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利用甲烷的混合培养物对氯乙烯的生物降解

Biodegradation of chlorinated ethenes by a methane-utilizing mixed culture.

作者信息

Fogel M M, Taddeo A R, Fogel S

出版信息

Appl Environ Microbiol. 1986 Apr;51(4):720-4. doi: 10.1128/aem.51.4.720-724.1986.

Abstract

Chlorinated ethenes are toxic substances which are widely distributed groundwater contaminants and are persistent in the subsurface environment. Reports on the biodegradation of these compounds under anaerobic conditions which might occur naturally in groundwater show that these substances degrade very slowly, if at all. Previous attempts to degrade chlorinated ethenes aerobically have produced conflicting results. A mixed culture containing methane-utilizing bacteria was obtained by methane enrichment of a sediment sample. Biodegradation experiments carried out in sealed culture bottles with radioactively labeled trichloroethylene (TCE) showed that approximately half of the radioactive carbon had been converted to 14CO2 and bacterial biomass. In addition to TCE, vinyl chloride and vinylidene chloride could be degraded to products which are not volatile chlorinated substances and are therefore likely to be further degraded to CO2. Two other chlorinated ethenes, cis and trans-1,2-dichloroethylene, were shown to degrade to chlorinated products, which appeared to degrade further. A sixth chlorinated ethene, tetrachloroethylene, was not degraded by the methane-utilizing culture under these conditions. The biodegradation of TCE was inhibited by acetylene, a specific inhibitor of methane oxidation by methanotrophs. This observation supported the hypothesis that a methanotroph is responsible for the observed biodegradations.

摘要

氯乙烯是有毒物质,是广泛分布于地下水中的污染物,且在地下环境中具有持久性。关于这些化合物在地下水中可能自然发生的厌氧条件下的生物降解的报告表明,这些物质即使会降解,降解速度也非常缓慢。以前在需氧条件下对氯乙烯进行降解的尝试产生了相互矛盾的结果。通过对沉积物样本进行甲烷富集,获得了一种含有利用甲烷细菌的混合培养物。在装有放射性标记的三氯乙烯(TCE)的密封培养瓶中进行的生物降解实验表明,大约一半的放射性碳已转化为14CO2和细菌生物量。除了TCE,氯乙烯和偏二氯乙烯可以降解为非挥发性氯化物质的产物,因此可能会进一步降解为CO2。另外两种氯乙烯,顺式和反式1,2 - 二氯乙烯,被证明可以降解为氯化产物,这些产物似乎会进一步降解。在这些条件下,第六种氯乙烯,四氯乙烯,未被利用甲烷的培养物降解。TCE的生物降解受到乙炔的抑制,乙炔是甲烷氧化菌氧化甲烷的特异性抑制剂。这一观察结果支持了甲烷氧化菌对观察到的生物降解负责的假设。

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