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首页> 外文期刊>Journal of microbiology and biotechnology >Anaerobic Degradation of cis-1,2-Dichloroethylene by Cultures Enriched from a Landfill Leachate Sediment
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Anaerobic Degradation of cis-1,2-Dichloroethylene by Cultures Enriched from a Landfill Leachate Sediment

机译:通过垃圾填埋液沉积物富集的培养物厌氧降解顺式-1,2-二氯乙烯

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The production of microbiologically enriched cultures that degrade cis-1,2-dichlorethylene (DCE) under anaerobic conditions was investigated. Among 80 environmental samples, 19 displayed significant degradation of 10 μM cis-DCE during 1 month of anaerobic incubation, and one sediment sample collected at a landfill area (Nanji-do,Seoul, Korea) showed the greatest degradation (94%). When this sediment culture was subcultured repeatedly, the ability to degrade cis-DCE gradually decreased. However, under Fe(III)-reducing conditions, cis-DCE degradation by the subculture was found to be maintained effectively. In the Fe(III)-reducing subculture, vinyl chloride (VC) was also degraded at the same extent as cis-DCE. No accumulation of VC during the cis-DCE degradation was observed. Thus, Fe(III)-reducing microbes might be involved in the anaerobic degradation of the chlorinated ethenes. However, the subcultures established with Fe(III) could function even in the absence of Fe(III), showing that the degradation of cis-DCE and VC was not directly coupled with the Fe(III) reduction. Consequently, the two series of enrichment cultures could not be obtained that degrade both cis-DCE and VC in the presence or absence of Fe(III). Considering the lack of VC accumulation, both cultures reported herein may involve interesting mechanism(s) for the microbial remediation of environments contaminated with chlorinated ethenes. A number of fermentative reducers (microbes) which are known to reduce Fe(III) during their anaerobic growth are potential candidates involved in cis-DCE degradation in the presence and absence of Fe(III).
机译:研究了在厌氧条件下降解CIS-1,2-二氯乙烯(DCE)的微生物富集的培养物。在80个环境样品中,在1个月的厌氧孵育过程中,19次显示出10μm的CIS-DCE,并且在垃圾填埋场(Nanji-Do,首尔,韩国)收集了一个沉积物样品,显示出最大的降解(94%)。当重复转移这种沉积物培养物时,降解CIS-DCE的能力逐渐降低。然而,在Fe(III)的-READIENDION的条件下,发现亚培养的顺式DCE降解被效果保持。在Fe(III) - 再培养中,氯乙烯(Vc)也与CIS-DCE相同程度地降解。观察到在CIS-DCE降解期间没有VC的积累。因此,Fe(III)的微生物可能参与氯化替代的厌氧降解。然而,即使在没有Fe(III)的情况下,用Fe(III)建立的潜水率也可以起作用,表明CIS-DCE和VC的降解没有与Fe(III)还原联系。因此,不能获得两种富集培养物,以在Fe(III)的存在或不存在下降解CIS-DCE和VC。考虑到缺乏VC积累,本文报告的这两种培养物可能涉及有趣的机制,用于含有氯化替代品污染的环境的微生物修复。已知许多已知在厌氧生长期间减少Fe(III)的发酵还原剂(Microbes)是在存在和不存在Fe(III)的情况下参与CIS-DCE降解的潜在候选者。

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