001     13003
005     20180208223323.0
024 7 _ |2 pmid
|a pmid:21121649
024 7 _ |2 DOI
|a 10.1021/jf103577j
024 7 _ |2 WOS
|a WOS:000285236400042
037 _ _ |a PreJuSER-13003
041 _ _ |a eng
082 _ _ |a 630
084 _ _ |2 WoS
|a Agriculture, Multidisciplinary
084 _ _ |2 WoS
|a Chemistry, Applied
084 _ _ |2 WoS
|a Food Science & Technology
100 1 _ |a Jablonowski, N. D.
|b 0
|u FZJ
|0 P:(DE-Juel1)129475
245 _ _ |a Metabolism and Persistence of Atrazine in Several Field Soils with Different Atrazine Application Histories
260 _ _ |a Washington, DC [u.a.]
|b American Chemical Society (ACS)
|c 2010
300 _ _ |a 12869 - 12877
336 7 _ |a Journal Article
|0 PUB:(DE-HGF)16
|2 PUB:(DE-HGF)
336 7 _ |a Output Types/Journal article
|2 DataCite
336 7 _ |a Journal Article
|0 0
|2 EndNote
336 7 _ |a ARTICLE
|2 BibTeX
336 7 _ |a JOURNAL_ARTICLE
|2 ORCID
336 7 _ |a article
|2 DRIVER
440 _ 0 |a Journal of Agricultural and Food Chemistry
|x 0021-8561
|0 3005
|y 24
|v 58
500 _ _ |a Record converted from VDB: 12.11.2012
520 _ _ |a To assess the potential occurrence of accelerated herbicide degradation in soils, the mineralization and persistence of (14)C-labeled and nonlabeled atrazine was evaluated over 3 months in two soils from Belgium (BS, atrazine-treated 1973-2008; BC, nontreated) and two soils from Germany (CK, atrazine-treated 1986-1989; CM, nontreated). Prior to the experiment, accelerated solvent extraction of bulk field soils revealed atrazine (8.3 and 15.2 μg kg(-1)) in BS and CK soils and a number of metabolites directly after field sampling, even in BC and CM soils without previous atrazine treatment, by means of LC-MS/MS analyses. For atrazine degradation studies, all soils were incubated under different moisture conditions (50% maximum soil water-holding capacity (WHC(max))/slurried conditions). At the end of the incubation, the (14)C-atrazine mineralization was high in BS soil (81 and 83%) and also unexpectedly high in BC soil (40 and 81%), at 50% WHC(max) and slurried conditions, respectively. In CK soil, the (14)C-atrazine mineralization was higher (10 and 6%) than in CM soil (4.7 and 2.7%), but was not stimulated by slurried conditions. The results revealed that atrazine application history dramatically influences its degradation and mineralization. For the incubation period, the amount of extractable atrazine, composed of residues from freshly applied atrazine and residues from former field applications, remained significantly greater (statistical significance = 99.5 and 99.95%) for BS and CK soils, respectively, than the amount of extractable atrazine in the bulk field soils. This suggests that (i) mostly freshly applied atrazine is accessible for a complex microbial community, (ii) the applied atrazine is not completely mineralized and remains extractable even in adapted soils, and (iii) the microbial atrazine-mineralizing capacity strongly depends on atrazine application history and appears to be conserved on long time scales after the last application.
536 _ _ |a Terrestrische Umwelt
|c P24
|2 G:(DE-HGF)
|0 G:(DE-Juel1)FUEK407
|x 0
588 _ _ |a Dataset connected to Web of Science, Pubmed
650 _ 2 |2 MeSH
|a Agriculture
650 _ 2 |2 MeSH
|a Atrazine: analysis
650 _ 2 |2 MeSH
|a Atrazine: metabolism
650 _ 2 |2 MeSH
|a Bacteria: metabolism
650 _ 2 |2 MeSH
|a Biodegradation, Environmental
650 _ 2 |2 MeSH
|a Herbicides: analysis
650 _ 2 |2 MeSH
|a Herbicides: metabolism
650 _ 2 |2 MeSH
|a Soil: analysis
650 _ 2 |2 MeSH
|a Soil Microbiology
650 _ 2 |2 MeSH
|a Soil Pollutants: analysis
650 _ 2 |2 MeSH
|a Soil Pollutants: metabolism
650 _ 7 |0 0
|2 NLM Chemicals
|a Herbicides
650 _ 7 |0 0
|2 NLM Chemicals
|a Soil
650 _ 7 |0 0
|2 NLM Chemicals
|a Soil Pollutants
650 _ 7 |0 1912-24-9
|2 NLM Chemicals
|a Atrazine
650 _ 7 |a J
|2 WoSType
653 2 0 |2 Author
|a Metabolites
653 2 0 |2 Author
|a microbial adaptation
653 2 0 |2 Author
|a enhanced biodegradation
653 2 0 |2 Author
|a mineralization
653 2 0 |2 Author
|a persistence
700 1 _ |a Hamacher, G.
|b 1
|u FZJ
|0 P:(DE-Juel1)VDB89486
700 1 _ |a Martinazzo, R.
|b 2
|u FZJ
|0 P:(DE-Juel1)VDB89485
700 1 _ |a Langen, U.
|b 3
|u FZJ
|0 P:(DE-Juel1)VDB89488
700 1 _ |a Köppchen, S.
|b 4
|u FZJ
|0 P:(DE-Juel1)VDB4032
700 1 _ |a Hofman, D.
|b 5
|u FZJ
|0 P:(DE-Juel1)VDB96214
700 1 _ |a Burauel, P.
|b 6
|u FZJ
|0 P:(DE-Juel1)VDB202
773 _ _ |a 10.1021/jf103577j
|g Vol. 58, p. 12869 - 12877
|p 12869 - 12877
|q 58<12869 - 12877
|0 PERI:(DE-600)1483109-0
|t Journal of agricultural and food chemistry
|v 58
|y 2010
|x 0021-8561
856 7 _ |u http://dx.doi.org/10.1021/jf103577j
909 C O |o oai:juser.fz-juelich.de:13003
|p VDB
913 1 _ |k P24
|v Terrestrische Umwelt
|l Terrestrische Umwelt
|b Erde und Umwelt
|0 G:(DE-Juel1)FUEK407
|x 0
914 1 _ |y 2010
915 _ _ |0 StatID:(DE-HGF)0010
|a JCR/ISI refereed
920 1 _ |k IBG-3
|l Agrosphäre
|g IBG
|0 I:(DE-Juel1)IBG-3-20101118
|x 0
970 _ _ |a VDB:(DE-Juel1)124805
980 _ _ |a VDB
980 _ _ |a ConvertedRecord
980 _ _ |a journal
980 _ _ |a I:(DE-Juel1)IBG-3-20101118
980 _ _ |a UNRESTRICTED


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