Nucleotide sequence and functional analysis of the meta-cleavage pathway involved in biphenyl and polychlorinated biphenyl degradation in Pseudomonas sp. strain KKS102

Recent advances in the biodegradation of polychlorinated biphenyls

Polychlorinated biphenyls (PCBs) are typical lasting organic pollutants. Persistence and recalcitrance to biodegradation of PCBs have hampered the transformation of PCB congeners from the environment. Biological transformation of polychlorinated biphenyls could take place through anaerobic dechlorination, aerobic microbial degradation, and a combination of transformation of anaerobic dechlorination and aerobic degradation. Under anaerobic conditions, microbial dechlorination is an important degradation mode for PCBs, especially high-chlorinated congeners. The low-chlorinated compounds formed after reductive dechlorination could be further aerobically degraded and completely mineralized. This paper reviews the recent advances in biological degradation of PCBs, introduces the functional bacteria and enzymes involved in the anaerobic and aerobic degradation of PCBs, and discusses the synergistic action of anaerobic reduction and aerobic degradation. In addition, the different ways to the microbial remediation of PCBs-contaminated environments are discussed. This review provides a theoretical foundation and practical basis to use PCBs-degrading microorganisms for bioremediation.

Biphenyl degradation by recombinant photosynthetic cyanobacterium Synechocystis sp. PCC6803 in an oligotrophic environment using unphysiological electron transfer

Cyanobacteria are potentially useful photosynthetic microorganisms for bioremediation under oligotrophic environments. Here, the biphenyl degradation pathway genes of β-proteobacterium Acidovorax sp. strain KKS102 were co-expressed in cyanobacterium Synechocystis sp. PCC6803 cells under control of the photo-inducible psbE promoter. In the KKS102 cells, biphenyl is dioxygenated by bphA1 and bphA2 gene products complex using electrons supplied from NADH via bphA4 and bphA3 gene products (BphA4 and BphA3, respectively), and converted to benzoic acid by bphB, bphC and bphD gene products. Unexpectedly, biphenyl was effectively hydroxylated in oligotrophic BG11 medium by co-expressing the bphA3, bphA1 and bphA2 genes without the bphA4 gene, suggesting that endogenous cyanobacteria-derived protein(s) can supply electrons to reduce BphA3 at the start of the biphenyl degradation pathway. Furthermore, biphenyl was converted to benzoic acid by cyanobacterial cells co-expressing bphA3, bphA1, bphA2, bphB, bphC and bphD. Structural gene-screening using recombinant Escherichia coli cells co-expressing bphA3, bphA1, bphA2, bphB and bphC suggested that petH, which encodes long- and short-type NADP-ferredoxin oxidoreductase isomers (FNRL and FNRS, respectively), and slr0600, which is annotated as an NADPH-thioredoxin reductase gene in CyanoBase, were BphA3-reducible proteins. Purified FNRL and FNRS, and the slr0600 gene product showed BphA3 reductase activity dependent on NADPH and the reduced form of glutathione, respectively, potentially shedding light on the physiological roles of the slr0600 gene product in cyanobacterial cells. Collectively, our results demonstrate the utility of Synechocystis sp. PCC6803 cells as a host for bioremediation of biphenyl compounds under oligotrophic environments without an organic carbon source.

Identification and characterization of a meta-cleavage product hydrolase involved in biphenyl degradation from Arthrobacter sp. YC-RL1

Polychlorinated biphenyls (PCBs) are a group of persistent organic pollutants (POPs) widely existing in the environment. Arthrobacter sp. YC-RL1 is a biphenyl-degrading bacterium that shows metabolic versatility towards aromatic compounds. A 2-hydroxy-6-oxo-6-phenylhexa-2, 4-dienoate (HOPDA) hydrolase (BphD) gene involved in the biodegradation of biphenyl was cloned from strain YC-RL1 and heterologously expressed in Escherichia coli BL21 (DE3). The recombinant BphD_YC-RL1 was purified and characterized. BphD_YC-RL1 showed the highest activity at 45 °C and pH 7. It was stable under a wide range of temperature (20-50 °C). The enzyme had a K_m value of 0.14 mM, K_cat of 11.61 s^-1, and V_max of 0.027 U/mg. Temperature dependence catalysis exhibited a biphasic Arrhenius Plot with a transition at 20 °C. BphD_YC-RL1 was inactivated by SDS, Tween 20, Tween 80, Trition X-100, DTT, CHAPS, NBS, PMSF, and DEPC, but insensitive to EDTA. Site-directed mutagenesis of the active-site residues revealed that the catalytic triad residues (Ser115, His275, and Asp247) of BphD_YC-RL1 were necessary for its activity. The investigation of BphD_YC-RL1 not only provides new potential enzyme resource for the biodegradation of biphenyl but also helps deepen our understanding on the catalytic process and mechanism.

Insight Into Metabolic Versatility of an Aromatic Compounds-Degrading Arthrobacter sp. YC-RL1

The genus Arthrobacter is ubiquitously distributed in different natural environments. Many xenobiotic-degrading Arthrobacter strains have been isolated and described; however, few have been systematically characterized with regard to multiple interrelated metabolic pathways and the genes that encode them. In this study, the biodegradability of seven aromatic compounds by Arthrobacter sp. YC-RL1 was investigated. Strain YC-RL1 could efficiently degrade p-xylene (PX), naphthalene, phenanthrene, biphenyl, p-nitrophenol (PNP), and bisphenol A (BPA) under both separated and mixed conditions. Based on the detected metabolic intermediates, metabolic pathways of naphthalene, biphenyl, PNP, and BPA were proposed, which indicated that strain YC-RL1 harbors systematic metabolic pathways toward aromatic compounds. Further, genomic analysis uncovered part of genes involved in the proposed pathways. Both intradiol and extradiol ring-cleavage dioxygenase genes were identified in the genome of strain YC-RL1. Meanwhile, gene clusters predicted to encode the degradation of biphenyl (bph), para-substituted phenols (npd) and protocatechuate (pca) were identified, and bphA1A2BCD was proposed to be a novel biphenyl-degrading gene cluster. The complete metabolic pathway of biphenyl was deduced via intermediates and functional gene analysis (bph and pca gene clusters). One of the these genes encoding ring-cleavage dioxygenase in bph gene cluster, a predicted 2,3-dihydroxybiphenyl 1,2-dioxygenase (BphC) gene, was cloned and its activity was confirmed by heterologous expression. This work systematically illuminated the metabolic versatility of aromatic compounds in strain YC-RL1 via the combination of metabolites identification, genomics analysis and laboratory experiments. These results suggested that strain YC-RL1 might be a promising candidate for the bioremediation of aromatic compounds pollution sites.

Intracellular toxicity exerted by PCBs and role of VBNC bacterial strains in biodegradation

Polychlorinated biphenyls (PCBs) are xenobiotic compounds that persists in the environment for long-term, though its productivity is banned. Abatement of the pollutants have become laborious due to it's recalcitrant nature in the environment leading to toxic effects in humans and other living beings. Biphenyl degrading bacteria co-metabolically degrade low chlorinated PCBs using the active metabolic pathway. bph operon possess different genetic arrangements in gram positive and gram negative bacteria. The binding ability of the genes and the active sites were determined by PCB docking studies. The active site of bphA gene with conserved amino acid residues determines the substrate specificity and biodegradability. Accumulation of toxic intermediates alters cellular behaviour, biomass production and downturn the metabolic activity. Several bacteria in the environment attain unculturable state which is viable and metabolically active but not cultivable (VBNC). Resuscitation-promoting factor (Rpf) and Rpf homologous protein retrieve the culturability of the so far uncultured bacteria. Recovery of this adaptive mechanism against various physical and chemical stressors make a headway in understanding the functionality of both environmental and medically important unculturable bacteria. Thus, this paper review about the general aspects of PCBs, cellular toxicity exerted by PCBs, role of unculturable bacterial strains in biodegradation, genes involved and degradation pathways. It is suggested to extrapolate the research findings on extracellular organic matters produced in culture supernatant of VBNC thus transforming VBNC to culturable state.

Characterization of the metabolic pathway and catabolic gene expression in biphenyl degrading marine bacterium Pseudomonas aeruginosa JP-11

Metabolic pathway of biphenyl assimilation and the catabolic gene expression in a marine bacterium Pseudomonas aeruginosa JP-11, isolated from the coastal sediments of Odisha, India have been studied. This strain utilized 98.86% ± 2.29% of biphenyl within 72 h when supplied as the sole source of carbon, however, preferential utilization of glucose was observed over catechol and biphenyl when grown in a complex medium. Combination of chromatographic and spectrophotometric techniques confirmed the catechol pathway and identified 2-Hydroxy-6-oxo-6-phenylhexa-2, 4-dienoate as the intermediate metabolic product. Assimilation of biphenyl was initiated by its dioxygenation, forming cis-2, 3-dihydro-2, 3-dihydroxybiphenyl subsequently transformed to 2-hydroxy-6-oxo-6-phenylhexa-2, 4-dienoate. In the lower pathway, cis-1, 6-dihydroxy-2, 4-cyclohexadiene-1-carboxylic acid was detected which formed catechol before entering into the Krebs cycle. Detection of key enzyme catechol-1, 2-dioxygenase in the cell-free extract of P. aeruginosa JP-11 supported the proposed degradation pathway. The primary enzyme for biphenyl assimilation, biphenyl dioxygenase encoded by bphA gene was found in the genome of the isolate. On increasing biphenyl stress (50, 100, 150 and 200 mg L(-1)), bphA gene showed a significant (P < 0.01) up-regulation upto 43.5 folds. Production of biosurfactant was confirmed and the rhamnolipid synthesizing gene rhlAB was amplified. This gene also showed a significant (P < 0.01) up-regulation upto 258 folds on increasing biphenyl stress.

Complete pyridine-nucleotide-specific conversion of an NADH-dependent ferredoxin reductase

The coenzyme specificity of enzymes is one of the critical parameters for the engineered production of biological compounds using bacteria. Since NADPH is produced abundantly in photosynthetic organisms, conversion of an NADH-specific enzyme into an NADPH-specific one is a useful approach for the efficient carbon-neutral production of biological compounds in photosynthetic organisms. In the present study, an NADH-specific ferredoxin reductase component, BphA4 of biphenyl dioxygenase BphA from Acidovorax sp. strain KKS102, was changed to an NADPH-dependent form using a method combining structure-based systematic mutations and site-directed random mutagenesis. The resultant CRG mutant, in which Glu175-Thr176-Gln177 of an NADH-recognition loop in the wild-type BphA4 was replaced with Cys175-Arg176-Gly177, was highly specific and active for NADPH, and its biochemical and structural properties for NADPH were nearly the same as those of the wild-type BphA4 for NADH. In addition, this mutation project was assessed by a semi-empirical prediction method of mutation effects, and the results suggested that the CRG mutant was one of the best NADPH-specific mutants.

Biodegradation of biphenyl and 2-chlorobiphenyl by a Pseudomonas sp. KM-04 isolated from PCBs-contaminated coal mine soil

The biphenyl-degrading strain, Pseudomonas sp. KM-04, was isolated from polychlorinated biphenyls-contaminated soil sample obtained from the vicinity of a former coal mine. We herein report that strain KM-04 can use biphenyl as a sole carbon source, and resting cells convert biphenyl to its corresponding metabolic intermediates. Incubation of KM-04 with autoclaved mining-contaminated soil for 10 days in a slurry system reduced the levels of biphenyl and 2-chlorobiphenyl by 98.5 % and 82.3 %, respectively. Furthermore, treatment of a mine-soil microcosm with strain KM-04 for 15 days in a composting system under laboratory conditions reduced the levels of biphenyl and 2-chlorobiphenyl by 87.1 % and 68.7 %, respectively. These results suggest that KM-04 is a potential candidate for the biological removal of biphenyl and its chlorinated derivatives from polychlorinated biphenyl-contaminated mining areas.

The Dual Functions of Biphenyl-degrading Ability ofPseudomonassp. KKS102: Energy Acquisition and Substrate Detoxification

The bph operon of Pseudomonas sp. KKS102 is constituted of 11 bph genes which encode enzymes for biphenyl assimilation. Growth of a mutant in which a large part of the bph operon was deleted was inhibited by biphenyl in a concentration-dependent manner. We constructed a series of bph operon deletion mutants and tested for their biphenyl sensitivity. Growth inhibition by biphenyl was more prominent with the mutants defective in bphA1, bphB, bphC, and bphD, which were clustered in the bph operon and working in the early stage of the biphenyl degradation. The mutant defective in bphE, which was working at the late stage and forming a different cluster from the early stage genes, was not much inhibited by biphenyl. These indicate that biphenyl is detoxified by enzymes which function in the early stage of biphenyl assimilation and thus detoxification of substrates as well as energy acquisition could have played an important role in the evolution of the KKS102 bph operon.

Cloning of three 2,3-dihydroxybiphenyl-1,2-dioxygenase genes from Achromobacter sp. BP3 and the analysis of their roles in the biodegradation of biphenyl

Three 2,3-dihydroxybiphenyl 1,2-dioxygenase genes (designated as bphC1, bphC2 and bphC3) were cloned from a biphenyl-degrading strain Achromobacter sp. BP3. The amino acid sequence of BphC1 and BphC3 had high similarity (>99%) with the reported BphCs, while BphC2 showed relatively low identity (29.51-50.17%) with the reported BphCs, which indicated that bphC2 might be a novel gene. The bphC1, bphC2 and bphC3 genes were expressed in Escherichia coli BL21 and the products were homogenously purified. BphC1, BphC2 and BphC3 displayed maximum activity at 30°C, 30°C and 40°C, respectively. Their optimal catalysis pH was 8.0, 9.0 and 9.0, respectively. BphC1 and BphC2 had higher substrate affinity and catalytic efficiency on 2,3-dihydroxybiphenyl, while BphC3 exhibited these features on aromatic monocyclic substrates. The bphC1 gene was only induced by biphenyl and bphC3 was induced by both biphenyl and toluene, while bphC2 was constitutively expressed in strain BP3. These results suggested that BphC1 and BphC3 played a role in the upstream and downstream metabolic pathways of biphenyl, respectively. However, BphC2 might play a supplementary role and contribute more to the upstream than to the downstream pathway.

The key role of a non-active-site residue Met148 on the catalytic efficiency of meta-cleavage product hydrolase BphD

meta-Cleavage product (MCP) hydrolases (EC 3.7.1.9) can catalyze a specific C-C bond fission during the microbial aerobic degradation of aromatics. The previous studies on structure-function relationship of MCP hydrolases mainly focus on the active site residues by site-directed mutagenesis. However, the information about the role of the non-active-site residues is still unclear. In this study, a non-active-site residue Met148 of MCP hydrolase BphD was selected as the mutagenesis site according to the sequence alignments, structure superimpose and the tunnel analysis, which underwent the saturation mutagenesis resulting 19 mutants. The catalytic efficiencies of the mutants on 6-oxo-6-phenylhexa-2,4-dienoic acid (HOPDA) were all decreased compared with the wild-type one except for the M148D mutant. Especially, the M148P mutant exhibited 290-fold lower k cat/K m than that of the wild-type BphD. Transient kinetic analyses of M148P showed the reciprocal relaxation time corresponded to C-C bond cleavage and product release steps (9.6 s(-1)) was 4.08-fold lower than BphD WT (39.2 s(-1)). Tunnel cluster analysis of BphD WT, M148P and M148W demonstrated that only the bulky Trp148 could block tunnel T2 in the BphD WT, but it exhibited slight effects on the catalytic efficiency (0.94-fold of BphD WT). Therefore, product release was not the main reason for the efficiency decrease of M148P. On the other hand, molecular dynamics simulations on the BphD WT and BphD M148P in complex with HOPDA indicated that the dramatic decrease of the catalytic efficiencies of BphD M148P should be due to the unproductive binding of HOPDA. The study demonstrated the catalytic efficiency of MCP hydrolase can be engineered by modification of non-active site residue.

Conjugal transfer of polychlorinated biphenyl/biphenyl degradation genes in Acidovorax sp. strain KKS102, which are located on an integrative and conjugative element

A polychlorinated biphenyl (PCB)/biphenyl degradation gene cluster in Acidovorax sp. strain KKS102, which is very similar to that in Tn4371 from Cupriavidus oxalaticus A5, was transferred to several proteobacterial strains by conjugation. The mobilized DNA fragment consisted of 61,807 bp and carried genes for mating-pair formation (mpf), DNA transfer (dtr), integrase (int), and replication-partition proteins (rep-parAB). In the transconjugants, transferred DNA was integrated at ATTGCATCAG or similar sequences. The circular-form integrative and conjugative element (ICE) was detected by PCR, and quantitative PCR analyses revealed that, in KKS102 cells, the ratio of the circular form to the integrated form was very low (approximately 10(-5)). The circular form was not detected in a mutant of the int gene, which was located at the extreme left and transcribed in the inward direction, and the level of int transcriptional activity was much higher in the circular form than in the integrated form. These findings clearly demonstrated that the genes for PCB/biphenyl degradation in KKS102 cells are located on an ICE, which was named ICE(KKS102)4677. Comparisons of similar ICE-like elements collected from the public database suggested that those of beta- and gammaproteobacteria were distinguishable from other ICE-like elements, including those in alphaproteobacteria, with respect to the gene composition and gene organization.

Metabolic characterization and genes for the conversion of biphenyl in Dyella ginsengisoli LA-4

A complete bph gene cluster (bphLA-4) containing 12,186 bp was amplified from Dyella ginsengisoli LA-4. The bphLA-4 was composed of bphABCXD, and an additional gene encoding a meta-fission product hydrolase was located in the bphX region. BphLA-4 was independently transcribed by the two operons, bphA1A2orf1A3A4BCX0 and bphX1orf2X2X3D, and significantly differed from bphKF707. Both benzoate and catechol induced the expression of both operons. 2-Hydroxypenta-2,4-dienoate was identified as the intermediate of the biphenyl degradation by strain LA-4. This finding suggested that there existed a novel lower pathway of biphenyl degradation in strain LA-4.

Isolation and characteristics of a novel biphenyl-degrading bacterial strain, Dyella ginsengisoli LA-4

A novel biphenyl-degrading bacterial strain LA-4 was isolated from activated sludge. It was identified as Dyella ginsengisoli according to phylogenetic similarity of 16S rRNA gene sequence. This isolate could utilize biphenyl as sole source of carbon and energy, which degraded over 95 mg/L biphenyl within 36 h. The major metabolites formed from biphenyl, such as 2-hydroxy-6-oxo-6-phenylhexa-2,4-dienoic acid (HOPDA) and benzoic acid, were identified by LC-MS. The crude cell extract of strain LA-4 exhibited the activity of 2,3-dihydroxybiphenyl 1,2-dioxygenase (2,3-DHBD) and the kinetic parameters K(m) was 26.48 micromol/L and V(max) was 8.12 U/mg protein. A conserved region of the biphenyl dioxygenase gene bphA1 of strain LA-4 was amplified by PCR and confirmed by DNA sequencing.

Characterization of novel carbazole catabolism genes from gram-positive carbazole degrader Nocardioides aromaticivorans IC177

Nocardioides aromaticivorans IC177 is a gram-positive carbazole degrader. The genes encoding carbazole degradation (car genes) were cloned into a cosmid clone and sequenced partially to reveal 19 open reading frames. The car genes were clustered into the carAaCBaBbAcAd and carDFE gene clusters, encoding the enzymes responsible for the degradation of carbazole to anthranilate and 2-hydroxypenta-2,4-dienoate and of 2-hydroxypenta-2,4-dienoate to pyruvic acid and acetyl coenzyme A, respectively. The conserved amino acid motifs proposed to bind the Rieske-type [2Fe-2S] cluster and mononuclear iron, the Rieske-type [2Fe-2S] cluster, and flavin adenine dinucleotide were found in the deduced amino acid sequences of carAa, carAc, and carAd, respectively, which showed similarities with CarAa from Sphingomonas sp. strain KA1 (49% identity), CarAc from Pseudomonas resinovorans CA10 (31% identity), and AhdA4 from Sphingomonas sp. strain P2 (37% identity), respectively. Escherichia coli cells expressing CarAaAcAd exhibited major carbazole 1,9a-dioxygenase (CARDO) activity. These data showed that the IC177 CARDO is classified into class IIB, while gram-negative CARDOs are classified into class III or IIA, indicating that the respective CARDOs have diverse types of electron transfer components and high similarities of the terminal oxygenase. Reverse transcription-PCR (RT-PCR) experiments showed that the carAaCBaBbAcAd and carDFE gene clusters are operonic. The results of quantitative RT-PCR experiments indicated that transcription of both operons is induced by carbazole or its metabolite, whereas anthranilate is not an inducer. Biotransformation analysis showed that the IC177 CARDO exhibits significant activities for naphthalene, carbazole, and dibenzo-p-dioxin but less activity for dibenzofuran and biphenyl.

Tolerance of the Rieske-type [2Fe-2S] cluster in recombinant ferredoxin BphA3 from Pseudomonas sp. KKS102 to histidine ligand mutations

BphA3 from Pseudomonas sp. KKS102 is a Rieske-type [2Fe-2S] ferredoxin that transfers electrons from an NADH-dependent oxidoreductase, BphA4, to a biphenyl dioxygenase complex. A high-level expression and purification system for the recombinant BphA3 in Escherichia coli was constructed. Two histidine ligands of the Rieske-type cluster in BphA3, were each replaced with serine, cysteine, asparagine and tyrosine. The single mutants, in which either His44 or His65 was replaced with a cysteine residue (CH and HC mutants respectively), and the double mutant, in which both histidine residues were replaced with cysteine residue (CC mutant), accumulated to high levels in the E. coli cells, while the other single mutants did not. The purified WT (wild-type) protein showed characteristic near-UV and visible absorption and CD spectra of Rieske-type clusters. The X-ray absorption spectra were suggestive of the existence of [2Fe-2S] clusters, with one histidine and three cysteine ligands in the CH and HC mutants, and an [2Fe-2S] cluster with four cysteine ligands in the CC mutant. The BphA4-dependent cytochrome c reductase activities of the mutants were less than 0.3% of that of the WT protein. The redox potential of the WT protein determined by cyclic voltammetry was -180+/-5 mV compared with the standard hydrogen electrode, and that of the CH mutant was approx. 175 mV lower. The changes in the near-UV and visible absorption spectra of the mutants showed that the reduced iron-sulphur clusters in the mutants were unstable. His44 and His65 in BphA3 can be replaced with cysteine residues, but are required for the stabilization of the reduced form of the cluster.

Aerobic degradation of polychlorinated biphenyls

The microbial degradation of polychlorinated biphenyls (PCBs) has been extensively studied in recent years. The genetic organization of biphenyl catabolic genes has been elucidated in various groups of microorganisms, their structures have been analyzed with respect to their evolutionary relationships, and new information on mobile elements has become available. Key enzymes, specifically biphenyl 2,3-dioxygenases, have been intensively characterized, structure/sequence relationships have been determined and enzymes optimized for PCB transformation. However, due to the complex metabolic network responsible for PCB degradation, optimizing degradation by single bacterial species is necessarily limited. As PCBs are usually not mineralized by biphenyl-degrading organisms, and cometabolism can result in the formation of toxic metabolites, the degradation of chlorobenzoates has received special attention. A broad set of bacterial strategies to degrade chlorobenzoates has recently been elucidated, including new pathways for the degradation of chlorocatechols as central intermediates of various chloroaromatic catabolic pathways. To optimize PCB degradation in the environment beyond these metabolic limitations, enhancing degradation in the rhizosphere has been suggested, in addition to the application of surfactants to overcome bioavailability barriers. However, further research is necessary to understand the complex interactions between soil/sediment, pollutant, surfactant and microorganisms in different environments.

Biphenyl and benzoate metabolism in a genomic context: outlining genome-wide metabolic networks in Burkholderia xenovorans LB400

We designed and successfully implemented the use of in situ-synthesized 45-mer oligonucleotide DNA microarrays (XeoChips) for genome-wide expression profiling of Burkholderia xenovorans LB400, which is among the best aerobic polychlorinated biphenyl degraders known so far. We conducted differential gene expression profiling during exponential growth on succinate, benzoate, and biphenyl as sole carbon sources and investigated the transcriptome of early-stationary-phase cells grown on biphenyl. Based on these experiments, we outlined metabolic pathways and summarized other cellular functions in the organism relevant for biphenyl and benzoate degradation. All genes previously identified as being directly involved in biphenyl degradation were up-regulated when cells were grown on biphenyl compared to expression in succinate-grown cells. For benzoate degradation, however, genes for an aerobic coenzyme A activation pathway were up-regulated in biphenyl-grown cells, while the pathway for benzoate degradation via hydroxylation was up-regulated in benzoate-grown cells. The early-stationary-phase biphenyl-grown cells showed similar expression of biphenyl pathway genes, but a surprising up-regulation of C(1) metabolic pathway genes was observed. The microarray results were validated by quantitative reverse transcription PCR with a subset of genes of interest. The XeoChips showed a chip-to-chip variation of 13.9%, compared to the 21.6% variation for spotted oligonucleotide microarrays, which is less variation than that typically reported for PCR product microarrays.

Characterization of transcriptional regulatory genes for biphenyl degradation in Rhodococcus sp. strain RHA1

Transcription of the bphA1A2A3A4C1B genes, which are responsible for the conversion of biphenyl and polychlorinated biphenyl to the meta-cleavage products in Rhodococcus sp. strain RHA1, was examined. The bphA1 promoter (P(bphA1)) was identified and was shown to promote transcription induction by biphenyl and ethylbenzene. An 8.8-kb HindIII fragment that promotes transcription induction of P(bphA1) in Rhodococcus erythropolis IAM1399 was isolated from the region downstream of bphB by using a reporter plasmid containing P(bphA1). Analysis of the nucleotide sequence of this fragment revealed a set of putative two-component regulatory system genes, which were designated bphS and bphT. Deletion analysis of the 8.8-kb HindIII fragment indicated that bphT is responsible for the basal activation of P(bphA1) and that both bphS and bphT are required for the elevated basal activation of and transcriptional induction by biphenyl of P(bphA1). These results support the notion that bphS and bphT encode a sensor kinase and a response regulator, respectively, of a two-component regulatory system. The bphS and bphT genes promote transcriptional induction by a variety of aromatic compounds, including biphenyl, benzene, alkylbenzenes, and chlorinated benzenes. A promoter activity assay and reverse transcription (RT)-PCR analysis revealed a weak constitutive promoter in the adjacent region upstream of bphS. RT-PCR analysis indicated that there is induced transcription of bphA1 through bphT, in which P(bphA1) is thought to take part. An insertionally inactivated bphS mutant, SDR1, did not grow on biphenyl. Growth was restored by introduction of an intact bphS gene into SDR1. These results indicate that at least bphS is indispensably responsible for the growth of RHA1 on biphenyl.

Dechlorination pathways of ortho-substituted PCBs by UV irradiation in n-hexane and their correlation to the charge distribution on carbon atom

The photodegradations of 22 individual polychlorinated biphenyl (PCB) congeners (including 21 non-coplanar ortho substituted and one non-ortho substituted) by irradiation with ultraviolet lamp in n-hexane solution were studied. Photoproducts were identified by matching their retention times and mass spectra with those of authentic standards. PCB congener with less than two chlorides was photodegraded within half an hour, if more than three chlorine on ring, the photodechlorination time for PCB needs one and half hours or more, sometimes even longer than 15 h. The half-life of PCB degradation by photodechlorination was much shorter than that by anaerobic biological dechlorination. Charge distribution on carbon atom combined with the monitoring products of individual PCB congeners were used to deduce the photodegradation pathways. The higher the charge distribution for carbon to which chlorine is attached, the easier for photodechlorination to occur. A lot of chlorine atoms attached PCB, the dechlorination was found to occur prior to the carbon with higher charge distribution at the benzene ring with more chlorine atoms attached.

Novel approach to the improvement of biphenyl and polychlorinated biphenyl degradation activity: promoter implantation by homologous recombination

To improve the capabilities of microorganisms relevant for biodegradation, we developed a new genetic approach and applied it to the bph operon (bphEGF[orf4]A1A2A3CD[orf1]A4R) of Pseudomonas sp. strain KKS102 to enhance its biphenyl- and polychlorinated biphenyl (PCB)-degrading activity. A native promoter of the bph operon, which was under control, was replaced through homologous recombination by a series of promoters that had constitutive activity. By testing a series of promoters with various strengths, we were able to obtain strains that have enhanced degradation activity for biphenyl and PCBs. This strategy removes the rate-limiting factor associated with transcription and has the potential to improve the degradation activity of a wide variety of microorganisms involved in biodegradation.

2-Hydroxypenta-2,4-dienoate metabolic pathway genes in a strong polychlorinated biphenyl degrader, Rhodococcus sp. strain RHA1

A gram-positive polychlorinated biphenyl (PCB) degrader, Rhodococcus sp. strain RHA1, metabolizes biphenyl through the 2-hydroxypenta-2,4-dienoate (HPD) and benzoate metabolic pathways. The HPD metabolic pathway genes, the HPD hydratase (bphE1), 4-hydroxy-2-oxovalerate aldolase (bphF1), and acetaldehyde dehydrogenase (acylating) (bphG) genes, were cloned from RHA1. The deduced amino acid sequences of bphGF1E1 have 30 to 58% identity with those of the HPD metabolic pathway genes of gram-negative bacteria. The order of these genes, bphG-bphF1-bphE1, differs from that of the HPD metabolic pathway genes, bphE-bphG-bphF, in gram-negative degraders of PCB, phenol, and toluene. Reverse transcription-PCR experiments indicated that the bphGF1E1 genes are inducibly cotranscribed in cells grown on biphenyl and ethylbenzene. Primer extension analysis revealed that the transcriptional initiation site exists within the bphR gene located adjacent to and upstream of bphG, which is deduced to code a transcriptional regulator. The respective enzyme activities of bphGF1E1 gene products were detected in Rhodococcus erythropolis IAM1399 carrying a bphGF1E1 plasmid. The insertional inactivation of the bphE1, bphF1, and bphG genes resulted in the loss of the corresponding enzyme activities and diminished growth on both biphenyl and ethylbenzene. Severe growth interference was observed during growth on biphenyl. The growth defects were partially restored by the introduction of plasmids containing the respective intact genes. These results indicated that the cloned bphGF1E1 genes are not only responsible for the primary metabolism of HPD during growth on both biphenyl and ethylbenzene but are also involved in preventing the accumulation of unexpected toxic metabolites, which interfere with the growth of RHA1.

BphS, a key transcriptional regulator of bph genes involved in polychlorinated biphenyl/biphenyl degradation in Pseudomonas sp. KKS102

The bph genes in Pseudomonas sp. KKS102, which are involved in the degradation of polychlorinated biphenyl/biphenyl, are induced in the presence of biphenyl. In this study our goal was to understand the regulatory mechanisms involved in the inducible expression. The bph genes (bphEGF(orf4)A1A2A3BCD(orf1)A4R) constitute an operon, and its expression is strongly dependent on the pE promoter located upstream of the bphE gene. A bphS gene, whose deduced amino acid sequence showed homology with the GntR family transcriptional repressors, was identified at the upstream region of the bphE gene. Disruption of the bphS gene resulted in constitutive expression of bph genes, suggesting that the bphS gene product negatively regulated the pE promoter. The gel retardation and DNase footprinting analyses demonstrated specific binding of BphS to the pE promoter region and identified four BphS binding sites that were located within and immediately downstream of the -10 box of the pE promoter. The four binding sites were functional in repression because their respective elimination resulted in derepression of the pE promoter. The binding of BphS was abolished in the presence of 2-hydroxy-6-oxo-6-phenylhexa-2,4-dienoic acid, an intermediate compound in the biphenyl degradation pathway. We concluded that the negative regulator BphS plays a central role in the regulation of bph gene expression through its action at the pE promoter.

Genetic characterization and evolutionary implications of a car gene cluster in the carbazole degrader Pseudomonas sp. strain CA10

The nucleotide sequences of the 27,939-bp-long upstream and 9,448-bp-long downstream regions of the carAaAaBaBbCAc(ORF7)Ad genes of carbazole-degrading Pseudomonas sp. strain CA10 were determined. Thirty-two open reading frames (ORFs) were identified, and the car gene cluster was consequently revealed to consist of 10 genes (carAaAaBaBbCAcAdDFE) encoding the enzymes for the three-step conversion of carbazole to anthranilate and the degradation of 2-hydroxypenta-2,4-dienoate. The high identities (68 to 83%) with the enzymes involved in 3-(3-hydroxyphenyl)propionic acid degradation were observed only for CarFE. This observation, together with the fact that two ORFs are inserted between carD and carFE, makes it quite likely that the carFE genes were recruited from another locus. In the 21-kb region upstream from carAa, aromatic-ring-hydroxylating dioxygenase genes (ORF26, ORF27, and ORF28) were found. Inductive expression in carbazole-grown cells and the results of homology searching indicate that these genes encode the anthranilate 1,2-dioxygenase involved in carbazole degradation. Therefore, these ORFs were designated antABC. Four homologous insertion sequences, IS5car1 to IS5car4, were identified in the neighboring regions of car and ant genes. IS5car2 and IS5car3 constituted the putative composite transposon containing antABC. One-ended transposition of IS5car2 together with the 5' portion of antA into the region immediately upstream of carAa had resulted in the formation of IS5car1 and ORF9. In addition to the insertion sequence-dependent recombination, gene duplications and presumed gene fusion were observed. In conclusion, through the above gene rearrangement, the novel genetic structure of the car gene cluster has been constructed. In addition, it was also revealed that the car and ant gene clusters are located on the megaplasmid pCAR1.

Ralstonia metallidurans CH34 RpoN sigma factor and the control of nitrogen metabolism and biphenyl utilization

Ralstonia metallidurans CH34 can use biphenyl as carbon and energy source when provided with the catabolic transposon Tn4371. Previous results suggested that this property was dependent on the RNA polymerase subunit sigma(54). The authors sequenced the CH34 rpoN gene and flanking DNA and isolated a CH34 rpoN-deficient strain. Analysis of the sequence revealed a set of features conserved in all rpoN genes and flanking DNA regions previously analysed in other bacterial species. Nevertheless, despite this conservation, CH34 differed even from the closely related strain R. eutropha H16 by one particular ORF. The rpoN null mutation did not affect expression of the Tn4371 bph operon although it did alter the ability of the Tn4371 host strain to grow on biphenyl. The CH34 rpoN mutant had lost the capacity for autotrophic growth and for responding to poor nitrogen sources by a decrease in urease and proline oxidase activity. CH34 RNA polymerase sigma(54) thus positively controls autotrophy as well as nitrogen metabolism but only indirectly affects Tn4371-directed biphenyl utilization.

Crystal structure of 2-hydroxyl-6-oxo-6-phenylhexa-2,4-dienoic acid (HPDA) hydrolase (BphD enzyme) from the Rhodococcus sp. strain RHA1 of the PCB degradation pathway

2-Hydroxyl-6-oxo-6-phenylhexa-2,4-dienoic acid (HPDA) hydrolase (the BphD enzyme) hydrolyzes a ring-cleavage product of an aromatic compound generated in a biphenyl/polychlorinated biphenyl (PCB) degradation pathway of bacteria. The crystal structure of the BphD enzyme has been determined at 2.4 A resolution by the multiple isomorphous replacement method. The final refined model of the BphD enzyme yields an R-factor of 17.5 % at 2.4 A resolution with reasonable geometry. The BphD enzyme is an octameric enzyme with a 422 point-group symmetry. The subunit can be divided into core and lid domains. The active site of the enzyme is situated in the substrate-binding pocket, which is located between the two domains. The substrate-binding pocket can be divided into hydrophobic and hydrophilic regions. This feature of the pocket seems to be necessary for substrate binding, as the substrate is composed of hydrophilic and hydrophobic parts. The proposed orientation of the substrate seems to be consistent with the general catalytic mechanism of alpha/beta-hydrolases.

Occurrence of Tn4371-related mobile elements and sequences in (chloro)biphenyl-degrading bacteria

Tn4371, a 55-kb transposable element involved in the degradation and biphenyl or 4-chlorobiphenyl identified in Ralstonia eutropha A5, displays a modular structure including a phage-like integrase gene (int), a Pseudomonas-like (chloro)biphenyl catabolic gene cluster (bph), and RP4- and Ti-plasmid-like transfer genes (trb) (C. Merlin, D. Springael, and A. Toussaint, Plasmid 41:40-54, 1999). Southern blot hybridization was used to examine the presence of different regions of Tn4371 in a collection of (chloro)biphenyl-degrading bacteria originating from different habitats and belonging to different bacterial genera. Tn4371-related sequences were never detected on endogenous plasmids. Although the gene probes containing only bph sequences hybridized to genomic DNA from most strains tested, a limited selection of strains, all beta-proteobacteria, displayed hybridization patterns similar to the Tn4371 bph cluster. Homology between Tn4371 and DNA of two of those strains, originating from the same area as strain A5, extended outside the catabolic genes and covered the putative transfer region of Tn4371. On the other hand, none of the (chloro)biphenyl degraders hybridized with the outer left part of Tn4371 containing the int gene. The bph catabolic determinant of the two strains displaying homology to the Tn4371 transfer genes and a third strain isolated from the A5 area could be mobilized to a R. eutropha recipient, after insertion into an endogenous or introduced IncP1 plasmid. The mobilized DNA of those strains included all Tn4371 homologous sequences previously identified in their genome. Our observations show that the bph genes present on Tn4371 are highly conserved between different (chloro)biphenyl-degrading hosts, isolated globally but belonging mainly to the beta-proteobacteria. On the other hand, Tn4371-related mobile elements carrying bph genes are apparently only found in isolates from the environment that provided the Tn4371-bearing isolate A5.

Biochemical and genetic bases of microbial degradation of polychlorinated biphenyls (PCBs)

The microbial degradation of polychlorinated biphenyls (PCBs) has been extensively conducted by many workers, and the following general results have been obtained. (1) PCBs are degraded oxidatively by aerobic bacteria and other microorganisms such as white rot fungi. PCBs are also reductively dehalogenated by anaerobic microbial consortia. (2) The biodegradability of PCBs is highly dependent on chlorine substitution, i.e., number and position of chlorine. The degradation and dehalogenation capabilities are also highly strain dependent. (3) Biphenyl-utilizing bacteria can cometabolize many PCB congeners to chlorobenzoates by biphenl-catabolic enzymes. (4) Enzymes involved in the PCB degradation were purified and characterized. Biphenyl dioxygenase, ring-cleavage dioxygenase, and hydrolase are crystallized, and two ring-cleavage dioxygenases are being solved by x-ray crystallography. (5) The bph gene clusters responsible for PCB degradation are cloned from a variety of bacterial strains. The structure and function are analyzed with respect to the evolutionary relationship. (6) The molecular engineering of biphenyl dioxygenases is successfully performed by DNA shuffling, domain exchange, and subunit exchange. The evolved enzymes exhibit wide and enhanced degradation capacities for PCBs and other aromatic compounds.

Crystal structure of NADH-dependent ferredoxin reductase component in biphenyl dioxygenase

Oxidative biodegradation of aromatic compounds by bacteria usually begins with hydroxylation of the aromatic ring by multi-component dioxygenases like benzene dioxygenase, biphenyl dioxygenase, and others. These enzymes are composed of ferredoxin reductase, ferredoxin, and terminal oxygenase. Reducing equivalents that originate from NADH are transferred from ferredoxin reductase to ferredoxin and, in turn, to the terminal oxygenase, thus resulting in the activation of a dioxygen. BphA4 is the ferredoxin reductase component of biphenyl dioxygenase from Pseudomonas sp. strain KKS102. The amino acid sequence of BphA4 exhibits significant homology with the putidaredoxin reductase of the cytochrome P450cam system in Pseudomonas putida, as well as with various other oxygenase-coupled NADH-dependent ferredoxin reductases (ONFRs) of bacteria. To date, no structural information has been provided for the ferredoxin reductase component of the dioxygenase systems. In order to provide a structural basis for discussing the mechanism of electron transport between ferredoxin reductase and ferredoxin, crystal structures of BphA4 and its NADH complex were solved. The three-dimensional structure of BphA4 is different from those of ferredoxin reductases whose structures have already been determined, but adopts essentially the same fold as the enzymes of the glutathione reductase (GR) family. Also the three-dimensional structure of the first two domains of BphA4 adopts a fold similar to that of adrenodoxin reductase (AdR) in the mitochondrial cytochrome P450 system. Comparing the amino acid sequence with what is known of the three-dimensional structure of BphA4 strongly suggests that the other ONFRs have secondary structural features that are similar to that of BphA4. This analysis of the crystal structures of BphA4 suggests that Lys53 and Glu159 seem to be involved in the hydride transfer from NADH to FAD. Since the amino acid residues around the active site, some of which seem to be important to electron transport, are highly conserved among ONFRs, it is likely that the mechanism of electron transport of BphA4 is quite applicable to other ONFRs.

Versatile transcription of biphenyl catabolic bph operon in Pseudomonas pseudoalcaligenes KF707

Pseudomonas pseudoalcaligenes KF707 possesses a chromosomally encoded bph gene cluster responsible for the catabolism of biphenyl/polychlorinated biphenyls. The gene cluster consists of (orf0)bphA1A2(orf3)bphA3A4BCX0X1X2X3D. We studied the role of orf0 and transcription in the KF707 bph operon. Primer extension analyses revealed that at least as many as six transcriptional initiation sites exist upstream of orf0, bphA1, bphX0, bphX1, and bphD, including two upstream of bphD. The orf0-disruptant failed to grow on biphenyl but accumulated large amounts of the biphenyl ring meta-cleavage yellow compound (2-hydroxy-6-oxo-6-phenylhexa-2, 4-dienoate). Western blot analysis revealed that ORF0 protein is inducibly expressed in KF707 in the presence of biphenyl. Gel shift assay revealed that ORF0 directly binds to the orf0 operator region. This binding was greatly enhanced by addition of the biphenyl ring meta-cleavage yellow compound. These results indicated that orf0, bphA1A2(orf3)bphA3A4BC and bphX0X1X2X3D are independently transcribed, and that ORF0 protein belonging to the GntR family is involved in the regulation of the bph operon in KF707 and is absolutely required for the expression of orf0 and bphX0X1X2X3D.

Expression of the bph genes involved in biphenyl/PCB degradation in Pseudomonas sp. KKS102 induced by the biphenyl degradation intermediate, 2-hydroxy-6-oxo-6-phenylhexa-2,4-dienoic acid

The bph genes involved in PCB/biphenyl degradation in Pseudomonas sp. KKS102 are clustered as bphEGFA1A2A3BCDA4R. The bph genes are inducibly expressed in the presence of biphenyl. In order to understand the induction more fully, the inducer of bph gene expression was investigated. To identify the inducer molecule, we constructed four deletion mutants of the structural genes and analyzed the inducibility of the bphE gene in each mutant strain. In the wild-type cell and the bphD deletion mutant, the levels of the bphE transcript were enhanced in the presence of biphenyl. On the other hand, in the bphA, bphB, and bphC deletion mutants, levels of the bphE transcript were not enhanced in the presence of biphenyl. These results demonstrated that the series of reactions catalyzed by biphenyl dioxygenase (BphA), dihydrodiol dehydrogenase (BphB), and 2, 3-dihydroxybiphenyl dioxygenase (BphC) are necessary to convert biphenyl to the inducer. It is known that these reactions convert biphenyl to 2-hydroxy-6-oxo-6-phenylhexa-2,4-dienoic acid (HOPDA), and it was found that the expression of the bph genes was induced by purified HOPDA. These results clearly indicate that HOPDA is the inducer of the bph genes in KKS102.

Characterization of the pcbE gene encoding 2-hydroxypenta-2,4-dienoate hydratase in Pseudomonas sp. DJ-12

Nucleotide sequence extending 2,3-dihydroxybiphenyl 1,2-dioxygenase gene (pcbC) and 2-hydroxy-6-oxo-6-phenylhexa-2,4-dienoate hydrolase gene (pcbD) of Pseudomonas sp. DJ-12 was previously analyzed and the two genes were present in the order of pcbD-pcbC preceded by a promoter from Pseudomonas sp. DJ-12. In this study, a 3.8-kb nucleotide sequence located downstream of the pcbC gene was analyzed to have three open reading frames (ORFs) that are designated as orf1, pcbE and orf2 genes. All of the ORFs were preceded by each ribosome-binding sequence of 5-GGAXA-3 (X=G or A). However, no promoter-like sequence and transcription terminator sequence were found in the analyzed region, downstream of pcbC gene. Therefore, the gene cluster appeared to be present in the order of pcbD-pcbC-orf1-pcbE-orf2 as an operon, which is unique organization characterized so far in biphenyl- and PCB-degrading bacteria. The orf1 gene was composed of 1,224 base pairs which can encode a polypeptide of molecular weight 44,950 containing 405 amino acid residues. A deduced amino acid sequence of the orf1 gene product exhibited 21-33% identity with those of indole dioxygenase and phenol hydroxylase components. The pcbE gene was composed of 783 base pairs encoding 2-hydroxypenta-2,4-dienoate hydratase involved in the 4-chlorobiphenyl catabolism. The orf2 gene was composed of 1,017 base pairs encoding a polypeptide of molecular weight 37,378 containing 338 amino acid residues. A deduced amino acid sequence of the orf2 gene product exhibited 31% identity with that of a nitrilotriacetate monooxygenase component.

Identification and sequencing of beta-myrcene catabolism genes from Pseudomonas sp. strain M1

The M1 strain, able to grow on beta-myrcene as the sole carbon and energy source, was isolated by an enrichment culture and identified as a Pseudomonas sp. One beta-myrcene-negative mutant, called N22, obtained by transposon mutagenesis, accumulated (E)-2-methyl-6-methylen-2,7-octadien-1-ol (or myrcen-8-ol) as a unique beta-myrcene biotransformation product. This compound was identified by gas chromatography-mass spectrometry. We cloned and sequenced the DNA regions flanking the transposon and used these fragments to identify the M1 genomic library clones containing the wild-type copy of the interrupted gene. One of the selected cosmids, containing a 22-kb genomic insert, was able to complement the N22 mutant for growth on beta-myrcene. A 5,370-bp-long sequence spanning the region interrupted by the transposon in the mutant was determined. We identified four open reading frames, named myrA, myrB, myrC, and myrD, which can potentially code for an aldehyde dehydrogenase, an alcohol dehydrogenase, an acyl-coenzyme A (CoA) synthetase, and an enoyl-CoA hydratase, respectively. myrA, myrB, and myrC are likely organized in an operon, since they are separated by only 19 and 36 nucleotides (nt), respectively, and no promoter-like sequences have been found in these regions. The myrD gene starts 224 nt upstream of myrA and is divergently transcribed. The myrB sequence was found to be completely identical to the one flanking the transposon in the mutant. Therefore, we could ascertain that the transposon had been inserted inside the myrB gene, in complete agreement with the accumulation of (E)-2-methyl-6-methylen-2,7-octadien-1-ol by the mutant. Based on sequence and biotransformation data, we propose a pathway for beta-myrcene catabolism in Pseudomonas sp. strain M1.

The phnIJ genes encoding acetaldehyde dehydrogenase (acylating) and 4-hydroxy-2-oxovalerate aldolase in Pseudomonas sp. DJ77 and their evolutionary implications

The two final steps of meta-cleavage pathway for catechol degradation involve conversion of 4-hydroxy-2-oxovalerate, via acetaldehyde, to acetyl coenzyme A. We report here the complete nucleotide sequences and overexpression of the phnIJ genes for an acetaldehyde dehydrogenase (acylating) (ADA) and a 4-hydroxy-2-oxovalerate aldolase (HOA) from the meta-pathway operon of the phenanthrene-degrading bacterium, Pseudomonas sp. strain DJ77. Additional partial sequence analysis of adjacent DNA shows the gene order within the operon to be phnHIJ, identical to the order found for the isofunctional genes in the other meta-pathway operons. The deduced amino acid sequences of the PhnI (312 amino acids) and PhnJ (343 amino acids) have identities of 51-71% with the corresponding genes of dmp, xyl, nah, bph_LB400, bph_KKS102, tod, cum, cmt, and MTCY03C7 operons. The phylogenetic analyses reveal the evolutionary relationships of HOA and ADA.

Development of hybrid strains for the mineralization of chloroaromatics by patchwork assembly

The persistence of chloroaromatic compounds can be caused by various bottlenecks, such as incomplete degradative pathways or inappropriate regulation of these pathways. Patchwork assembly of existing pathways in novel combinations provides a general route for the development of strains degrading chloroaromatics. The recruitment of known complementary enzyme sequences in a suitable host organism by conjugative transfer of genes might generate a functioning hybrid pathway for the mineralization of some chloroaromatics not degraded by the parent organisms. The rational combination uses (a) peripheral, funneling degradation sequences originating from aromatics-degrading strains to fulfill the conversion of the respective analogous chloroaromatic compound to chlorocatechols as the central intermediates; (b) a central chlorocatechol degradation sequence, the so-called modified ortho pathway, which brings about elimination of chlorine substituents; and (c) steps of the 3-oxoadipate pathway to reach the tricarboxylic acid cycle. The genetic organization of these pathway segments has been well characterized. The specificity of enzymes of the xylene, benzene, biphenyl, and chlorocatechol pathways and the specificity of the induction systems for the chlorinated substrates are analyzed in various organisms to illustrate eventual bottlenecks and to provide alternatives that are effective in the conversion of the "new" substrate. Hybrid pathways are investigated in "new" strains degrading chlorinated benzoates, toluenes, benzenes, and biphenyls. Problems occurring after the conjugative DNA transfer and the "natural" solution of these are examined, such as the prevention of misrouting into the meta pathway, to give a functioning hybrid pathway. Some examples clearly indicate that patchwork assembly also happens in nature.

Implications of the xylQ gene of TOL plasmid pWW102 for the evolution of aromatic catabolic pathways

Pseudomonas putida strain O2C2 is able to grow on toluene, m-xylene and p-xylene through benzoate and the corresponding methylbenzoates (toluates). The catabolic genes are encoded on a large TOL plasmid, pWW102, of > 220 kb. The complete catabolic genes were cloned on four large overlapping restriction fragments covering a total of 28 kb of the plasmid, which was carefully mapped by restriction enzyme analysis. The presence of the xyl genes on the cloned DNA was confirmed by assay of representative enzymes of both operons. Virtually all the genes were located on the cloned DNA by hybridization of Southern blots with gene-specific probes from related pathways of other catabolic plasmids. Within the limitations of available restriction sites, the analysis showed that the genes are in two blocks. The major block carries the meta pathway operon xylXYZLTEGFJQKIH with the two regulatory genes xylSR immediately downstream. The upper pathway operon xylUWCMAB(N) is about 2-3 kb downstream of the regulatory genes and transcribed in the same direction as the meta pathway operon. Within each operon the gene order appears to be identical to that found in other TOL plasmids, but the relative location of the operons most closely resembles that found on plasmid pWW53, although there is no evidence of any xyl duplications on pWW102. The nucleotide sequence of the xylQ gene for the acetaldehyde dehydrogenase (acylating; ADA), together with the 3'-end of the upstream xylJ (for 2-oxopent-4-enoate hydratase) and the 5'-end of the downstream xylK (for 4-hydroxy-2-oxovalerate aldolase), was determined. The xylQ gene was ligated into expression vector pTrc99a and high levels of XylQ protein were detected by enzyme assay and by SDS-PAGE. All three genes xylJQK showed a high degree of homology with genes encoding isofunctional proteins from other Pseudomonas meta pathways, the highest being with the naphthalene catabolic genes nahLOM from the plasmid of Pseudomonas sp. NCIB 9816. The implications of the sequence homologies to the evolution of these pathways are discussed.

Localization and sequence analysis of the phnH gene encoding 2-hydroxypent-2,4-dienoate hydratase in Pseudomonas sp. strain DJ77

The phnDEFG genes of Pseudomonas sp. DJ77, which are responsible for the degradation of polyaromatic hydrocarbons and chlorinated aromatics, were located previously on the 6.8 kb XhoI fragment of chromosomal DNA. Here, we sequenced a downstream region hitherto unknown and identified the phnH gene encoding a 2-hydroxypent-2,4-dienoate hydratase, which is required for the conversion of 2-hydroxypent-2,4-dienoate to 4-hydroxy-2-oxovalerate in the meta-cleavage pathway of catechols. The relative position of the hydratase gene in the phn operon is unique compared to the other meta-cleavage operons which have a dehydrogenative branch of the pathway. The PhnH hydratase contains 264 amino acids with a Mr of 28048. The deduced amino acid sequence of the PhnH enzyme is 60.9-31.6% identical to those of homologous enzymes encoded by the todG, bphE, cmtF, bphH, bphX1, xylJ, dmpE, cumE, MTCY03C7.20 and etbE genes.

Genetic characterization and expression in heterologous hosts of the 3-(3-hydroxyphenyl)propionate catabolic pathway of Escherichia coli K-12

We report the complete nucleotide sequence of the gene cluster encoding the 3-(3-hydroxyphenyl)propionate (3-HPP) catabolic pathway of Escherichia coli K-12. Sequence analysis revealed the existence of eight genes that map at min 8 of the chromosome, between the lac and hemB regions. Six enzyme-encoding genes account for a flavin-type monooxygenase (mhpA), the extradiol dioxygenase (mhpB), and the meta-cleavage pathway (mhpCDFE). The order of these catabolic genes, with the sole exception of mhpF, parallels that of the enzymatic steps of the pathway. The mhpF gene may encode the terminal acetaldehyde dehydrogenase (acylating) not reported previously in the proposed pathway. Enzymes that catalyze the early reactions of the pathway, MhpA and MhpB, showed the lowest level of sequence similarity to analogous enzymes of other aromatic catabolic pathways. However, the genes mhpCDFE present the same organization and appear to be homologous to the Pseudomonas xyl, dmp, and nah meta-pathway genes, supporting the hypothesis of the modular evolution of catabolic pathways and becoming the first example of this type of catabolic module outside the genus Pseudomonas. Two bacterial interspersed mosaic elements were found downstream of the mhpABCDFE locus and flank a gene, orfT, which encodes a protein related to the superfamily of transmembrane facilitators that might be associated with transport. All of the genes of the 3-HPP cluster are transcribed in the same direction, with the sole exception of mhpR. Inducible expression of the mhp catabolic genes depends upon the presence, in the cis or trans position, of a functional mhpR gene, which suggests that the mhpR gene product is the activator of the 3-HPP biodegradative pathway. The primary structure of MhpR revealed significant similarities to that of members of the IclR subfamily of transcriptional regulators. A 3-HPP catabolic DNA cassette was engineered and shown to be functional not only in enteric bacteria (E. coli and Salmonella typhimurium) but also in Pseudomonas putida and Rhizobium meliloti, thus facilitating its potential application to improve the catabolic abilities of bacterial strains for degradation of aromatic compounds.

The bphDEF meta-cleavage pathway genes involved in biphenyl/polychlorinated biphenyl degradation are located on a linear plasmid and separated from the initial bphACB genes in Rhodococcus sp. strain RHA1

The bphACB genes responsible for the initial oxidation of the aromatic ring of biphenyl/polychlorinated biphenyls (PCB) to meta-cleavage product in Rhodococcus sp. RHA1 have been characterized. We cloned the 6.1 kb EcoRI fragment containing another extradiol dioxygenase gene (etbC) which was induced during the growth on ethylbenzene. The bphD, bphE and bphF encoding 2-hydroxy-6-oxo-6-phenylhexa-2,4-dienoate (HOPD) hydrolase, 2-hydroxypenta-2,4-dienoate hydratase and 4-hydroxy-2-oxovalerate aldolase, respectively, were found downstream of etbC. The deduced amino acid (aa) sequence of RHA1 bphD and bphE had 27-33% and 32-38% identity, respectively, with those of the corresponding genes in Pseudomonas. BphE and BphF are closely related to the corresponding homoprotocatechuate meta-cleavage pathway enzymes of Escherichia coli C. The bphD and bphF were expressed in E. coli and the BphD activity was detected. The etbCphDEF genes were transcribed in biphenyl and ethylbenzene growing cells. Pulsed field gel electrophoresis (PFGE) analysis indicated that RHA1 contains three large linear plasmids. Southern blot analysis indicated that the meta-cleavage pathway for biphenyl/PCB catabolism in RHA1 is directed by the 390 kb plasmid borne bphDEF genes located separately from bphACB gene cluster on the 1100 kb plasmid.

Characterization of three distinct extradiol dioxygenases involved in mineralization of dibenzofuran by Terrabacter sp. strain DPO360

The dibenzofuran-degrading bacterial strain DPO360 represents a new species of the genus Terrabacter together with the previously described dibenzofuran-mineralizing bacterial strain DPO1361 (K.-H. Engesser, V. Strubel, K. Christoglou, P. Fischer, and H. G. Rast, FEMS Microbiol. Lett. 65:205-210, 1989; V. Strubel, Ph.D. thesis, University of Stuttgart, Stuttgart, Germany, 1991; V. Strubel, H. G. Rast, W. Fietz, H.-J. Knackmuss, and K.-H. Engesser, FEMS Microbiol. Lett. 58:233-238, 1989). Two 2,3-dihydroxybiphenyl-1,2-dioxygenases (BphC1 and BphC2) and one catechol-2,3-dioxygenase (C23O) were shown to be expressed in Terrabacter sp. strain DPO360 growing with dibenzofuran as a sole source of carbon and energy. These enzymes exhibited strong sensitivity to oxygen. They were purified to apparent homogeneity as homodimers (BphC and BphC2) and as a homotetrameric catechol-2,3-dioxygenase (C23O). According to their specificity constants kcat/Km, both BphC1 and BphC2 were shown to be responsible for the cleavage of 2,2',3-trihydroxybiphenyl, the first metabolite in dibenzofuran mineralization along the angular dioxygenation pathway. With this substrate, BphC2 exhibited a considerably higher kcat/Km, value (183 microM/min) than BphC1 (29 microM/min). Catechol-2,3-dioxygenase was recognized to be not involved in the ring cleavage of 2,2',3-trihydroxybiphenyl (kcat/Km, 1 microM/min). Analysis of deduced amino acid sequence data of bphC1 revealed 36% sequence identity to nahC from Pseudomonas putida PpG7 (S. Harayama and M. Rekik, J. Biol. Chem. 264:15328-15333, 1989) and about 40% sequence identity to various bphC genes from different Pseudomonas and Rhodococcus strains. In addition, another 2,3-dihydroxybiphenyl-1,2-dioxygenase gene (bphC3) was cloned from the genome of Terrabacter sp. strain DPO360. Expression of this gene, however, could not be detected in Terrabacter sp. strain DPO360 after growth with dibenzofuran.

Engineering hybrid pseudomonads capable of utilizing a wide range of aromatic hydrocarbons and of efficient degradation of trichloroethylene

We constructed hybrid Pseudomonas strains in which the bphA1 gene (coding for a large subunit of biphenyl dioxygenase) is replaced with the todC1 gene (coding for a large subunit of toluene dioxygenase of Pseudomonas putida Fl) within chromosomal biphenyl-catabolic bph gene clusters. Such hybrid strains gained the novel capability to grow on a wide range of aromatic hydrocarbons, and, more interestingly, they degraded chloroethenes such as trichloroethylene and cis-1,2-dichloroethylene very efficiently.

A marine oligobacterium harboring genes known to be part of aromatic hydrocarbon degradation pathways of soil pseudomonads

The far-ranging distribution of genes for aromatic hydrocarbon catabolism, predominantly studied in soil pseudomonads, is extended to a marine oligobacterium by finding five homologous sequences in a 5.7-kb chromosomal DNA from a new isolate, Cycloclasticus oligotrophus RB1. RB1 is capable of growth in unamended seawater or mineral salts media supplemented with a variety of aromatic compounds, including toluene, o-, m-, or p-xylenes, as sole carbon sources. The five open reading frames, designated xylM, K, G, C1, and C2, are 57% A+T-rich. XylM is predicted to be an integral membrane protein; XylK and XylG possess glutathione S-transferase (GST) and 2-hydroxy-5methyl-6-oxohexa2,4-dienoate dehydrogenase activities, respectively; XylC1C2 are homologs of the large and small subunits of the iron sulfur protein component of the biphenyl dioxygenase (e.g., BphA1A2).

p-Cumate catabolic pathway in Pseudomonas putida Fl: cloning and characterization of DNA carrying the cmt operon

Pseudomonas putida F1 utilizes p-cumate (p-isopropylbenzoate) as a growth substrate by means of an eight-step catabolic pathway. A 35.75-kb DNA segment, within which the cmt operon encoding the catabolism of p-cumate is located, was cloned as four separate overlapping restriction fragments and mapped with restriction endonucleases. By examining enzyme activities in recombinant bacteria carrying these fragments and sub-cloned fragments, genes encoding most of the enzymes of the p-cumate pathway were located. Subsequent sequence analysis of 11,260 bp gave precise locations of the 12 genes of the cmt operon. The first three genes, cmtAaAbAc, and the sixth gene, cmtAd, encode the components of p-cumate 2,3-dioxygenase (ferredoxin reductase, large subunit of the terminal dioxygenase, small subunit of the terminal dioxygenase, and ferredoxin, respectively); these genes are separated by cmtC, which encodes 2,3-dihydroxy-p-cumate 3,4-dioxygenase, and cmtB, coding for 2,3-dihydroxy-2,3-dihydro-p-cumate dehydrogenase. The ring cleavage product, 2-hydroxy-3-carboxy-6-oxo-7-methylocta-2,4-dienoate, is acted on by a decarboxylase encoded by the seventh gene, cmtD, which is followed by a large open reading frame, cmtI, of unknown function. The next four genes, cmtEFHG, encode 2-hydroxy-6-oxo-7-methylocta-2,4-dienoate hydrolase, 2-hydroxypenta-2,4-dienoate hydratase, 4-hydroxy-2-oxovalerate aldolase, and acetaldehyde dehydrogenase, respectively, which transform the decarboxylation product to amphibolic intermediates. The deduced amino acid sequences of all the cmt gene products except CmtD and CmtI have a recognizable but low level of identity with amino acid sequences of enzymes catalyzing analogous reactions in other catabolic pathways. This identity is highest for the last two enzymes of the pathway (4-hydroxy-2-oxovalerate aldolase and acetaldehyde dehydrogenase [acylating]), which have identities of 66 to 77% with the corresponding enzymes from other aromatic meta-cleavage pathways. Recombinant bacteria carrying certain restriction fragments bordering the cmt operon were found to transform indole to indigo. This reaction, known to be catalyzed by toluene 2,3-dioxygenase, led to the discovery that the tod operon, encoding the catabolism of toluene, is located 2.8 kb downstream from and in the same orientation as the cmt operon in P. putida F1.