Lovley D R
Water Resources Division, U.S. Geological Survey, Reston, Virginia 22092.
Microbiol Rev. 1991 Jun;55(2):259-87. doi: 10.1128/mr.55.2.259-287.1991.
The oxidation of organic matter coupled to the reduction of Fe(III) or Mn(IV) is one of the most important biogeochemical reactions in aquatic sediments, soils, and groundwater. This process, which may have been the first globally significant mechanism for the oxidation of organic matter to carbon dioxide, plays an important role in the oxidation of natural and contaminant organic compounds in a variety of environments and contributes to other phenomena of widespread significance such as the release of metals and nutrients into water supplies, the magnetization of sediments, and the corrosion of metal. Until recently, much of the Fe(III) and Mn(IV) reduction in sedimentary environments was considered to be the result of nonenzymatic processes. However, microorganisms which can effectively couple the oxidation of organic compounds to the reduction of Fe(III) or Mn(IV) have recently been discovered. With Fe(III) or Mn(IV) as the sole electron acceptor, these organisms can completely oxidize fatty acids, hydrogen, or a variety of monoaromatic compounds. This metabolism provides energy to support growth. Sugars and amino acids can be completely oxidized by the cooperative activity of fermentative microorganisms and hydrogen- and fatty-acid-oxidizing Fe(III) and Mn(IV) reducers. This provides a microbial mechanism for the oxidation of the complex assemblage of sedimentary organic matter in Fe(III)- or Mn(IV)-reducing environments. The available evidence indicates that this enzymatic reduction of Fe(III) or Mn(IV) accounts for most of the oxidation of organic matter coupled to reduction of Fe(III) and Mn(IV) in sedimentary environments. Little is known about the diversity and ecology of the microorganisms responsible for Fe(III) and Mn(IV) reduction, and only preliminary studies have been conducted on the physiology and biochemistry of this process.
与铁(III)或锰(IV)还原相耦合的有机物氧化是水生沉积物、土壤和地下水中最重要的生物地球化学反应之一。这一过程可能是有机物氧化为二氧化碳的首个具有全球意义的机制,在多种环境中对天然和污染有机化合物的氧化起着重要作用,并促成了其他具有广泛意义的现象,如金属和营养物质向水源中的释放、沉积物的磁化以及金属的腐蚀。直到最近,沉积环境中大部分铁(III)和锰(IV)的还原都被认为是非酶促过程的结果。然而,最近发现了能够有效地将有机化合物氧化与铁(III)或锰(IV)还原相耦合的微生物。以铁(III)或锰(IV)作为唯一电子受体,这些生物体能完全氧化脂肪酸、氢气或多种单芳香族化合物。这种代谢作用提供能量以支持生长。糖类和氨基酸可通过发酵微生物与氧化氢气和脂肪酸的铁(III)和锰(IV)还原菌的协同活动而被完全氧化。这为在铁(III)或锰(IV)还原环境中沉积有机物的复杂组合的氧化提供了一种微生物机制。现有证据表明,这种铁(III)或锰(IV)的酶促还原在沉积环境中与铁(III)和锰(IV)还原相耦合的有机物氧化中占了大部分。对于负责铁(III)和锰(IV)还原的微生物的多样性和生态学知之甚少,并且仅对这一过程的生理学和生物化学进行了初步研究。