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(Sphingobium spp.)好氧生物降解六氯环己烷过程中的对映体碳稳定同位素分馏

Enantioselective carbon stable isotope fractionation of hexachlorocyclohexane during aerobic biodegradation by Sphingobium spp.

机构信息

Department of Isotope Biogeochemistry, Helmholtz Centre for Environmental Research - UFZ , Permoserstraße 15, 04318, Leipzig, Germany.

出版信息

Environ Sci Technol. 2013 Oct 15;47(20):11432-9. doi: 10.1021/es402197s. Epub 2013 Sep 25.

Abstract

Carbon isotope fractionation was investigated for the biotransformation of γ- and α- hexachlorocyclohexane (HCH) as well as enantiomers of α-HCH using two aerobic bacterial strains: Sphingobium indicum strain B90A and Sphingobium japonicum strain UT26. Carbon isotope enrichment factors (ε(c)) for γ-HCH (ε(c) = -1.5 ± 0.1 ‰ and -1.7 ± 0.2 ‰) and α-HCH (ε(c) = -1.0 ± 0.2 ‰ and -1.6 ± 0.3 ‰) were similar for both aerobic strains, but lower in comparison with previously reported values for anaerobic γ- and α-HCH degradation. Isotope fractionation of α-HCH enantiomers was higher for (+) α-HCH (ε(c) = -2.4 ± 0.8 ‰ and -3.3 ± 0.8 ‰) in comparison to (-) α-HCH (ε(c) = -0.7 ± 0.2 ‰ and -1.0 ± 0.6 ‰). The microbial fractionation between the α-HCH enantiomers was quantified by the Rayleigh equation and enantiomeric fractionation factors (ε(e)) for S. indicum strain B90A and S. japonicum strain UT26 were -42 ± 16% and -22 ± 6%, respectively. The extent and range of isomer and enantiomeric carbon isotope fractionation of HCHs with Sphingobium spp. suggests that aerobic biodegradation of HCHs can be monitored in situ by compound-specific stable isotope analysis (CSIA) and enantiomer-specific isotope analysis (ESIA). In addition, enantiomeric fractionation has the potential as a complementary approach to CSIA and ESIA for assessing the biodegradation of α-HCH at contaminated field sites.

摘要

研究了两种好氧细菌菌株——印度鞘氨醇单胞菌 B90A 和日本鞘氨醇单胞菌 UT26 对γ-和α-六氯环己烷(HCH)以及α-HCH 对映异构体的生物转化的碳同位素分馏作用。γ-HCH(ε(c) = -1.5 ± 0.1 ‰和-1.7 ± 0.2 ‰)和α-HCH(ε(c) = -1.0 ± 0.2 ‰和-1.6 ± 0.3 ‰)的碳同位素富集因子(ε(c))对于两种好氧菌株相似,但与先前报道的厌氧γ-HCH 和α-HCH 降解值相比有所降低。与 (-) α-HCH(ε(c) = -0.7 ± 0.2 ‰和-1.0 ± 0.6 ‰)相比,α-HCH 对映异构体的同位素分馏作用更高(ε(c) = -2.4 ± 0.8 ‰和-3.3 ± 0.8 ‰)。通过瑞利方程定量了微生物在α-HCH 对映异构体之间的分馏作用,并且 S. indicum 菌株 B90A 和 S. japonicum 菌株 UT26 的对映体分馏因子(ε(e))分别为-42 ± 16%和-22 ± 6%。Sphingobium spp.对 HCHs 的异构体和对映体碳同位素分馏的程度和范围表明,好氧生物降解 HCHs 可以通过化合物特异性稳定同位素分析(CSIA)和对映体特异性同位素分析(ESIA)进行原位监测。此外,对映体分馏具有作为 CSIA 和 ESIA 的补充方法的潜力,用于评估污染现场的α-HCH 的生物降解。

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