Published April 2018 | Version v1
Journal article

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

  • 1. Lancaster Environment Centre, Lancaster University, Lancaster LA1 4YQ (United Kingdom)
  • 2. School of Environmental Studies, China University of Geosciences, Wuhan 430074 (China)
  • 3. State Key Laboratory of Biogeology and Environmental Geology, China University of Geosciences, Wuhan 430074 (China)
  • 4. State Key Laboratory of Environmental and Biological Analysis, Department of Chemistry, Hong Kong Baptist University, Hong Kong Special Administrative Region (China)
  • 5. Minnesota Supercomputing Institute, University of Minnesota, Minneapolis, MN 55455 (United States)

Description

Highlights: • DDT and related metabolites in soils were analyzed on a GC-MS/MS. • p,p'-(dicofol + DBP) were majorly originated from the degradation of p,p'-DDT. • Pathways of DDT→DDE→DDMU→DDNU, DDT→DDD→DDMU→DDNU and DDT→ (dicofol + DBP) were verified. • Both p,p'-DDE and p,p'-DDD are significant precursors for p,p'-DDMU in paddy fields. 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-chlorophenyl)-2-(p-chlorophenyl)ethane (o,p'-DDT)/1,1,1-trichloro-2,2-bis-(p-chlorophenyl)ethane (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 (∑2DDD + ∑2DDE)/∑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.

Availability note (English)

Available from http://dx.doi.org/10.1016/j.envpol.2017.12.071

Additional details

Identifiers

DOI
10.1016/j.envpol.2017.12.071;
PII
S0269749117341933;

Publishing Information

Journal Title
Environmental Pollution (1987)
Journal Volume
235
Journal Page Range
p. 560-570
ISSN
0269-7491
CODEN
ENPOEK

Optional Information

Copyright
Copyright (c) 2018 Elsevier Ltd. All rights reserved.