E−02 2.62E−02 1.18E−01
Tab.3  
Critical pollutants RCVs (mg/kg) RCVg (mg/L)
Benzene 0.80 0.55
Toluene 1630 1840
Ethylbenzene 6.12 1.59
1,2-DCP 0.21 0.28
BaA 5.50 107
BbF 5.50 834
DEHP 42.3 69800
Tab.4  
Fig.5  
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