Tetrameric structure and cellular location of catechol 2,3-dioxygenase

Catechol 2,3-dioxygenase from the meta-cleavage pathway encoded on the TOL plasmid of Pseudomonas putida (pWWO) was investigated by electron microscopy. Negatively stained samples of the purified catechol 2,3-dioxygenase revealed that the enzyme consists of four subunits arranged in a tetrahedral conformation. Monoclonal antibodies raised against catechol 2,3-dioxygenase showed highly specific reactions and were used to localize the enzyme in Escherichia coli (pAW31) and P. putida (pWWO), using the protein A-gold technique carried out as a post-embedding immunoelectron microscopy procedure. Our in situ labeling studies revealed a cytoplasmic location of the catechol 2,3-dioxygenase in both cell types.Abbreviations C23O Catechol 2,3-dioxygenase - 3MB 3 Methylbenzoate - AK1 Anti-C23O-IgG-antibody - G Gold particle     

Bacterial metabolism of side chain fluorinated aromatics: cometabolism of 4-trifluoromethyl(TFM)-benzoate by 4-isopropylbenzoate grown Pseudomonas putida JT strains

Enzymes of the p-cymene pathway in Pseudomonas putida strains cometabolized the intermediate analogue 4-trifluoromethyl(TFM)benzoate. Three products, 4-TFM-2,3-dihydro-2,3-dihydroxybenzoate, 4-TFM-2,3-dihydroxy-benzoate and 2-hydroxy-6-oxo-7,7,7-trifluorohepta-2,4-dienoate (7-TFHOD) were identified chemically and by spectroscopic proterties.Certain TFM-substituted analogue metabolites of the p-cymene pathway were transformed at drastically reduced rates.Hammett type analysis of ring cleavage reactions of 4-substituted 2,3-dihydroxybenzoates revealed the negative inductive and especially mesomeric effect of substituents to be rate determining. Whereas decarboxylation of 3-carboxy-7-TFHOD was not affected by fluorine substitution the subsequent hydrolysis of 7-TFHOD proceeded very slowly. The negative inductive effect of the TFM-group probably inhibited heterolysis of the carbon bond between C₅ and C₆ of 7-TFHOD.Abbreviations DHB 1,2-Dihydroxy-2-hydrobenzoate - DHC 2,3-Dihydro-2,3-dihydroxybenzoate, this compound was termed DHC simply to distinguish it from the similar 1,2-dihydroxy-2-hydrobenzoate (DHB) as described in the preceeding paper (Engesser et al. 1988) - HMS 2-Hydroxymuconic semialdehyde - HOD 2-Hydroxy-6-oxohepta-2,4-dienoate - 7-TFHOD 2-Hydroxy-6-oxo-7,7,7-trifluorohepta-2,4-dienoate - TFM Trifluoromethyl This work was supported, in part, by the Gesellschaft für Strahlen- und Umweltforschung, Neuherberg/München, FRG     

Induction of ortho- and meta-cleavage pathways in Pseudomonas in biodegradation of high benzoate concentration: MS identification of catabolic enzymes

The degradation pathways of benzoate at high concentration in Pseudomonas putida P8 were directly elucidated through mass spectrometric identification of some key catabolic enzymes. Proteins from P. putida P8 grown on benzoate or succinate were separated using two-dimensional gel electrophoresis. For cells grown on benzoate, eight distinct proteins, which were absent in the reference gel patterns from succinate-grown cells, were found. All the eight proteins were identified by matrix-assisted laser desorption/ionization time-of-flight mass spectrometry as catabolic enzymes involved in benzoate degradation. Among them, CatB (EC5.5.1.1), PcaI (EC2.8.3.6), and PcaF (EC2.3.1.174) were the enzymes involved in the ortho-cleavage pathway; DmpC (EC1.2.1.32), DmpD (EC3.1.1.-), DmpE (EC4.2.1.80), DmpF (EC1.2.1.10), and DmpG (EC4.1.3.-) were the meta-cleavage pathway enzymes. In addition, enzyme activity assays showed that the activities of both catechol 1,2-dioxygenase (C12D; EC1.13.11.1) and catechol 2,3-dioxygenase (C23D; EC1.13.11.2) were detected in benzoate-grown P. putida cells, undoubtedly suggesting the simultaneous expression of both the ortho- and the meta-cleavage pathways in P. putida P8 during the biodegradation of benzoate at high concentration.     

Horizontal transfer of catabolic plasmids in the process of naphthalene biodegradation in model soil systems

The process of naphthalene degradation by indigenous, introduced, and transconjugant strains was studied in laboratory soil microcosms. Conjugation transfer of catabolic plasmids was demonstrated in naphthalene-contaminated soil. Both indigenous microorganisms and an introduced laboratory strain BS394 (pNF142::TnMod-OTc) served as donors of these plasmids. The indigenous bacterial degraders of naphthalene isolated from soil were identified as Pseudomonas putida and Pseudomonas fluorescens. The frequency of plasmid transfer in soil was 10^?5–10^?4 per donor cell. The activity of the key enzymes of naphthalene biodegradation in indigenous and transconjugant strains was studied. Transconjugant strains harboring indigenous catabolic plasmids possessed high salicylate hydroxylase and low catechol-2,3-dioxygenase activities, in contrast to indigenous degraders, which had a high level of catechol-2,3-dioxygenase activity and a low level of salicylate hydroxylase. Naphthalene degradation in batch culture in liquid mineral medium was shown to accelerate due to cooperation of the indigenous naphthalene degrader P. fluorescens AP1 and the transconjugant strain P. putida KT2442 harboring the indigenous catabolic plasmid pAP35. The role of conjugative transfer of naphthalene biodegradation plasmids in acceleration of naphthalene degradation was demonstrated in laboratory soil microcosms.     

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     

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.     

The meta cleavage operon of TOL degradative plasmid pWWO comprises 13 genes

Summary The meta-cleavage operon of TOL plasmid pWWO of Pseudomonas putida encodes a set of enzymes which transform benzoate/toluates to Krebs cycle intermediates via extradiol (meta-) cleavage of (methyl)catechol. The genetic organization of the operon was characterized by cloning of the meta-cleavage genes into an expression vector and identification of their products in Escherichia coli maxicells. This analysis showed that the meta-cleavage operon contains 13 genes whose order and products (in kilodaltons) are The xyIXYZ genes encode three subunits of toluate 1,2-dioxygenase. The xylL, xyIE, xyIG, xylF, xylJ, xylK, xylI and xylH genes encode 1,2-dihydroxy-3,5-cyclohexadiene-1-carboxylate dehydrogenase, catechol 2,3-dioxygenase, 2-hydroxymuconic semialdehyde dehydrogenase, 2-hydroxymuconic semialdehyde hydrolase, 2-oxopent-4-enoate hydratase, 4-hydroxy-2-oxovalerate aldolase, 4-oxalocrotonate decarboxylase and 4-oxalocrotonate tautomerase, respectively. The functions of xyIT and xylQ are not known at present. The comparison of the coding capacity and the sizes of the products of the meta-cleavage operon genes indicated that most of the DNA between xyIX and xyIH consists of coding sequences.     

Enhancement ofcis,cis-muconate productivity by overexpression of catechol 1,2-dioxygenase inPseudomonas putida BCM114

For enhancement ofcis,cis-muconate productivity from benzoate, catechol 1,2-dioxygenase (C12O) which catalyzes the rate-limiting step (catechol conversion tocis,cis-muconate) was cloned and expressed in recombinantPseudomonas putida BCM114. At higher benzoate concentrations (more than 15 mM),cis,cis-muconate productivity gradually decreased and unconverted catechol was accumulated up to 10 mM in the case of wildtypeP. putida BM014, whereascis,cis-muconate productivity continuously increased and catechol was completely transformed tocis,cis-muconate forP. putida BCM114. Specific C12O activity ofP. putida BCM114 was about three times higher than that ofP. putida BM014, and productivity was enhanced more than two times.     

Oil biodegradation by Bacillus strains isolated from the rock of an oil reservoir located in a deep-water production basin in Brazil

Sixteen spore forming Gram-positive bacteria were isolated from the rock of an oil reservoir located in a deep-water production basin in Brazil. These strains were identified as belonging to the genus Bacillus using classical biochemical techniques and API 50CH kits, and their identity was confirmed by sequencing of part of the 16S rRNA gene. All strains were tested for oil degradation ability in microplates using Arabian Light and Marlin oils and only seven strains showed positive results in both kinds of oils. They were also able to grow in the presence of carbazole, n-hexadecane and polyalphaolefin (PAO), but not in toluene, as the only carbon sources. The production of key enzymes involved with aromatic hydrocarbons biodegradation process by Bacillus strains (catechol 1,2-dioxygenase and catechol 2,3-dioxygenase) was verified spectrophotometrically by detection of cis,cis-muconic acid and 2-hydroxymuconic semialdehyde, and results indicated that the ortho ring cleavage pathway is preferential. Furthermore, polymerase chain reaction (PCR) products were obtained when the DNA of seven Bacillus strains were screened for the presence of catabolic genes encoding alkane monooxygenase, catechol 1,2-dioxygenase, and/or catechol 2,3-dioxygenase. This is the first study on Bacillus strains isolated from an oil reservoir in Brazil.     

Analysis of bacterial degradation pathways for long-chain alkylphenols involving phenol hydroxylase, alkylphenol monooxygenase and catechol dioxygenase genes

Eighteen 4-t-octylphenol-degrading bacteria were isolated and screened for the presence of degradative genes by polymerase chain reaction method using four designed primer sets. The primer sets were designed to amplify specific fragments from multicomponent phenol hydroxylase, single component monooxygenase, catechol 1,2-dioxygenase and catechol 2,3-dioxygenase genes. Seventeen of the 18 isolates exhibited the presence of a 232 bp amplicon that shared 61-92% identity to known multicomponent phenol hydroxylase gene sequences from short and/or medium-chain alkylphenol-degrading strains. Twelve of the 18 isolates were positive for a 324 bp region that exhibited 78-95% identity to the closest published catechol 1,2-dioxygenase gene sequences. The two strains, Pseudomonas putida TX2 and Pseudomonas sp. TX1, contained catechol 1,2-dioxygenase genes also have catechol 2,3-dioxygenase genes. Our result revealed that most of the isolated bacteria are able to degrade long-chain alkylphenols via multicomponent phenol hydroxylase and the ortho-cleavage pathway.     

Grouping of phenol hydroxylase and catechol 2,3-dioxygenase genes among phenol- and p-cresol-degrading Pseudomonas species and biotypes

Phenol- and p-cresol-degrading pseudomonads isolated from phenol-polluted water were analysed by the sequences of a large subunit of multicomponent phenol hydroxylase (LmPH) and catechol 2,3-dioxygenase (C23O), as well as according to the structure of the plasmid-borne pheBA operon encoding catechol 1,2-dioxygenase and single component phenol hydoxylase. Comparison of the carA gene sequences (encodes the small subunit of carbamoylphosphate synthase) between the strains showed species- and biotype-specific phylogenetic grouping. LmPHs and C23Os clustered similarly in P. fluorescens biotype B, whereas in P. mendocina strains strong genetic heterogeneity became evident. P. fluorescens strains from biotypes C and F were shown to possess the pheBA operon, which was also detected in the majority of P. putida biotype B strains which use the ortho pathway for phenol degradation. Six strains forming a separate LmPH cluster were described as the first pseudomonads possessing the Mop type LmPHs. Two strains of this cluster possessed the genes for both single and multicomponent PHs, and two had genetic rearrangements in the pheBA operon leading to the deletion of the pheA gene. Our data suggest that few central routes for the degradation of phenolic compounds may emerge in bacteria as a result of the combination of genetically diverse catabolic genes.     

Genetic analysis of a relaxed substrate specificity aromatic ring dioxygenase, toluate 1,2-dioxygenase, encoded by TOL plasmid pWW0 of Pseudomonas putida

Summary Toluate 1,2-dioxygenase is the first enzyme of a meta-cleavage pathway for the oxidative catabolism of benzoate and substituted benzoates to Krebs cycle intermediates that is specified by TOL plasmid pWW0 of Pseudomonas putida. A collection of derivatives harbouring Tn1000 insertions and defective in toluate dioxygenase have been isolated from pPL392, a pBR322-based hybrid plasmid carrying the TOL plasmid meta-cleavage pathway operon. In parallel, a series of N-methyl-N-nitro-N-nitrosoguanidine-induced mutant plasmids defective in this enzyme activity were isolated from pNM72, a pKT231-based hybrid plasmid carrying the same operon. Pairs of mutant plasmids, consisting of one Tn1000 derivative and one nitrosoguanidine-induced derivative, were used for complementation analysis of toluate dioxygenase in Escherichia coli recA bacteria, in which the formation of 2-hydroxymuconic semialdehyde from benzoate was examined. Four cistrons for toluate 1,2-dioxygenase were thus identified. DNA fragments containing nitrosoguanidine-induced mutant cistrons plus the other meta-cleavage operon genes were cloned into pOT5, an R388-based vector, and complementation tests between different nitrosoguanidine-induced mutant cistrons were carried out in Pseudomonas putida cells, this time scoring for growth on p-toluate. This analysis also identified four cistrons. Examination of the products of these cistrons, by means of E. coli minicells containing pPL392 or its Tn1000 insertion derivatives, indicated that the first two cistrons of the operon comprise a single gene, xylX, which encodes a 57 kilodalton protein, and that the third cistron, xy/Y, encodes a 20 kilodalton protein.     

Biotransformation of anisole and phenetole by aerobic hydrocarbonoxidizing bacteria

Wild type, mutant, and recombinant bacterial strains capable of oxidizing aromatic hydrocarbons were screened for their ability to oxidize anisole (methoxybenzene) and phenetole (ethoxybenzene). Toluene-induced cells ofPseudomonas putida F39/D transformed anisole to a compound tentatively identified ascis-1,2-dihydroxy-3-methoxyclohexa-3,5-diene (anisole-2,3-dihydrodiol), 2-methoxyphenol, catechol, and trace amounts of phenol while phenetole was converted primarily tocis-1,2-dihydroxy-3-ethoxycyclohexa-3,5-diene (phenetole-2,3-dihydrodiol) and 2-ethoxyphenol. Induced cells ofPseudomonas sp. NCIB 9816/11 andBeijerinckia sp. B8/36 transformed anisole to phenol, and phenetole to phenol and ethenyloxybenzene. Toluene-induced cells ofP. putida BG1 converted anisole to phenol but did not oxidize phenetole. In contrast, toluene-induced cells ofP. mendocina KR1, which oxidize toluene via monooxygenation at thepara position, transformed anisole to 4-methoxyphenol, and phenetole to 2-, 3- and 4-ethoxyphenol. The involvement of toluene and naphthalene dioxygenases in the reactions catalyzed by strains F39/D and NCIB 9816/11, respectively, was confirmed with recombinantE. coli strains expressing the cloned dioxygenase genes. The results show that the oxygenases from differentPseudomonas strains oxidize anisole and phenetole to different hydroxylated products.     

Competition of plasmid-bearing Pseudomonas putida strains catabolizing naphthalene via various pathways in chemostat culture

Plasmid-carrying Pseudomonas putida strains degrade naphthalene through different biochemical pathways. The influence of various combinations of host bacteria and plasmids on growth characteristics and competitiveness of P. putida strains was studied in chemostat culture at a low dilution rate (D=0.05 h⁻¹) with naphthalene as the sole source of carbon and energy. Under naphthalene limitation, the plasmid-bearing strains degrading naphthalene that use catechol 1,2-dioxygenase for catechol oxidation (ortho pathway), were the most competitive. The strains bearing plasmids that control naphthalene catabolism via catechol 2,3-dioxygenase (meta pathway), were less competitive. Under these conditions the strain carrying plasmid pBS4, which encodes for naphthalene catabolism via gentisic acid, was the least competitive. Received: 24 February 1997 / Received revision: 22 May 1997 / Accepted: 25 May 1997     

Biological degradation of 4-chlorobenzoic acid by a PCB-metabolizing bacterium through a pathway not involving (chloro)catechol

Cupriavidus sp. strain SK-3, previously isolated on polychlorinated biphenyl mixtures, was found to aerobically utilize a wide spectrum of substituted aromatic compounds including 4-fluoro-, 4-chloro- and 4-bromobenzoic acids as a sole carbon and energy source. Other chlorobenzoic acid (CBA) congeners such as 2-, 3-, 2,3-, 2,5-, 3,4- and 3,5-CBA were all rapidly transformed to respective chlorocatechols (CCs). Under aerobic conditions, strain SK-3 grew readily on 4-CBA to a maximum concentration of 5 mM above which growth became impaired and yielded no biomass. Growth lagged significantly at concentrations above 3 mM, however chloride elimination was stoichiometric and generally mirrored growth and substrate consumption in all incubations. Experiments with resting cells, cell-free extracts and analysis of metabolite pools suggest that 4-CBA was metabolized in a reaction exclusively involving an initial hydrolytic dehalogenation yielding 4-hydroxybenzoic acid, which was then hydroxylated to protocatechuic acid (PCA) and subsequently metabolized via the β-ketoadipate pathway. When strain SK-3 was grown on 4-CBA, there was gratuitous induction of the catechol-1,2-dioxygenase and gentisate-1,2-dioxygenase pathways, even if both were not involved in the metabolism of the acid. While activities of the modified ortho- and meta-cleavage pathways were not detectable in all extracts, activity of PCA-3,4-dioxygenase was over ten-times higher than those of catechol-1,2- and gentisate-1,2-dioxygenases. Therefore, the only reason other congeners were not utilized for growth was the accumulation of CCs, suggesting a narrow spectrum of the activity of enzymes downstream of benzoate-1,2-dioxygenase, which exhibited affinity for a number of substituted analogs, and that the metabolic bottlenecks are either CCs or catabolites of the modified ortho-cleavage metabolic route.     

The mechanism of action of hexahydro-1,3,5-triethyl-s-triazine

Summary The mechanism of antimicrobial action of hexahydro-1,3,5-triethyl-s-triazine (HHTT) was studied using the HHTT-resistant isolate,Pseudomonas putida 3-T-15², its HHTT-sensitive, novobiocin-cured derivative,P. putida 3-T-15² 11:21,P. putida ATCC 12633,Pseudomonas aeruginosa PA01 andEscherichia coli J53 (RP4). HHTT was oxidized byP. putida 3-T-15², while respiration ofP. putida 3-T-15² 11:21 was inhibited by HHTT. Chemical assays showed that HHTT released formaldehyde.P. putida 3-T-15² was highly resistant to formaldehyde, whileP. putida 3-T-15² 11:21 was highly sensitive to formaldehyde. Both HHTT and formaldehyde acted similarly to inhibit proline uptake in bacterial cells and to inhibit the synthesis of the inducible enzymes, -galactosidase and glucose-6-phosphate dehydrogenase. HHTT did not have uncoupler-like activity.P. putida 3-T-15² used either HHTT or ethylamine, a component of HHTT, as a nitrogen source for growth, but neither HHTT, ethylamine or formaldehyde served as a carbon and energy source for growth. We concluded that a major mechanism of antimicrobial action of HHTT was through its degradation product, formaldehyde.     

Conjugative transfer of preferential utilization of aromatic compounds from <Emphasis Type="Italic">Pseudomonas putida</Emphasis> CSV86

Pseudomonas putida CSV86 utilizes naphthalene (Nap), salicylate (Sal), benzyl alcohol (Balc), and methylnaphthalene (MN) preferentially over glucose. Methylnaphthalene is metabolized by ring-hydroxylation as well as side-chain hydroxylation pathway. Although the degradation property was found to be stable, the frequency of obtaining Nap⁻Sal⁻MN⁻Balc⁻ phenotype increased to 11% in the presence of curing agents. This property was transferred by conjugation to Stenotrophomonas maltophilia CSV89 with a frequency of 7 × 10⁻⁸ per donor cells. Transconjugants were Nap⁺Sal⁺MN⁺Balc⁺ and metabolized MN by ring- as well as side-chain hydroxylation pathway. Transconjugants also showed the preferential utilization of aromatic compounds over glucose indicating transfer of the preferential degradation property. The transferred properties were lost completely when transconjugants were grown on glucose or 2YT. Attempts to detect and isolate plasmid DNA from CSV86 and transconjugants were unsuccessful. Transfer of degradation genes and its subsequent loss from the transconjugants was confirmed by PCR using primers specific for 1,2-dihydroxynaphthalene dioxygenase and catechol 2,3-dioxygenase (C23O) as well as by DNA–DNA hybridizations using total DNA as template and C23O PCR fragment as a probe. These results indicate the involvement of a probable conjugative element in the: (i) metabolism of aromatic compounds, (ii) ring- and side-chain hydroxylation pathways for MN, and (iii) preferential utilization of aromatics over glucose.     

Catechol 1,2-dioxygenase from the new aromatic compounds - Degrading Pseudomonas putida strain N6

This study aimed to characterization of catechol 1,2-dioxygenase from a Gram-negative bacterium, being able to utilize a wide spectrum of aromatic substrates as a sole carbon and energy source. Strain designated as N6, was isolated from the activated sludge samples of a sewage treatment plant at Bentwood Furniture Factory Jasienica, Poland. Morphology, physio-biochemical characteristics and phylogenetic analysis based on 16S rDNA sequence indicate that strain belongs to Pseudomonas putida. When cells of strain N6 grown on protocatechuate or 4-hydroxybenzoic acid mainly protocatechuate 3,4-dioxygenase was induced. The activity of catechol 1,2-dioxygenase was rather small. The cells grown on benzoic acid, catechol or phenol showed high activity of only catechol 1,2-dioxygenase. This enzyme was optimally active at 35 °C and pH 7.4. Kinetic studies showed that the value of K_m and V_max was 85.19 ??M and 14.54 ??M min⁻¹ respectively. Nucleotide sequence of gene encoding catechol 1,2-dioxygenase in strain N6 has 100% identity with catA genes from two P. putida strains. The deduced 301-residue sequence of enzyme corresponds to a protein of molecular mass 33.1 kDa. The deduced molecular structure of the catechol 1,2-dioxygenase from P. putida N6 was very similar and characteristic for the other intradiol dioxygenases.     

Expression and homology modeling of 2′-aminobiphenyl-2,3-diol-1,2-dioxygenase from Pseudomonas stutzeri carbazole degradation pathway

The enzyme 2′-aminobiphenyl-2,3-diol-1,2-dioxygenase (CarB), encoded by two genes (carBa and carBb), is an α₂β₂ heterotetramer that presents meta-cleavage activity toward the hydroxylated aromatic ring in the carbazole degradation pathway from petroleum-degrader bacteria Pseudomonas spp. The 1082-base, pair polymerase chain reaction product corresponding to, carBaBb genes from Pseudomonas stutzeri ATCC 31258 was cloned by site-specific recombination and expressed in high levels in Escherichia coli BL21-SI with a histidine-tag and in native form. The CarB activity toward 2,3-dihydroxybiphenyl was similar for these two constructions. The α₂β₂ 3D model of CarB dioxygenase was proposed by homology modeling using the protocatechuate 4,5-dioxygenase (LigAB) structure as template. Accordingly, His12, His53, and Glu230 coordinate the Fe(II) in the catalytic site at the subunit CarBb. The model also indicates that His182 is the catalytic base responsible for deprotonating one of the hydroxyl group of the substrate by a hydrogen bond. The hydrophobic residues Trp257 and Phe258 in the CarB structure substituted the LigAB amino acid residues Ser269 and Asn270. These data could explain why the CarB was active for 2,3-dihydroxybiphenyl and not for protocatechuate.     

Dioxygenase activity and relative behaviour of Pseudomonas strains from soil in the presence of different aromatic compounds

Ten different Pseudomonas strains isolated from contaminated soils were tested for expression of active dioxygenases. Of these, two different clusters, related to strain origin were observed. The first included two P. fluorescens strains and two P. aeruginosa strains isolated from soils polluted with polyaromatic hydrocarbons and the second two P. cepacia strains and four P. chlororaphis strains from soils with polyphenols. All the isolates showed catechol 1,2-dioxygenase basal activity, while other dioxygenases (catechol 2,3-dioxygenase, protocatechuate 2,3-, 3,4- and 4,5-dioxygenases) were detected only after growth in the presence of suitable inducers (benzoate, catechol, salicylate, phenol). Significant induction of catechol 1,2-dioxygenase, the major activity of the tested strains, was also observed when combining starvation with the presence of high molecular weight aromatic hydrocarbons with recalcitrant structures (fluoranthene, chrysene, benzanthracene, pyrene).