Microbial degradation of aromatic compounds - from one strategy to four

Aromatic compounds are both common growth substrates for microorganisms and prominent environmental pollutants. The crucial step in their degradation is overcoming the resonance energy that stabilizes the ring structure. The classical strategy for degradation comprises an attack by oxygenases that hydroxylate and finally cleave the ring with the help of activated molecular oxygen. Here, we describe three alternative strategies used by microorganisms to degrade aromatic compounds. All three of these methods involve the use of CoA thioesters and ring cleavage by hydrolysis. However, these strategies are based on different ring activation mechanisms that consist of either formation of a non-aromatic ring-epoxide under oxic conditions, or reduction of the aromatic ring under anoxic conditions using one of two completely different systems.     

Molecular mechanisms of genetic adaptation to xenobiotic compounds.

Microorganisms in the environment can often adapt to use xenobiotic chemicals as novel growth and energy substrates. Specialized enzyme systems and metabolic pathways for the degradation of man-made compounds such as chlorobiphenyls and chlorobenzenes have been found in microorganisms isolated from geographically separated areas of the world. The genetic characterization of an increasing number of aerobic pathways for degradation of (substituted) aromatic compounds in different bacteria has made it possible to compare the similarities in genetic organization and in sequence which exist between genes and proteins of these specialized catabolic routes and more common pathways. These data suggest that discrete modules containing clusters of genes have been combined in different ways in the various catabolic pathways. Sequence information further suggests divergence of catabolic genes coding for specialized enzymes in the degradation of xenobiotic chemicals. An important question will be to find whether these specialized enzymes evolved from more common isozymes only after the introduction of xenobiotic chemicals into the environment. Evidence is presented that a range of genetic mechanisms, such as gene transfer, mutational drift, and genetic recombination and transposition, can accelerate the evolution of catabolic pathways in bacteria. However, there is virtually no information concerning the rates at which these mechanisms are operating in bacteria living in nature and the response of such rates to the presence of potential (xenobiotic) substrates. Quantitative data on the genetic processes in the natural environment and on the effect of environmental parameters on the rate of evolution are needed.     

Microbial metabolism of pyridine, quinoline, acridine, and their derivatives under aerobic and anaerobic conditions.

Our review of the metabolic pathways of pyridines and aza-arenes showed that biodegradation of heterocyclic aromatic compounds occurs under both aerobic and anaerobic conditions. Depending upon the environmental conditions, different types of bacteria, fungi, and enzymes are involved in the degradation process of these compounds. Our review indicated that different organisms are using different pathways to biotransform a substrate. Our review also showed that the transformation rate of the pyridine derivatives is dependent on the substituents. For example, pyridine carboxylic acids have the highest transformation rate followed by mono-hydroxypyridines, methylpyridines, aminopyridines, and halogenated pyridines. Through the isolation of metabolites, it was possible to demonstrate the mineralization pathway of various heterocyclic aromatic compounds. By using 14C-labeled substrates, it was possible to show that ring fission of a specific heterocyclic compound occurs at a specific position of the ring. Furthermore, many researchers have been able to isolate and characterize the microorganisms or even the enzymes involved in the transformation of these compounds or their derivatives. In studies involving 18O labeling as well as the use of cofactors and coenzymes, it was possible to prove that specific enzymes (e.g., mono- or dioxygenases) are involved in a particular degradation step. By using H2 18O, it could be shown that in certain transformation reactions, the oxygen was derived from water and that therefore these reactions might also occur under anaerobic conditions.     

Anaerobic and aerobic metabolism of diverse aromatic compounds by the photosynthetic bacterium Rhodopseudomonas palustris.

The purple nonsulfur photosynthetic bacterium Rhodopseudomonas palustris used diverse aromatic compounds for growth under anaerobic and aerobic conditions. Many phenolic, dihydroxylated, and methoxylated aromatic acids, as well as aromatic aldehydes and hydroaromatic acids, supported growth of strain CGA001 in both the presence and absence of oxygen. Some compounds were metabolized under only aerobic or under only anaerobic conditions. Two other strains, CGC023 and CGD052, had similar anaerobic substrate utilization patterns, but CGD052 was able to use a slightly larger number of compounds for growth. These results show that R. palustris is far more versatile in terms of aromatic degradation than had been previously demonstrated. A mutant (CGA033) blocked in aerobic aromatic metabolism remained wild type with respect to anaerobic degradative abilities, indicating that separate metabolic pathways mediate aerobic and anaerobic breakdown of diverse aromatics. Another mutant (CGA047) was unable to grow anaerobically on either benzoate or 4-hydroxybenzoate, and these compounds accumulated in growth media when cells were grown on more complex aromatic compounds. This indicates that R. palustris has two major anaerobic routes for aromatic ring fission, one that passes through benzoate and one that passes through 4-hydroxybenzoate.     

Biodegradation of Phenol: Mechanisms and Applications

Phenol, or hydroxybenzene, is both a synthetically and naturally produced aromatic compound. Microorganisms capable of degrading phenol are common and include both aerobes and anaerobes. Many aerobic phenol-degrading microorganisms have been isolated and the pathways for the aerobic degradation of phenol are now firmly established. The first steps include oxygenation of phenol by phenol hydroxylase enzymes to form catechol, followed by ring cleavage adjacent to or in between the two hydroxyl groups of catechol. Phenol hydroxylases ranging from simple flavoprotein monooxygenases to multicomponent hydroxylases, as well as the genes coding for these enzymes, have been described for a number of aerobic phenol-degrading microorganisms. Phenol can also be degraded in the absence of oxygen. Our knowledge of this process is less advanced than that of the aerobic process, and only a few anaerobic phenol-degrading bacteria have been isolated to date. Convincing evidence from both pure culture studies with the denitrifying organism Thauera aromatica K172 and with two Clostridium species, as well as from mixed culture studies, indicates that the first step in anaerobic phenol degradation is carboxylation in the para-position to form 4-hydroxybenzoate. Following para-carboxylation, thioesterification of 4-hydroxybenzoate to co-enzyme A allows subsequent ring reduction, hydration, and fission. Para-carboxylation appears to be involved in the anaerobic degradation of a number of aromatic compounds. Numerous practical applications exist for microbial phenol degradation. These include the exploitation of indigenous anaerobic phenol-degrading bacteria in the in situ bioremediation of creosote-contaminated subsurface environments, and the use of phenol as a co-substrate for indigenous aerobic phenol-degrading bacteria to enhance in situ biodegradation of chlorinated solvents.     

ATP‐dependent/‐independent enzymatic ring reductions involved in the anaerobic catabolism of naphthalene

Polycyclic aromatic hydrocarbons are among the most hazardous environmental pollutants. However, in contrast to aerobic degradation, the respective degradation pathways in anaerobes are greatly unknown which has so far prohibited many environmental investigations. In this work, we studied the enzymatic dearomatization reactions involved in the degradation of the PAH model compounds naphthalene and 2‐methylnaphthalene in the sulfate‐reducing enrichment culture N47. Cell extracts of N47 grown on naphthalene catalysed the sodium dithionite‐dependent four‐electron reduction of the key intermediate 2‐naphthoyl‐coenzyme A (NCoA) to 5,6,7,8‐tetrahydro‐2‐naphthoyl‐CoA (THNCoA). The NCoA reductase activity was independent of ATP and was, surprisingly, not sensitive to oxygen. In cell extracts in the presence of various electron donors the product THNCoA was further reduced by a two‐electron reaction to most likely a conjugated hexahydro‐2‐naphthoyl‐CoA isomer (HHNCoA). The reaction assigned to THNCoA reductase strictly depended on ATP and was oxygen‐sensitive with a half‐life time between 30 s and 1 min when exposed to air. The rate was highest with NADH as electron donor. The results indicate that two novel and completely different dearomatizing ring reductases are involved in anaerobic naphthalene degradation. While the THNCoA reducing activity shows some properties of ATP‐dependent class I benzoyl‐CoA reductases, NCoA reduction appears to be catalysed by a previously unknown class of dearomatizing aryl‐carboxyl‐CoA reductases.     

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.     

Microbial breakdown of halogenated aromatic pesticides and related compounds

Abstract Considerable progress has been made in the last few years in understanding the mechanisms of microbial degradation of halogenated aromatic compounds. Much is already known about the degradation mechanisms under aerobic conditions, and metabolism under anaerobiosis has lately received increasing attention. The removal of the halogen substituent is a key step in degradation of halogenated aromatics. This may occur as an initial step via reductive, hydrolytic or oxygenolytic mechanisms, or after cleavage of the aromatic ring at a later stage of metabolism. In addition to degradation, several biotransformation reactions, such as methylation and polymerization, may take place and produce more toxic or recalcitrant metabolites. Studies with pure bacterial and fungal cultures have given detailed information on the biodegradation pathways of several halogenated aromatic compounds. Several of the key enzymes have been purified or studied in cell extracts, and there is an increasing understanding of the organization and regulation of the genes involved in haloaromatic degradation. This review will focus on the biodegradation and biotransformation pathways that have been established for halogenated phenols, phenoxyalkanoic acids, benzoic acids, benzenes, anilines and structurally related halogenated aromatic pesticides. There is a growing interest in developing microbiological methods for clean-up of soil and water contaminated with halogenated aromatic compounds.     

Microbial breakdown of halogenated aromatic pesticides and related compounds.

Considerable progress has been made in the last few years in understanding the mechanisms of microbial degradation of halogenated aromatic compounds. Much is already known about the degradation mechanisms under aerobic conditions, and metabolism under anaerobiosis has lately received increasing attention. The removal of the halogen substituent is a key step in degradation of halogenated aromatics. This may occur as an initial step via reductive, hydrolytic or oxygenolytic mechanisms, or after cleavage of the aromatic ring at a later stage of metabolism. In addition to degradation, several biotransformation reactions, such as methylation and polymerization, may take place and produce more toxic or recalcitrant metabolites. Studies with pure bacterial and fungal cultures have given detailed information on the biodegradation pathways of several halogenated aromatic compounds. Several of the key enzymes have been purified or studied in cell extracts, and there is an increasing understanding of the organization and regulation of the genes involved in haloaromatic degradation. This review will focus on the biodegradation and biotransformation pathways that have been established for halogenated phenols, phenoxyalkanoic acids, benzoic acids, benzenes, anilines and structurally related halogenated aromatic pesticides. There is a growing interest in developing microbiological methods for clean-up of soil and water contaminated with halogenated aromatic compounds.     

Conversion of cis‐2‐carboxycyclohexylacetyl‐CoA in the downstream pathway of anaerobic naphthalene degradation

The cyclohexane derivative cis‐2‐(carboxymethyl)cyclohexane‐1‐carboxylic acid [(1R,2R)‐/(1S,2S)‐2‐(carboxymethyl)cyclohexane‐1‐carboxylic acid] has previously been identified as metabolite in the pathway of anaerobic degradation of naphthalene by sulfate‐reducing bacteria. We tested the corresponding CoA esters of isomers and analogues of this compound for conversion in cell free extracts of the anaerobic naphthalene degraders Desulfobacterium strain N47 and Deltaproteobacterium strain NaphS2. Conversion was only observed for the cis‐isomer, verifying that this is a true intermediate and not a dead‐end product. Mass‐spectrometric analyses confirmed that conversion is performed by an acyl‐CoA dehydrogenase and a subsequent hydratase yielding an intermediate with a tertiary hydroxyl‐group. We propose that a novel kind of ring‐opening lyase is involved in the further catabolic pathway proceeding via pimeloyl‐CoA. In contrast to degradation pathways of monocyclic aromatic compounds where ring‐cleavage is achieved via hydratases, this lyase might represent a new ring‐opening strategy for the degradation of polycyclic compounds. Conversion of the potential downstream metabolites pimeloyl‐CoA and glutaryl‐CoA was proved in cell free extracts, yielding 2,3‐dehydropimeloyl‐CoA, 3‐hydroxypimeloyl‐CoA, 3‐oxopimeloyl‐CoA, glutaconyl‐CoA, crotonyl‐CoA, 3‐hydroxybutyryl‐CoA and acetyl‐CoA as observable intermediates. This indicates a link to central metabolism via β‐oxidation, a non‐decarboxylating glutaryl‐CoA dehydrogenase and a subsequent glutaconyl‐CoA decarboxylase.     

A patchwork pathway for oxygenase‐independent degradation of side chain containing steroids

The denitrifying betaproteobacterium Sterolibacterium denitrificans serves as model organism for studying the oxygen‐independent degradation of cholesterol. Here, we demonstrate its capability of degrading various globally abundant side chain containing zoo‐, phyto‐ and mycosterols. We provide the complete genome that empowered an integrated genomics/proteomics/metabolomics approach, accompanied by the characterization of a characteristic enzyme of steroid side chain degradation. The results indicate that individual molybdopterin‐containing steroid dehydrogenases are involved in C25‐hydroxylations of steroids with different isoprenoid side chains, followed by the unusual conversion to C26‐oic acids. Side chain degradation to androsta‐1,4‐diene‐3,17‐dione (ADD) via aldolytic C–C bond cleavages involves acyl‐CoA synthetases/dehydrogenases specific for the respective 26‐, 24‐ and 22‐oic acids/‐oyl‐CoAs and promiscuous MaoC‐like enoyl‐CoA hydratases, aldolases and aldehyde dehydrogenases. Degradation of rings A and B depends on gene products uniquely found in anaerobic steroid degraders, which after hydrolytic cleavage of ring A, again involves CoA‐ester intermediates. The degradation of the remaining CD rings via hydrolytic cleavage appears to be highly similar in aerobic and anaerobic bacteria. Anaerobic cholesterol degradation employs a composite repertoire of more than 40 genes partially known from aerobic degradation in gammaproteobacteria/actinobacteria, supplemented by unique genes that are required to circumvent oxygenase‐dependent reactions.     

Identification and characterization of 2‐naphthoyl‐coenzyme A reductase,the prototype of a novel class of dearomatizing reductases

The enzymatic dearomatization of aromatic ring systems by reduction represents a highly challenging redox reaction in biology and plays a key role in the degradation of aromatic compounds under anoxic conditions. In anaerobic bacteria, most monocyclic aromatic growth substrates are converted to benzoyl‐coenzyme A (CoA), which is then dearomatized to a conjugated dienoyl‐CoA by ATP‐dependent or ‐independent benzoyl‐CoA reductases. It was unresolved whether or not related enzymes are involved in the anaerobic degradation of environmentally relevant polycyclic aromatic hydrocarbons (PAHs). In this work, a previously unknown dearomatizing 2‐naphthoyl‐CoA reductase was purified from extracts of the naphthalene‐degrading, sulphidogenic enrichment culture N47. The oxygen‐tolerant enzyme dearomatized the non‐activated ring of 2‐naphthoyl‐CoA by a four‐electron reduction to 5,6,7,8‐tetrahydro‐2‐naphthoyl‐CoA. The dimeric 150 kDa enzyme complex was composed of a 72 kDa subunit showing sequence similarity to members of the flavin‐containing ‘old yellow enzyme’ family. NCR contained FAD, FMN, and an iron‐sulphur cluster as cofactors. Extracts of Escherichia coli expressing the encoding gene catalysed 2‐naphthoyl‐CoA reduction. The identified NCR is a prototypical enzyme of a previously unknown class of dearomatizing arylcarboxyl‐CoA reductases that are involved in anaerobic PAH degradation; it fundamentally differs from known benzoyl‐CoA reductases.     

基于电活性微生物的芳香烃类污染物转化机制研究进展

芳香烃类化合物(aromatic hydrocarbon compounds)是一类基于苯环结构的有机物,广泛分布在自然环境中,难以自然降解、易被生物积累,且有很大的环境危害性。生物法是有机化合物转化降解的主流工艺,而电活性微生物(electroactive microorganisms, EAM)因其独特的胞外电子传递(extracellular electron transfer, EET)能力和生理代谢模式在芳香烃类化合物污染修复领域具有巨大的应用潜力。电活性微生物可以通过还原脱卤、脱硝与氧化开环过程相结合的方式,最终实现芳香烃类污染物的降解矿化。本文重点综述了电活性微生物降解芳香烃类污染物过程中主要还原/氧化反应机理,归纳了电活性微生物高效还原脱卤、脱硝的关键酶活、代谢途径及转化机理,分析了不同含氧条件下电活性微生物开环方式及降解代谢途径,并通过调控微生物胞外聚合物与添加导电材料等途径来提升电活性微生物的胞外电子传递过程,总结了电极电位、电极材料、电解液性质及温度等环境因子对芳香烃类化合物降解的影响,探讨了芳香烃类污染物的强化生物降解策略的可行性。最后,展望了电活性微生物降解技...     

Structural and Biophysical Characterization of BoxC from Burkholderia xenovorans LB400: A NOVEL RING-CLEAVING ENZYME IN THE CROTONASE SUPERFAMILY*

The mineralization of aromatic compounds by microorganisms relies on a structurally and functionally diverse group of ring-cleaving enzymes. The recently discovered benzoate oxidation pathway in Burkholderia xenovorans LB400 encodes a novel such ring-cleaving enzyme, termed BoxC, that catalyzes the conversion of 2,3-dihydro-2,3-dihydroxybenzoyl-CoA to 3,4-dehydroadipyl-CoA without the requirement for molecular oxygen. Sequence analysis indicates that BoxC is a highly divergent member of the crotonase superfamily and nearly double the size of the average superfamily member. The structure of BoxC determined to 1.5 Å resolution reveals an intriguing structural demarcation. A highly divergent region in the C terminus probably serves as a structural scaffold for the conserved N terminus that encompasses the active site and, in conjunction with a conserved C-terminal helix, mediates dimer formation. Isothermal titration calorimetry and molecular docking simulations contribute to a detailed view of the active site, resulting in a compelling mechanistic model where a pair of conserved glutamate residues (Glu¹⁴⁶ and Glu¹⁶⁸) work in tandem to deprotonate the dihydroxylated ring substrate, leading to cleavage. A final deformylation step incorporating a water molecule and Cys¹¹¹ as a general base completes the formation of 3,4-dehydroadipyl-CoA product. Overall, this study establishes the basis for BoxC as one of the most divergent members of the crotonase superfamily and provides the first structural insight into the mechanism of this novel class of ring-cleaving enzymes.Aromatic compounds comprise approximately one-quarter of the earth''s biomass (1) and are the second most abundant natural product next to carbohydrates. The majority of aromatic compounds in the environment are in the form of the organic polymer lignin that plays a structural role in cross-linking cell wall polysaccharides in plants. Despite the inherent thermostability of the aromatic ring, these naturally occurring compounds are efficiently mineralized by various microorganisms. Human-made aromatic compounds, such as those used in industrial processes, however, are often recalcitrant to microbial degradation due to their chemical complexity, decreased bioavailability, and increased thermostability. Moreover, bacteria have only been exposed to these compounds for a relatively short period of time. As a result, these compounds persist in the environment, where they can increase to toxic levels and cause irreversible damage to the biosphere.The common structural blueprint shared by natural and human-made aromatic compounds is the resonance-stabilized planar ring system. Microorganisms overcome the stability of these aromatic structures by employing specific ring-cleaving enzymes that form part of complex catabolic pathways. Until recently, two general classes of microbial processes were characterized that catalyze the degradation of aromatic compounds. These classifications, termed the aerobic and anaerobic pathways, were based primarily on the mode of initial activation and subsequent cleavage of the aromatic ring. The aerobic pathway, exemplified by the peripheral biphenyl and the central ben-cat pathway, relies on the extensive use of molecular oxygen for both the hydroxylation (activation) and cleavage of the aromatic ring (2–4). The anaerobic pathway, however, mediates a reductive dearomatization followed by a hydrolytic ring cleavage, as observed in the classical benzoate pathway (5–7). In both cases, the underlying mechanism incorporates an activation step that renders the ring susceptible to cleavage.Recently, a third aromatic degradation pathway was identified in Burkholderia xenovorans strain LB400 (LB400) (8–10) and Azoarcus evansii (11–13). This novel pathway, termed the box (benzoate oxidation) pathway, incorporates features of both the aerobic and anaerobic pathways, resulting in a hybrid pathway. Microarray analysis of the 9.7-Mb genome of LB400 revealed two paralogous copies of the box pathway, one encoded on chromosome 1 (box_c) and the second on the megaplasmid (box_m) (9). Knock-out studies confirm that both box pathways are capable of assimilating benzoate (10) yet are differentially regulated based on available carbon source and growth phase of the organism (9). Recent structural and biochemical characterization of benzoate CoA ligase (14) and aldeheyde dehydrogenase (15) from the box pathway in LB400 have provided valuable insight into the basis of substrate specificity and details describing the molecular mechanisms.A unique feature of the hybrid box pathway is the incorporation of both CoA ligation and hydroxylation prior to ring cleavage (16), suggesting that both strategies are important for ring activation. It is noteworthy that although CoA ligation is common in the activation of aromatic acids under anaerobic conditions, it has thus far been unseen in the aerobic degradation of aromatic compounds. Furthermore, investigation of the box pathway intermediates from the related A. evansii demonstrated that the thioesterified dihydrodiol intermediate was not oxidized and rearomatized as normally occurs in aerobic aromatic metabolism (11). Instead, it was shown to be directly cleaved without the requirement of molecular oxygen in a reaction that resulted in the loss of one unit of carbon and oxygen as formate (11). This critical ring cleavage step in the box pathway is catalyzed by BoxC (2,3-dihydro-2,3-dihydroxybenzoyl-CoA lyase/hydrolase) (11), which differs from traditional aerobic and anaerobic ring-cleaving enzymes in that oxygen is not used in catalysis, and the ring substrate is only partially reduced. Based on sequence analysis, BoxC is assigned to the crotonase superfamily. The cleavage reaction catalyzed by BoxC, however, suggests that BoxC defines a new mechanistic niche and intriguingly is one of the four outstanding crotonase superfamily members for which no structural information exists (17).A mechanism for BoxC from A. evansii was recently proposed based on the identification of chemical species using NMR and mass spectrometry (11). In the absence of structural information of BoxC, however, the mechanistic details, including the identity of the catalytic residues, remain undefined. To investigate the detailed molecular mechanism of BoxC, we carried out a structural and biophysical analysis complemented with molecular docking. The resulting data provide a compelling mechanistic model with the identification of key catalytic residues and active site structure that stabilize proposed transition state intermediates. Furthermore, the 1.5 Å resolution structure of BoxC reveals intriguing divergent architectural features with respect to other members of the crotonase superfamily. Overall, this study provides the first structural characterization of the novel BoxC family of enzymes and is interpreted with respect to the proposed molecular mechanism and divergence within the crotonase superfamily.     

Reactions involved in the lower pathway for degradation of 4-nitrotoluene by Mycobacterium strain HL 4-NT-1

In spite of the variety of initial reactions, the aerobic biodegradation of aromatic compounds generally yields dihydroxy intermediates for ring cleavage. Recent investigation of the degradation of nitroaromatic compounds revealed that some nitroaromatic compounds are initially converted to 2-aminophenol rather than dihydroxy intermediates by a number of microorganisms. The complete pathway for the metabolism of 2-aminophenol during the degradation of nitrobenzene by Pseudomonas pseudoalcaligenes JS45 has been elucidated previously. The pathway is parallel to the catechol extradiol ring cleavage pathway, except that 2-aminophenol is the ring cleavage substrate. Here we report the elucidation of the pathway of 2-amino-4-methylphenol (6-amino-m-cresol) metabolism during the degradation of 4-nitrotoluene by Mycobacterium strain HL 4-NT-1 and the comparison of the substrate specificities of the relevant enzymes in strains JS45 and HL 4-NT-1. The results indicate that the 2-aminophenol ring cleavage pathway in strain JS45 is not unique but is representative of the pathways of metabolism of other o-aminophenolic compounds.     

Functional genomics by NMR spectroscopy. Phenylacetate catabolism in Escherichia coli.

Aerobic metabolism of phenylalanine in most bacteria proceeds via oxidation to phenylacetate. Surprisingly, the further metabolism of phenylacetate has not been elucidated, even in well studied bacteria such as Escherichia coli. The only committed step is the conversion of phenylacetate into phenylacetyl-CoA. The paa operon of E. coli encodes 14 polypeptides involved in the catabolism of phenylacetate. We have found that E. coli K12 mutants with a deletion of the paaF, paaG, paaH, paaJ or paaZ gene are unable to grow with phenylacetate as carbon source. Incubation of a paaG mutant with [U-13C8]phenylacetate yielded ring-1,2-dihydroxy-1,2-dihydrophenylacetyl lactone as shown by NMR spectroscopy. Incubation of the paaF and paaH mutants with phenylacetate yielded delta3-dehydroadipate and 3-hydroxyadipate, respectively. The origin of the carbon atoms of these C6 compounds from the aromatic ring was shown using [ring-13C6]phenylacetate. The paaG and paaZ mutants also converted phenylacetate into ortho-hydroxyphenylacetate, which was previously identified as a dead end product of phenylacetate catabolism. These data, in conjunction with protein sequence data, suggest a novel catabolic pathway via CoA thioesters. According to this, phenylacetyl-CoA is attacked by a ring-oxygenase/reductase (PaaABCDE proteins), generating a hydroxylated and reduced derivative of phenylacetyl-CoA, which is not re-oxidized to a dihydroxylated aromatic intermediate, as in other known aromatic pathways. Rather, it is proposed that this nonaromatic intermediate CoA ester is further metabolized in a complex reaction sequence comprising enoyl-CoA isomerization/hydration, nonoxygenolytic ring opening, and dehydrogenation catalyzed by the PaaG and PaaZ proteins. The subsequent beta-oxidation-type degradation of the resulting CoA dicarboxylate via beta-ketoadipyl-CoA to succinyl-CoA and acetyl-CoA appears to be catalyzed by the PaaJ, PaaF and PaaH proteins.     

Studies on the mechanism of ring hydrolysis in phenylacetate degradation: a metabolic branching point

The widespread, long sought-after bacterial aerobic phenylalanine/phenylacetate catabolic pathway has recently been elucidated. It proceeds via coenzyme A (CoA) thioesters and involves the epoxidation of the aromatic ring of phenylacetyl-CoA, subsequent isomerization to an uncommon seven-membered C-O-heterocycle (oxepin-CoA), and non-oxygenolytic ring cleavage. Here we characterize the hydrolytic oxepin-CoA ring cleavage catalyzed by the bifunctional fusion protein PaaZ. The enzyme consists of a C-terminal (R)-specific enoyl-CoA hydratase domain (formerly MaoC) that cleaves the ring and produces a highly reactive aldehyde and an N-terminal NADP(+)-dependent aldehyde dehydrogenase domain that oxidizes the aldehyde to 3-oxo-5,6-dehydrosuberyl-CoA. In many phenylacetate-utilizing bacteria, the genes for the pathway exist in a cluster that contains an NAD(+)-dependent aldehyde dehydrogenase in place of PaaZ, whereas the aldehyde-producing hydratase is encoded outside of the cluster. If not oxidized immediately, the reactive aldehyde condenses intramolecularly to a stable cyclic derivative that is largely prevented by PaaZ fusion in vivo. Interestingly, the derivative likely serves as the starting material for the synthesis of antibiotics (e.g. tropodithietic acid) and other tropone/tropolone related compounds as well as for ω-cycloheptyl fatty acids. Apparently, bacteria made a virtue out of the necessity of disposing the dead-end product with ring hydrolysis as a metabolic branching point.     

An Oxygenase-Independent Cholesterol Catabolic Pathway Operates under Oxic Conditions

Cholesterol is one of the most ubiquitous compounds in nature. The 9,10-seco-pathway for the aerobic degradation of cholesterol was established thirty years ago. This pathway is characterized by the extensive use of oxygen and oxygenases for substrate activation and ring fission. The classical pathway was the only catabolic pathway adopted by all studies on cholesterol-degrading bacteria. Sterolibacterium denitrificans can degrade cholesterol regardless of the presence of oxygen. Here, we aerobically grew the model organism with ¹³C-labeled cholesterol, and substrate consumption and intermediate production were monitored over time. Based on the detected ¹³C-labeled intermediates, this study proposes an alternative cholesterol catabolic pathway. This alternative pathway differs from the classical 9,10-seco-pathway in numerous important aspects. First, substrate activation proceeds through anaerobic C-25 hydroxylation and subsequent isomerization to form 26-hydroxycholest-4-en-3-one. Second, after the side chain degradation, the resulting androgen intermediate is activated by adding water to the C-1/C-2 double bond. Third, the cleavage of the core ring structure starts at the A-ring via a hydrolytic mechanism. The ¹⁸O-incorporation experiments confirmed that water is the sole oxygen donor in this catabolic pathway.     

Bacterial aerobic degradation of benzene,toluene, ethylbenzene and xylene

Several aerobic metabolic pathways for the degradation of benzene, toluene, ethylbenzene and xylene (BTEX), which are provided by two enzymic systems (dioxygenases and monooxygenases), have been identified. The monooxygenase attacks methyl or ethyl substituents of the aromatic ring, which are subsequently transformed by several oxidations to corresponding substituted pyrocatechols or phenylglyoxal, respectively. Alternatively, one oxygen atom may be first incorporated into aromatic ring while the second atom of the oxygen molecule is used for oxidation of either aromatic ring or a methyl group to corresponding pyrocatechols or protocatechuic acid, respectively. The dioxygenase attacks aromatic ring with the formation of 2-hydroxy-substituted compounds. Intermediates of the “upper” pathway are then mineralized by eitherortho-ormeta-ring cleavage (“lower” pathway). BTEX are relatively water-soluble and there-fore they are often mineralized by indigenous microflora. Therefore, natural attenuation may be considered as a suitable way for the clean-up of BTEX contaminants from gasoline-contaminated soil and groundwater.