4.7 Article

Omnipresent distribution of herbicides and their transformation products in all water body types of an agricultural landscape in the North German Lowland

Journal

ENVIRONMENTAL SCIENCE AND POLLUTION RESEARCH
Volume 28, Issue 32, Pages 44183-44199

Publisher

SPRINGER HEIDELBERG
DOI: 10.1007/s11356-021-13626-x

Keywords

Flufenacet; Metazachlor; Drainage; Shallow groundwater; Drinking water; Stream water; Rainfall pattern; Physical-chemical properties

Funding

  1. German Federal Ministry for Education and Research (BMBF) [02WRM1366C]

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The research on the environmental fate of pesticides showed that transformation products of herbicides were more widespread and in higher concentrations than their parent compounds in various water bodies. Particularly, metazachlor sulfonic acid, metazachlor oxalic acid, and flufenacet oxalic acid were detected in almost every drainage and stream sample. This transformation process leads to more mobile and persistent molecules, causing higher detection frequencies and concentrations, even occurring a year or more after application. Vulnerability of shallow groundwater and private drinking water wells to leaching compounds was proven by detection of metazachlor-TP.
The research of the environmental fate of pesticides has demonstrated that applied compounds are altered in their molecular structure over time and are distributed within the environment. To assess the risk for contamination by transformation products (TP) of the herbicides flufenacet and metazachlor, the following four water body types were sampled in a small-scale catchment of 50 km(2) in 2015/2016: tile drainage water, stream water, shallow groundwater, and drinking water of private wells. The TP were omnipresent in every type of water body, more frequently and in concentrations up to 10 times higher than their parent compounds. Especially metazachlor sulfonic acid, metazachlor oxalic acid, and flufenacet oxalic acid were detected in almost every drainage and stream sample. The transformation process leads to more mobile and more persistent molecules resulting in higher detection frequencies and concentrations, which can even occur a year or more after the application of the parent compound. The vulnerability of shallow groundwater and private drinking water wells to leaching compounds is proved by numerous positives of metazachlor-TP with maximum concentrations of 0.7 mu g L-1 (drinking water) and 20 mu g L-1 (shallow groundwater) of metazachlor sulfonic acid. Rainfall events during the application period cause high discharge of the parent compound and lower release of TP. Later rainfall events lead to high displacement of TP. For an integrated risk assessment of water bodies, the environmental behavior of pesticide-TP has to be included into regular state-of-the-art water quality monitoring.

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