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氧化还原条件对地表水沉积物中甲基叔丁基醚生物降解的影响。

Effect of redox conditions on MTBE biodegradation in surface water sediments.

作者信息

Bradley P M, Chapelle F H, Landmeyer J E

机构信息

US Geological Survey, Columbia, South Carolina 29210-7651, USA.

出版信息

Environ Sci Technol. 2001 Dec 1;35(23):4643-7. doi: 10.1021/es010794x.

Abstract

Microbial degradation of methyl tert-butyl ether (MTBE) was observed in surface water-sediment microcosms under anaerobic conditions. The efficiency and products of anaerobic MTBE biodegradation were dependent on the predominant terminal electron-accepting conditions. In the presence of substantial methanogenic activity, MTBE biodegradation was nominal and involved reduction of MTBE to the toxic product, tert-butyl alcohol (TBA). In the absence of significant methanogenic activity, accumulation of [14C]TBA generally decreased, and mineralization of [U-14C]MTBE to 14CO2 generally increased as the oxidative potential of the predominant terminal electron acceptor increased in the order of SO4, Fe(III), Mn(IV) < NO3 < O2. Microbial mineralization of MTBE to CO2 under Mn(IV)-or SO4-reducing conditions has not been reported previously. The results of this study indicate that microorganisms inhabiting the sediments of streams and lakes can degrade MTBE effectively under a range of anaerobic terminal electron-accepting conditions. Thus, anaerobic bed sediment microbial processes may provide a significant environmental sink for MTBE in surface water systems throughout the United States.

摘要

在厌氧条件下的地表水 - 沉积物微观世界中观察到了甲基叔丁基醚(MTBE)的微生物降解。厌氧MTBE生物降解的效率和产物取决于主要的末端电子受体条件。在存在大量产甲烷活性的情况下,MTBE生物降解作用微弱,且涉及MTBE还原为有毒产物叔丁醇(TBA)。在不存在显著产甲烷活性的情况下,随着主要末端电子受体的氧化电位按SO4、Fe(III)、Mn(IV) < NO3 < O2的顺序增加,[14C]TBA的积累通常会减少,而[U - 14C]MTBE矿化为14CO2的程度通常会增加。此前尚未报道过在Mn(IV)或SO4还原条件下MTBE向CO2的微生物矿化。本研究结果表明,栖息于溪流和湖泊沉积物中的微生物能够在一系列厌氧末端电子受体条件下有效降解MTBE。因此,厌氧床沉积物微生物过程可能为美国各地地表水系统中的MTBE提供一个重要的环境汇。

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