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脱硫肠状菌将1,1,2-三氯乙烷解毒为乙烯及其功能性还原酶基因的鉴定

Detoxification of 1,1,2-trichloroethane to ethene by desulfitobacterium and identification of its functional reductase gene.

作者信息

Zhao Siyan, Ding Chang, He Jianzhong

机构信息

Department of Civil and Environmental Engineering, National University of Singapore, Singapore, 117576, Singapore.

出版信息

PLoS One. 2015 Apr 2;10(3):e0119507. doi: 10.1371/journal.pone.0119507. eCollection 2015.

DOI:10.1371/journal.pone.0119507
PMID:25835017
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC4383557/
Abstract

1,1,2-trichloroethane (1,1,2-TCA) has become a common groundwater pollutant due to historically extensive utilization, improper disposal, as well as from incomplete dechlorination of 1,1,2,2-tetrachloroethane. Currently, limited information is available on microbial detoxification of 1,1,2-TCA. Desulfitobacterium sp. strain PR, which was isolated from an anaerobic bioreactor maintained to dechlorinate chloroethenes/ethanes, exhibited the capacity to dechlorinate 1,1,1-trichloroethane and chloroform. In this study, the dechlorinating ability of strain PR was further explored. Strain PR showed the capability to dechlorinate 1,1,2-TCA (~1.12 mM) predominantly to 1,2-dichloroethane (1,2-DCA) and chloroethane, and to trace amounts of vinyl chloride and ethene within 20 days. Strain PR coupled growth with dechlorination of 1,1,2-TCA to 1,2-DCA, while no cell growth was observed with dechlorination of 1,2-DCA to chloroethane. Later, through transcriptomic and enzymatic analysis, the reductive dehalogenase CtrA, which was previously reported to be responsible for 1,1,1-trichloroethane and chloroform dechlorination, was identified as the 1,1,2-TCA reductive dehalogenase. Since trichloroethene (TCE) is usually co-contaminated with 1,1,2-TCA, a co-culture containing Dehalococcoides mccartyi strain 11a capable of detoxifying TCE and 1,2-DCA and strain PR was established. Interestingly, this co-culture dechlorinated 1,1,2-TCA and TCE to the non-toxic end-product ethene within 48 days without chloroethane production. This novel pathway avoids production of the carcinogenic intermediate dechlorination product vinyl chloride, providing a more environmentally friendly strategy to treat 1,1,2-TCA.

摘要

1,1,2-三氯乙烷(1,1,2-TCA)由于历史上的广泛使用、不当处置以及1,1,2,2-四氯乙烷的不完全脱氯,已成为一种常见的地下水污染物。目前,关于1,1,2-TCA微生物解毒的信息有限。从维持氯乙烯/乙烷脱氯的厌氧生物反应器中分离出的脱硫脱硫弧菌属菌株PR,表现出对1,1,1-三氯乙烷和氯仿的脱氯能力。在本研究中,进一步探索了菌株PR的脱氯能力。菌株PR能够在20天内将1,1,2-TCA(约1.12 mM)主要脱氯为1,2-二氯乙烷(1,2-DCA)和氯乙烷,并产生痕量的氯乙烯和乙烯。菌株PR将1,1,2-TCA脱氯为1,2-DCA的过程与生长耦合,而将1,2-DCA脱氯为氯乙烷的过程未观察到细胞生长。后来,通过转录组学和酶分析,先前报道负责1,1,1-三氯乙烷和氯仿脱氯的还原脱卤酶CtrA被鉴定为1,1,2-TCA还原脱卤酶。由于三氯乙烯(TCE)通常与1,1,2-TCA共同污染,建立了一种共培养体系,其中包含能够解毒TCE和1,2-DCA的麦氏脱卤球菌属菌株11a和菌株PR。有趣的是,这种共培养体系在48天内将1,1,2-TCA和TCE脱氯为无毒终产物乙烯,且不产生氯乙烷。这种新途径避免了致癌中间脱氯产物氯乙烯的产生,为处理1,1,2-TCA提供了一种更环保的策略。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/06a5/4383557/d375f037a524/pone.0119507.g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/06a5/4383557/ca8218cc73d2/pone.0119507.g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/06a5/4383557/eae9c4709e84/pone.0119507.g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/06a5/4383557/fb90c28fb51e/pone.0119507.g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/06a5/4383557/049051cbcb12/pone.0119507.g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/06a5/4383557/77fd5de95389/pone.0119507.g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/06a5/4383557/d375f037a524/pone.0119507.g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/06a5/4383557/ca8218cc73d2/pone.0119507.g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/06a5/4383557/eae9c4709e84/pone.0119507.g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/06a5/4383557/fb90c28fb51e/pone.0119507.g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/06a5/4383557/049051cbcb12/pone.0119507.g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/06a5/4383557/77fd5de95389/pone.0119507.g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/06a5/4383557/d375f037a524/pone.0119507.g006.jpg

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