细菌产黄素类化合物介导的电子传递及对环境污染物的厌氧生物转化研究进展

氧化还原介体能够加速有毒环境污染物的厌氧生物转化。黄素类化合物是一类微生物自身合成分泌的氧化还原介体,其应用可有效地避免外源性介体带来的成本较高及造成二次污染的问题,因此引起了广泛的关注。研究表明,细菌合成的微量黄素类化合物不仅能够作为黄素蛋白的辅酶因子参与偶氮染料、铬酸盐和硝基芳烃等污染物的厌氧生物转化,并且还可以分泌到胞外将电子传递给固态电子受体如含铁矿物和电极等来参与生物修复过程。根据黄素类化合物的功能,本文综述了黄素类化合物的合成与分泌,及其介导的胞内外电子传递和对环境污染物厌氧生物转化的影响,以促进其在实际环境污染物处理中的应用。     

电活性微生物胞外聚合物的特征与应用

电活性微生物是一类能够通过直接接触、导电菌毛或氧化还原介质与电极或者其他细胞进行胞外电子传递的微生物。而在这个过程中,胞外聚合物(extracellular polymeric substances, EPS)扮演着重要的角色。EPS是微生物生长过程中通过细胞裂解、水解分泌的高分子聚合物的混合物,主要由蛋白质、多糖和腐殖质等物质组成。来自电活性微生物的EPS的不同组成成分和特性会对EPS的电活性以及电活性微生物胞外电子传递产生一定的影响,同时在环境应用方面发挥重要作用。因此,为了更全面了解电活性微生物EPS的电活性及其对电活性微生物胞外电子传递的作用,本文总体介绍了电活性微生物EPS的电活性的直接表征方法,再从组成成分、化学性质、物理性质和空间分布4个方面综述了其对EPS电活性的影响及其在电子传递中的作用,介绍了当前电活性微生物EPS在染料废水脱色、重金属吸附、有机污染物的生物转化和渗滤液管理等方面的环境应用,并从表征方法、试验规模和互作机理研究等角度展望了未来的研究方向。     

微生物电合成-电能驱动的CO_2固定

CO_2代表着地球上最广泛的可再生资源,通过生物固碳途径将CO_2转化为有机物,是生产生物燃料和生物基化学品的重要方向,由于能量供给不足和微生物自身生理代谢的限制,生物固碳效率还有待提高.利用电能驱动微生物还原CO_2是实现CO_2高效转化的新策略,被称为微生物电合成.本文从电合成微生物种类、胞外电子传递、电极材料等方面综述了微生物电合成的研究进展,并对微生物电合成的未来研究方向进行了展望.     

生物工程强化微生物电合成转化CO_2的研究进展

微生物电合成(Microbial electrosynthesis,MES)可直接利用电能驱动微生物还原固定CO_2合成多碳化合物,为可再生新能源转化、精细化学品制备和生态环境保护提供新机遇。但是,微生物吸收胞外电极电子速率慢、产物合成效率低和产品品位不高,限制了MES实现工业化应用。在概述阴极电活性微生物吸收胞外电子的分子机制的基础上,重点综述近5年应用生物工程的理论和技术强化MES用于CO_2转化的策略与研究进展,包括改造和调控胞外电子传递通路和胞内代谢途径以及定向构建有限微生物混合培养菌群三方面,阐明了生物工程可有效突破MES中电子传递慢和可用代谢途径相对单一等瓶颈。针对目前生物工程在改进MES所面临的主要问题,从胞外电子传递机理研究、基因工具箱开发、组学技术与现代分析技术联用等角度展望了今后的研究方向。     

基于细胞色素c的胞外电子传递过程

电活性微生物具有独特的胞外电子传递功能,在地球化学循环和环境污染修复中起着重要作用。细胞色素c在电活性微生物胞外电子传递过程中扮演了重要角色,不仅参与直接电子传递途径,还参与电子媒介介导的间接电子传递。其电子传递功能不仅对地球环境中铁、锰、碳等元素的循环具有重要作用,还应用于能源生产、废水处理、生物修复等众多领域,具有良好的应用潜力。本文以电活性微生物的2个模式菌属(希瓦氏菌属和地杆菌属)为例,综述了电活性微生物将电子由胞内转移至胞外的方式和途径,详细阐述了细胞色素c在该胞外电子传递过程中的重要作用,总结了细胞色素c介导的胞外电子传递过程所涉及的分析方法,并对微生物胞外电子传递未来的研究方向提出了展望。     

微生物胞外电子传递过程及其应用研究进展

电活性微生物的胞外电子传递在微生物电合成、矿物生物浸出、生物质能回收及污染物原位修复等方面表现出广阔的应用前景,因而受到研究者们的广泛关注。现综述近年来电活性微生物胞外电子传递过程及其应用的相关研究成果,指出该领域面临的主要问题和发展方向。未来应加强微生物胞外电子传递路径及分子机制等方面的研究,分离筛选更高效的电活性菌种,优化反应器工艺设计,拓宽电活性微生物的应用领域,提高相应设备的效率。     

生物地球化学锰循环中的微生物胞外电子传递机制

微生物是生物地球化学元素循环的重要驱动者,在锰等变价金属元素的氧化还原过程中起着至关重要的作用。近年来,Mn(Ⅲ)的发现以及在一些环境中的广泛存在,丰富了人们对Mn(Ⅲ)以及自然界锰循环过程的认识。研究发现,锰的生物地球化学循环,尤其是锰还原过程,与微生物胞外电子传递紧密相关,且目前已知的5种胞外电子传递机制均与锰还原有关联。因此,本文综述了锰的生物地球化学循环及其意义,并从微生物胞外电子传递的机制、微生物介导锰氧化、微生物介导锰还原等3个方面来介绍参与锰循环的微生物多样性;以及微生物地球化学锰循环的环境意义。对微生物参与锰循环过程的研究不仅可以进一步丰富相关理论,同时也能推动生物除锰、污染物原位修复及生物冶金等应用领域的发展。     

微生物代谢环境难降解性有机物的酶学研究进展

随着人类社会的快速发展,工业化水平不断提高,产生大量的污染物并排放到环境中,给人类的生活和身体健康造成了严重的影响。这些污染物中包含种类繁多的难降解有机物,如多芳香烃(PAHs)、环硝胺类物质(RDX、HMX和CL-20)、多氯联苯(PCBs)及烷烃类化合物等,对自然界的污染危害大。微生物可以消除它们对污染的影响,研究结果表明微生物的代谢或共代谢活动是降解这些物质的有效途径,降解起始阶段需要一些关键酶的参与活动,以氧化还原酶为主。这些氧化还原酶一般与细胞膜上其他的活性组分在一起,形成一个氧化还原系统氧化底物。被氧化的中间物质再通过一系列酶催化继续氧化成三羧酸中间代谢产物被微生物所利用。以下综述了与这些物质降解相关的代谢途径和关键的酶,展望今后在开展这类研究工作时要加强降解微生物的筛选和相关酶学的研究,进一步研究这些污染物的代谢或共代谢途径和机理,为工程化治理环境污染提供依据。     

分子生物学方法提高电活性微生物胞外电子传递效率的研究进展*

微生物细胞与电极之间的胞外电子传递效率是限制微生物电化学技术发展的关键因素,而分子生物学的发展为提高胞外电子传递效率带来了光明前景。从四种具有代表性的纯培养电活性微生物(奥奈达希瓦氏菌、铜绿假单胞菌、硫还原地杆菌和工程大肠杆菌)和混合培养电活性微生物出发,综述了利用分子生物学手段改造几种电活性微生物的研究成果,阐明了针对特异的电活性微生物,如何采取相应的分子生物学手段提高其胞外电子传递的效率,并展望了未来的研究方向。     

奥奈达希瓦氏菌CctA介导周质甲基橙还原的电子传递机理

电活性微生物奥奈达希瓦氏菌的胞外电子传递（extracellular electron transfer,EET）在污染物降解、环境修复、生物电化学传感、能源利用等方面具有广泛的应用潜力;四血红素细胞色素CctA （small tetraheme cytochrome）是希瓦氏菌周质空间中最丰富的蛋白质之一,能够参与多种氧化还原过程,但目前对CctA在EET中的行为和机理认识仍然有限。【目的】研究阐明CctA蛋白在希瓦氏菌模式菌株MR-1周质空间以偶氮染料作为电子受体的EET中的作用,补充和拓展希瓦氏菌的厌氧呼吸产能机制。【方法】以周质还原型偶氮染料甲基橙（methyl orange,MO）作为电子受体,在mteal reduction （Mtr）蛋白缺失菌株Δmtr中研究MO的周质还原特点,并通过基因敲除和回补表达研究CctA蛋白在周质电子传递中的作用。【结果】在缺失Mtr通道的情况下,细胞色素CctA可以介导周质空间的电子传递而还原MO。重组表达CctA在低水平时,MO在周质空间中的还原速率与其表达水平呈正相关,更高水平的CctA表达无助于进一步提高MO的还原速率。蛋白膜伏安结果展示了CctA与周质空间内其他高电位氧化还原蛋白的显著区别,可能参与构成一条低电位的MO还原通道。【结论】从分子动力学层面揭示了CctA在周质MO还原中的独特电子传递行为,为进一步推进对细菌周质电子传递机制的理解,以及通过合成生物学设计或改造胞外氧化还原系统、强化生物电化学在污染物降解中的应用提供了重要信息。     

Anaerobic biotransformations of pollutant chemicals in aquifers

Summary Anaerobic microbial communities sampled from either a methanogenic or sulfate-reducing aquifer site have been tested for their ability to degrade a variety of groundwater pollutants, including halogenated aromatic compounds, simple alkyl phenols and tetrachloroethylene. The haloaromatic chemicals were biodegraded in methanogenic incubations but not under sulfate-reducing conditions. The primary degradative event was typically the reductive removal of the aryl halides. Complete dehalogenation of the aromatic moiety was required before substrate mineralization was observed. The lack of dehalogenation activity in sulfatereducing incubations was due, at least in part, to the high levels of sulfate rather than a lack of metabolic potential. In contrast, the degradation of cresol isomers occurred in both types of incubations but proved faster under sulfate-reducing conditions. The requisite microorganisms were enriched and the degradation pathway forp-cresol under the latter conditions involved the anaerobic oxidation of the aryl methyl group. Tetrachloroethylene was also degraded by reductive dehalogenation but under both incubation conditions. The initial conversion of this substrate to trichloroethylene was generally faster under methanogenic conditions. However, the transformation pathway slowed when dichloroethylene was produced and only trace concentrations of vinyl chloride were detected. These results illustrate that pollutant compounds can be biodegraded under anoxic conditions and a knowledge of the predominant ecological conditions is essential for accurate predictions of the transport and fate of such materials in aquifers.     

Biodegradation of polycyclic aromatic hydrocarbons

The intent of this review is to provide an outline of the microbial degradation of polycyclic aromatic hydrocarbons. A catabolically diverse microbial community, consisting of bacteria, fungi and algae, metabolizes aromatic compounds. Molecular oxygen is essential for the initial hydroxylation of polycyclic aromatic hydrocarbons by microorganisms. In contrast to bacteria, filamentous fungi use hydroxylation as a prelude to detoxification rather than to catabolism and assimilation. The biochemical principles underlying the degradation of polycyclic aromatic hydrocarbons are examined in some detail. The pathways of polycyclic aromatic hydrocarbon catabolism are discussed. Studies are presented on the relationship between the chemical structure of the polycyclic aromatic hydrocarbon and the rate of polycyclic aromatic hydrocarbon biodegradation in aquatic and terrestrial ecosystems.     

Redox and reduction potentials as parameters to predict the degradation pathway of chlorinated benzenes in anaerobic environments

Abstract The anaerobic degradation pathway of hexachlorobenzene starts with a series of reductive dehalogeneration steps. In the present paper it was evaluated whether the dehalogenation pathway observed in microbial ecosystems could be predicted by the redox potential and/or the reduction potential (the latter determined in dimethylsulfoxide) of the various potential intermediates. It was found that these two parameters suggest different pathways. The redox potential correctly predicts the dominant pathway observed in microbial systems, while the reduction potential does not. The redox potential of the various redox couples showed no correlation with the kinetic constants for the various dechlorination steps as determined with a quantitative structure-activity relationship developed for the environmental reductive dehalogenation of chlorinated aromatic compounds, even though both approaches predicted the same pathway.     

Metabolic diversity in bacterial degradation of aromatic compounds

Aromatic compounds pose a major threat to the environment, being mutagenic, carcinogenic, and recalcitrant. Microbes, however, have evolved the ability to utilize these highly reduced and recalcitrant compounds as a potential source of carbon and energy. Aerobic degradation of aromatics is initiated by oxidizing the aromatic ring, making them more susceptible to cleavage by ring-cleaving dioxygenases. A preponderance of aromatic degradation genes on plasmids, transposons, and integrative genetic elements (and their shuffling through horizontal gene transfer) have lead to the evolution of novel aromatic degradative pathways. This enables the microorganisms to utilize a multitude of aromatics via common routes of degradation leading to metabolic diversity. In this review, we emphasize the exquisiteness and relevance of bacterial degradation of aromatics, interlinked degradative pathways, genetic and metabolic regulation, carbon source preference, and biosurfactant production. We have also explored the avenue of metagenomics, which opens doors to a plethora of uncultured and uncharted microbial genetics and metabolism that can be used effectively for bioremediation.     

Epoxy coenzyme a thioester pathways for degradation of aromatic compounds

Aromatic compounds (biogenic and anthropogenic) are abundant in the biosphere. Some of them are well-known environmental pollutants. Although the aromatic nucleus is relatively recalcitrant, microorganisms have developed various catabolic routes that enable complete biodegradation of aromatic compounds. The adopted degradation pathways depend on the availability of oxygen. Under oxic conditions, microorganisms utilize oxygen as a cosubstrate to activate and cleave the aromatic ring. In contrast, under anoxic conditions, the aromatic compounds are transformed to coenzyme A (CoA) thioesters followed by energy-consuming reduction of the ring. Eventually, the dearomatized ring is opened via a hydrolytic mechanism. Recently, novel catabolic pathways for the aerobic degradation of aromatic compounds were elucidated that differ significantly from the established catabolic routes. The new pathways were investigated in detail for the aerobic bacterial degradation of benzoate and phenylacetate. In both cases, the pathway is initiated by transforming the substrate to a CoA thioester and all the intermediates are bound by CoA. The subsequent reactions involve epoxidation of the aromatic ring followed by hydrolytic ring cleavage. Here we discuss the novel pathways, with a particular focus on their unique features and occurrence as well as ecological significance.     

Dioxygen activation responsible for oxidation of aliphatic and aromatic hydrocarbon compounds: current state and variants

The most significant aspect in microbial metabolisms, especially those of bacteria and archaea, is their marvelously wide acceptability of substrate electron donors and acceptors. This feature makes them to be attractive catalysts for environmental biotechnology in terms of degradation of harmful recalcitrant compounds, including hydrocarbons. Transformation of highly reduced and inert hydrocarbon compounds is with no doubt a challenging biochemical reaction for a single enzyme. However, several multi-component enzyme systems enable microorganisms to utilize hydrocarbons as carbon and energy (electron) sources. Initial biological attack to hydrocarbons is, in most cases, the hydroxylation that requires molecular dioxygen as a co-substrate. Dioxygen also contributes to the ring cleavage reaction of homo- and hetero-cyclic aromatic hydrocarbons. Although the molecular dioxygen is omnipresent and highly soluble in water, activation and splitting this triplet ground-state molecule to wed with difficult hydrocarbons need special devices. Non-heme iron, heme iron, or flavin nucleotide was designated as a major hidden dagger for this purpose.     

Microbial reductive dehalogenation.

A wide variety of compounds can be biodegraded via reductive removal of halogen substituents. This process can degrade toxic pollutants, some of which are not known to be biodegraded by any other means. Reductive dehalogenation of aromatic compounds has been found primarily in undefined, syntrophic anaerobic communities. We discuss ecological and physiological principles which appear to be important in these communities and evaluate how widely applicable these principles are. Anaerobic communities that catalyze reductive dehalogenation appear to differ in many respects. A large number of pure cultures which catalyze reductive dehalogenation of aliphatic compounds are known, in contrast to only a few organisms which catalyze reductive dehalogenation of aromatic compounds. Desulfomonile tiedjei DCB-1 is an anaerobe which dehalogenates aromatic compounds and is physiologically and morphologically unusual in a number of respects, including the ability to exploit reductive dehalogenation for energy metabolism. When possible, we use D. tiedjei as a model to understand dehalogenating organisms in the above-mentioned undefined systems. Aerobes use reductive dehalogenation for substrates which are resistant to known mechanisms of oxidative attack. Reductive dehalogenation, especially of aliphatic compounds, has recently been found in cell-free systems. These systems give us an insight into how and why microorganisms catalyze this activity. In some cases transition metal complexes serve as catalysts, whereas in other cases, particularly with aromatic substrates, the catalysts appear to be enzymes.     

Anaerobic biodegradation of aromatic hydrocarbons: pathways and prospects

Aromatic hydrocarbons contaminate many environments worldwide, and their removal often relies on microbial bioremediation. Whereas aerobic biodegradation has been well studied for decades, anaerobic hydrocarbon biodegradation is a nascent field undergoing rapid shifts in concept and scope. This review presents known metabolic pathways used by microbes to degrade aromatic hydrocarbons using various terminal electron acceptors; an outline of the few catabolic genes and enzymes currently characterized; and speculation about current and potential applications for anaerobic degradation of aromatic hydrocarbons.     

Physiology of aliphatic hydrocarbon-degrading microorganisms

This paper reviews aspects of the physiology and biochemistry of the microbial biodegradation of alkanes larger than methane, alkenes and alkynes with particular emphasis upon recent developments. Subject areas discussed include: substrate uptake; metabolic pathways for alkenes and straight and branched-chain alkanes; the genetics and regulation of pathways; co-oxidation of aliphatic hydrocarbons; the potential for anaerobic aliphatic hydrocarbon degradation; the potential deployment of aliphatic hydrocarbon-degrading microorganisms in biotechnology.     

Biodegradation of halogenated organic compounds.

In this review we discuss the degradation of chlorinated hydrocarbons by microorganisms, emphasizing the physiological, biochemical, and genetic basis of the biodegradation of aliphatic, aromatic, and polycyclic compounds. Many environmentally important xenobiotics are halogenated, especially chlorinated. These compounds are manufactured and used as pesticides, plasticizers, paint and printing-ink components, adhesives, flame retardants, hydraulic and heat transfer fluids, refrigerants, solvents, additives for cutting oils, and textile auxiliaries. The hazardous chemicals enter the environment through production, commercial application, and waste. As a result of bioaccumulation in the food chain and groundwater contamination, they pose public health problems because many of them are toxic, mutagenic, or carcinogenic. Although synthetic chemicals are usually recalcitrant to biodegradation, microorganisms have evolved an extensive range of enzymes, pathways, and control mechanisms that are responsible for catabolism of a wide variety of such compounds. Thus, such biological degradation can be exploited to alleviate environmental pollution problems. The pathways by which a given compound is degraded are determined by the physical, chemical, and microbiological aspects of a particular environment. By understanding the genetic basis of catabolism of xenobiotics, it is possible to improve the efficacy of naturally occurring microorganisms or construct new microorganisms capable of degrading pollutants in soil and aquatic environments more efficiently. Recently a number of genes whose enzyme products have a broader substrate specificity for the degradation of aromatic compounds have been cloned and attempts have been made to construct gene cassettes or synthetic operons comprising these degradative genes. Such gene cassettes or operons can be transferred into suitable microbial hosts for extending and custom designing the pathways for rapid degradation of recalcitrant compounds. Recent developments in designing recombinant microorganisms and hybrid metabolic pathways are discussed.