Sources and transformation pathways for dichlorodiphenyltrichloroethane (DDT) and metabolites in soils from Northwest Fujian, China

Sources and transformation pathways for dichlorodiphenyltrichloroethane (DDT) and metabolites in soils from Northwest Fujian, China
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中国闽西北土壤中二氯二苯基三氯乙烷(DDT)及其代谢物的来源和转化途径

DOI:
10.1016/j.envpol.2017.12.071
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发表时间:
2018-04-01
影响因子:
8.9
通讯作者:
Qi, Shihua
Qi, Shihua
中科院分区:
环境科学与生态学2区
文献类型:
--
作者:
Huang, Huanfang;Zhang, Yuan;Qi, Shihua

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三氯杀螨醇(2,2,2-三氯-1,1-双-(对氯苯基)乙醇)是一种存在于环境中的杀螨剂,它不仅是一种商业用途的杀螨剂,而且是二氯二苯三氯乙烷(DDT)的一种代谢物,而DDT往往被人们所忽视。为探明土壤中DDT及其代谢物的来源和转化途径,测定了闽西北土壤中p,p'-(三氯杀螨醇+DBP)(p,p'-三氯杀螨醇和4,4'-二氯二苯甲酮的总和)、DDT及其6种代谢物的含量。1,1,1-三氯-2-(邻氯苯基)-2-(对氯苯基)乙烷(o,p'-DDT)/1,1,1-三氯-2,2-双-(对氯苯基)乙烷(p,p'-DDT)的比例和质量平衡表明,p,p'-(三氯杀螨醇+DBP)主要来自p,p'-DDT的转化,而不是三氯杀螨醇的实际应用。p,p '-(三氯杀螨醇+邻苯二甲酸二丁酯)占DDT主要代谢产物的45.0%,超过1,1-二氯-2,2-二对氯苯基乙烯(p,p'-DDE)和1,1-二氯-2,2-双-对氯苯基乙烷(p,p'-DDD),这可能会导致使用传统的(Sigma 2DDD + Sigma 2DDE)/Sigma 2DDT(包括所有o,p'-和p,p'-异构体)。在好氧(干旱期)和厌氧(湿润期)交替的稻田中,p,p'-DDD和p,p'-DDE都有可能降解为1-氯-2,2-二(对氯苯基)乙烯(p,p'-DDMU),后者进一步转化为2,2-二(对氯苯基)乙烯(p,p'-DDNU)。p,p'-DDMU降解为p,p'-DDNU主要发生在涝渍水稻土中。然而,p,p'-DDNU可能不会转化为其他高阶代谢产物在好氧表层土壤。本研究证实p,p'-(三氯杀螨醇+DBP)是p,p'-DDT的代谢产物,DDE和DDD是DDMU的平行前体,进一步验证了DDT在表层土壤中的转化途径。(C)2018爱思唯尔有限公司版权所有
Dicofol (2,2,2-trichloro-1,1-bis-(p-chlorophenyl)ethanol) found in the environment is not only a miticide originated from commercial use, but also a metabolite of dichlorodiphenyltrichloroethane (DDT), which is often overlooked. To verify the sources and transformation pathways of DDT and related metabolites in soils, we measured p,p'-(dicofol + DBP) (sum of p,p'-dicofol and 4,4'-dichlorobenzophenone), DDT and six metabolites in soils from Northwest Fujian, China. The ratios of 1,1,1-trichloro-2-(o-chloropheny1)-2-(p-chlorophenyl)ethane (o,p'-DDT)/1,1,1-trichloro-2,2-bis-(p-chlorophenyflethane (p,p'-DDT) and the mass balance demonstrated that p,p'-(dicofol + DBP) predominantly originated from p,p'-DDT transformation rather than from actual dicofol application. p,p'-(dicofol + DBP) accounted for 45.0% as the primary metabolites of DDT in this study, more than 1,1-dichloro-2,2-bis-(p-chlorophenyl)ethylene (p,p'-DDE) and 1,1-dichloro-2,2-bis-(p-chlorophenyl)ethane (p,p'-DDD), which might lead to large overestimations of the fresh DDT input by using the traditional ratio of (Sigma 2DDD + Sigma 2DDE)/Sigma 2DDT (with all o,p'- and p,p'-isomers included). In paddy fields where the conditions alternate between aerobic (dry period) and anaerobic (wet period), both p,p'-DDD and p,p'-DDE were likely to degrade to 1-chloro-2,2-bis-(p-chlorophenyl)ethylene (p,p'-DDMU), which further transformed to 2,2-bis(p-chlorophenyl) ethylene (p,p'-DDNU). Degradation of p,p'-DDMU to p,p'-DDNU mainly occurred in waterlogged paddy soils. However, p,p'-DDNU might not transform to other higher-order metabolites in aerobic surface soils. Overall, our study confirmed p,p'-(dicofol + DBP) as metabolites of p,p'-DDT, suggested DDE and DDD were parallel precursors of DDMU, and further verified the transformation pathways of DDT in surface soils. (C) 2018 Elsevier Ltd. All rights reserved.