Cloning of the Arthrobacter globiformis fcbA gene for dehalogenase and construction of a hybrid pathway of 4-chlorobenzoic acid degradation in Pseudomonas putida

The Artrobacter globiformis KZT1 fcbA gene responsible for dehalogenase (4-chlorobenzoate-4-hydroxylase) activity was cloned in Escherichia coli and Pseudomonas putida cells. The character of the fcbA gene expression was studied. Notwithstanding amplification of the gene dose and control of the inducible Plac promoter, the level of substrate dehalogenation by recombinant E. coli strains was lower, as compared with that in the original KZT1 strain. Cloning of the fcbA gene in P. putida KZ6R cells utilizing 4HBA resulted in a recombinant pathway of 4CBA degradation, which proved more effective for substrate consumption, in comparison with the original KZT1 strain.     

Cloning and expression of the Arthrobacter globiformis fcb genes in Bacillus subtilis]

The fcb genes of Arthrobacter globiformis KZT1 coding for the dehalogenase (4-chlorobenzoate-4-hydroxylase) activity have been cloned. The characteristics of fcb genes expression have been studied. The recombinant strains of Bacillus subtilis 6JM15 (pCBS 311) and 6JM15 (pCBS1) have shown the decreased level of substrate dehalogenation as compared with the one in the parent strain KZT1 and the recombinant strains of Escherichia coli and Pseudomonas putida.     

Construction and characterization of two recombinant bacteria that grow on ortho- and para-substituted chlorobiphenyls

Cloning and expression of the aromatic ring dehalogenation genes in biphenyl-growing, polychlorinated biphenyl (PCB)-cometabolizing Comamonas testosteroni VP44 resulted in recombinant pathways allowing growth on ortho- and para-chlorobiphenyls (CBs) as a sole carbon source. The recombinant variants were constructed by transformation of strain VP44 with plasmids carrying specific genes for dehalogenation of chlorobenzoates (CBAs). Plasmid pE43 carries the Pseudomonas aeruginosa 142 ohb genes coding for the terminal oxygenase (ISPOHB) of the ortho-halobenzoate 1,2-dioxygenase, whereas plasmid pPC3 contains the Arthrobacter globiformis KZT1 fcb genes, which catalyze the hydrolytic para-dechlorination of 4-CBA. The parental strain, VP44, grew only on low concentrations of 2- and 4-CB by using the products from the fission of the nonchlorinated ring of the CBs (pentadiene) and accumulated stoichiometric amounts of the corresponding CBAs. The recombinant strains VP44(pPC3) and VP44(pE43) grew on, and completely dechlorinated high concentrations (up to 10 mM), of 4-CBA and 4-CB and 2-CBA and 2-CB, respectively. Cell protein yield corresponded to complete oxidation of both biphenyl rings, thus confirming mineralization of the CBs. Hence, the use of CBA dehalogenase genes appears to be an effective strategy for construction of organisms that will grow on at least some congeners important for remediation of PCBs.     

Phenanthrene degradation by bacteria of the genera Pseudomonas and Burkholderia in model soil systems

Degradation of phenanthrene by strains Pseudomonas putida BS3701 (pBS1141, pBS1142), Pseudomonas putida BS3745 (pBS216), and Burkholderia sp. BS3702 (pBS1143) was studied in model soil systems. The differences in accumulation and uptake rate of phenanthrene intermediates between the strains under study have been shown, Accumulation of 1-hydroxy-2-naphthoic acid in soil in the course of phenanthrene degradation by strain BS3702 (pBS143) in a model system has been revealed. The efficiency of phenanthrene biodegradation was assessed using the mathematical model proposed previously for assessment of naphthalene degradation efficiency. The efficiency of degradation of both phenanthrene and the intermediate products of its degradation in phenanthrene-contaminated soil is expected to increase with the joint use of strains P. putida BS3701 (pBS1141, pBS1142) and Burkholderia sp. BS3702 (pBS1143).     

Construction and Characterization of Two Recombinant Bacteria That Grow on ortho- and para-Substituted Chlorobiphenyls

Cloning and expression of the aromatic ring dehalogenation genes in biphenyl-growing, polychlorinated biphenyl (PCB)-cometabolizing Comamonas testosteroni VP44 resulted in recombinant pathways allowing growth on ortho- and para-chlorobiphenyls (CBs) as a sole carbon source. The recombinant variants were constructed by transformation of strain VP44 with plasmids carrying specific genes for dehalogenation of chlorobenzoates (CBAs). Plasmid pE43 carries the Pseudomonas aeruginosa 142 ohb genes coding for the terminal oxygenase (ISP_OHB) of the ortho-halobenzoate 1,2-dioxygenase, whereas plasmid pPC3 contains the Arthrobacter globiformis KZT1 fcb genes, which catalyze the hydrolytic para-dechlorination of 4-CBA. The parental strain, VP44, grew only on low concentrations of 2- and 4-CB by using the products from the fission of the nonchlorinated ring of the CBs (pentadiene) and accumulated stoichiometric amounts of the corresponding CBAs. The recombinant strains VP44(pPC3) and VP44(pE43) grew on, and completely dechlorinated high concentrations (up to 10 mM), of 4-CBA and 4-CB and 2-CBA and 2-CB, respectively. Cell protein yield corresponded to complete oxidation of both biphenyl rings, thus confirming mineralization of the CBs. Hence, the use of CBA dehalogenase genes appears to be an effective strategy for construction of organisms that will grow on at least some congeners important for remediation of PCBs.     

Degradation of polychloroaromatic insecticides by Pseudomonas aeruginosa containing biodegradation plasmids

The work was aimed at studying the degradation of DDT, its metabolites and analogs by BS 816 and BS 827 strains constructed on the basis of Pseudomonas aeruginosa 640x strains and carrying biodegradation plasmids pBS2 and pBS3, respectively. DDT and kelthane were degraded by the BS 816 strain at a greater rate than by the parent culture. The investigation of enzymes involved in the oxidation of the aromatic cycle has shown that the plasmid-carrying strains possess the activity of metapyrocatechase and salicylate hydroxylase which is absent in P. aeruginosa 640x. The activity of pyrocatechase increased. In contrast to the parent strain where homogentisate induced only homogentisate oxygenase, this compound induces also metapyrocatechase in the constructed strains.     

Phenanthrene degradation by bacteria of the genera <Emphasis Type="Italic">Pseudomonas</Emphasis> and <Emphasis Type="Italic">Burkholderia</Emphasis> in model soil systems

Degradation of phenanthrene by strains Pseudomona, Moscow, KMK, 2004simova, I.A. and Chernov, I.s putida BS3701 (pBS1141, pBS1142), Pseudomonas putida BS3745 (pBS216), and Burkholderia sp. BS3702 (pBS1143) were studied in model soil systems. The differences in accumulation and uptake rate of phenanthrene intermediates between the strains under study have been shown. Accumulation of 1-hydroxy-2-naphthoic acid in soil in the course of phenanthrene degradation by strain BS3702 (pBS1143) in a model system has been revealed. The efficiency of phenanthrene biodegradation was assessed using the mathematical model proposed previously for assessment of naphthalene degradation efficiency. The efficiency of degradation of both phenanthrene and the intermediate products of its degradation in phenanthrene-contaminated soil is expected to increase with the joint use of strains P. Putida BS3701 (pBS1141, pBS1142) and Burkholderia sp. BS3702 (pBS1143).     

Physiological and genetic characteristics of two bacterial strains utilizing phenoxypropionate and phenoxyacetate herbicides

Two strains, Rhodoferax sp. P230 and Delftia (Comamonas) acidovorans MCI, have previously been shown to carry activities for the degradation of the two enantiomers of (RS)-2-(2,4-dichlorophenoxy-)propionate (dichlorprop) and (RS)-2-(4-chloro-2-methylphenoxy-)propionate (mecoprop) and, in addition, are capable of degrading phenoxyacetate derivatives 2.4-dichlorophenoxyacetate (2,4-D) and 4-chloro-2-methylphenoxyacetate (MCPA). Metabolism of the herbicides is initiated by alpha-ketoglutarate-dependent dioxygenases for both enantiomers of the phenoxypropionate herbicides and for 2,4-D. These activities were constitutively expressed for both enantiomers of dichlorprop in strain MC1 and for the Renantiomer in strain P230. Enzyme activities for the complete degradation of phenoxyacetate and phenoxypropionate herbicides were induced during incubation on either of these herbicides. Strain MC1 has about threefold higher activities for the degradation of dichlorprop and for growth on this substrate (mumax = 0.15 h(-1)) than strain P230; the maximum growth rate on 2,4-D amounts to 0.045 h(-1) with strain MC1. Dichlorprop is utilized faster than mecoprop and the R-enantiomers are cleaved with higher rates than the S-enantiomers. The degradation of the chlorophenolic intermediates seems to proceed via the modified ortho cleavage pathway as indicated by activities of the respective enzymes. The enzymatic results were supported by genetic investigations by which the presence of the genes tfdB (encoding a dichlorophenol hydroxylase), tfdC (encoding a chlorocatechol 1,2-dioxygenase) and tfdD (encoding a chloromuconate cycloisomerase) could be demonstrated in both strains by PCR after application of respective primers. The presence of the tfdA gene (encoding a 2,4-D/alpha-ketoglutarate dioxygenase) was only shown for strain P230 but was lacking in strain MC1. Sequence analysis of the tfd gene fragments revealed high homology to the degradative genes of other proteobacterial strains degrading chloroaromatic compounds. Strain MC1 carries a plasmid of about 120 kb which apparently harbors herbicide degradative genes as concluded from deletion mutants which have lost 2,4-D[phenoxalkanoate]/alpha-ketoglutarate dioxygenase activities for cleavage of the R- and S-enantiomer, and of 2,4-D. For strain P230, no plasmid could be demonstrated; the activity was stably conserved in this strain during growth under nonselective conditions.     

Plasmids for biphenyl, chlorobiphenyl and metatoluylate degradation from Pseudomonas putida

Pseudomonas putida strain SU83, harbors the pBS311 plasmid coding for the degradation of biphenyl, 2- and 4-chlorbiphenyl, meta- and paratoluylate. The insertional mutants of the plasmid obtained by the transposon Tn5 insertion were isolated. One of the mutants was used for cloning of the biphenyl degradation genes. The plasmid pBS311:: Tn5 DNA was inserted into the BamHI site of the plasmid pBR322 and cloned. 11 recombinants of 354 tested were treated with 0.1% solution of 2,3-dioxybiphenyl. One of them has acquired the yellow colour testifying to conversion of 2,3-dioxyphenyl to "2-hydroxy-6-keto-6-phenylhexa-2,4-diene acid. The recombinant plasmid pBS312 from this clone is 10.5 kb in size, the size of the insert being 6.2 kb. Escherichia coli SU185 cells harbouring pBS312 are able to support metacleavage of 2,3-dioxybiphenyl, 3-methylcatechol and catechol, but not of 4-methylcatechol. The results suggest the cloned fragment to contain a gene for 2,3-dioxybiphenyl-1,2-dioxygenase, the third enzyme for biphenyl catabolism.     

Mutants of the plasmid for biodegradation of naphthalene, determining catechol oxidation via the meta-pathway

Most of the known naphthalene biodegradation plasmids determine the process of naphthalene degradation via salicylate and catechol using the meta pathway of catechol degradation. However, Pseudomonas putida strains with plasmids pBS2, pBS216, pBS217 and NPL-1 exert no activity of the enzymes involved in the meta pathway of catechol degradation. When 2-methylnaphthalene was added to the medium as a sole carbon source, mutants growing on this compound were isolated in the strains with the studied plasmids. Plasmid localization of the mutations was established using conjugation transfer as well as by obtaining spontaneous variants that had lost the ability to grow on 2-methylnaphthalene; the respective plasmid mutants were referred to as pBS101, pBS102, pBS103 and pBS105. The strains with the mutant plasmids were tested for the activity of the key enzymes involved in naphthalene catabolism and the activity of catechol-2,3-dioxygenase was found. The data allow one to arrive at the conclusion that plasmids pBS2, pBS216, pBS217 and NPL-1 contain silent genes for the meta pathway of catechol degradation, which are activated by the respective mutations.     

The filamentation pathway controlled by the Efg1 regulator protein is required for normal biofilm formation and development in Candida albicans

Ralstonia eutropha JMP134 (pJP4) grows on 3-chlorobenzoate (3-CB) or 2,4-dichlorophenoxyacetate (2,4-D). The copy number of chlorocatechol genes has been observed to be important for allowing growth of bacterial strains on chloroaromatic compounds. Despite the fact that two functional chlorocatechol degradation tfd gene clusters are harbored on plasmid pJP4, a single copy of the region comprising all tfd genes in strain JMP134-F was insufficient to allow growth on 3-CB, whereas growth on 2,4-D was only slightly retarded compared to the wild-type strain. Using competitive PCR, approximately five copies of pJP4 per genome were observed to be present in the wild-type strain, whereas only one copy of pJP4 was present per chromosome in strain JMP134-F. Therefore, several copies of pJP4 per chromosome are required for full expression of the tfd-encoded growth abilities in the wild-type R. eutropha strain.     

Plasmids for biodegradation of 2,6-dimethylpyridine, 2,4-dimethylpyridine, and pyridine in strains of Arthrobacter]

Arthrobacter crysallopoietes strain KM-4 degrading 2,6-dimethylpyridine and strain KM-4a degrading both 2,6-dimethylpyridine and pyridine, Arthrobacter sp. KM-4b degrading 2,4-dimethylpyridine were isolated from soil. Arthrobacter crystallopoietes KM-4 and Arthrobacter sp. KM-4b contain 100 Md plasmids pBS320 and pBS323. Arthrobacter crystallopietes KM-4a harbours a 100 Md and 80 Md plasmids. Plasmid curing and conjugation transfer results confirm that these plasmids are involved in degradation of 2,6-dimethylpyridine, 2,4-dimethylpyridine and pyridine. A mutant with lost ability to degrade 2,6-dimethylpyridine was isolated during the growth of strain KM-4 rifR at 42 degrees C. Electrophoretic analysis of the plasmid from temperature sensitive mutant revealed the deletion the size of 26 Md from pBS320 plasmid.     

Cloning of Pseudomonas sp. strain CBS3 genes specifying dehalogenation of 4-chlorobenzoate.

The degradation of 4-chlorobenzoate (4-CBA) by Pseudomonas sp. strain CBS3 is thought to proceed first by the dehalogenation of 4-CBA to 4-hydroxybenzoate (4-HBA), which is then metabolized following the protocatechuate branch of the beta-ketoadipate pathway. The cloning of the 4-CBA dehalogenation system was carried out by constructing a gene bank of Pseudomonas sp. strain CBS3 in Pseudomonas putida. Hybrid plasmid pPSA843 contains a 9.5-kilobase-pair fragment derived from the chromosome of Pseudomonas sp. strain CBS3. This plasmid confers on P. putida the ability to dehalogenate 4-CBA and grow on 4-CBA as the only source of carbon. However, pPSA843 did not complement mutants of P. putida unable to grow on 4-HBA (POB-), showing that the genes involved in the metabolism of 4-HBA were not cloned. Subcloning of Pseudomonas sp. strain CBS3 genes revealed that most of the insert is required for the dehalogenation of 4-CBA, suggesting that more than one gene product is involved in this dehalogenation.     

Regulation of the expression of plasmid determination responsible for caprolactam degradation by bacteria of the genus Pseudomonas]

On the basis of the study of some Tn5 induced mutants in Pseudomonas putida strain BS836 containing the plasmid pBS268 coding caprolactam degradation, growth on caprolactam and its intermediates, and the data on the induction of oxidative activities in plasmid containing P. putida strain BS831 it was shown that plasmid and chromosome genes regulated the expression of CAP-determinants. The regulation has some elements of the negative control mechanism. Caprolactam is the inducer of the synthesis of key enzymes cleaving it and its intermediates (aminocaproic and adipic acids). At the same time each of its intermediates induced the synthesis of enzymes responsible for its cleavage.     

Characterization of a chromosomally encoded 2,4-dichlorophenoxyacetic acid/alpha-ketoglutarate dioxygenase from Burkholderia sp. strain RASC.

The findings of previous studies indicate that the genes required for metabolism of the pesticide 2,4-dichlorophenoxyacetic acid (2,4-D) are typically encoded on broad-host-range plasmids. However, characterization of plasmid-cured strains of Burkholderia sp. strain RASC, as well as mutants obtained by transposon mutagenesis, suggested that the 2,4-D catabolic genes were located on the chromosome of this strain. Mutants of Burkholderia strain RASC unable to degrade 2,4-D (2,4-D- strains) were obtained by insertional inactivation with Tn5. One such mutant (d1) was shown to have Tn5 inserted in tfdARASC, which encodes 2,4-D/alpha-ketoglutarate dioxygenase. This is the first reported example of a chromosomally encoded tfdA. The tfdARASC gene was cloned from a library of wild-type Burkholderia strain RASC DNA and shown to express 2,4-D/alpha-ketoglutarate dioxygenase activity in Escherichia coli. The DNA sequence of the gene was determined and shown to be similar, although not identical, to those of isofunctional genes from other bacteria. Moreover, the gene product (TfdARASC) was purified and shown to be similar in molecular weight, amino-terminal sequence, and reaction mechanism to the canonical TfdA of Alcaligenes eutrophus JMP134. The data presented here indicate that tfdA genes can be found on the chromosome of some bacterial species and suggest that these catabolic genes are rather mobile and may be transferred by means other than conjugation.     

Cloning of the genes for degradation of the herbicides EPTC (S-ethyl dipropylthiocarbamate) and atrazine from Rhodococcus sp. strain TE1.

The degradation of the herbicides EPTC (S-ethyl dipropylthiocarbamate) and atrazine (2-chloro-4-ethyl-amino-6-isopropylamino-1,3,5-triazine) is associated with an indigenous plasmid in Rhodococcus sp. strain TE1. Plasmid DNA libraries of Rhodococcus sp. strain TE1 were constructed in a Rhodococcus-Escherichia coli shuttle vector, pBS305, and transferred into Rhodococcus sp. strain TE3, a derivative of Rhodococcus sp. strain TE1 lacking herbicide degradation activity, to select transformants capable of growing on EPTC as the sole source of carbon (EPTC+). Analysis of plasmids from the EPTC+ transformants indicated that the eptA gene, which codes for the enzyme required for EPTC degradation, residues on a 6.2-kb KpnI fragment. The cloned fragment also harbored the gene required for atrazine N dealkylation (atrA). The plasmid carrying the cloned fragment could be electroporated into a number of other Rhodococcus strains in which both eptA and atrA were fully expressed. No expression of the cloned genes was evident in E. coli strains. Subcloning of the 6.2-kb fragment to distinguish between EPTC- and atrazine-degrading genes was not successful.     

Oxidation of n-alkanes by Pseudomonas aeruginosa strain carrying the plasmid pBS251

Pseudomonas aeruginosa PAO8 cannot use n-alkanes or their respective alcohols as a sole carbon source. However, it can grow on n-alkanes when plasmid pBS251 is transferred into its cells. The hybrid plasmid pBS251 is a plasmid RP4 containing genes which control the capability to grow on n-alkanes of the C6-C12 series. Studies of n-alkane oxidation by P. aeruginosa PAO8 carrying pBS251 have shown that this plasmid controls the inducible alkane and alcohol oxidizing activities; the subsequent steps of n-alkane oxidation controlled by chromosomal genes are constitutive.     

NADPH-dependent reductive ortho dehalogenation of 2,4-dichlorobenzoic acid in Corynebacterium sepedonicum KZ-4 and Coryneform bacterium strainNTB-1 via 2,4-dichlorobenzoyl coenzyme A.

Corynebacterium sepedonicum KZ-4, described earlier as a strain capable of growth on 2,4-dichlorobenzoate (G.M. Zaitsev and Y.N. Karasevich, Mikrobiologiya 54:356-369, 1985), is known to metabolize this substrate via 4-hydroxybenzoate and protocatechuate, and evidence consistent with an initial reductive dechlorination step to form 4-chlorobenzoate was found in another coryneform bacterium, strain NTB-1 (W.J.J. van den Tweel, J.B. Kok, and J.A.M. de Bont, Appl. Environ. Microbiol. 53:810-815, 1987). 2-Chloro-4-fluorobenzoate was found to be converted stoichiometrically to 4-fluorobenzoate by resting cells of strain KZ-4, compatible with a reductive process. Experiments with cell extracts demonstrated that Mg - ATP and coenzyme A (CoA) were required to stimulate reductive dehalogenation, consistent with the intermediacy of 2-chloro-4-fluoro-benzoyl-CoA and 2,4-dichlorobenzoyl-CoA thioesters. 2,4-Dichlorobenzoyl-CoA was shown to be converted to 4-chlorobenzoyl-CoA in a novel NADPH-dependent reaction in extracts of both KZ-4 and NTB-1. In addition to the ligase and reductive dehalogenase activities, hydrolytic 4-chlorobenzoyl-CoA dehalogenase and thioesterase activities, 4-hydroxybenzoate 3-monooxygenase, and protocatechuate 3,4-dioxygenase activities were demonstrated to be present in the soluble fraction of KZ-4 extracts following ultracentrifugation. We propose that the pathway for 2,4-dichlorobenzoate catabolism in strains KZ-4 and NTB-1 involves formation of 2,4-dichlorobenzoyl-CoA, NADPH-dependent ortho dehalogenation yielding 4-chlorobenzoyl-CoA, hydrolytic removal of chlorine from the para position to generate 4-hydroxybenzoyl-CoA, hydrolysis to form 4-hydroxybenzoate, oxidation to yield protocatechuate, and oxidative ring cleavage.     

Nah-genes of Pseudomonas putida: molecular genetic analysis of the plasmid pBS286

The hybridization and restriction analysis of the plasmid pBS286 (73 Kb, the P-9 Inc group) as well as parental plasmids NPL-1, NPL-41 demonstrated that pBS286 plasmid (delta NPL-41::TnA) with the constitutive synthesis of naphthalene dioxygenase carried genes for naphthalene oxidation to salicylate and those participating in degradation of catechol. Restriction map of pBS286 using XhoI restriction endonuclease and that of the nah region using EcoRI, BamHI, SalI and XhoI were established. Structural peculiarities of nah genes from pBS286 are compared with previously described NAH7. Some nah genes were localized. An inverted DNA segment involved in nah gene regulation was shown to be closely linked to a proximal part of the nah1 operon or overlapped. Possible occurrence of a regulatory R locus in this region is suggested.     

Effect of arsenite on the physiological and cytological properties of Pseudomonas putida strains capable of degrading polycyclic aromatic hydrocarbons]

Some physiological and cytological properties of Pseudomonas putida strains resistant to arsenite and capable of degrading polycyclic aromatic hydrocarbons were studied. The resistance of P. putida BS202 (NPL-1) to arsenite proved to be determined by chromosomal genes, while the arsenite resistance of P. putida BS238 (pBS2; pBS3031) was by plasmid-borne genes. Arsenite affected the pattern and rate of growth of strain BS202 (NPL-1) in media with naphthalene or salicylate as carbon sources; particularly, it lengthened the lag phase. Electron-microscope analysis of the strains studied did not reveal any arsenite-induced destructive changes in the cell envelope. At the same time, arsenite in the growth medium induced some alterations in the structure of the outer membrane of strain BS202 (NPL-1) and the cytoplasmic membrane of strain BS238 (pBS2; pBS3031) and, in both strains, led to an increase in the density of intramembrane particles on the EF face of the freeze-fractured cytoplasmic membrane. Arsenite resistance probably evidently protects cells of both strains from greater damage. Physiological and cytological data suggest that the mechanisms of arsenite resistance in the strains studied are different.