2015
DOI: 10.1007/s11274-015-1817-2
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Enhancement of L-2-haloacid dehalogenase expression in Pseudomonas stutzeri DEH138 based on the different substrate specificity between dehalogenase-producing bacteria and their dehalogenases

Abstract: There was no direct correlation in substrate specificity between the metabolism of Pseudomonas stutzeri DEH138 and its corresponding dehalogenase. Dehalogenase substrates that could be dehalogenated might not be degraded by DEH138 or vice versa. Basing on this, different approaches to enhance L-2-haloacid dehalogenase (L-DEX) production in DEH138 via the combination of non-halogenated compounds with different inducers were applied. The optimum approach to obtain more L-DEX from DEH138 was the combination of DL… Show more

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Cited by 6 publications
(3 citation statements)
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References 15 publications
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“…397 The genus Pseudomonas presented two predominantly active OTUs in all analyzed samples, 411 belonging to Pseudomonas lingynensis (6-57% RA, similarity of 99.6%) and Pseudomonas 412 stutzeri (1-10% RA, similarity of 99-100%) ( Table A4). P. stutzeri constituted 9-10% RA ( Table 413 As aerobic or facultative-anaerobic bacteria were present in the microcosm, oxygen availability 432 as a co-substrate could be explained by: (i) the occurrence of nitrite-driven processes that would 433 supplement molecular oxygen to monooxygenase activity (Ettwig et al, 2010) as well as to the 434 cometabolism for the degradation of halomethanes; ii) the availability of O2 from chlorite 435 dismutase activity in P. stutzeri (Cladera et al, 2006;Schaffner et al, 2015); iii) in the presence 436 of L-2-haloacid dehalogenases, known to obtain an oxygen atom of the solvent water, in detected 437 species including A. aquaticus (Kumar et al, 2016), P. stutzeri (Wang et al, 2015), and Rhizobium 438 sp. RC1 (Adamu et al, 2016) (the last genus with 1-3% RA in all analyzed samples).…”
Section: Active Microbial Populations Assessment 376mentioning
confidence: 99%
“…397 The genus Pseudomonas presented two predominantly active OTUs in all analyzed samples, 411 belonging to Pseudomonas lingynensis (6-57% RA, similarity of 99.6%) and Pseudomonas 412 stutzeri (1-10% RA, similarity of 99-100%) ( Table A4). P. stutzeri constituted 9-10% RA ( Table 413 As aerobic or facultative-anaerobic bacteria were present in the microcosm, oxygen availability 432 as a co-substrate could be explained by: (i) the occurrence of nitrite-driven processes that would 433 supplement molecular oxygen to monooxygenase activity (Ettwig et al, 2010) as well as to the 434 cometabolism for the degradation of halomethanes; ii) the availability of O2 from chlorite 435 dismutase activity in P. stutzeri (Cladera et al, 2006;Schaffner et al, 2015); iii) in the presence 436 of L-2-haloacid dehalogenases, known to obtain an oxygen atom of the solvent water, in detected 437 species including A. aquaticus (Kumar et al, 2016), P. stutzeri (Wang et al, 2015), and Rhizobium 438 sp. RC1 (Adamu et al, 2016) (the last genus with 1-3% RA in all analyzed samples).…”
Section: Active Microbial Populations Assessment 376mentioning
confidence: 99%
“…P. aeruginosa HS9 could degrade 69% HBCDs in the MSM in 14 days, but removed 88% HBCDs in the plant soil (Huang et al 2019). It indicated that the different factor in growing environment of bacteria could affect their transformation ability, in corresponding to biodehalogenation of other organic halogenated compounds (Wang et al 2015). Diastereoisomers-speci c biotransformation of HBCD was also observed in other functional strains.…”
Section: Discussionmentioning
confidence: 92%
“…[3], in addition to causing serious environmental pollution owing to their toxicity, their toxic breakdown products, persistence and bioaccumulation in the food chain and water bodies [4]. These compounds are poisonous and very difficult to degrade [5].…”
Section: Introductionmentioning
confidence: 99%