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Desulfitobacterium contributes to the microbial transformation of 2,4,5‐T by methanogenic enrichment cultures from a Vietnamese active landfill.

Authors :
Lechner, Ute
Al‐Fathi, Hassan
Schwoch, Stefan
Franke, Stefan
Gerlach, Michelle‐Sophie
Türkowsky, Dominique
Bergen, Martin
Jehmlich, Nico
Dinh, Thi Thu Hang
Dang, Thi Cam Ha
Koch, Mandy
Source :
Microbial Biotechnology; Nov2018, Vol. 11 Issue 6, p1137-1156, 20p
Publication Year :
2018

Abstract

Summary: The herbicide 2,4,5‐trichlorophenoxyacetic acid (2,4,5‐T) was a major component of Agent Orange, which was used as a defoliant in the Vietnam War. Little is known about its degradation under anoxic conditions. Established enrichment cultures using soil from an Agent Orange bioremediation plant in southern Vietnam with pyruvate as potential electron donor and carbon source were shown to degrade 2,4,5‐T via ether cleavage to 2,4,5‐trichlorophenol (2,4,5‐TCP), which was further dechlorinated to 3,4‐dichlorophenol. Pyruvate was initially fermented to hydrogen, acetate and propionate. Hydrogen was then used as the direct electron donor for ether cleavage of 2,4,5‐T and subsequent dechlorination of 2,4,5‐TCP. 16S rRNA gene amplicon sequencing indicated the presence of bacteria and archaea mainly belonging to the Firmicutes, Bacteroidetes, Spirochaetes, Chloroflexi and Euryarchaeota. Desulfitobacterium hafniense was identified as the dechlorinating bacterium. Metaproteomics of the enrichment culture indicated higher protein abundances of 60 protein groups in the presence of 2,4,5‐T. A reductive dehalogenase related to RdhA3 of D. hafniense showed the highest fold change, supporting its function in reductive dehalogenation of 2,4,5‐TCP. Despite an ether‐cleaving enzyme not being detected, the inhibition of ether cleavage but not of dechlorination, by 2‐bromoethane sulphonate, suggested that the two reactions are catalysed by different organisms. Anaerobic enrichment cultures from an Agent Orange‐treating active landfill degraded 2,4,5‐T via cleavage of the ether bond and subsequent reductive dechlorination. 16S rRNA gene amplicon sequencing and metaproteomics revealed the presence of diverse fermenting bacteria, which provided the community with hydrogen.The latter served as electron donor for both 2,4,5‐T degradation steps. Whereas the ether‐cleaving organism could not be identified, Desulfitobacterium hafniense harbouring the RdhA3 reductive dehalogenase was indicated as the reductively dehalogenating bacterium. [ABSTRACT FROM AUTHOR]

Details

Language :
English
ISSN :
17517907
Volume :
11
Issue :
6
Database :
Complementary Index
Journal :
Microbial Biotechnology
Publication Type :
Academic Journal
Accession number :
132532436
Full Text :
https://doi.org/10.1111/1751-7915.13301