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PubMed2002

TfdD(II), one of the two chloromuconate cycloisomerases of Ralstonia eutropha JMP134 (pJP4), cannot efficiently convert 2-chloro- cis, cis-muconate to trans-dienelactone to allow growth on 3-chlorobenzoate.

Ralstonia eutropha JMP134 (pJP4) harbors two functional gene clusters for the degradation of chlorocatechols, i.e. tfdCDEF (in short: tfd (I)) and tfdD (II) C (II) E (II) F (II) (in short: tfd (II)), which are both present on the catabolic plasmid pJP4. In this study, we compared the function of both gene clusters for degradation of chlorocatechols by constructing isolated and hybrid tfd (I)- tfd (II) clusters on plasmids in R. eutropha, by activity assays of Tfd enzymes, and by HPLC/MS of individual enzymatic catalytic steps in chlorocatechol conversion. R. eutropha containing the tfd (II) cluster alone or hybrid tfd-clusters with tfdD (II) as sole gene for chloromuconate cycloisomerase were impaired in growth on 3-chlorobenzoate, in contrast to R. eutrophaharboring the complete tfd (I) cluster. Enzyme activities for TfdD(II) and for TfdE(II) were very low in R. eutropha when induced with 3-chlorobenzoate. By contrast, a relatively high enzyme activity was found for TfdF(II). Spectral conversion assays with extracts from R. eutropha strains expressing tfdD (II) all showed accumulation of a compound with a similar UV spectrum as 2-chloro- cis,cis-muconate from 3-chlorocatechol. HPLC analysis of in vitro assays in which each individual step in 3-chlorocatechol conversion was reproduced by sequentially adding cell extracts of an Escherichia coli expressing one Tfd enzyme only demonstrated that TfdD(II) was unable to cause conversion of 2-chloro- cis,cis-muconate. No accumulation of intermediates was observed with 4-chlorocatechol. From these results, we conclude that at least TfdD(II) is a bottleneck in conversion of 3-chlorocatechol and, therefore, in efficient metabolism of 3-chlorobenzoate. This study showed the subtle functional and expression differences between similar enzymes of the tfd-encoded pathway and demonstrated that extreme care has to be taken when inferring functionality from sequence data alone.

Adipates↗
PubMed1989

A novel metabolite in the microbial degradation of 2-chlorobenzoate.

A bacterium which utilizes 2-chlorobenzoate as sole source of carbon and energy was isolated from water and tentatively identified as a Pseudomonas sp. During growth on 2-chlorobenzoate, the chlorine substituent was released quantitatively and a metabolite accumulated in the culture medium. Based on thin-layer chromatography, high-pressure liquid chromatography and gas chromatography linked to mass spectrometry this compound was unequivocally identified as 2,3-dihydroxybenzoate, a compound not described before in the degradation of 2-chlorobenzoate.

Chlorobenzoates↗
PubMed1991

Identification of 4-chlorobenzoyl-coenzyme A as intermediate in the dehalogenation catalyzed by 4-chlorobenzoate dehalogenase from Pseudomonas sp. CBS3.

The intermediate in the reaction catalyzed by 4-chlorobenzoate dehalogenase from Pseudomonas sp. CBS3 was identified as 4-chlorobenzoyl-CoA. One component of 4-chlorobenzoate dehalogenase worked as a a 4-chlorobenzoyl-CoA ligase catalyzing the formation of 4-chlorobenzoyl-CoA from 4-chlorobenzoate, coenzyme A and ATP. This intermediate was detected spectrophotometrically and by HPLC. 4-chlorobenzoyl-CoA was the substrate for the dehalogenase component, which catalyzed the conversion to 4-hydroxybenzoate with concomitant release of coenzyme A.

Adenosine Triphosphate↗
PubMed1999

Specific detection of p-chlorobenzoic acid by Escherichia coli bearing a plasmid-borne fcbA'::lux fusion.

In this communication we report on a genetically engineered bacterium that reacts by light emission to the presence of 4-chlorobenzoic acid. To construct this strain, DNA fragment (1.7 kb) upstream from the 4-chlorobenzoic acid dehalogenase (fcb) operon of Arthrobacter SU was fused to Vibriofischeri luxCDABE genes. An Escherichia coli strain transformed with a multi-copy plasmid (pASU) bearing this fusion responded to the presence of 4-chlorobenzoic acid and a few closely related compounds by increased luminescence, exhibiting a high specificity but a relatively low sensitivity. While it could be somewhat, improved by manipulating the experimental pH, sensitivity remained too low for real time applicability. Nevertheless, the principle of using dehalogenase promoters as environmental pollution sensor was demonstrated.

Arthrobacter↗
PubMed1997

Acyl-adenylate motif of the acyl-adenylate/thioester-forming enzyme superfamily: a site-directed mutagenesis study with the Pseudomonas sp. strain CBS3 4-chlorobenzoate:coenzyme A ligase.

4-Chlorobenzoate:coenzyme A (4-CBA:CoA) ligase catalyzes 4-chlorobenzoyl-coenzyme A formation in a two-step reaction consisting of the adenylation of 4-chlorobenzoate with adenosine 5'-triphosphate followed by acyl transfer from the 4-chlorobenzoyl adenosine 5'-monophosphate diester intermediate to coenzyme A. In this study, two core motifs present in the Pseudomonas sp. strain CBS3 4-CBA:CoA ligase (motif I, 161T-S-G-T-T-G-L-P-K-G170, and motif II, 302Y-G-T-T-E306) and conserved among the sequences representing the acyl-adenylate/thioester-forming enzyme family (to which the ligase belongs) were tested for their possible role in substrate binding and/or catalysis. The site-directed mutants G163I, G166I, P168A, K169M, and E306Q were prepared and then subjected to steady-state and transient kinetic studies. The results, which indicate reduced catalysis of the adenylation of 4-chlorobenzoate in the mutant enzymes, are interpreted within the context of the three-dimensional structure of the acyl-adenylate/thioester-forming enzyme family member, firefly luciferase.

Adenosine Triphosphate↗
PubMed2004

Adsorption of aromatic counterions at the surfactant/water interface: a neutron reflectivity study of hydroxybenzoate and chlorobenzoate counterions at the hexadecyl trimethylammonium surfactant/water interface.

Specular neutron reflectivity has been used to investigate the adsorption of the aromatic counterions hydroxybenzoate and chlorobenzoate at the hexadecyl trimethylammonium bromide surfactant monolayer/water interface. The degree of counterion binding and the location of the counterions at the interface are shown to depend on the isomeric form of the counterion. For hydroxybenzoate, the para-substituted counterion is located within the headgroup region of the surfactant monolayer, and there is of order one counterion for every two surfactant ions. For the ortho-substituted counterion, the degree of counterion binding is higher. There is of order 0.85 counterions for each surfactant ion, and the counterion is located within the hydrophobic region of the monolayer, some 5 A from the center of the headgroup distribution. Similar results were found for the chlorobenzoate counterion, but in that case it was the para-substituted counterion that was more tightly bound and located within the hydrophobic region of the surfactant monolayer. The results for the ortho-substituted hydroxybenzoate and for the para-substituted chlorobenzoate are consistent with those previously reported for the para-tosylate. The results are discussed in the context of the ability of the specific aromatic counterion isomer to promote massive micellar growth, and the results shed light on that mechanism.

Adsorption↗
PubMed2000

Pathways for 3-chloro- and 4-chlorobenzoate degradation in Pseudomonas aeruginosa 3mT.

A bacterial isolate, Pseudomonas aeruginosa 3mT exhibited the ability to degrade high concentrations of 3-chlorobenzoate (3-CBA, 8 g l(-1)) and 4-chlorobenzoate (4-CBA 12 g l(-1)) (Ajithkumar 1998). In this study, by delineating the initial biochemical steps involved in the degradation of these compounds, we investigated how this strain can do so well. Resting cells, permeabilised cells as well as cell-free extracts failed to dechlorinate both 3-CBA and 4-CBA under anaerobic conditions, whereas the former two readily degraded both compounds under aerobic conditions. Accumulation of any intermediary metabolite was not observed during growth as well as reaction with resting cells under highly aerated conditions. However, on modification of reaction conditions, 3-chlorocatechol (3-CC) and 4-chlorocatechol (4-CC) accumulated in 3-CBA and 4-CBA flasks, respectively. Fairly high titres of pyrocatechase II (chlorocatechol 1,2-dioxygenase) activity were obtained in extracts of cells grown on 3-CBA and 4-CBA. Meta-pyrocatechase (catechol 2,3-dioxygenase) activity against 4-CC and catechol, but not against 3-CC, was also detected in low titres. Accumulation of small amounts of 2-chloro-5-hydroxy muconic semialdehyde, the meta-cleavage product of 4-CC, was detected in the medium, when 4-CBA concentration was 4 mM or greater, indicating the presence of a minor meta-pathway in strain 3mT. However, 3-CBA exclusively, and more than 99% of 4-CBA were degraded through the formation of the respective chlorocatechol, via a modified ortho-pathway. This defies the traditional view that the microbes that follow chlorocatechol pathways are not very good degraders of chlorobenzoates. 4-Hydroxybenzoate was readily (and 3-hydroxybenzoate to a lesser extent) degraded by the strain, through the formation of protocatechuate and gentisate, respectively, as intermediary dihydroxy metabolites.

2,2'-Dipyridyl↗
PubMed2001

Induction of the halobenzoate catabolic pathway and cometabolism of ortho-chlorobenzoates in Pseudomonas aeruginosa 142 grown on glucose-supplemented media.

The aerobic cometabolism of ortho-substituted chlorobenzoates by Pseudomonas aeruginosa strain 142 growing on glucose-supplemented medium was analyzed. The strain, which can use 2-chlorobenzoate (2-CBA) and 2,4-dichlorobenzoate (2,4-DCBA) as sole carbon and energy sources, showed high rates of 2-CBA metabolism in glucose-fed cells. In contrast, 2,4-DCBA was metabolized only after extended incubation of the full grown culture and depletion of glucose. In addition to the ortho-dehalogenation (ohb142) genes encoding the alpha and beta subunits of the oxygenase component of a 2-halobenzoate dioxygenase, strain 142 harbours a closely related ohbABCDFG gene cluster previously identified in P. aeruginosa JB2 (ohbJB2). The genes for the chlorocatechol ortho-catabolic pathway were identified and sequenced in this strain, showing a near complete identity with the clcABD operon of the pAC27 plasmid. Relative quantification of mRNA by RT-PCR shows a preferential induction of ohb142 by 2-CBA, which is abolished in glucose-grown cultures. The alternate ohbJB2 and clc genes were expressed preferentially in 2,4-DCBA grown cultures. Only ohbJB2 appears to be expressed in the presence of the carbohydrate. Detection of chlorocatechol-1,2-dioxygenase activity in 2,4-DCBA plus glucose grown cultures suggests the presence of an alternate system for the ortho-cleavage of chlorobenzoates. The recruitment of elements from two halobenzoate dioxygenase systems with different induction patterns, together with a chlorocatechol degradative pathway not repressed by carbon catabolite, may allow P. aeruginosa 142 to cometabolize haloaromatics in carbohydrate grown cultures.

Biodegradation, Environmental↗
PubMed1999

Characterization of chlorobenzoate degraders isolated from polychlorinated biphenyl-contaminated soil and sediment in the Czech Republic.

Two polychlorinated biphenyl-contaminated sites in the Czech Republic, a soil at Zamberk and a sediment sludge at Milevsko, were screened for the presence of chlorobenzoate degraders. Sixteen different chlorobenzoate degraders were isolated from the soil compared with only three strains isolated from the sediment. From these strains, only four soil degraders and one strain isolated from the sediment, respectively, were shown to possess a complete chlorobenzoate (CB) pathway. Bacteria isolated from the soil have expressed more flexibility for CB degradation, namely in the case of ortho-chlorinated benzoates. They all possessed large plasmids, the restriction patterns of which were compared. Plasmids in Pseudomonas sp. A7, A8, A18 and A19, respectively, were cured and found to encode at least part of the metabolic pathway involved in the growth on ortho-chlorinated benzoates.

Biodegradation, Environmental↗
PubMed1979

Utilization of chlorobenzoates by microbial populations in sewage.

Microorganisms in sewage decomposed 3.4-dichlorobenzoate and m-, p-, and o-chlorobenzoates. As the substrate disappeared, populations capable of growing on these compounds proliferated. Neither 2,4-dichlorobenzoate nor 2,3,6-trichlorobenzoate was destroyed by the sewage microflora. The addition of glucose or benzoate and m-chlorobenzoate to the sewage did not promote degradation of 2,4-di- or 2,3,6-trichlorobenzoates. The populations responsible for the biodegradation of the chlorinated compounds were initially less than 100 cells/ml. During the metabolism of m-chlorobenzoate, 5-chlorosalicylate and 4-chlorocatechol were formed.

Bacteria↗
PubMed1987

Reductive dechlorination of 2,4-dichlorobenzoate to 4-chlorobenzoate and hydrolytic dehalogenation of 4-chloro-, 4-bromo-, and 4-iodobenzoate by Alcaligenes denitrificans NTB-1.

Alcaligenes denitrificans NTB-1, previously isolated on 4-chlorobenzoate, also utilized 4-bromo-, 4-iodo-, and 2,4-dichlorobenzoate but not 4-fluorobenzoate as a sole carbon and energy source. During growth, stoichiometric amounts of halide were released. Experiments with whole cells and cell extracts revealed that 4-bromo- and 4-iodobenzoate were metabolized like 4-chlorobenzoate, involving an initial hydrolytic dehalogenation yielding 4-hydroxybenzoate, which in turn was hydroxylated to 3,4-dihydroxybenzoate. The initial step in the metabolism of 2,4-dichlorobenzoate was catalyzed by a novel type of reaction for aerobic organisms, involving inducible reductive dechlorination to 4-chlorobenzoate. Under conditions of low and controlled oxygen concentrations, A. denitrificans NTB-1 converted all 4-halobenzoates and 2,4-dichlorobenzoate almost quantitatively to 4-hydroxybenzoate.

Alcaligenes↗
PubMed1991

Metabolism of and inhibition by chlorobenzoates in Pseudomonas putida P111.

Pseudomonas putida P111 was isolated by enrichment culture on 2,5-dichlorobenzoate and was also able to grow on 2-chloro-, 3-chloro-, 4-chloro-, 2,3-dichloro-, 2,4-dichloro-, and 2,3,5-trichlorobenzoates. However, 3,5-dichlorobenzoate completely inhibited growth of P111 on all ortho-substituted benzoates that were tested. When 3,5-dichlorobenzoate was added as a cosubstrate with either 3- or 4-chlorobenzoate, cell yields and chloride release were greater than those observed from growth on either monochlorobenzoate alone. Moreover, resting cells of P111 grown on 4-chlorobenzoate released chloride from 3,5-dichlorobenzoate and produced no identifiable intermediate. In contrast, resting cells grown on 2,5-dichlorobenzoate metabolized 3,5-dichlorobenzoate without release of chloride and accumulated a degradation product, which was identified as 1-carboxy-1,2-dihydroxy-3,5-dichlorocyclohexadiene on the basis of gas chromatography-mass spectrometry confirmation of its two acid-hydrolyzed products, 3,5- and 2,4-dichlorophenol. Since 3,5-dichlorocatechol was rapidly metabolized by cells grown on 2,5-dichlorobenzoate, it is apparent that 1-carboxy-1,2-dihydroxy-3,5-dichlorocyclohexadiene is not further metabolized by these cells. Moreover, induction of a functional dihyrodiol dehydrogenase would not be required for growth of P111 on other ortho-chlorobenzoates since the corresponding chlorodihydrodiols produced from a 1,2-dioxygenase attack would spontaneously decompose to the corresponding catechols. In contrast, growth on 3-chloro-, 4-chloro-, or 3,5-dichlorobenzoate requires a functional dihydrodiol dehydrogenase, yet only the two monochlorobenzoates appear to induce for it.

Biodegradation, Environmental↗
PubMed1983

Genetic homology between independently isolated chlorobenzoate-degradative plasmids.

Two chlorobenzoate-degradative plasmids were studied by the hybridization of the restriction endonuclease-generated fragments of one plasmid after transfer to a nitrocellulose filter with nick-translated radioactive DNA of the other plasmid as a probe. Two strains harboring the 3-chlorobenzoic acid-degradative plasmids were isolated in two different parts of the world at two different times. The plasmids are now found to be closely related to each other by hybridization studies. The chlorobenzoate-degradative plasmid from Pseudomonas sp. strain B13 (termed pB13) has a 6-kilobase deletion but otherwise is homologous with previously described plasmid pAC25.

Base Sequence↗
PubMed1985

Transposon mutagenesis and cloning analysis of the pathways for degradation of 2,4-dichlorophenoxyacetic acid and 3-chlorobenzoate in Alcaligenes eutrophus JMP134(pJP4).

Plasmid pJP4 permits its host bacterium, strain JMP134, to degrade and utilize as sole sources of carbon and energy 3-chlorobenzoate and 2,4-dichlorophenoxyacetic acid (R. H. Don and J. M. Pemberton, J. Bacteriol. 145:681-686, 1981). Mutagenesis of pJP4 by transposons Tn5 and Tn1771 enabled localization of five genes for enzymes involved in these catabolic pathways. Four of the genes, tfdB, tfdC, tfdD, and tfdE, encoded 2,4-dichlorophenol hydroxylase, dichlorocatechol 1,2-dioxygenase, chloromuconate cycloisomerase, and chlorodienelactone hydrolase, respectively. No function has been assigned to the fifth gene, tfdF, although it may encode a trans-chlorodiene-lactone isomerase. Inactivation of genes tfdC, tfdD, and tfdE, which encode the transformation of dichlorocatechol to chloromaleylacetic acid, prevented host strain JMP134 from degrading both 3-chlorobenzoate and 2,4-dichlorophenoxyacetic acid, which indicates that the pathways for these two substrates utilize common enzymes for the dissimilation of chlorocatechols. Studies with cloned catabolic genes from pJP4 indicated that whereas all essential steps in the degradation of 2,4-dichlorophenoxyacetic acid are plasmid encoded, the conversion of 3-chlorobenzoate to chlorocatechol is specified by chromosomal genes.

2,4-Dichlorophenoxyacetic Acid↗
PubMed1994

Pseudomonas aeruginosa 142 uses a three-component ortho-halobenzoate 1,2-dioxygenase for metabolism of 2,4-dichloro- and 2-chlorobenzoate.

Cell extracts of Pseudomonas aeruginosa 142, which was previously isolated from a polychlorinated biphenyl-degrading consortium, were shown to degrade 2,4-dichlorobenzoate, 2-chlorobenzoate, and a variety of other substituted ortho-halobenzoates by a reaction that requires oxygen, NADH, Fe(II), and flavin adenine dinucleotide. By using extracts that were chromatographically depleted of chlorocatechol and catechol 1,2-dioxygenase activities, products of the initial reaction with 2,4- or 2,5-dichlorobenzoate and 2-chlorobenzoate were identified by mass spectrometry as 4-chlorocatechol and catechol. In contrast to the well-characterized benzoate dioxygenases or the recently described 2-halobenzoate 1,2-dioxygenase from P. cepacia 2CBS (S. Fetzner, R. Müller, and F. Lingens, J. Bacteriol. 174:279-290, 1992) that possess two protein components, the P. aeruginosa enzyme was resolved by ion-exchange chromatography into three components, each of which is required for activity. To verify the distinct nature of this enzyme, we purified, characterized, and identified one component as a ferredoxin (M(r), approximately 13,000) containing a single [2Fe-2S] Rieske-type cluster (electron paramagnetic resonance spectroscopic values of gx = 1.82, gy = 1.905, and gz = 2.02 in the reduced state) that is related in sequence to ferredoxins found in the naphthalene and biphenyl three-component dioxygenase systems. By analogy to these enzymes, we propose that the P. aeruginosa ferredoxin serves as an electron carrier between an NADH-dependent ferredoxin reductase and the terminal component of the ortho-halobenzoate 1,2-dioxygenase. The broad specificity and high regiospecificity of the enzyme make it a promising candidate for use in the degradation of mixtures of chlorobenzoates.

Amino Acid Sequence↗
PubMed1991

[Cloning of genes degrading 3-chlorobenzoate from Pseudomonas putida strain 87].

The ability of Pseudomonas putida strain 87 to catabolize 3-chlorobenzoate was shown to be mediated by genes of pBS109 plasmid. The plasmid may be transferred by conjugation into P. aeruginosa PAO2175. It seems possible that the pBS109 plasmid codes for pyrocatechase II specific for halogenated catechol, but not catechol. The genes specifying utilization of 3-chlorobenzoate from pBS109 plasmid were cloned in the 5.5 kb BgIII fragment by using broad-host cloning system. The resulting pBS110 plasmid was transferred into P. putida, which results in utilization of 3-chlorobenzoate by transconjugants.

Biodegradation, Environmental↗
PubMedDate not supplied

[Degradation of 3-chlorobenzoic acid by a Pseudomonas putida strain].

A Pseudomonas putida strain 87 capable of assimilating 3-chlorobenzoic acid as a sole source of carbon and energy (3Cba+) was isolated. Treatment with mitomycin C eliminated the 3Cba+ phenotype in 1% of cells in the population. The 3Cba+ phenotype was transferred at a low frequency in the process of conjugation to other bacteria belonging to the genus Pseudomonas. Determinants localized on the plasmid are presumed to be responsible for the capability to assimilate 3-chlorobenzoic acid. A scheme is proposed for the oxidation of 3-chlorobenzoic acid on the basis of studying the products of its degradation. Two catechol 1,2-dioxygenases are present in strains with the 3Cba+ phenotype as was shown by analysing the activity of enzymes catalysing cleavage of the aromatic cycle and by studying their induction. One of the two seems to be encoded by chromosomal genes while the other is encoded by plasmid genes and determines the capability of the culture to cleave the chlorinated pyrocatechol.

Biodegradation, Environmental↗
PubMed1984

Incorporation of [18O]water into 4-hydroxybenzoic acid in the reaction of 4-chlorobenzoate dehalogenase from pseudomonas spec. CBS 3.

4-Chlorobenzoate is dehalogenated by 4-chlorobenzoate dehalogenase from Pseudomonas spec. CBS 3 to form 4-hydroxybenzoate. In 18O enriched water the hydroxygroup of 4-hydroxybenzoate is quantitatively labelled with 18O. This result clearly shows, that 4-chlorobenzoate dehalogenase catalyzes the hydrolytic cleavage of the halogen-carbon bond, without the involvement of molecular oxygen, a reaction not yet described.

Chromatography, Gas↗