Biodegradation of 3-chlorobenzoate by Pseudomonas putida 10.2

Pseudomonas putida 10.2, a 3-chlorobenzoate (3CBa)-degrading bacterium, was isolated from a soil sample obtained from an agricultural area in Chiang Mai, Thailand. This bacterium could degrade 2mm 3CBa very rapidly with the concomitant formation of chloride ion when grown in mineral salt-yeast extract medium. The presence of glucose, lactose and pyruvate in the medium reduced the capability of this bacterium to degrade 3CBa. Metabolites such as 3-chlorocatechol (3CC), catechol and cis,cis-muconic acid (muconate) could be detected in the growth medium or in cell suspensions when 3CBa was used as the substrate. Furthermore, when crude enzyme extract prepared from 3CBa-grown P. putida 10.2 was incubated with 3CC, catechol and muconate could be detected in the reaction mixtures. Thus, the biodegradation pathway of 3CBa by P. putida 10.2 was proposed to involve transformation of 3CBa to 3CC. The dehalogenation step is believed to involve removal of chloride from 3CC to form catechol, which is subsequently converted to muconate.     

Enzymatic dehalogenation of 4-chlorobenzoate by 4-chlorobenzoate dehalogenase from Pseudomonas sp. CBS3 in organic solvents

Summary 4-Chlorobenzoate dehalogenase from Pseudomonas sp. CBS3 showed dehalogenating activity in various organic solvents. In alcohols like methanol (150%) or ethanol (120%) higher activities than in water (100%) were obtained. In apolar solvents like petroleum ether (5%) and nhexane (5%) only trace activities were observed. The solvents did not increase the stability of the enzyme. 4-Chlorobenzoic acid methylester, a substance not soluble in water, was not dehalogenated in organic solvents.     

Simultaneous degradation of 3-chlorobenzoate and phenolic compounds by a defined mixed culture ofPseudomonas spp.

A mixed culture of a chlorobenzoate-(3-CBA)-degradingPseudomonas aeruginosa, strain 3mT, and a phenol/cresols-degradingPseudomonas sp., strain CP4, simultaneously and efficiently degraded mixtures of 3-CBA and phenol/cresols. However, strains 3mT and CP4 usedortho- andmeta-ring cleavage pathways, respectively. Degradation of 3-CBA was complete when the 3-CBA was equal in amount to or less than that of phenol. CP4/3mT inoculum ratios (w/w) of 1:1 or 1:2 gave the most effective degradation of both the substrates in the mixture. The mixed culture degraded equimolar mixtures of 3-CBA/phenol up to 10mm. Equimolar mixtures of 3-CBA ando-, m- orp-cresol were also degraded by the mixed culture.The authors are with the Microbiology and Bioengineering Department, Central Food Technological Research Institute, Mysore-570013, India;     

Metabolism of dodecyldimethylamine by Pseudomonas MA3

Pseudomonas MA3 was isolated from activated sludge on the basis of its capacity to use dodecyldimethylamine as a sole carbon (C) and energy source. Dodecylamine, dodecanal, dodecanoic acid and acetic acid also supported growth of Pseudomonas MA3. Dodecyldimethylamine-grown cells oxidized a wide range of alkylamine derivatives, dodecanal, dodecanoic acid and acetic acid. Degradation of the alkyl chain of dodecyldimethylamine by Pseudomonas MA3 appeared from the stoichiometric liberation of dimethylamine. A dehydrogenase catalysed the cleavage of the C_alkyl-N bond. The first intermediate of the proposed degradation pathway, dodecanal, accumulated in the presence of decanal used as a competitive inhibitor. The second intermediate,dodecanoic acid, was formed in the presence of acrylic acid during the degradation of dodecyldimethylamine. Dodecanal was converted into dodecanoic acid by a dehydrogenase and dodecanoic acid was then degraded via the oxidation pathway.     

Degradation of 2-chlorobenzoate by Pseudomonas cepacia 2CBS

A bacterium was isolated from water by enrichment on 2-chlorobenzoate as sole source of carbon and energy. Based on morphological and physiological properties, this microorganism was assigned to the species Pseudomonas cepacia. The organism was designated Pseudomonas cepacia 2CBS. During growth on 2-chlorobenzoate, the chlorine substituent was released quantitatively, and a small amount of 2,3-dihydroxybenzoate accumulated in the culture medium. Mutants of Pseudomonas cepacia 2CBS were induced by treatment with N-methyl-N'-nitro-N-nitrosoguanidine. Some of these mutants produced catechol from 2-chlorobenzoate. Other mutants accumulated the meta-cleavage product of catechol, 2-hydroxy-cis,cis-muconic acid semialdehyde. In crude cell-free extracts of Pseudomonas cepacia 2CBS, an enzyme was detected which catalysed the conversion of 2-chlorobenzoate to catechol. Molecular oxygen, NADH and exogenous Fe2+ were required for activity. Stoichiometric amounts of chloride were released. Experiments with 18O2 revealed that both oxygen atoms in the hydroxyl groups of the product were derived from molecular oxygen. Thus, the enzyme catalysing the conversion of 2-chlorobenzoate was identified as 2-chlorobenzoate 1,2-dioxygenase (1,2-hydroxylating, dehalogenating, decarboxylating). 2-Chlorobenzoate 1,2-dioxygenase from Pseudomonas cepacia 2CBS was shown to be a multicomponent enzyme system. The activities of catechol 2,3-dioxygenase and catechol 1,2-dioxygenase were detected in crude cell-free extracts. The activity of catechol 2,3-dioxygenase was 60 times higher than the activity of catechol 1,2-dioxygenase, indicating that catechol is mainly degraded via meta-cleavage in Pseudomonas cepacia 2CBS. No enzyme was found which converted 2,3-dihydroxybenzoate, suggesting that this compound is a dead-end metabolite of 2-chlorobenzoate catabolism. A pathway for the degradation of 2-chlorobenzoate by Pseudomonas cepacia 2CBS is proposed.     

Pathways for 3-chloro- and 4-chlorobenzoate degradationin 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 against4-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-Hydroxybenzoatewas readily (and 3-hydroxybenzoate to a lesser extent) degraded by the strain, through the formation of protocatechuate and gentisate, respectively, as intermediary dihydroxy metabolites.     

Isolation and preliminary characterization of a 2-chlorobenzoate degrading Pseudomonas

Pseudomonas sp. strain B-300, which is able to utilize 2-chlorobenzoic acid, was isolated from a soil sample by enrichment culture. This strain was shown to grow on 2-chlorobenzoic acid and to completely degrade the substrate with concomitant chlorine ion release. Concentrations of 2-chlorobenzoic acid higher than 0.5% (w/v) were toxic to the cells. Our study also suggested that in the presence of glucose, 2-chlorobenzoic acid is converted to catechol or chlorocatechol; these are in turn transformed to muconic and chloromuconic acid, respectively, suggesting a repression by glucose of some of the degradation pathway enzymes. A similar scheme was already described for 3-chlorobenzoate degradation by pAC25 plasmid.     

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.     

Initial characterisation of 4-chlorobenzoate dehalogenase from Pseudomonas sp. CBS3

Extracts of Pseudomonas sp. CBS3 converted 4-chlorobenzoate into 4-hydroxybenzoate. The enzyme responsible for this conversion was enriched by ammonium sulphate fractionation (30–60% saturation, 1.3-fold). The optimum conditions for the reaction were 30–35°C and pH 7–7.5. The enzyme was activated by Mn²⁺ (1 mM final concentration) up to 120-fold, and by Co²⁺ (1 mM final concentration) up to 60-fold. Other divalent ions had no effect. EDTA inhibited the enzyme. 4-Bromobenzoate and 4-iodobenzoate were substrates for the enzyme, but 4-fluorobenzoate was not converted.     

Metabolism of Lignin Model Compounds of the Arylglycerol-beta-Aryl Ether Type by Pseudomonas acidovorans D(3)

A natural bacterial isolate that we have classified as Pseudomonas acidovorans grows on the lignin model compounds 1-(3,4-dimethoxyphenyl)-2-(2-methoxyphenoxy)propane-1,3-diol (compound 1) and 1-(4-hydroxy-3-methoxyphenyl)-2-(2-methoxyphenoxy)propane-1,3-diol (compound 1'), as well as on the corresponding 1-oxo compounds (2 and 2') as sole sources of carbon and energy. Metabolic intermediates present in cultures growing on compound 1 included compound 2, 2-methoxyphenol (guaiacol [compound 3]), beta-hydroxypro-pioveratrone (compound 4), acetoveratrone (compound 5), and veratric acid (compound 6). Also identified were compounds 1', 2', beta-hydroxypropiovanillone (compound 4'), and acetovanillone (compound 5'), indicating that 4-O demethylation also occurs. The phenolic intermediates were the same as those found in cultures growing on compound 1'. Compounds 2 and 2' were in part also reduced to compounds 1 and 1', respectively. Compound 3 was shown to be derived from the 2-methoxyphenoxy moiety. A suggested degradation scheme is as follows: compound 1-->2-->(3 + 4)-->5-->6 (and similarly for 1'). In this scheme, the key reaction is cleavage of the ether linkage between C-2 (C(beta)) of the phenylpropane moiety and the 2-methoxyphenoxy moiety in compounds 2 and 2' (i.e., beta-aryl ether cleavage). On the basis of compounds identified, viz., 3 and 4 (4'), cleavage appears formally to be reductive. Because this is unlikely, the initial cleavage products probably were not detected. The implications of these results for the enzyme(s) responsible are discussed.     

Characterization of a degradative plasmid coding for metabolism of 3-chlorobenzoate by Pseudomonas putida and its expression in Escherichia coli

World Journal of Microbiology and Biotechnology -     

Metabolism of Lignin Model Compounds of the Arylglycerol-beta-Aryl Ether Type by Pseudomonas acidovorans D(3)

[This corrects the article on p. 2608 in vol. 53.].     

Degradation of 3-chlorobenzoate by thermophilic micro-organisms

Thermophilic (75°C), anaerobic biodegradation of chlorobenzoates was investigated using different inocula from geothermal and non-geothermal environments. Microbial dehalogenation of 3-chlorobenzoate (0·5 mmol l⁻¹) was achieved by two mixed cultures growing anaerobically at 75°C. One culture consisted of a facultative anaerobe and two obligate anaerobes, one of which was a methanogen, isolated from terrestrial sediments from hot springs in New Zealand. The other culture, derived from a non-geothermal environment, consisted of a Clostridium spp. and a non-spore-forming obligate anaerobe. No degradation of either 2-chlorobenzoate or 4-chlorobenzoate was achieved by these thermophilic cultures over the same time period. This is the first reported biotransformation of this chlorinated aromatic at a temperature of 75°C.     

Biosynthesis and cytoplasmic accumulation of a chlorinated catechol pigment during 3-chlorobenzoate aerobic co-metabolism in Pseudomonas fluorescens

A strain of Pseudomonas fluorescens was capable of co-metabolizing 3-chlorobenzoic acid with the production of a chlorinated catechol black pigment. A peroxidase and another enzymatic activity referred to as a polyphenol oxidase were found to be involved in the oxidation of 4-chlorocatechol to 4-chloro-1,2-benzoquinone, i.e. in the production of highly reactive substrates for pigment formation. Therefore, P. fluorescens cells were seen to take an active part not only in 3-chlorobenzoate mineralization but also in overall pigment production. pH was found to be a key parameter in the regulation of the activity of P. fluorescens oxidoreductive enzymes. Ultrastructural investigations showed that electron dense granules of pigment were distributed throughout the cytoplasm of Pseudomonas fluorescens cells grown in presence of 3-chlorobenzoate, as confirmed also by Thiéry cytochemical investigations.In these cells, an extensive contraction of the cytoplasm as well as a significant damage to the cell wall after two days of incubation, suggested that pigment production caused a premature death of the cells accompanied by the leakage of the cell content. Pigment production seemed to occur mostly in the cytoplasmic context where the electron dense material accumulates until it is released in the medium after the cell lysis.Abbreviations 3-CBA 3-chlorobenzoic acid - BA benzoic acid - 4-CC 4-chlorocatechol - 3-CC 3-chlorocatechol - MBTH 3-methyl-2-benzothiazolinone hydrazone - l-DOPA l-3,4-dihydroxyphenyl-alanine - SPB sodium phosphate buffer     

Metabolism of sitosterol by a Pseudomonas species.

Fermentation of sitosterol by a Pseudomonas species (SK-25) resulted in the formation of 5-stigmastene-3 beta, 7 alpha-diol; 5,6 alpha-epoxy-5 alpha-stigmastan-3 beta-ol; 5,6 beta-epoxy-5 beta-stigmastan-3 beta-ol and 5 alpha-stigmastan-3 beta, 5,6 beta-triol. The metabolites were characterized by a variety of conventional chemical and spectrometric techniques.     

Metabolism of phenylbenzoate by Pseudomonas sp. strain TR3

A bacterial isolate, tentatively identified as Pseudomonas sp. strain TR3, was found to utilize the diaryl ester phenylbenzoate as sole source of carbon and energy. This strain has the ability to productively degrade phenylbenzoate and some substituted derivatives by a catabolic sequence which was characterized biochemically. The biodegradation of phenylbenzoate is thus initiated by an inducible esterase, effectively hydrolyzing the diaryl esters to produce stoichiometric amounts of two monoaromatic metabolites, identified as benzoate and phenol in the case of phenylbenzoate. The diaryl ester p-tolylbenzoate was hydrolyzed to yield benzoate and 4-methylphenol while 4-chlorophenylbenzoate gave rise to the production of benzoate and 4-chlorophenol. These monoaromatic catabolites were further degraded via the oxoadipate pathway.