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Target and non-target analysis of organochlorine pesticides and their transformation products in an agrochemical-contaminated area

农药 环境化学 污染 污染物 杀虫剂 土壤污染 污染 环境科学 土壤污染物 化学 农业 生态学 生物 有机化学
作者
Di Huang,Lirong Gao,Shuai Zhu,Lin Qiao,Yang Liu,Qiaofeng Ai,Chi Xu,Wenwen Wang,Meiling Lü,Minghui Zheng
出处
期刊:Chemosphere [Elsevier BV]
卷期号:324: 138314-138314 被引量:19
标识
DOI:10.1016/j.chemosphere.2023.138314
摘要

Organochlorine pesticides show biological toxicity and their degradation typically takes many years. Previous studies of agrochemical-contaminated areas have mainly focused on limited target compounds, and emerging pollutants in soil have been overlooked. In this study, we collected soil samples from an abandoned agrochemical-contaminated area. Target analysis and non-target suspect screening by gas chromatography coupled with time-of-flight mass spectrometry were combined for qualitative and quantitative analysis of organochlorine pollutants. Target analysis showed that dichlorodiphenyltrichloroethane (DDT), dichlorodiphenyldichloroethylene (DDE), and dichlorodiphenyldichloroethane (DDD) were the main pollutants. With concentrations between 3.96 × 106 and 1.38 × 107 ng/g, these compounds posed significant health risks at the contaminated site. Non-target suspect screening identified 126 organochlorine compounds, most of which were chlorinated hydrocarbons and 90% of the compounds contained a benzene ring structure. The possible transformation pathways of DDT were inferred from proven pathways and the compounds identified by non-target suspect screening that had similar structures to DDT. This study will be useful for studies of the degradation mechanism of DDT. Semi-quantitative and hierarchical cluster analysis of compounds in soil showed that the distribution of contaminants in soil was influenced by the types of pollution sources and distance to them. Twenty-two contaminants were found in the soil at relatively high concentrations. The toxicities of 17 of these compounds are currently not known. These results improve our understanding of the environmental behavior of organochlorine contaminants in soil and are useful for further risk assessments of agrochemical-contaminated areas.
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