DiStefano T D, Gossett J M, Zinder S H
School of Civil and Environmental Engineering, Cornell University, Ithaca, New York 14853.
Appl Environ Microbiol. 1991 Aug;57(8):2287-92. doi: 10.1128/aem.57.8.2287-2292.1991.
Tetrachloroethene, also known as perchloroethylene (PCE), is a common groundwater contaminant throughout the United States. The incomplete reductive dechlorination of PCE--resulting in accumulations of trichloroethene, dichloroethene isomers, and/or vinyl chloride--has been observed by many investigators in a wide variety of methanogenic environments. Previous mixed-culture studies have demonstrated that complete dechlorination to ethene is possible, although the final dechlorination step from vinyl chloride to ethene is rate limiting, with significant levels of vinyl chloride typically persisting. In this study, anaerobic methanol-PCE enrichment cultures which proved capable of dechlorinating high concentrations PCE to ethene were developed. Added concentrations of PCE as high as 550 microM (91-mg/liter nominal concentration; approximately 55-mg/liter actual aqueous concentration) were routinely dechlorinated to 80% ethene and 20% vinyl chloride within 2 days at 35 degrees C. The methanol level used was approximately twice that needed for complete dechlorination of PCE to ethene. The observed transformations occurred in the absence of methanogenesis, which was apparently inhibited by the high concentrations of PCE. When incubation was allowed to proceed for as long as 4 days, virtually complete conversion of PCE to ethene resulted, with less than 1% persisting as vinyl chloride. An electron balance demonstrated that methanol consumption was completely accounted for by dechlorination (31%) and acetate production (69%). The high volumetric rates of PCE dechlorination (up to 275 mumol/liter/day) and the relatively large fraction (ca. one-third) of the supplied electron donor used for dechlorination suggest that reductive dechlorination could be exploited for bioremediation of PCE-contaminated sites.
四氯乙烯,也被称为全氯乙烯(PCE),是美国各地常见的地下水污染物。许多研究人员在各种各样的产甲烷环境中都观察到了PCE的不完全还原脱氯现象,这导致了三氯乙烯、二氯乙烯异构体和/或氯乙烯的积累。以往的混合培养研究表明,完全脱氯生成乙烯是可能的,尽管从氯乙烯到乙烯的最终脱氯步骤是限速步骤,通常会有大量的氯乙烯残留。在本研究中,开发了厌氧甲醇-PCE富集培养物,该培养物能够将高浓度的PCE脱氯生成乙烯。在35℃下,添加浓度高达550微摩尔(标称浓度91毫克/升;实际水相浓度约55毫克/升)的PCE通常在2天内被脱氯,生成80%的乙烯和20%的氯乙烯。所用的甲醇水平约为将PCE完全脱氯生成乙烯所需水平的两倍。观察到的转化过程是在没有产甲烷作用的情况下发生的,这显然受到高浓度PCE的抑制。当培养时间长达4天时,PCE几乎完全转化为乙烯,残留的氯乙烯不到1%。电子平衡表明,甲醇的消耗完全由脱氯(31%)和乙酸盐生成(69%)来解释。PCE的高脱氯体积速率(高达275微摩尔/升/天)以及用于脱氯的供电子体相对较大的比例(约三分之一)表明,还原脱氯可用于受PCE污染场地的生物修复。