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Quantitative and qualitative differences in the metabolism of pesticides in biobed substrates and soil

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Auteur
Karanasios, E. C.; Tsiropoulos, N. G.; Karpouzas, D. G.
Date
2013
DOI
10.1016/j.chemosphere.2013.04.049
Sujet
Terbuthylazine
Metribuzin
Chlorpyrifos
Metabolism
Biobed
Biomixture
SOURCE CONTAMINATION
SURFACE-WATER
GROUND-WATER
DEGRADATION
CHLORPYRIFOS
TERBUTHYLAZINE
METRIBUZIN
ATRAZINE
MOBILITY
3,5,6-TRICHLORO-2-PYRIDINOL
Environmental Sciences
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Résumé
Biobed substrates commonly exhibit high degradation capacity. However, degradation does not always lead to detoxification and information on the metabolic pathways of pesticides in biobeds is scarce. We studied the degradation and metabolism of three pesticides in selected biomixtures and soil. Biomixtures stimulated degradation of terbuthylazine and metribuzin, whereas chlorpyrifos degraded faster in soil. The latter was attributed to the lipophilicity of chlorpyrifos which increased adsorption and limited biodegradation in organic-rich biomixtures. Although the same metabolites were detected in all substrates, qualitative and quantitative differences in the metabolic routes of pesticides in the various substrates were observed. Chlorpyrifos was hydrolyzed to 3,5,6-tricholorpyridinol (TCP) which was further degraded only in compost-biomixture CBX1. Metabolism of terbuthylazine in compost biomixtures (BX) and soil resulted in the formation of desethyl-terbuthylazine (DES) which was fully degraded only in the compost-biomixture CBX2, whereas peat-based biomixture (OBX) promoted the hydroxylation of terbuthylazine. Desamino- (DA) (dominant) and diketo- (DK) metribuzin appear as intermediate metabolites in all substrates and were further transformed to desamino-diketo-metribuzin (DADK) which was fully degraded only in compost-biomixture GSBX. Overall, lower amounts of metabolites were accumulated in biomixtures compared to soil stressing the higher depuration efficiency of biobeds. (C) 2013 Elsevier Ltd. All rights reserved.
URI
http://hdl.handle.net/11615/29033
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