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.     

Catechol ring-cleavage in Pseudomonas cepacia: the simultaneous induction of ortho and meta pathways

This work demonstrates the ring-cleavage pathways of catechol on Pseudomonas cepacia ATCC 29351, formed upon its growth on salicylate and benzoate, each as a sole carbon source. When grown on salicylate, P. cepacia induces only the catechol ortho pathway by its induction of catechol 1,2-dioxygenase. However, interestingly, benzoate-grown cells induce the ortho and meta pathways for the biodegradation of catechol, by inducing simultaneously catechol 1,2-dioxygenase and 2,3-dioxygenase, respectively, in the ratio of 7:1. The results indicate that P. cepacia ATCC 29351 possesses the genetic capacity for enzymes of both the ortho- and meta-cleavage pathways of benzoate degradation, although the phenotypic expression for the ortho pathway is higher. The simultaneous induction of catechol 1,2- and 2,3-dioxygenase is not detected in salicylate degradation. Although catechol is the metabolic intermediate for both salicylate and benzoate, catechol did not induce either pathway when used as a sole carbon source.     

Simultaneous Degradation of Atrazine and Phenol by Pseudomonas sp. Strain ADP: Effects of Toxicity and Adaptation

The strain Pseudomonas sp. strain ADP is able to degrade atrazine as a sole nitrogen source and therefore needs a single source for both carbon and energy for growth. In addition to the typical C source for Pseudomonas, Na₂-succinate, the strain can also grow with phenol as a carbon source. Phenol is oxidized to catechol by a multicomponent phenol hydroxylase. Catechol is degraded via the ortho pathway using catechol 1,2-dioxygenase. It was possible to stimulate the strain in order to degrade very high concentrations of phenol (1,000 mg/liter) and atrazine (150 mg/liter) simultaneously. With cyanuric acid, the major intermediate of atrazine degradation, as an N source, both the growth rate and the phenol degradation rate were similar to those measured with ammonia as an N source. With atrazine as an N source, the growth rate and the phenol degradation rate were reduced to ~35% of those obtained for cyanuric acid. This presents clear evidence that although the first three enzymes of the atrazine degradation pathway are constitutively present, either these enzymes or the uptake of atrazine is the bottleneck that diminishes the growth rate of Pseudomonas sp. strain ADP with atrazine as an N source. Whereas atrazine and cyanuric acid showed no significant toxic effect on the cells, phenol reduces growth and activates or induces typical membrane-adaptive responses known for the genus Pseudomonas. Therefore Pseudomonas sp. strain ADP is an ideal bacterium for the investigation of the regulatory interactions among several catabolic genes and stress response mechanisms during the simultaneous degradation of toxic phenolic compounds and a xenobiotic N source such as atrazine.     

Salicylate degradation by <Emphasis Type="Italic">Pseudomonas putida</Emphasis> strains not involving the “Classical” <Emphasis Type="Italic">nah2</Emphasis> operon

Genetic systems for salicylate catabolism were analyzed in 12 strains of Pseudomonas putida, isolated from polluted soil samples collected in the Murmansk and Tula oblasts. All of the studied P. putida strains utilize salicylate in the ortho-pathway of catechol cleavage without employing the enzymes of the “classical” nah2 operon. The data demonstrates that salicylate degradation in the studied strains is performed with the involvement of the salicylate hydroxylase gene analogous to the nahU gene of strain P. putida ND6. New variants of salicylate hydroxylase genes nahG1 and nahU were found.     

Metabolism of naphthalene, 2-methylnaphthalene, salicylate, and benzoate by Pseudomonas PG: regulation of tangential pathways.

Naphthalene is metabolized by Pseudomonas PG through 1,2-dihydroxynaphthalene and salicylate to catechol, which is then degraded by the meta pathway. 2-Methylnaphthalene, but not 1-methylnaphthalene, also serves as a growth substrate and is metabolized by the same route, through 4-methylcatechol. The same nonspecific meta pathway enzymes appear to be induced by growth on either naphthalene or 2-methylnaphthalene. The level to which 2-hydroxymuconic semialdehyde hydrolase is induced is low and probably of no metabolic significance. Growth on salicylate or catechol, both intermediates of naphthalene degradation, or benzoate results in induction of the ortho pathway, the alternative route for catechol dissimilation. No induction of 1,2-dihydroxynaphthalene oxygenase was found in salicylate-grown cells. Anaerobic growth on a succinate-nitrate medium in the presence of various inducers indicates that cis, cis-muconate, or one of its metabolites is the inducer of the ortho pathway enzymes. The inducer or inducers of the early enzymes of naphthalene degradation and of the meta pathway enzymes must be an early intermediate of the naphthalene pathway above salicylate.     

Phenol degradation by <Emphasis Type="Italic">Rhodococcus opacus</Emphasis> strain 1G

During cultivation in a liquid medium, the bacterium Rhodococcus opacus 1G was capable of growing on phenol at a concentration of up to 0.75 g/l. Immobilization of Rhodococcus opacus 1G had a positive effect on cell growth in the presence of phenol at high concentrations. The substrate at concentrations of 1.0 and 1.5 g/l was completely utilized over 24 and 48 h, respectively. The key enzymes of phenol degradation (two catechol 1,2-dioxygenases and muconate cycloisomerase) were isolated. One of the dioxygenases was very unstable. By substrate specificity, another enzyme belonged to catechol 1,2-dioxygenases of the classical ortho-pathway. Chlorocatechols and chlorophenols served as competitive inhibitors of catechol 1,2-dioxygenases. The inhibitory effect of other aromatic compounds was less significant. Our results suggest that this strain holds promise for bioremediation of phenol wastewater.     

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.     

Isolation and Characterization of Phenol-Degrading Soil Bacterium Xanthobacter flavus

A soil bacterium isolated from a contaminated site degraded phenol when provided as the sole carbon and energy source in the medium. The bacterium was identified as Xanthobacter flavus MTCC 9130. This microbial strain was able to tolerate phenol up to 1000 mg L^?1 concentration. The lag phase increased with the increase in phenol concentration. The optimum growth temperature was 37°C. The organism efficiently utilized phenol and could degrade it completely within 120 h when initial concentration was less than 600 mg L^?1. Degradation of phenol was through ortho pathway, enzyme assay through cell-free extract exhibited the presence of catechol 1,2-dioxygenase. The specific activity was 0.146 μ mol min^?1 mg^?1 protein. However, higher concentrations of phenol in the medium had a negative effect on the growth of the bacterium. Hence this ability of Xanthobacter flavus can be effectively used for bioremediation studies of phenol-contaminated sites.     

Utilization of the Plant Hormone Indole-3-Acetic Acid for Growth by Pseudomonas putida Strain 1290

We have isolated from plant surfaces several bacteria with the ability to catabolize indole-3-acetic acid (IAA). One of them, isolate 1290, was able to utilize IAA as a sole source of carbon, nitrogen, and energy. The strain was identified by its 16S rRNA sequence as Pseudomonas putida. Activity of the enzyme catechol 1,2-dioxygenase was induced during growth on IAA, suggesting that catechol is an intermediate of the IAA catabolic pathway. This was in agreement with the observation that the oxygen uptake by IAA-grown P. putida 1290 cells was elevated in response to the addition of catechol. The inability of a catR mutant of P. putida 1290 to grow at the expense of IAA also suggests a central role for catechol as an intermediate in IAA metabolism. Besides being able to destroy IAA, strain 1290 was also capable of producing IAA in media supplemented with tryptophan. In root elongation assays, P. putida strain 1290 completely abolished the inhibitory effect of exogenous IAA on the elongation of radish roots. In fact, coinoculation of roots with P. putida 1290 and 1 mM concentration of IAA had a positive effect on root development. In coinoculation experiments on radish roots, strain 1290 was only partially able to alleviate the inhibitory effect of bacteria that in culture overproduce IAA. Our findings imply a biological role for strain 1290 as a sink or recycler of IAA in its association with plants and plant-associated bacteria.     

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).     

Cloning of Catechol 2,3-Dioxygenase Gene and Construction of a Stable Genetically Engineered Strain for Degrading Crude Oil

Pseudomonas putida strain BNF1 was isolated to degrade aromatic hydrocarbons efficiently and use phenol as a main carbon and energy source to support its growth. Catechol 2,3-dioxygenase was found to be the responsible key enzyme for the biodegradation of aromatic hydrocarbons. Catechol 2,3-dioxygenase gene was cloned from plasmid DNA of P. putida strain BNF1. The nucleotide base sequence of a 924 bp segment encoding the catechol 2,3-dioxygenase (C23O) was determined. This segment showed an open reading frame, which encoded a polypeptide of 307 amino acids. C23O gene was inserted into NotI-cut transposon vector pUT/mini-Tn5 (Km^r) to get a novel transposon vector pUT/mini-Tn5-C23O. With the helper plasmid PRK2013, the transposon vector pUT/mini-Tn5-C23O was introduced into one alkanes degrading strain Acinetobacter sp. BS3 by triparental conjugation, and then the C23O gene was integrated into the chromosome of Acinetobacter sp. BS3. And the recombinant BS3-C23O, which could express catechol 2,3-dioxygenase protein, was obtained. The recombinant BS3-C23O was able to degrade various aromatic hydrocarbons and n-alkanes. Broad substrate specificity, high enzyme activity, and the favorable stability suggest that the BS3-C23O was a potential candidate used for the biodegradation of crude oil.     

Aerobic batch degradation of phenol using immobilized Pseudomonas putida

Alginate concentrations between 2 and 4% had little effect on the degradation rate of phenol by alginate-immobilized Pseudomonas putida. Ten-degree shifts from 25°C resulted in approximately 30% slower degradation. Maximal degradation rates were favored at pH 5.5–6.0. The response of degradation rate to increased air flow in the bubble column used was almost linear and an optimal higher than 16 vol vol⁻¹ was indicated, although free cells appeared in the reaction medium above 12 vol vol⁻¹. When the initial phenol concentration was raised, degradation rate was not significantly affected until levels higher than 1200 mg ml⁻¹ where performance was markedly reduced. Increasing the ratio of total bead volume to medium volume gave progressively smaller increases in degradation rate. At a medium volume to total bead volume ratio of 5:1, the maximum degradation rate was 250 mg L⁻¹ h⁻¹. Received 24 November 1998/ Accepted in revised form 27 January 1999     

Novel metabolic pathway for salicylate biodegradation via phenol in yeast <Emphasis Type="Italic">Trichosporon moniliiforme</Emphasis>

A novel metabolic pathway was found in the yeast Trichosporon moniliiforme WU-0401 for salicylate degradation via phenol as the key intermediate. When 20 mM salicylate was used as the sole carbon source for the growth of strain WU-0401, phenol was detected as a distinct metabolite in the culture broth. Analysis of the products derived from salicylate or phenol through reactions with resting cells and a cell-free extract of strain WU-0401 indicated that salicylate is initially decarboxylated to phenol and then oxidized to catechol, followed by aromatic ring cleavage to form cis-cis muconate.     

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.     

Molecular cloning of genenahH encoding extradiol-type dioxygenase from the NAH plasmid ofPseudomonas stutzeri NA1

Naphthalene-degradingPseudomonas stutzeri NA1 was found to harbour the NAH plasmid, which contains the classical upper and lower catabolic genes required for naphthalene mineralization. The lower pathway inP. stutzeri NA1 was found to proceedviameta-ring cleavage of catechol due to the presence of thenahH gene encoding extradiol catechol 2,3-dioxygenase. Naphthalene-induced cells were able to mineralise both salicylate and catechol. Absorption spectra and gas chromatography/mass spectrometry analysis ofritermediate metabolites of salicylate or catechol degradation by a crude extract ofP. stutzeri NA1 revealed the presence of themeta-ring cleavage product 2-hydroxymuconate semialdehyde as a major constituent. The extradiol ring cleavage genenahH was amplified successfully from the NAH plasmid ofP. stutzeri NA1 with catechol 2,3-dioxygenase-specific primers and cloned inEscherichia coli JM109 The complete nucleotide sequence of cloned PCR fragment was determined. Sequence analysis of cloned PCR fragment revealed an open reading frame with similarity to other extradiol dioxygenases. The deduced amino acid sequence ofnahH fromP. stutzeri NA1 showed 96% sequence identity with the catechol 2,3-dioxygenase gene fromPseudomonas putida strain H. However, when compared to othernahH genes from different pseudomonads, it was in a separate phylogenetic branch, indicating a degree of speciation among the extradiol dioxygenase family.     

Biodegradation of phenol by a filamentous fungi isolated from industrial effluents—identification and degradation potential

Thirty filamentous fungal strains were isolated from effluents of a stainless steel industry (Minas Gerais, Brazil) and tested for phenol tolerance. Fifteen strains of the genera Fusarium sp., Aspergillus sp., Penicillium sp. and Graphium sp. tolerants up to 10 mM of phenol were selected and tested for their ability to degrade phenol. Phenol degradation was a function of strain, time of incubation and initial phenol concentration. FIB4, LEA5 and AE2 strains of Graphium sp. and FE11 of Fusarium sp. presented the highest percentage phenol degradation, with 75% degradation of 10 mM phenol in 168 h for FIB4. A higher starting cell density of Graphium sp. FIB4 lead to a decrease in the time needed for full phenol degradation and increased the phenol degradation rate. All strains exhibited activity of catechol 1,2-dioxygenase and phenol hydroxylase in free cell extracts obtained from cells grown on phenol, suggesting that catechol was oxidized by the ortho type of ring fission. These data reported demonstrate the prospect after the application of filamentous fungal strains in protecting the environment from phenol pollution.     

Degradation of polycyclic aromatic hydrocarbons by a strain of Pseudomonas fluorescens 16N2

The growth of Pseudomonas fluorescens 16N2 on naphthalene was accompanied with accumulation of salicylate in the culture medium and induction of gentisate 1,2-dioxygenase and catechol 1,2-dioxygenase. The transformation of anthracene by the cells growing on hexadecane led to the formation of 3-hydroxy-2-naphthoate and salicylate. Pathways for naphthalene and anthracene degradation are proposed.     

Mathematical modeling of phenol degradation system using fuzzy comprehensive evaluation

New mathematical model for phenol degradation is developed that uses fuzzy comprehensive evaluation. Biodegradation of phenol by Pseudomonas putida (NICM 2174), a potential biodegradent of phenol has been investigated for its degrading potential under different conditions. In the present work, results of batch study on P. putida (NICM 2174) and its degradation activity on phenolic compounds such as phenol, o-cresol, p-cresol, p-nitrophenol and resorcinol each of concentration 0.300 g/l are considered. In the present study, the effect of glucose, yeast extract, ammonium sulphate and NaCl each at 0.5, 1.5, 2.0, 3.0 and 4 g/l on degradation of aforementioned phenolic compounds have been investigated and a fuzzy control model has been developed to predict the extent of degradation. Main aspect of this study is to establish a fuzzy relation matrix R for objective evaluation of phenol degradation. A series of membership functions for the degradation are being evaluated after investigating the growth properties of bacteria at various levels of carbon and nitrogen sources. Important element is the factor vector A, which is deduced from a survey of panel of judges (n=25). A in conjunction with R generates a multifactorial equation which can be used to calculate the extent of phenol degradation. Biomass growth contributed significantly to phenol degradation rates especially when the degradation medium was supplemented with a utilizable carbon and nitrogen sources.