Cloning of a gene cluster encoding biphenyl and chlorobiphenyl degradation in Pseudomonas pseudoalcaligenes.

A gene cluster encoding biphenyl- and chlorobiphenyl-degrading enzymes was cloned from a soil pseudomonad into Pseudomonas aeruginosa PAO1161. Chromosomal DNA from polychlorinated biphenyl-degrading Pseudomonas pseudoalcaligenes KF707 was digested with restriction endonuclease XhoI and cloned into the unique XhoI site of broad-host-range plasmid pKF330. Of 8,000 transformants tested, only 1, containing the chimeric plasmid pMFB1, rendered the host cell able to convert biphenyls and chlorobiphenyls to ring meta cleavage compounds via dihydrodiols and dihydroxy compounds. The chimeric plasmid contained a 7.9-kilobase XhoI insert. Subcloning experiments revealed that the genes bphA (encoding biphenyl dioxygenase), bphB (encoding dihydrodiol dehydrogenase), and bphC (encoding 2,3-dihydroxybiphenyl dioxygenase) were coded for by the 7.9-kilobase fragment. The gene order was bphA-bphB-bphC. The hydrolase activity, which converted the intermediate meta cleavage compounds to the final product, chlorobenzoic acids, and was encoded by a putative bphD gene, was missing from the cloned 7.9-kilobase fragment.     

Pseudomonas putida KF715 bphABCD operon encoding biphenyl and polychlorinated biphenyl degradation: cloning, analysis, and expression in soil bacteria.

We cloned the entire bphABCD genes encoding degradation of biphenyl and polychlorinated biphenyls to benzoate and chlorobenzoates from the chromosomal DNA of Pseudomonas putida KF715. The nucleotide sequence revealed two open reading frames corresponding to the bphC gene encoding 2,3-dihydroxybiphenyl dioxygenase and the bphD gene encoding 2-hydroxy-6-oxo-6-phenylhexa-2,4-dienoic acid (ring-meta-cleavage compound) hydrolase.     

Nucleotide sequence of the 2,3-dihydroxybiphenyl dioxygenase gene of Pseudomonas pseudoalcaligenes.

2,3-Dihydroxybiphenyl dioxygenase, which catalyzes ring metacleavage of 2,3-dihydroxybiphenyl, is encoded by the bphC gene of Pseudomonas pseudoalcaligenes KF707 (K. Furukawa and T. Miyazaki, J. Bacteriol. 166:392-398, 1986). We determined the nucleotide sequence of a DNA fragment of 2,040 base pairs which included the bphC gene. The fragment included one open reading frame of 912 base pairs to accommodate the enzyme. The predicted processed amino acid sequence of the enzyme subunit consisted of 302 residues, and its 12 NH2-terminal residues were in perfect agreement with those determined for the enzyme. Approximately 10 base pairs upstream from the initiation codon for 2,3-dihydroxybiphenyl dioxygenase, there was a base sequence complementary to the 3' end of the 16S rRNA from Pseudomonas aeruginosa. There was no promoterlike sequence in the region upstream of the bphC gene, but another long open reading frame was present. A putative bphD gene encoding a metacleavage compound-hydrolyzing enzyme was suggested in the region downstream of the bphC gene.     

Purification of 2,3-dihydroxybiphenyl 1,2-dioxygenase from Pseudomonas putida OU83 and characterization of the gene (bphC).

The 2,3-dihydroxybiphenyl 1,2-dioxygenase (2,3-DBPD) of Pseudomonas putida OU83 was constitutively expressed and purified to apparent homogeneity. The apparent molecular mass of the native enzyme was 256 kDa, and the subunit molecular mass was 32 kDa. The data suggested that 2,3-DBPD was an octamer of identical subunits. The nucleotide sequence of a DNA fragment containing the bphC region was determined. The deduced protein sequence for 2,3-DBPD consisted of 292 amino acid residues, with a calculated molecular mass of 31.9 kDa, which was in agreement with data for the purified 2,3-DBPD. Nucleotide and amino acid sequence analyses of the bphC gene and its product, respectively, revealed that there was a high degree of homology between the OU83 bphC gene and the bphC genes of Pseudomonas cepacia LB400 and Pseudomonas pseudoalcaligenes KF707.     

Comparison of enzymatic and immunochemical properties of 2,3-dihydroxybiphenyl-1,2-dioxygenases from four Pseudomonas strains

Abstract A 2,3-dihydroxybiphenyl-1,2-dioxygenase gene has been cloned from chromosomal DNA of Pseudomonas sp. DJ-12 which can grow on biphenyl or 4-chlorobiphenyl as the sole carbon and energy source. Enzymatic and immunochemical properties of the cloned 2,3-dihydroxybiphenyl-1,2-dioxygenase were characterized, and compared with those of P. pseudoalcaligenes KF707, Pseudomonas sp. KKS102, and P. putida OU83. The dioxygenase of Pseudomonas sp. DJ-12 was similar to those of P. pseudoalcaligenes KF707, and Pseudomonas sp. KKS102, but significantly different from that of P. putida OU83 in electrophoretic mobilities on native PAGE and SDS-PAGE. The dioxygenases of Pseudomonas sp. DJ-12 and P. putida OU83 exhibited the highest ring-fission activity to 3-methylcatechol, and those of P. pseudoalcaligenes KF707 and Pseudomonas sp. KKS102 to 2,3-dihydroxybiphenyl among 2,3-dihydroxybiphenyl, catechol, 3-methylcatechol, 4-methylcatechol, and 4-chlorocatechol as substrates. 2,3-dihydroxybiphenyl-1,2-dioxygenase of P. pseudoalcaligenes KF707 was immunochemically related to that of Pseudomonas sp. KKS102, but was different from those of Pseudomonas sp. DJ-12 and P. putida OU83.     

Cloning and sequencing of two tandem genes involved in degradation of 2,3-dihydroxybiphenyl to benzoic acid in the polychlorinated biphenyl-degrading soil bacterium Pseudomonas sp. strain KKS102.

Two genes involved in the degradation of biphenyl were isolated from a gene library of a polychlorinated biphenyl-degrading soil bacterium, Pseudomonas sp. strain KKS102, by using a broad-host-range cosmid vector, pKS13. When a 3.2-kilobase (kb) PstI fragment of a 29-kb cosmid DNA insert was subcloned into pUC18 at the PstI site downstream of the lacZ promoter, Escherichia coli cells carrying this recombinant plasmid expressed 2,3-dihydroxybiphenyl dioxygenase activity. Nucleotide sequencing of the 3.2-kb PstI fragment revealed that there were two open reading frames (ORFI [882 base pairs] and ORFII [834 base pairs], in this gene order). Results of analysis of Tn5 insertion mutants and unidirectional deletion mutants suggested that the ORFI coded for 2,3-dihydroxybiphenyl dioxygenase. When the sequence of ORFI was compared with that of bphC of Pseudomonas pseudoalcaligenes KF707 (K. Furukawa, N. Arima, and T. Miyazaki, J. Bacteriol. 169:427-429, 1987), the homology was 68%, with both strains having the same Shine-Dalgarno sequence. The result of gas chromatography-mass spectrometry analysis of the metabolic product suggested that the ORFII had meta cleavage compound hydrolase activity to produce benzoic acid. DNA sequencing suggested that these two genes were contained in one operon.     

Molecular relationship of chromosomal genes encoding biphenyl/polychlorinated biphenyl catabolism: some soil bacteria possess a highly conserved bph operon.

All the genes we examined that encoded biphenyl/polychlorinated biphenyl (PCB) degradation were chromosomal, unlike many other degradation-encoding genes, which are plasmid borne. The molecular relationship of genes coding for biphenyl/PCB catabolism in various biphenyl/PCB-degrading Pseudomonas, Achromobacter, Alcaligenes, Moraxella, and Arthrobacter strains was investigated. Among 15 strains tested, 5 Pseudomonas strains and one Alcaligenes strain possessed the bphABC gene cluster on the XhoI 7.2-kilobase fragment corresponding to that of Pseudomonas pseudoalcaligenes KF707. More importantly, the restriction profiles of these XhoI 7.2-kilobase fragments containing bphABC genes were very similar, if not identical, despite the dissimilarity of the flanking chromosomal regions. Three other strains also possessed bphABC genes homologous with those of KF707, and five other strains showed weak or no significant genetic homology with bphABC of KF707. The immunological cross-reactivity of 2,3-dihydroxybiphenyl dioxygenases from various strains corresponded well to the DNA homology. On the other hand, the bphC gene of another PCB-degrading strain, Pseudomonas paucimobilis Q1, lacked genetic as well as immunological homology with any of the other 15 biphenyl/PCB degraders tested. The existence of the nearly identical chromosomal genes among various strains may suggest that a segment containing the bphABC genes has a mechanism for transferring the gene from one strain to another.     

Metabolism of naphthalene by the biphenyl-degrading bacterium Pseudomonas paucimobilis Q1

Pseudomonas paucimobilis Q1 originally isolated as biphenyl degrading organism (Furukawa et al. 1983), was shown to grow with naphthalene. After growth with biphenyl or naphthalene the strain synthesized the same enzyme for the ring cleavage of 2,3-dihydroxybiphenyl or 1,2-dihydroxynaphthalene. The enzyme, although characterized as 2,3-dihydroxybiphenyl dioxygenase (Taira et al. 1988), exhibited considerably higher relative activity with 1,2-dihydroxynaphthalene. These results demonstrate that this enzyme can function both in the naphthalene and biphenyl degradative pathway.Abbreviations DHBP dihydroxybiphenyl - DHBPDO 2,3-dihydroxybiphenyl dioxygenase - DHDHNDH 1,2-dihydroxy-1,2-dihydronaphthalene dehydrogenase - DHN 1,2-dihydroxynaphthalene - DHNDO 1,2-dihydroxynaphthalene dioxygenase - HBP cis-2-hydroxybenzalpyruvate - HOPDA 2-hydroxy-6-oxo-6-phenylhexa-2,4-dienoate - PCB polychlorinated biphenyl - 2NS naphthalene-2-sulfonic acid     

Molecular breeding of 2,3-dihydroxybiphenyl 1,2-dioxygenase for enhanced resistance to 3-chlorocatechol

3-Chlorobiphenyl is known to be mineralized by biphenyl-utilizing bacteria to 3-chlorobenzoate, which is further metabolized to 3-chlorocatechol. An extradiol dioxygenase, 2,3-dihydroxybiphenyl 1,2-dioxygenase (DHB12O; EC 1.13.11.39), which is encoded by the bphC gene, catalyzes the third step of the upper pathway of 3-chlorobiphenyl degradation. In this study, two full-length bphCs and nine partial fragments of bphCs fused to the 3' end of bphC in Pseudomonas pseudoalcaligenes KF707 were cloned from different biphenyl-utilizing soil bacteria and expressed in Escherichia coli. The enzyme activities of the expressed DHB12Os were inhibited to varying degrees by 3-chlorocatechol, and the E. coli cells overexpressing DHB12O could not grow or grew very slowly in the presence of 3-chlorocatechol. These sensitivities of enzyme activity and cell growth to 3-chlorocatechol were well correlated, and this phenomenon was employed in screening chimeric BphCs formed by family shuffling of bphC genes isolated from Comamonas testosteroni KF704 and C. testosteroni KF712. The resultant DHB12Os were more resistant by a factor of two to 3-chlorocatechol than one of the best parents, KF707 DHB12O.     

Three of the seven bphC genes of Rhodococcus erythropolis TA421, isolated from a termite ecosystem, are located on an indigenous plasmid associated with biphenyl degradation.

Rhodococcus erythropolis TA421, a polychlorinated biphenyl and biphenyl degrader isolated from a termite ecosystem, has seven bphC genes expressing 2,3-dihydroxybiphenyl dioxygenase activity. R. erythropolis TA421 harbored a large and probably linear plasmid on which three (bphC2, bphC3, and bphC4) of the seven bphC genes were located. A non-biphenyl-degrading mutant, designated strain TA422, was obtained spontaneously from R. erythropolis TA421. TA422 lacked the plasmid, suggesting that the three bphC genes were involved in the degradation of biphenyl. Southern blot analyses showed that R. erythropolis TA421 and Rhodococcus globerulus P6 have a similar set of bphC genes and that the genes for biphenyl catabolism are located on plasmids of different sizes. These results indicated that the genes encoding the biphenyl catabolic pathway in Rhodococcus strains are borne on plasmids.     

Functional and structural relationship of various extradiol aromatic ring-cleavage dioxygenases of Pseudomonas origin

Abstract The extradiol ring-cleavage dioxygenases derived from seven different Pseudomonas strains were expressed in Escherichia coli and the substrate specificities were investigated for a variety of catecholic compounds. The substrate range of four 2,3-dihydroxybiphenyl dioxygenases from biphenyl-utilizing bacteria, 3-methylcatechol dioxygenase from toluene utilizing Pseudomonas putida F1, 1,2-dihydroxynaphthalene dioxygenase from a NAH7 plasmid, and catechol 2,3-dioxygenase from a TOL plasmid pWW0 were compared. Among the dioxygenases, that from Pseudomonas pseudoalcaligenes KF707 showed a very narrow substrate range. Contrary to this, the dioxygenase from pWW0 showed a relaxed substrate range. The seven extradiol dioxygenases from the various Pseudomonas strains are highly diversified in terms of substrate specificity.     

Substrate specificity and expression of three 2,3-dihydroxybiphenyl 1,2-dioxygenases from Rhodococcus globerulus strain P6

Rhodococcus globerulus strain P6 contains at least three genes, bphC1, bphC2, and bphC3, coding for 2,3-dihydroxybiphenyl 1,2-dioxygenases; the latter two specify enzymes of the family of one-domain extradiol dioxygenases. In order to assess the importance of these different isoenzymes for the broad catabolic activity of this organism towards the degradation of polychlorinated biphenyls (PCBs), the capacities of recombinant enzymes expressed in Escherichia coli to transform different chlorosubstituted dihydroxybiphenyls formed by the action of R. globerulus P6 biphenyl dioxygenase and biphenyl 2,3-dihydrodiol dehydrogenase were determined. Whereas both BphC2 and BphC3 showed similar activities for 2,3-dihydroxybiphenyl and all monochlorinated 2,3-dihydroxybiphenyls, BphC1 exhibited only weak activity for 2'-chloro-2,3-dihydroxybiphenyl. More highly chlorinated 2'-chlorosubstituted 2,3-dihydroxybiphenyls were also transformed at high rates by BphC2 and BphC3 but not BphC1. In R. globerulus P6, BphC2 was constitutively expressed, BphC1 expression was induced during growth on biphenyl, and BphC3 was not expressed at significant levels under the experimental conditions. Although we cannot rule out the expression of BphC3 under certain environmental conditions, it seems that the contrasting substrate specificities of BphC1 and BphC2 contribute significantly to the versatile PCB-degrading phenotype of R. globerulus P6.     

Molecular genetics and evolutionary relationship of PCB-degrading bacteria

Biphenyl-utilizing soil bacteria are ubiquitously distributed in the natural environment. They cometabolize a variety of polychlorinated biphenyl (PCB) congeners to chlorobenzoic acids through a 2,3-dioxygenase pathway, or alternatively through a 3,4-dioxygenase system. Thebph genes coding for the metabolism of biphenyl have been cloned from several pseudomonads. The biochemistry and molecular genetics of PCB degradation are reviewed and discussed from the viewpoint of an evolutionary relationship.Abbreviations BP biphenyl - bph BP/PCB-degradative gene - 23DHBP 2,3-dihydroxybiphenyl - HPDA 2-hydroxy-6-oxo-6-phenylhexa 2,4-dienoic acid - KF707 P. pseudoalcaligenes strain KF707 - LB400 Pseudomonas sp. strain LB400 - PCB polychlorinated biphenyls - Q1 P. paucimobilis strain Q1tod; toluene catabolic gene     

Enhanced biodegradation of polychlorinated biphenyls after site-directed mutagenesis of a biphenyl dioxygenase gene.

Biphenyl dioxygenase catalyzes the first step in the aerobic degradation of polychlorinated biphenyls (PCBs). The nucleotide and amino acid sequences of the biphenyl dioxygenases from two PCB-degrading strains (Pseudomonas sp. strain LB400 and Pseudomonas pseudoalcaligenes KF707) were compared. The sequences were found to be nearly identical, yet these enzymes exhibited dramatically different substrate specificities for PCBs. Site-directed mutagenesis of the LB400 bphA gene resulted in an enzyme combining the broad congener specificity of LB400 with increased activity against several congeners characteristic of KF707. These data strongly suggest that the BphA subunit of biphenyl dioxygenase plays an important role in determining substrate selectivity. Further alteration of this enzyme can be used to develop a greater understanding of the structural basis for congener specificity and to broaden the range of degradable PCB congeners.     

Gene-specific transposon mutagenesis of the biphenyl/polychlorinated biphenyl-degradation-controlling bph operon in soil bacteria.

A transposon, Tn5-B21, was gene-specifically inserted into the chromosomal biphenyl/polychlorinated biphenyl-catabolic operon (bph operon) of soil bacteria. The cloned bphA, bphB and bphC genes of Pseudomonas pseudoalcaligenes KF707, coding for conversion of biphenyl into a ring meta-cleavage product (2-hydroxy-6-oxo-6-phenylhexa-2,4-dienoic acid), carried random insertions of Tn5-B21. The mutagenized bphABC DNA, carried by a suicide plasmid, was introduced back into the parent strain KF707, resulting in the appearance of gene-specific transposon mutants by double crossover homologous recombination: the bphA::Tn5-B21 mutant did not attack 4-chlorobiphenyl, the bphB::Tn5-B21 mutant accumulated dihydrodiol, and the bphC::Tn5-B21 mutant produced dihydroxy compound. Gene-specific transposon mutants of the bph operon were also obtained for some other biphenyl-utilizing strains which possess bph operons nearly identical to that of KF707.     

Purification, characterization, and substrate specificity of two 2,3-dihydroxybiphenyl 1,2-dioxygenase from Rhodococcus sp. R04, showing their distinct stability at various temperature

The genes of two 2,3-dihydroxybiphenyl 1,2-dioxygenases (BphC1 and BphC2) were obtained from the gene library of Rhodococcus sp. R04. The enzymes have been purified to apparent electrophoretic homogeneity from the cell extracts of the recombinant harboring bphC1 and bphC2. Both BphC1 and BphC2 were hexamers, consisting of six subunits of 35 and 33kDa as determined by sodium dodecyl sulfate-polyacrylamide gel electrophoresis, respectively. The enzymes had similar optimal pH (pH 9.0), but different temperatures for their maximum activity (30 degrees C for BphC1, 80 degrees C for BphC2). In addition, they exhibited distinct stability at various temperatures. The enzymes could cleave a wide range of catechols, with 2,3-dihydroxybiphenyl being the optimum substrate for BphC1 and BphC2. BphC1 was inhibited by 2,3-dihydroxybiphenyl, catechol and 3-chlorocatechol, whereas BphC2 showed strong substrate inhibition for all the given substrates. BphC2 exhibited a half-life of 15min at 80 degrees C and 50min at 70 degrees C, making it the most thermostable extradiol dioxygenase studied in mesophilic bacteria. After disruption of bphC1 and bphC2 genes, R04DeltaC1 (bphC1 mutant) delayed the time of their completely eliminating biphenyl another 15h compared with its parent strain R04, but R04DeltaC2 (bphC2 mutant) lost the ability to grow on biphenyl, suggesting that BphC1 plays an assistant role in the degrading of biphenyl by strain R04, while BphC2 is essential for the growth of strain R04 on biphenyl.     

Multiple genes encoding 2,3-dihydroxybiphenyl 1,2-dioxygenase in the gram-positive polychlorinated biphenyl-degrading bacterium Rhodococcus erythropolis TA421, isolated from a termite ecosystem.

Rhodococcus erythropolis TA421 was isolated from a termite ecosystem and is able to degrade a wide range of polychlorinated biphenyl (PCB) congeners. Genetic and biochemical analyses of the PCB catabolic pathway of this organism revealed that there are four different bphC genes (bphC1, bphC2, bphC3, and bphC4) which encode 2,3-dihydroxybiphenyl dioxygenases. As determined by Southern hybridization, none of the bphC genes exhibits homology to any other bphC gene. bphC1, bphC2, and bphC4 encode enzymes that have narrow substrate specificities and cleave the first aromatic ring in the meta position. In contrast, bphC3 encodes a meta cleavage dioxygenase with broad substrate specificity. Asturias et al. have shown that the closely related organism Rhodococcus globerulus P6 contains three different bphC genes (bphC1, bphC2, and bpHC3) which encode meta cleavage dioxygenases. The data suggest that there is a diverse family of bphC genes which encode PCB meta cleavage dioxygenases in members of the genus Rhodococcus.     

Multiplicity of 2,3-dihydroxybiphenyl dioxygenase genes in the Gram-positive polychlorinated biphenyl degrading bacterium Rhodococcus rhodochrous K37

Rhodococcus rhodochrous K37, a Gram-positive bacterium grown under alkaline conditions, was isolated for its ability to metabolize PCBs. Analysis revealed that it has eight genes encoding extradiol dioxygenase, which has 2,3-dihydroxybiphenyl 1,2-dioxygenase activity, and these genes were designated bphC1 to bphC8. According to the classification of extradiol dioxygenases [Eltis, L. D., and Bolin, J. T., J. Bacteriol., 178, 5930-5937 (1996)], BphC3 and BphC6 belong to the type II enzyme group. The other six BphCs were classified as members of the type I extradiol dioxygenase group. BphC4 and BphC8 were classified into a new subfamily of type I, family 3. Two linear plasmids, 200 kb and 270 kb in size, were found in K37, and the bphC6 and bphC8 genes were located in the 200 kb linear plasmid. Northern hybridization analysis revealed that the bphC1, bphC2, and bphC7 genes were induced in the presence of testosterone, the bphC6 gene was induced by fluorene, and the bphC8 gene was induced by biphenyl. All eight BphC products exhibited much higher substrate activity for 2,3-dihydroxybiphenyl than for catechol, 3-methylcatechol, or 4-methylcatechol.     

Degradation of Polychlorinated Biphenyl Metabolites by Naphthalene-Catabolizing Enzymes

The ability of the dehydrogenase and ring cleavage dioxygenase of the naphthalene degradation pathway to transform 3,4-dihydroxylated biphenyl metabolites was investigated. 1,2-Dihydro-1,2-dihydroxynaphthalene dehydrogenase was expressed as a histidine-tagged protein. The purified enzyme transformed 2,3-dihydro-2,3-dihydroxybiphenyl, 3,4-dihydro-3,4-dihydroxybiphenyl, and 3,4-dihydro-3,4-dihydroxy-2,2′,5,5′-tetrachlorobiphenyl to 2,3-dihydroxybiphenyl, 3,4-dihydroxybiphenyl (3,4-DHB), and 3,4-dihydroxy-2,2′,5,5′-tetrachlorobiphenyl (3,4-DH-2,2′,5,5′-TCB), respectively. Our data also suggested that purified 1,2-dihydroxynaphthalene dioxygenase catalyzed the meta cleavage of 3,4-DHB in both the 2,3 and 4,5 positions. This enzyme cleaved 3,4-DH-2,2′,5,5′-TCB and 3,4-DHB at similar rates. These results demonstrate the utility of the naphthalene catabolic enzymes in expanding the ability of the bph pathway to degrade polychlorinated biphenyls.