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首页> 外文期刊>Reviews of environmental contamination and toxicology >Biodegradation of perfluorinated compounds.
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Biodegradation of perfluorinated compounds.

机译:全氟化合物的生物降解。

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The information available in the literature provides evidence for the biodegradation of some poly- and per-fluorinated compounds, but such biodegradation is incomplete and may not result in mineralization. Recent publications have demonstrated that 8:2 fluorotelomer alcohol, for example, can be degraded by bacteria from soil and wastewater treatment plants to perfluorooctanoic acid. Similarly, 2-N-ethyl(perfluorooctane sulfonamido)ethanol can be degraded by wastewater treatment sludge to perfluorooctanesulfonate. It is presently unclear whether these two products are degraded further. Therefore, the question remains as to whether there is a potential for defluorination and biodegradation of PFCs that contributes significantly to their environmental fate. The lack of mineralization observed is probably caused by the stability of the C-F bond, although there are examples of microbially catalyzed defluorination reactions. As is the case with reductive dechlorination or debromination, reductive defluorination is energetically favorable under anaerobic conditions and releases more energy than that available from sulfate reduction or methanogenesis. Consequently, we should consider the possibility that bacteria will adapt to utilize this source of energy, although evolving mechanisms to overcome the kinetic barriers to degradation of these compounds may take some time. The fact that such reactions are absent for some PFCs, to date, may be because too little time has passed for microorganisms to adapt to these potential substrates. Hence, the situation may be comparable to that of chlorinated organic compounds several decades ago. For many years, organochlorine compounds were considered to be catabolically recalcitrant; today, reductive chlorination reactions of many organochlorines, including PCBs and dioxins, are regularly observed in anaerobic environments. Hence, it is opportune and important to continue studying the potential degradation of perfluorinated compounds in carefully designed experiments with either microbial populations from contaminated sites or cultures of bacteria known to dehalogenate chlorinated compounds.
机译:文献中提供的信息为某些多氟化和全氟化化合物的生物降解提供了证据,但是这种生物降解是不完全的,可能不会导致矿化。最近的出版物表明,例如8:2的氟代端粒醇可被土壤和废水处理厂中的细菌降解为全氟辛酸。类似地,可以通过废水处理污泥将2-N-乙基(全氟辛烷磺酰胺基)乙醇降解为全氟辛烷磺酸盐。目前尚不清楚这两种产物是否进一步降解。因此,问题仍然在于,PFC是否有可能发生脱氟和生物降解,从而对其环境命运产生重大影响。尽管存在微生物催化的脱氟反应的实例,但观察到的缺乏矿化可能是由C-F键的稳定性引起的。与还原性脱氯或脱溴作用一样,在厌氧条件下还原性脱氟在能量上是有利的,并且比硫酸盐还原或甲烷化产生的能量释放更多的能量。因此,我们应该考虑细菌将适应利用这种能量的可能性,尽管克服这些物质降解动力学障碍的进化机制可能需要一些时间。迄今为止,某些PFC尚无此类反应的事实,可能是因为微生物经过的时间太短,无法适应这些潜在的底物。因此,这种情况可能与几十年前的氯化有机化合物相当。多年以来,有机氯化合物被认为是分解代谢难降解的。如今,在厌氧环境中经常观察到许多有机氯的还原性氯化反应,包括多氯联苯和二恶英。因此,在精心设计的实验中继续研究全氟化合物的潜在降解是合适的,这很重要,无论是来自受污染部位的微生物种群,还是已知会使氯化化合物脱卤的细菌培养物。

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