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Groundwater monitoring for 1,3‐dichloropropene in high fumigant use areas of North America and Europe

BACKGROUND: 1,3‐Dichloropropene (1,3‐D) is a soil fumigant used for the control of nematodes in high‐value fruit, nut and vegetable crops globally. Extensive water monitoring efforts have been undertaken over the past four decades by public and private institutions, given the widespread agricultural...

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Detalles Bibliográficos
Autores principales: van Wesenbeeck, Ian J, Knowles, Steve
Formato: Online Artículo Texto
Lenguaje:English
Publicado: John Wiley & Sons, Ltd. 2019
Materias:
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC6767602/
https://www.ncbi.nlm.nih.gov/pubmed/30843340
http://dx.doi.org/10.1002/ps.5398
Descripción
Sumario:BACKGROUND: 1,3‐Dichloropropene (1,3‐D) is a soil fumigant used for the control of nematodes in high‐value fruit, nut and vegetable crops globally. Extensive water monitoring efforts have been undertaken over the past four decades by public and private institutions, given the widespread agricultural use of 1,3‐D, and environmental fate and metabolism data suggesting the potential for 1,3‐D to leach into groundwater. The aim of this study is to review the results of groundwater monitoring studies for 1,3‐D conducted in North America and the European Union (EU) since 1980. RESULTS: Analysis of > 50 000 water samples by state and federal agencies in the USA resulted in 151 detections of 1,3‐D. An additional 4000 samples analyzed in groundwater studies specifically targeting high 1,3‐D use areas in Europe and the USA resulted in 74 detections of 1,3‐D or its primary metabolites. The combined detection rate of 1,3‐D and its primary metabolites in high‐use areas of the EU and North America was 0.7%. CONCLUSIONS: The availability of extensive groundwater monitoring information developed through decades of study supports the conclusion that soil fumigation with 1,3‐D poses an inconsequential risk for drinking water exposure. The lack of significant detections of 1,3‐D from targeted monitoring studies is due to the high volatility of 1,3‐D, the rapid degradation of 1,3‐D in most agricultural soils, the rapid degradation of 1,3‐D and its metabolites in aerobic aquatic systems, and the rapid hydrolysis of 1,3‐D in water. © 2019 The Authors. Pest Management Science published by John Wiley & Sons Ltd on behalf of Society of Chemical Industry.