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Dual C–Br Isotope Fractionation Indicates Distinct Reductive Dehalogenation Mechanisms of 1,2-Dibromoethane in Dehalococcoides- and Dehalogenimonas-Containing Cultures

[Image: see text] Brominated organic compounds such as 1,2-dibromoethane (1,2-DBA) are highly toxic groundwater contaminants. Multi-element compound-specific isotope analysis bears the potential to elucidate the biodegradation pathways of 1,2-DBA in the environment, which is crucial information to a...

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Detalles Bibliográficos
Autores principales: Palau, Jordi, Trueba-Santiso, Alba, Yu, Rong, Mortan, Siti Hatijah, Shouakar-Stash, Orfan, Freedman, David L., Wasmund, Kenneth, Hunkeler, Daniel, Marco-Urrea, Ernest, Rosell, Monica
Formato: Online Artículo Texto
Lenguaje:English
Publicado: American Chemical Society 2023
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC9910042/
https://www.ncbi.nlm.nih.gov/pubmed/36700533
http://dx.doi.org/10.1021/acs.est.2c07137
Descripción
Sumario:[Image: see text] Brominated organic compounds such as 1,2-dibromoethane (1,2-DBA) are highly toxic groundwater contaminants. Multi-element compound-specific isotope analysis bears the potential to elucidate the biodegradation pathways of 1,2-DBA in the environment, which is crucial information to assess its fate in contaminated sites. This study investigates for the first time dual C–Br isotope fractionation during in vivo biodegradation of 1,2-DBA by two anaerobic enrichment cultures containing organohalide-respiring bacteria (i.e., either Dehalococcoides or Dehalogenimonas). Different ε(bulk)(C) values (−1.8 ± 0.2 and −19.2 ± 3.5‰, respectively) were obtained, whereas their respective ε(bulk)(Br) values were lower and similar to each other (−1.22 ± 0.08 and −1.2 ± 0.5‰), leading to distinctly different trends (Λ(C–Br) = Δδ(13)C/Δδ(81)Br ≈ ε(bulk)(C)/ε(bulk)(Br)) in a dual C–Br isotope plot (1.4 ± 0.2 and 12 ± 4, respectively). These results suggest the occurrence of different underlying reaction mechanisms during enzymatic 1,2-DBA transformation, that is, concerted dihaloelimination and nucleophilic substitution (S(N)2-reaction). The strongly pathway-dependent Λ(C–Br) values illustrate the potential of this approach to elucidate the reaction mechanism of 1,2-DBA in the field and to select appropriate ε(bulk)(C) values for quantification of biodegradation. The results of this study provide valuable information for future biodegradation studies of 1,2-DBA in contaminated sites.