Heker Isabelle, Samak Nadia A, Kong Yachao, Meckenstock Rainer U
Institute for Environmental Microbiology and Biotechnology, Aquatic Microbiology, Faculty of Chemistry, University of Duisburg-Essen, Essen, Germany.
Appl Environ Microbiol. 2025 Apr 23;91(4):e0226824. doi: 10.1128/aem.02268-24. Epub 2025 Apr 2.
Polycyclic aromatic hydrocarbons (PAHs) are ubiquitous and toxic pollutants in the environment that are mostly introduced through anthropogenic activities. They are very stable with low bioavailability and, because aerobic degradation is mostly limited in aquifers and sediments, often persist in anoxic systems. In this review, we elucidate the recent advances in PAH degradation by anaerobic, mostly sulfate-reducing cultures. The best-studied compound is naphthalene, the smallest and simplest PAH, which often serves as a model compound for anaerobic PAH degradation. In recent years, three-ring PAHs have also shifted into focus, using phenanthrene as a representative compound. Anaerobic degradation of PAHs has to overcome several biochemical problems. First, non-substituted PAHs have to be activated by carboxylation, which is chemically challenging and proposed to involve a 1,3-cycloaddition with a UbiD-like carboxylase and a prenylated flavin cofactor. The second key reaction is to overcome the resonance energy of the ring system, which is performed by consecutive two-electron reduction steps involving novel type III aryl-CoA reductases belonging to the old-yellow enzyme family. In naphthalene degradation, a type I aryl-CoA reductase is also involved in reducing a benzene ring structure. The third key reaction is the ring cleavage, involving β-oxidation-like reactions in cleaving ring I of naphthalene. Ring II, however, is opened by a novel lyase reaction at a tertiary, hydroxylated carbon atom. These principles are explained using examples of anaerobic naphthalene and phenanthrene degradation to give an overview of recent advances, from the initial activation of the molecules to the complete degradation to CO.
多环芳烃(PAHs)是环境中普遍存在的有毒污染物,主要通过人为活动进入环境。它们非常稳定,生物可利用性低,而且由于含水层和沉积物中的好氧降解大多受到限制,所以常常在缺氧系统中持续存在。在本综述中,我们阐述了通过厌氧(主要是硫酸盐还原培养)降解多环芳烃的最新进展。研究最多的化合物是萘,它是最小且最简单的多环芳烃,常作为厌氧多环芳烃降解的模型化合物。近年来,三环多环芳烃也成为研究重点,以菲作为代表性化合物。多环芳烃的厌氧降解必须克服几个生化问题。首先,未取代的多环芳烃必须通过羧化作用被激活,这在化学上具有挑战性,据推测涉及与类泛素D羧化酶和异戊二烯化黄素辅因子的1,3 - 环加成反应。第二个关键反应是克服环系统的共振能,这是通过连续的双电子还原步骤来实现的,这些步骤涉及属于老黄酶家族的新型III型芳基 - 辅酶A还原酶。在萘的降解过程中,I型芳基 - 辅酶A还原酶也参与苯环结构的还原。第三个关键反应是环裂解,在萘的环I裂解过程中涉及类似β - 氧化的反应。然而,环II是通过一种新型裂合酶反应在一个叔羟基化碳原子处打开的。本文通过厌氧萘和菲降解的例子解释了这些原理,以概述从分子的初始激活到完全降解为二氧化碳的最新进展。