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Leaching and degradation of (13)C(2)-(15)N-glyphosate in field lysimeters

Glyphosate (GLYP), the globally most important herbicide, may have effects in various compartments of the environment such as soil and water. Although laboratory studies showed fast microbial degradation and a low leaching potential, it is often detected in various environmental compartments, but pa...

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Detalles Bibliográficos
Autores principales: Gros, Peter, Meissner, Ralph, Wirth, Marisa A., Kanwischer, Marion, Rupp, Holger, Schulz-Bull, Detlef E., Leinweber, Peter
Formato: Online Artículo Texto
Lenguaje:English
Publicado: Springer International Publishing 2020
Materias:
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC6970956/
https://www.ncbi.nlm.nih.gov/pubmed/31960150
http://dx.doi.org/10.1007/s10661-019-8045-4
Descripción
Sumario:Glyphosate (GLYP), the globally most important herbicide, may have effects in various compartments of the environment such as soil and water. Although laboratory studies showed fast microbial degradation and a low leaching potential, it is often detected in various environmental compartments, but pathways are unknown. Therefore, the objective was to study GLYP leaching and transformations in a lysimeter field experiment over a study period of one hydrological year using non-radioactive (13)C(2)-(15)N-GLYP labelling and maize cultivation. (15)N and (13)C were selectively measured using isotopic ratio mass spectrometry (IR-MS) in leachates, soil, and plant material. Additionally, HPLC coupled to tandem mass spectrometry (HPLC-MS/MS) was used for quantitation of GLYP and its main degradation product aminomethylphosphonic acid (AMPA) in different environmental compartments (leachates and soil). Results show low recoveries for GLYP (< 3%) and AMPA (< level of detection) in soil after the study period, whereas recoveries of (15)N (11–19%) and (13)C (23–54%) were higher. Time independent enrichment of (15)N and (13)C and the absence of GLYP and AMPA in leachates indicated further degradation. (15)N was enriched in all compartments of maize plants (roots, shoots, and cobs). (13)C was only enriched in roots. Results confirmed rapid degradation to further degradation products, e.g., (15)NH(4)(+), which plausibly was taken up as nutrient by plants. Due to the discrepancy of low GLYP and AMPA concentrations in soil, but higher values for (15)N and (13)C after the study period, it cannot be excluded that non-extractable residues of GLYP remained and accumulated in soil. ELECTRONIC SUPPLEMENTARY MATERIAL: The online version of this article (10.1007/s10661-019-8045-4) contains supplementary material, which is available to authorized users.