Degradation of 4-Chlorophenol via the meta Cleavage Pathway by Comamonas testosteroni JH5

Comamonas testosteroni JH5 used 4-chlorophenol (4-CP) as its sole source of energy and carbon up to a concentration of 1.8 mM, accompanied by the stoichiometric release of chloride. The degradation of 4-CP mixed with the isomeric 2-CP by resting cells led to the accumulation of 3-chlorocatechol (3-CC), which inactivated the catechol 2,3-dioxygenase. As a result, further 4-CP breakdown was inhibited and 4-CC accumulated as a metabolite. In the crude extract of 4-CP-grown cells, catechol 1,2-dioxygenase and muconate cycloisomerase activities were not detected, whereas the activities of catechol 2,3-dioxygenase, 2-hydroxymuconic semialdehyde dehydrogenase, 2-hydroxymuconic semialdehyde hydrolase, and 2-oxopent-4-enoate hydratase were detected. These enzymes of the meta cleavage pathway showed activity with 4-CC and with 5-chloro-2-hydroxymuconic semialdehyde. The activities of the dioxygenase and semialdehyde dehydrogenase were constitutive. Two key metabolites of the meta cleavage pathway, the meta cleavage product (5-chloro-2-hydroxymuconic semialdehyde) and 5-chloro-2-hydroxymuconic acid, were detected. Thus, our previous postulation that C. testosteroni JH5 uses the meta cleavage pathway for the complete mineralization of 4-CP was confirmed.     

Co-metabolism of methyl- and chloro-substituted catechols by an Achromobacter sp. possessing a new meta-cleaving oxygenase

Co-metabolism of 3-methylcatechol, 4-chlorocatechol and 3,5-dichlorocatechol by an Achromobacter sp. was shown to result in the accumulation of 2-hydroxy-3-methylmuconic semialdehyde, 4-chloro-2-hydroxymuconic semialdehyde and 3,5-dichloro-2-hydroxymuconic semialdehyde respectively. Formation of these products indicated that cleavage of the aromatic nucleus of the substituted catechols was accomplished by a new meta-cleaving enzyme, catechol 1,6-oxygenase. This enzyme was equally active on both chloro- and methyl-substituted catechols.     

Degradation of 4-chlorophenol in municipal wastewater by adsorptiv immobilized Alcaligenes sp. A 7-2

Summary Alcaligenes sp. A 7-2 has been applied in a packed-bed fermenter to degrade 4-chlorophenol in municipal wastewater continuously. With sterile wastewater degradation rates up to 300 mol/l/h were reached when precultivated Alcaligenes sp. A 7-2 had been adsorbed onto the Lecaton-packed-bed-material.The natural microbial population of the wastewater was not able to degrade 4-chlorophenol. Beside an accumulation of the haloaromatic compound a yellow-greenish substance exhibiting the spectral characteristics of 5-chloro-2-hydroxymuconic acid semialdehyde was found.This compound caused a rapid decrease in metabolic activity of the microbial culture.With non-sterile wastewater Alcaligenes sp. A 7-2 could not be established as member of the natural mixed population. Due to the poor retainment of the specialized strain in the packed-bed the degradation capacity of the fermentation system decreased and 4-chlorophenol was accumulated.     

Cooxidation of chloro- and methylphenols by Alcaligenes xylosoxidans JH1

Alcaligenes xylosoxidans subspecies denitrificans JH1 was enriched with 2-chlorophenol from a mixed culture degrading different chloro- and methylphenols. The strain used all monochloro- and monomethylphenols apart from 2-methylphenol as sole source of energy and carbon with stoichiometric release of chloride. 4-Chlorophenol was mineralized up to a concentration of 1.3 mM. Degradation of mixtures of monochloro- and monomethylphenols occurred at least partially except for the mixture of 2-chlorophenol and 3-methylphenol. Depending upon the growth substrates used, enzymes of the ortho and/or meta cleavage pathway catalysed the degradation of the phenols. The transformation of chlorophenols was concluded to occur exclusively via the ortho cleavage pathway because no chlorocatechol 2,3-dioxygenase activity was found in chlorophenol-grown cells. Degradation of 4-methylphenol in strain JH1 occurred both by the ortho and meta cleavage pathway as indicated by the finding that the ortho- and meta-cleaving dioxygenases were expressed in 4-methylphenol-grown cells. Transformation of methylphenols by the ortho cleavage pathway led to the accumulation of methyllactones as dead-end products. Mixtures of methyl- and chlorophenols were metabolized mainly by the ortho cleavage pathway because chlorocatechols formed inactivated the constitutive catechol 2,3-dioxygenase which caused channelling of methylphenols into the ortho cleavage pathway.     

A meta cleavage pathway for 4-chlorobenzoate, an intermediate in the metabolism of 4-chlorobiphenyl by Pseudomonas cepacia P166.

Bacterial degradation of biphenyl and polychlorinated biphenyls proceeds by a well-studied pathway which produces benzoate and 2-hydroxypent-2,4-dienoate (or, in the case of polychlorinated biphenyls, the chlorinated derivatives of these compounds). Pseudomonas cepacia P166 utilizes 4-chlorobiphenyl for growth and produces 4-chlorobenzoate as a central intermediate. In this study we found that strain P166 further transforms 4-chlorobenzoate to 4-chlorocatechol, which is mineralized by a meta cleavage pathway. Key metabolites which we identified include the meta cleavage product (5-chloro-2-hydroxymuconic semialdehyde), 5-chloro-2-hydroxymuconate, 5-chloro-2-oxopent-4-enoate, 5-chloro-4-hydroxy-2-oxopentanoate, and chloroacetate. Chloroacetate accumulated transiently, and slow but stoichiometric dehalogenation was observed.     

Distal Cleavage of 3-Chlorocatechol by an Extradiol Dioxygenase to 3-Chloro-2-Hydroxymuconic Semialdehyde

A 2,3-dihydroxybiphenyl 1,2-dioxygenase from the naphthalenesulfonate-degrading bacterium Sphingomonas sp. strain BN6 oxidized 3-chlorocatechol to a yellow product with a strongly pH-dependent absorption maximum at 378 nm. A titration curve suggested (de)protonation of an ionizable group with a pK_a of 4.4. The product was isolated, purified, and converted, by treatment with diazomethane, to a dimethyl derivative and, by incubation with ammonium chloride, to a picolinic acid derivative. Mass spectra and ¹H and ¹³C nuclear magnetic resonance (NMR) data for these two derivatives prove a 3-chloro-2-hydroxymuconic semialdehyde structure for the metabolite, resulting from distal (1,6) cleavage of 3-chlorocatechol. 3-Methylcatechol and 2,3-dihydroxybiphenyl are oxidized by this enzyme, in contrast, via proximal (2,3) cleavage.     

5-Chloropicolinic acid is produced by specific degradation of 4-chlorobenzoic acid by Sphingomonas paucimobilis BPSI-3

We have previously shown that the bacterium Sphingomonas paucimobilis BPSI-3, isolated from PCB-contaminated soil, can degrade halogenated biphenyls, naphthalenes, catechols and benzoic acids. However, before such an organism can be used in bioremediation, it is important to characterise the degradation products and determine the degradation pathways to ensure that compounds more toxic or mobile than the original contaminants are not produced. In the degradation of 4-chlorobiphenyl, S. paucimobilis BPSI-3 produces a novel chlorinated picolinic acid. In this paper, we show that 4-chlorobenzoate is an intermediate in this degradation and, through ¹⁵N-labelling, that 5-chloropicolinate is the only nitrogenous metabolite isolated under the extraction conditions used. The position of the chlorine indicates that degradation of 4-chlorocatechol occurs exclusively via a 2,3-extradiol cleavage. These data allow us to postulate a more definitive catabolic pathway for the biodegradation of 4-chlorobiphenyl to 5-chloro-2-hydroxymuconic acid semialdehyde via 4-chlorobenzoate in S. paucimobilis BPSI-3. Received 19 April 1999/ Accepted in revised form 23 July 1999     

Transformation and mineralization of halophenols by Penicillium simplicissimum SK9117

The metabolism of monohalophenols by Penicillium simplicissimum SK9117, isolated from a sewage plant was investigated. In submerged cultures, 3-, 4-chlorophenol, and 4-bromophenol were metabolized in the presence of phenol. 3-Chlorophenol was transformed to chlorohydroquinone, 4-chlorocatechol, 4-chloro-1,2,3-trihydroxybenzene, and 5-chloro-1,2,3-trihydroxybenzene. With 4-chlorophenol only 4-chlorocatechol was observed as transient product. A release of chloride ions was not observed. Whereas monobromo-, and monochlorophenols could not support growth as sole carbon and energy source, growth and release of fluoride ions were observed with monofluorophenols as substrates. In presence of phenol, the degradation of all monofluorophenols was enhanced. Substrate and cosubstrate disappeared simultaneously. 3-Fluorophenol and 4-fluorophenol were completely mineralized as shown by the equimolar release of fluoride ions.Parts of the results have been presented at the annual meeting of the VAAM in Stuttgart, Germany, March 1995.     

Metabolism of 2,4-dichlorophenoxyacetic acid, 4-chloro-2-methylphenoxyacetic acid and 2-methylphenoxyacetic acid by Alcaligenes eutrophus JMP 134

Of eleven substituted phenoxyacetic acids tested, only three (2,4-dichloro-, 4-chloro-2-methyl- and 2-methylphenoxyacetic acid) served as growth substrates for Alcaligenes eutrophus JMP 134. Whereas only one enzyme seems to be responsible for the initial cleavage of the ether bond, there was evidence for the presence of three different phenol hydroxylases in this strain. 3,5-Dichlorocatechol and 5-chloro-3-methylcatechol, metabolites of the degradation of 2,4-dichlorophenoxyacetic acid and 4-chloro-2-methylphenoxyacetic acid, respectively, were exclusively metabolized via the ortho-cleavage pathway. 2-Methylphenoxyacetic acid-grown cells showed simultaneous induction of meta- and ortho-cleavage enzymes. Two catechol 1,2-dioxygenases responsible for ortho-cleavage of the intermediate catechols were partially purified and characterized. One of these enzymes converted 3,5-dichlorocatechol considerably faster than catechol or 3-chlorocatechol. A new enzyme for the cycloisomerisation of muconates was found, which exhibited high activity against the ring-cleavage products of 3,5-dichlorocatechol and 4-chlorocatechol, but low activities against 2-chloromuconate and muconate.Non-standard abbreviations MCPA 4-chloro-2-methylphenoxyacetic acid - 2MPA 2-methylphenoxyacetic acid - PA phenoxyacetic acid     

Biotransformation of halophenols by a thermophilic Bacillus sp.

The thermophilic Bacillus sp. A2 transformed various halophenols. 2-Chlorophenol, 2-bromophenol, 3-bromophenol and 2-fluorophenol were transformed under resting cell conditions at 60°C to 3-chlorocatechol, 3-bromocatechol, 4-bromocatechol and 3-fluorocatechol, respectively. The hydroxylation of 3-bromophenol occurred at the proximal and distal position relative to the halogen substituent. In complex medium this strain completely transformed 2-chlorophenol and 2-bromophenol at concentrations up to 1 mM. Concomitantly, an accumulation of oxygen-and temperature sensitive halocatechols was observed. 3-Chlorocatechol possesses a half-life of 11.5 h at 60°C and is therefore readily decomposed during incubation. The hydroxylating system was present in phenolgrown cells but not in glucose-grown cells. The hydroxylase activity could also be induced by 2-chlorophenol. The product, 3-chlorocatechol, is not a substrate for the catechol 2,3-dioxygenase.Abbreviations 2-CP 2-chlorophenol - DCP dichlorophenol - TCP trichlorophenol - tetraCP tetrachlorophenol - MIC minimal inhibitory concentration - CF chloride-free - CFG chloride-free plus glucose - CFGY chloride-free plus glycerol - CFP chloride-free plus phenol - CAM chloramphenicol     

Microorganisms degrading chlorobenzene via a meta-cleavage pathway harbor highly similar chlorocatechol 2,3-dioxygenase-encoding gene clusters

Pseudomonas putida GJ31 harbors a degradative pathway for chlorobenzene via meta-cleavage of 3-chlorocatechol. Pseudomonads using this route for chlorobenzene degradation, which was previously thought to be generally unproductive, were isolated from various contaminated environments of distant locations. The new isolates, Pseudomonas fluorescens SK1 (DSM16274), Pseudomonas veronii 16-6A (DSM16273), Pseudomonas sp. strain MG61 (DSM16272), harbor a chlorocatechol 2,3-dioxygenase (CbzE). The cbzE-like genes were cloned, sequenced, and expressed from the isolates and a mixed culture. The chlorocatechol 2,3-dioxygenases shared 97% identical amino acids with CbzE from strain GJ31, forming a distinct family of catechol 2,3-dioxygenases. The chlorocatechol 2,3-dioxygenase, purified from chlorobenzene-grown cells of strain SK1, showed an identical N-terminal sequence with the amino acid sequence deduced from cloned cbzE. In all investigated chlorobenzene-degrading strains, cbzT-like genes encoding ferredoxins are located upstream of cbzE. The sequence data indicate that the ferredoxins are identical (one amino acid difference in CbzT of strain 16-6A compared to the others). In addition, the structure of the operon downstream of cbzE is identical in strains GJ31, 16-6A, and SK1 with genes cbzX (unknown function) and the known part of cbzG (2-hydroxymuconic semialdehyde dehydrogenase) and share 100% nucleotide sequence identity with the entire downstream region. The current study suggests that meta-cleavage of 3-chlorocatechol is not an atypical pathway for the degradation of chlorobenzene.This publication is dedicated to the memory of Olga V. Maltseva, who contributed greatly to our current knowledge of biochemistry of degradative pathways for chloroaromatic compounds.This publication is dedicated to Prof. Dr. Hans G. Schlegel in honor of his 80th birthday.     

Degradation and dehalogenation of monochlorophenols by the phenol-assimilating yeast Candida maltosa

The phenol-assimilating yeast Candida maltosa is able to degrade monochlorophenols but cannot grow on these substrates. 3- and 4-chlorophenol were broken down very rapidly by phenol-grown cells under the formation of 4-chlorocatechol, 5-chloropyrogallol and 4-carboxymethylenebut-2-en-4-olide with concomitant release of chloride.2-Chlorophenol was partially converted into cis,cis-2-chloromuconic acid via 3-chlorocatechol which was also obtained from 3-chlorophenol in low amounts. No further metabolites containing chloride were found.The dehalogenation step in the chlorophenol degradation is the cycloisomerization of the cis,cis-chloromuconic acid to 4-carboxymethylenebut-2-en-4-olide in the ortho fission pathway.Dedicated to prof.Dr. E. Bayer, Tübingen, on the occasion of his 65th birthday.     

Nuclear Magnetic Resonance Spectroscopic Studies on the Microbial Degradation of Mononitrophenol Isomers

The biochemical pathways followed by a mixed bacterial culture and one of its constituent strains, Sarcina maxima, MTCC 5216 (hitherto unreported) during the degradation of mononitrophenol isomers was studied using extensive nuclear magnetic resonance (NMR) spectroscopy (One- and Two-Dimensional Heteronuclear Multiple Quantum Coherence Transfer-2D HMQCT NMR). NMR investigations revealed that o-nitrophenol (ONP) could be degraded by the consortium to metabolites such as catechol, cis, cis-muconic acid, γ-hydroxymuconic semialdehyde, maleylacetate and β-ketoadipate. The spectra of ONP reaction mixture degraded by S.␣maxima showed that formation of maleylacetate from γ-hydroxymuconic semialdehyde should go through a new metabolite γ-hydroxymaleylacetate, hitherto unreported. The consortium could breakdown m-nitrophenol (MNP) to 4-aminocatechol indicating that it came from 3-hydroxyaminophenol. However, S. maxima MTCC 5216, could convert MNP to hitherto unreported 2-nitrohydroquinone and the subsequent 2-hydroxylaminohydroquinone to 1,2,4-benzenetriol along with γ-hydroxymuconic semialdehyde, muconolactone and maleylacetate. The pathway followed by the consortium during p-nitrophenol (PNP) degradation was by the formation of 4-nitrocatechol, maleylacetate and β-ketoadipate. PNP reaction mixture of S.␣maxima, MTCC 5216 on the other hand, showed that the pathway could proceed through the formation of p-hydroquinone as the initial metabolite. The present study conclusively established the nitrophenol-degrading ability of both the consortium and S. maxima MTCC 5216, including exhibiting slight deviations from the pathways followed by the other reported microorganisms.     

Metabolism of 4-chlorophenol by Azotobacter sp. GP1: Structure of the meta cleavage product of 4-chlorocatechol

Abstract A mutant strain of Azobacter sp. GP1 converted 4-chlorphenol to 4-chlorocatechol under cometabolic conditions. Under the same conditions the wild-type strain accumulated yellow compound, which by chemical and spectroscopic methods was identified as 5-chloro-2-hydroxy-6-oxohexadienoic acid (5-chloro-2-hydroxy-muconic semialdehyde). The structure of this compound indicates a meta -proximal cleavage of 4-chlorocatechol.     

Transformation and mineralization of halophenols by Penicillium simplicissimum SK9117

The metabolism of monohalophenols by Penicillium simplicissimum SK9117, isolated from a sewage plant was investigated. In submerged cultures, 3-, 4-chlorophenol, and 4-bromophenol were metabolized in the presence of phenol. 3-Chlorophenol was transformed to chlorohydroquinone, 4-chlorocatechol, 4-chloro-1,2,3-trihydroxybenzene, and 5-chloro-1,2,3-trihydroxybenzene. With 4-chlorophenol only 4-chlorocatechol was observed as transient product. A release of chloride ions was not observed. Whereas monobromo-, and monochlorophenols could not support growth as sole carbon and energy source, growth and release of fluoride ions were observed with monofluorophenols as substrates. In presence of phenol, the degradation of all monofluorophenols was enhanced. Substrate and cosubstrate disappeared simultaneously. 3-Fluorophenol and 4-fluorophenol were completely mineralized as shown by the equimolar release of fluoride ions.     

Substrate-dependent autoaggregation of <Emphasis Type="Italic">Pseudomonas putida</Emphasis> CP1 during the degradation of mono-chlorophenols and phenol

A bacterium, CP1, identified as Pseudomonas putida strain, was investigated for its ability to grow on and degrade mono-chlorophenols and phenols as sole carbon sources in aerobic shaking batch culture. The organism degraded up to 1.56 mM 2- and 3-chlorophenol, 2.34 mM 4-chlorophenol and 8.5 mM phenol using an ortho-cleavage pathway. P. putida CP1, acclimated to degrade 2-chlorophenol, was capable of 3-chlorocatechol degradation, while P. putida, acclimated to 4-chlorophenol degradation, degraded 4-chlorocatechol. Growth of P. putida CP1 on higher concentrations of the mono-chlorophenols, ≥1.56 mM 4-chlorophenol and ≥0.78 mM 2- and 3-chlorophenol, resulted in decreases in cell biomass despite metabolism of the substrates, and the formation of large aggregates of cells in the culture medium. Increases in cell biomass with no clumping of the cells resulted from growth of P. putida CP1 on phenol or on lower concentrations of mono-chlorophenol. Bacterial adherence to hydrocarbons (BATH) assays showed cells grown on the higher concentrations of mono-chlorophenol to be more hydrophobic than those grown on phenol and lower concentrations of mono-chlorophenol. The results suggested that increased hydrophobicity and autoaggregation of P. putida CP1 were a response to toxicity of the added substrates. Journal of Industrial Microbiology & Biotechnology (2002) 28, 316–324 DOI: 10.1038/sj/jim/7000249 Received 27 June 2001/ Accepted in revised form 09 February 2002     

Microbial metabolism of chlorosalicylates: accelerated evolution by natural genetic exchange

Methylsalicylate-grown cells of Pseudomonas sp. WR 401 cometabolized 3-, 4- and 5-substituted halosalicylates to the corresponding halocatechols. Further degradation was unproductive due to the presence of high levels of catechol 2,3-dioxygenase. This strain acquired the ability to utilize 3-chlorobenzoate following acquisition of genes from Pseudomonas sp. B 13 which are necessary for the assimilation of chlorocatechols. This derivative (WR 4011) was unable to use 4- or 5-chlorosalicylates. Derivatives able to use these compounds were obtained by plating WR 4011 on 5-chlorosalicylate minimal medium; one such derivative was designated WR 4016. The acquisition of this property was accompanied by concomitant loss of the methylsalicylate phenotype. During growth on 4- or 5-chlorosalicylate the typical enzymes of chlorocatechol assimilation were detected in cell free extracts, whereas catechol 2,3-dioxygenase activity was not induced. Repeated subcultivation of WR 4016 in the presence of 3-chlorosalicylate produced variants (WR 4016-1) which grew on all three isomers.Abbreviations CS chlorosalicylate - MS methylsalicylate - 3CB 3-chlorobenzoate - nal^r nalidixin-resistant - str^r streptomycin-resistant - C230 catechol-2,3-dioxygenase - C120 catechol-1,2-dioxygenase - HMSH 2-hydroxymuconic semialdehyde hydrolase or 2-hydroxy-6-oxo-hexa-2,4-dienoic acid-hydrolase - HMSD 2-hydroxymuconic semialdehyde dehydrogenase - Dienlacton hydrolase 4-carboxymethylenebut-2-en-4-olide hydrolase     

Cloning and nucleotide sequence analysis of xylE gene responsible for meta-cleavage of 4-chlorocatechol from Pseudomonas sp. S-47

Pseudomonas sp. S-47 expresses catechol 2,3-dioxygenase (C230) catalyzing the conversion of 4-chlorocatechol (4CC) as well as catechol to 5-chloro-2-hydroxymuconic semialdehyde and 2-hydroxymuconic semialdehyde, respectively, through meta-ring cleavage. The xylE gene encoding C230 for meta-cleavage was cloned from strain S-47 and its nucleotide sequence was analyzed. The pRES101 containing the xylE gene exhibited high C230 activity toward catechol and 4CC without altering the substrate specificity from natural strain. The xylE gene was composed of 924 bp and encoded polypeptide of molecular mass 35 kDa containing 307 amino acids. A deduced amino acid sequence of the C230 from strain S-47 exhibited over 80% identity with those of Pseudomonas putida mt-2, Pseudomonas putida G7, and Pseudomonas sp. CF600. However, it shows below 45% identity with those of Pseudomonas cepacia LB400 and Pseudomonas sp. KKS102. The C230 of strain S-47 was conserved in the amino acids (His150, His214, Glu261) for metal binding ligands and those (His199, His242, and Tyr251) for catalytic sites. Therefore, Pseudomonas sp. S-47 can be explained as acting by degrading catechol as well as 4CC by xylE-encoding C230 which was fused by N domain of nahH and C domain of dmpB from other Pseudomonas strains.     

Molecular characterization of the alpha subunit of multicomponent phenol hydroxylase from 4-chlorophenol-degrading Pseudomonas sp. strain PT3

Multicomponent phenol hydroxylases (mPHs) are diiron enzymes that use molecular oxygen to hydroxylate a variety of phenolic compounds. The DNA sequence of the alpha subunit (large subunit) of mPH from 4-chlorophenol (4-CP)-degrading bacterial strain PT3 was determined. Strain PT3 was isolated from oil-contaminated soil samples adjacent to automobile workshops and oil stations after enrichment and establishment of a chlorophenol-degrading consortium. Strain PT3 was identified as a member of Pseudomonas sp. based on sequence analysis of the 16S rRNA gene fragment. The 4-CP catabolic pathway by strain PT3 was tentatively proposed to proceed via a meta-cleavage pathway after hydroxylation to the corresponding chlorocatechol. This hypothesis was supported by polymerase chain reaction (PCR) detection of the LmPH encoding sequence and UV/VIS spectrophotometric analysis of the culture filtrate showing accumulation of 5-chloro-2-hydroxymuconic semialdehyde (5-CHMS) with λ_max 380. The detection of catabolic genes involved in 4-CP degradation by PCR showed the presence of both mPH and catechol 2,3-dioxygenase (C23DO). Nucleotide sequence analysis of the alpha subunit of mPH from strain PT3 revealed specific phylogenetic grouping to known mPH. The metal coordination encoding regions from strain PT3 were found to be conserved with those from the homologous dinuclear oxo-iron bacterial monooxygenases. Two DE(D)XRH motifs was detected in LmPH of strain PT3 within an approximate 100 amino acid interval, a typical arrangement characteristic of most known PHs.     

Oxidative Pathway for the Biodegradation of Nitrobenzene by Comamonas sp. Strain JS765

Previous studies have shown that the biodegradation of nitrobenzene by Pseudomonas pseudoalcaligenes JS45 proceeds by the reduction of nitrobenzene through nitrosobenzene and hydroxylaminobenzene, followed by rearrangement to 2-aminophenol, which then undergoes meta ring cleavage. We report here the isolation of a Comamonas sp. that uses an oxidative pathway for the complete mineralization of nitrobenzene. The isolate, designated strain JS765, uses nitrobenzene as a sole source of carbon, nitrogen, and energy. Nitrobenzene-grown cells oxidized nitrobenzene, with the stoichiometric release of nitrite. Extracts of nitrobenzene-grown JS765 showed high levels of catechol 2,3-dioxygenase activity that were not abolished by heating the cell extracts to 60(deg)C for 10 min. The ring cleavage product had an absorbance maximum at 375 nm, consistent with that of 2-hydroxymuconic semialdehyde. Both NAD-dependent dehydrogenase and NAD-independent hydrolase activities towards 2-hydroxymuconic semialdehyde were induced in extracts of nitrobenzene-grown cells. Catechol accumulated in the reaction mixture when cells preincubated with 3-chlorocatechol were incubated with nitrobenzene. Conversion of nitrobenzene to catechol by induced cells in the presence of 3-chlorocatechol and (sup18)O(inf2) demonstrated the simultaneous incorporation of two atoms of oxygen, which indicated that the initial reaction was dioxygenation. The results indicate that the catabolic pathway involves an initial dioxygenase attack on nitrobenzene with the release of nitrite and formation of catechol, which is subsequently degraded by a meta cleavage pathway.