Bph Gene Cluster Research Articles

Micro-synteny conservation analysis revealed the evolutionary history of bacterial biphenyl degradation pathway.

Phenolic compounds have been enlisted by the United States Environmental Protection Agency (USEPA) and the European Union (EU) as pollutants of priority concern. The biphenyl degradation pathway plays an essential role in prokaryote polychlorinated biphenyls degradation. Our understanding of prokaryotic pathways and their evolution has dramatically increased in recent years with the advancements in prokaryotic genome sequencing and analysis tools. In this work, we applied bioinformatics tools to study the evolution of the biphenyl degradation pathway focusing on the phylogeny and initiation of four representative species (Burkholderia xenovorans LB400, Polaromonas naphthalenivorans CJ2, Pseudomonas putida F1 and Rhodococcus jostii RHA1). These species contained partial or full concatenated genes from bph gene cluster (i.e. bphRbphA1A2A3A4BCKHJID). The aim was to establish this pathway's origin and development mode in the prokaryotic world. Genomic screening revealed that many bacterial species possess genes for the biphenyl degradation pathway. However, the micro-synteny conservation analysis indicated that massive gene recruitment events might have occurred during the evolution of the biphenyl degradation pathway. Combining with the phylogenetic positions, this work points to the evolutionary process of acquiring the biphenyl degradation pathway by different fragments through horizontal gene transfer in these bacterial groups. This study reports the first-ever evidence of the birth of this pathway in the represented species.

Recent Strategies for Detection and Improvement of Brown Planthopper Resistance Genes in Rice: A Review.

Brown planthopper (BPH; Nilaparvata lugens Stal) is considered the main rice insect pest in Asia. Several BPH-resistant varieties of rice have been bred previously and released for large-scale production in various rice-growing regions. However, the frequent surfacing of new BPH biotypes necessitates the evolution of new rice varieties that have a wide genetic base to overcome BPH attacks. Nowadays, with the introduction of molecular approaches in varietal development, it is possible to combine multiple genes from diverse sources into a single genetic background for durable resistance. At present, above 37 BPH-resistant genes/polygenes have been detected from wild species and indica varieties, which are situated on chromosomes 1, 3, 4, 6, 7, 8, 9, 10, 11 and 12. Five BPH gene clusters have been identified from chromosomes 3, 4, 6, and 12. In addition, eight BPH-resistant genes have been successfully cloned. It is hoped that many more resistance genes will be explored through screening of additional domesticated and undomesticated species in due course.

Biphenyl/PCB Degrading bph Genes of Ten Bacterial Strains Isolated from Biphenyl-Contaminated Soil in Kitakyushu, Japan: Comparative and Dynamic Features as Integrative Conjugative Elements (ICEs).

We sequenced the entire genomes of ten biphenyl/PCB degrading bacterial strains (KF strains) isolated from biphenyl-contaminated soil in Kitakyushu, Japan. All the strains were Gram-negative bacteria belonging to β- and γ-proteobacteria. Out of the ten strains, nine strains carried a biphenyl catabolic bph gene cluster as integrative conjugative elements (ICEs), and they were classified into four groups based on the structural features of the bph genes. Group I (five strains) possessed bph genes that were very similar to the ones in Pseudomonas furukawaii KF707 (formerly Pseudomonas pseudoalcaligenes KF707), which is one of the best characterized biphenyl-utilizing strains. This group of strains carried salicylate catabolic sal genes that were approximately 6-kb downstream of the bph genes. Group II (two strains) possessed bph and sal genes similar to the ones in KF707, but these strains lacked the bphX region between bphC and bphD, which is involved in the downstream catabolism of biphenyl. These bph-sal clusters in groups I and II were located on an integrative conjugative element that was larger than 110 kb, and they were named ICEbph-sal. Our previous study demonstrated that the ICEbph-sal of Pseudomonas putida KF715 in group II existed both in an integrated form in the chromosome (referred to as ICEbph-salKF715 (integrated)) and in a extrachromosomal circular form (referred to as ICEbph-sal (circular)) (previously called pKF715A, 483 kb) in the stationary culture. The ICEbph-sal was transferred from KF715 into P. putida AC30 and P. putida KT2440 with high frequency, and it was maintained stably as an extrachromosomal circular form. The ICEbph-salKF715 (circular) in these transconjugants was further transferred to P. putida F39/D and then integrated into the chromosome in one or two copies. Meanwhile, group III (one strain) possessed bph genes, but not sal genes. The nucleotide sequences of the bph genes in this group were less conserved compared to the genes of the strains belonging to groups I and II. Currently, there is no evidence to indicate that the bph genes in group III are carried by a mobile element. Group IV (two strains) carried bph genes as ICEs (59–61 kb) that were similar to the genes found in Tn4371 from Cupriavidus oxalacticus A5 and ICEKKS1024677 from the Acidovorax sp. strain KKS102. Our study found that bph gene islands have integrative functions, are transferred among soil bacteria, and are diversified through modification.

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.

Gene cluster and regulation system for 1,1-dichloro-2,2-bis(4-chlorophenyl)ethylene (DDE) degradation in Janibacter sp. TYM3221

A DDE-degrading bacterium, Janibacter sp. TYM3221, is able to grow on biphenyl and degrades 1,1-dichloro-2,2-bis(4-chlorophenyl)ethylene (DDE) via a meta-ring cleavage pathway. The bphAa gene, encoding a biphenyl dioxygenase large subunit, was previously demonstrated to be involved in the degradation of DDE in TYM3221. The bph gene cluster, containing orf2 and bphDAaAbAcAdBCST was cloned and characterized. Reverse transcription-PCR (RT-PCR) analysis indicated that these genes were transcribed as an operon. The real-time RT-PCR on orf2, bphAa, bphC, and bphS suggest the presence of the inducible orf2 promoter (orf2p) and constitutive bphAa promoter (bphAap). The TYM3221 bphST conducted biphenyl-dependent inducible activation plus constitutive basal activation of orf2p and constitutive activation of bphAap in a rhodococcal host strain, Rhodococcus erythropolis IAM1399, suggesting that expression of the TYM3221 bph operon depends on the bphST-coded two-component regulatory system. Both of these promoters were also induced by the bphS1T1 of a biphenyl degrader, Rhodococcus jostii RHA1, and contained the 24-bp consensus sequences of RHA1 bphS1T1-dependent promoters. The replacement of RHA1 bphS1 with TYM3221 bphS in combination with RHA1 bphT1 suggests that TYM3221 bphS is responsible for low inducible and high constitutive activation of orf2p in IAM1399 by the TYM3221 bphST-system. Expression of bphAaAbAcAdBC in IAM1399 resulted in the transformation of DDE to the meta-ring cleavage product via 2,3-hydroxylation, suggesting that these genes are involved in DDE degradation.

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.

Hybrid pseudomonads engineered by two-step homologous recombination acquire novel degradation abilities toward aromatics and polychlorinated biphenyls

Pseudomonas pseudoalcaligenes KF707 possesses a chromosomally encoded bph gene cluster responsible for the catabolism of biphenyl and polychlorinated biphenyls. Previously, we constructed chimeric versions of the bphA1 gene, which encodes a large subunit of biphenyl dioxygenase, by using DNA shuffling between bphA1 genes from P. pseudoalcaligenes KF707 and Burkholderia xenovorans LB400. In this study, we demonstrate replacement of the bphA1 gene with chimeric bphA1 sequence within the chromosomal bph gene cluster by two-step homologous recombination. Notably, some of the hybrid strains acquired enhanced and/or expanded degradation capabilities for specific aromatic compounds, including single aromatic hydrocarbons and polychlorinated biphenyls.

Isolation of a biphenyl-degrading bacterium, Achromobacter sp. BP3, and cloning of the bph gene cluster

A bacterial strain, BP3, capable of degrading biphenyl, was isolated from petroleum-contaminated soil. Strain BP3 was identified preliminarily as Achromobacter sp. based on its physiological and biochemical characteristics and 16S rRNA gene sequence analysis. Strain BP3 was able to degrade 50 mg l −1 of biphenyl within 12 h. A 16.7-kb DNA fragment consisting of the entire bph cluster ( bphRA1A2XA3A4BCKHJID) was obtained by normal PCR amplification and chromosome walking. Genes encoding integrase and transposon related genes were detected upstream and downstream of the bph cluster, respectively, which indicated that the bph cluster might locate on a big mobile genetic element (MGE).

Characterization and functional analysis of a novel gene cluster involved in biphenyl degradation in Rhodococcus sp. strain R04

Isolation of the genes relative to PCB biodegradation and identification of the bph gene function in Rhodococcus sp. R04. A 8.7-kb fragment carrying the biphenyl catabolic genes bphABCD was isolated from the gene library in Rhodococcus sp. R04. Based on the deduced amino acid sequence homology, seven bph genes, bphA1A2A3A4, bphB, bphC and bphD, were thought to be responsible for the initial four steps of biphenyl degradation. In Escherichia coli, BphA exhibited poor activity for biphenyl transformation, and BphB, BphC and BphD were found to be catalytically active towards 2,3-dihydro-2,3-dihydroxybiphenyl, 2,3-dihydroxybiphenyl and 2-hydroxy-6-oxo-6-phenylhexa-2,4-dienoate, respectively (activities of 50, 8.1 and 2.4 micromol l(-1) min(-1) mg(-1)). SDS-PAGE analysis indicated that the sizes of bphA1A2A3A4, bphB, bphC and bphD gene products were 49, 19, 14, 47, 32, 30 and 31 kDa, respectively. After disruption of bph genes, the bphA1 mutants lost the ability to grow on biphenyl, the bphB and bphD mutants were able to transform a little of biphenyl, but hardly grew on biphenyl. The cloned bph genes indeed play an important role in the biphenyl catabolism in this strain. This bph gene organization in Rhodococcus sp. R04 differs from that of other biphenyl degraders reported previously, indicating it is a novel type of bph gene cluster. Analysis of the phylogenetic tree suggested that BphA1 and BphA2 in Rhodococcus sp. R04 had a different evolutionary relationship with those in the other PCB degraders.

Polychlorinated Biphenyl/Biphenyl Degrading Gene Clusters inRhodococcussp. K37, HA99, and TA431 Are Different from Well-KnownbphGene Clusters of Rhodococci

Four kinds of polychlorinated biphenyl (PCB)-degrading Rhodococcus sp. (TA421, TA431, HA99, and K37) have been isolated from termite ecosystem and under alkaline condition. The bph gene cluster involved in the degradation of PCB/biphenyl has been analyzed in strain TA421. This gene cluster was highly homologous to bph gene clusters in R. globerulus P6 and Rhodococcus sp. RHA1. In this study, we cloned and analyzed the bph gene cluster essential to PCB/biphenyl degradation from R. rhodochrous K37. The order of the genes and the sequence were different in K37 than in P6, RHA1, and TA421. The bphC8(K37) gene was more homologous to the meta-cleavage enzyme involved in phenanthrene metabolism than bphC genes involved in biphenyl metabolism. Two other Rhodococcus strains (HA99 and TA431) had PCB/biphenyl degradation gene clusters similar to that in K37. These findings suggest that these bph gene clusters evolved separately from the well-known bph gene clusters of PCB/biphenyl degraders.

Total degradation of pentachloroethane by an engineered Alcaligenes strain expressing a modified camphor monooxygenase and a hybrid dioxygenase.

We engineered biphenyl-degrading Alcaligenes sp. strain KF711 for total degradation of pentachloroethane (PCA), which expresses a modified camphor monooxygenase and a hybrid dioxygenase consisting of TodC1 (a large subunit of toluene dioxygenase of Pseudomonas putida F1) and BphA2-BphA3-pbhA4 (a small subunit, ferredoxin and ferredoxin reductase of biphenyl dioxygenase, respectively, in strain KF707). Modified camphor monooxygenase genes (camCAB) were supplied as a plasmid and the todC1 gene was integrated within the chromosomal bph gene cluster by a single crossover recombination. The resultant strain KF711S-3cam dechlorinated PCA to trichloroethene by the action of the modified camphor monooxygenase under anaerobic conditions. The same strain subsequently degraded trichloroethene formed oxidatively by the action of the Tol-Bph hybrid dioxygenase under aerobic conditions. Thus sequential anaerobic and aerobic treatments of the KF711S-3cam resting cells resulted in efficient and total degradation of PCA.

Versatile Transcription of Biphenyl Catabolic bphOperon 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.

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.

Occurrence and expression of glutathione-S-transferase-encoding bphK genes in Burkholderia sp. strain LB400 and other biphenyl-utilizing bacteria.

The gene bphK of Burkholderia sp. strain LB400 has previously been shown to be located within the bph locus, which specifies the degradation of biphenyl (BP) and chlorobiphenyls, and to encode a glutathione S-transferase (GST) which accepts 1-chloro-2,4-dinitrobenzene (CDNB) as substrate. The specific physiological role of this gene is not known. It is now shown that the gene is expressed in the parental organism and that GST activity is induced more than 20-fold by growth of the strain on BP relative to succinate when these compounds serve as sole carbon source. Approximately the same induction factor was observed for 2,3-dihydroxybiphenyl 1,2-dioxygenase activity, which is encoded by the 5'-adjacent bphC gene. This suggests that the expression of bphK is coregulated with the expression of genes responsible for the catabolism of BP. A bphK probe detected only a single copy of the gene in strain LB400. A spontaneous BP- mutant of the organism neither gave a signal with the bphK probe nor showed CDNB-accepting GST activity, suggesting that this activity is solely encoded by bphK. Complementation of the mutant with a bph gene cluster devoid of bphK restored the ability to grow on BP, indicating that bphK is not essential for utilization of this carbon source. BphK activity proved to be almost unaffected by up to 100-fold differences in proton concentration or ionic strength. The enzyme showed a narrow range with respect to a variety of widely used electrophilic GST substrates, accepting only CDNB. A number of established laboratory strains as well as novel isolates able to grow on BP as sole carbon and energy source were examined for BphK activity and the presence of a bphK analogue. CDNB assays, probe hybridizations and PCR showed that several, but not all, BP degraders possess this type of GST activity and/or a closely related gene. In all bacteria showing BphK activity, this was induced by growth on BP as sole carbon source, although activity levels differed by up to 10-fold after growth on BP and by up to 60-fold after growth on succinate. This resulted in a variation of induction factors between 2 and 30. In the majority of bphK+ bacteria examined, the gene appeared to be part of LB400-like bph gene clusters. DNA sequencing revealed almost complete identity of bphK genes from five different bph gene clusters. These results suggest that bphK genes, although not essential, fulfill a strain-specific function related to the utilization of BPs by their host organisms. The usefulness of BphK as a reporter enzyme for monitoring the expression of catabolic pathways is discussed.

Regiospecificity of dioxygenation of di- to pentachlorobiphenyls and their degradation to chlorobenzoates by the bph-encoded catabolic pathway of Burkholderia sp. strain LB400.

Burkholderia sp. strain LB400 is one of the most potent aerobic polychlorobiphenyl (PCB)-degrading microorganisms that have been characterized. Its PCB-dioxygenating activity originates predominantly or exclusively from the biphenyl dioxygenase encoded by its bph gene cluster. Analysis of the dioxygenation products of several di- to pentachlorinated biphenyls formed by this enzyme revealed a complex dependence of the regiospecificity and the yield of dioxygenation on the substitution patterns of both the oxidized and the nonoxidized rings. No dioxygenolytic attack involving chlorinated meta or para carbons was observed. Therefore, the ability of the enzyme to hydroxylate chlorinated carbons appears to be limited to the ortho position. However, it is not limited to monochlorinated rings, as evidenced by dioxygenation of the 2, 4-disubstituted ring at carbons 2 and 3. This site of attack is strikingly different from that of the 2,5-dichlorinated ring, which has been shown to be dihydroxylated at positions 3 and 4 (J. D. Haddock, J. R. Horton, and D. T. Gibson, J. Bacteriol. 177:20-26, 1995). These results demonstrate that a second substituent of ortho-chlorinated rings crucially influences the site of dioxygenation at this ring and thereby determines whether or not the initial chlorobiphenyl oxidation product is further metabolized through the bph-encoded pathway. The 2,4-dichlorinated ring can alternatively be attacked at carbons 5 and 6. The preferred site crucially depends on the substitution pattern of the other ring. The formation of more than a single dioxygenation product was found predominantly with congeners that contain two chlorinated rings, both of which are similarly prone to dioxygenation or one is substituted only at carbon 3.

Organisation of the bph gene cluster of transposon Tn4371, encoding enzymes for the degradation of biphenyl and 4-chlorobiphenyl compounds.

Tn4371 is a 55 kb transposon which encodes enzymes for the degradation of biphenyl and 4-chlorobiphenyl compounds into benzoate and 4-chlorobenzoate derivatives. We constructed a cosmid library of Tn4371 DNA. The bph genes involved in biphenyl/4-chlorobiphenyl degradation were found to be clustered in the middle of the transposon. Sequencing revealed an organisation of the bph genes similar to that previously found in Pseudomonas sp. KKS102, i.e. the bphEGF genes are located upstream of bphA1A2A3 and bphA4 is separated from bphA1A2A3 by bphBCD. Consensus sequences for sigma54-associated RNA polymerase were found upstream of bphA1 and bphEGF. Plasmid RP4::Tn4371 was transferred into a mutant of Alcaligenes eutrophus H16 lacking sigma54. In contrast to wild-type H16 exconjugants, the sigma54 mutant exconjugants could not grow on biphenyl, indicating the dependence of Tn4371 bph gene expression on sigma54. The Tn4371-encoded bph pathway was activated when biphenyl and various biphenyl-like compounds were present in the growth medium. Preliminary observations indicate the presence of a region outside the catabolic genes downstream of bphA4 which is involved in mediating at least the basal expression of BphC.

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.

Sequencing of Comamonas testosteroni strain B-356-biphenyl/chlorobiphenyl dioxygenase genes: evolutionary relationships among Gram-negative bacterial biphenyl dioxygenases

In a previous work, all three components of Comamonas testosteroni B-356 biphenyl (BPH)/chlorobiphenyls (PCBs) dioxygenase (dox) have been purified and characterized. They include an iron-sulphur protein (ISP BPH) which is the terminal oxygenase composed of two subunits (encoded by bphA and bphE), a ferredoxin (FER BPH) encoded by bphF and a reductase (RED BPH) encoded by bphG. bphG Is not located in the neighbourhood of bphAEF in B-356. We are reporting the cloning of B-356-bphG and the sequencing of B-356-BPH dox genes. Comparative analysis of the genes provided genetic evidence showing that two BPH dox lineages have emerged in Gram-negative bacteria. The main features of the lineage that includes B-356 are the location of bphG outside the bph gene cluster and the structure of RED BPH which is very distinct from all other aryl dioxygenase-reductases.

Identification and mapping of the gene translation products involved in the first steps of the Comamonas testosteroni B-356 biphenyl/chlorobiphenyl biodegradation pathway

In this study, we have mapped Comamonas testosteroni B-356 genes encoding enzymes for the conversion of biphenyl and 4-chlorobiphenyl into the corresponding meta-cleavage compounds onto a 6.3-kb DNA fragment, and we have determined the subunit composition of the enzymes involved in this pathway. The various proteins encoded by this 6.3-kb DNA fragment and by subclones derived from it were overexpressed and selectively labelled using the T7 polymerase promoter system in Escherichia coli. They were then analyzed using SDS-PAGE, which allowed the encoding locus of each polypeptide to be mapped. Despite apparent dissimilarity in the congener selectivity patterns of the initial oxygenase of strain B-356 with those of Pseudomonas sp. strain LB400, the number and sizes of the polypeptides involved in the enzymatic conversion of biphenyl or 4-chlorobiphenyl into the meta-cleavage product appear to be similar in the two strains. In both strains, the bph operon encodes the following: the large (51-kDa polypeptide encoded by bphA) and the small (22-kDa polypeptide encoded by bphE) subunits of the iron sulphur protein, which is thought to interact directly with the substrate to introduce the oxygen molecule; the ferredoxin (12-kDa polypeptide encoded by bphF) involved in electron transfer from the reduced ferredoxin reductase to the oxidized iron sulphur protein; the 29-kDa polypeptide of the 2,3-dihydro-2,3-dihydroxybiphenyl dehydrogenase encoded by bphB; and the 32-kDa polypeptide of the 2,3-dihydroxybiphenyl-1,2-dioxygenase encoded by bphC, which catalyzes meta-1,2 fission of the aromatic ring. A major difference between strain B-356 and strain LB400 is that the bphG gene encoding biphenyl dioxygenase ferredoxin reductase is located outside the bph gene cluster in strain B-356. Several lines of evidence indicate that bphG is absent in clones carrying the bph operon from strain B-356.

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

Pseudomonas sp. strain KKS102 is able to degrade biphenyl and polychlorinated biphenyls via the meta-cleavage pathway. We sequenced the upstream region of the bphA1A2A3BCD (open reading frame 1 [ORF1]) A4 and found four ORFs in this region. As the deduced amino acid sequences of the first, second, and third ORFs are homologous to the meta-cleavage enzymes from Pseudomonas sp. strain CF600 (V. Shingler, J. Powlowski, and U. Marklund, J. Bacteriol. 174:711-724, 1992), these ORFs have been named bphE, bphG, and bphF, respectively. The fourth ORF (ORF4) showed homology with ORF3 from Pseudomonas pseudoalcaligenes KF707 (K. Taira, J. Hirose, S. Hayashida, and K. Furukawa, J. Biol. Chem. 267:4844-4853, 1992), whose function is unknown. The functions of meta-cleavage enzymes (BphE, BphG, and BphF) were analyzed by using crude extracts of Escherichia coli which expressed the encoding genes. The results showed that bphE, bphG, and bphF encode 2-hydroxypenta-2,4-dienoate hydratase, acetaldehyde dehydrogenase (acylating), and 4-hydroxy-2-oxovalerate aldolase, respectively. The biphenyl and polychlorinated biphenyl degradation pathway of KKS102 is encoded by 12 genes in the order bphEGF (ORF4)A1A2A3BCD (ORF1)A4. The functions of ORF1 and ORF4 are unknown. The features of this bph gene cluster are discussed.