Biodegradation of mixtures of substituted benzenes by Pseudomonas sp. strain JS150.

Pseudomonas sp. strain JS150 was isolated as a nonencapsulated variant of Pseudomonas sp. strain JS1 that contains the genes for the degradative pathways of a wide range of substituted aromatic compounds. Pseudomonas sp. strain JS150 grew on phenol, ethylbenzene, toluene, benzene, naphthalene, benzoate, p-hydroxybenzoate, salicylate, chlorobenzene, and several 1,4-dihalogenated benzenes. We designed experiments to determine the conditions required for induction of the individual pathways and to determine whether multiple substrates could be biodegraded simultaneously. Oxygen consumption studies with whole cells and enzyme assays with cell extracts showed that the enzymes of the meta, ortho, and modified ortho cleavage pathways can be induced in strain JS150. Strain JS150 contains a nonspecific toluene dioxygenase with a substrate range similar to that found in strains of Pseudomonas putida. The presence of the dioxygenase along with multiple pathways for metabolism of substituted catechols allows facile extension of the growth range by spontaneous mutation and degradation of mixtures of substituted benzenes and phenols. Chlorobenzene-grown cells of strain JS150 degraded mixtures of chlorobenzene, benzene, toluene, naphthalene, trichloroethylene, and 1,2- and 1,4-dichlorobenzenes in continuous culture. Under similar conditions, phenol-grown cells degraded a mixture of phenol, 2-chloro-, 3-chloro, and 2,5-dichlorophenol and 2-methyl- and 3-methylphenol. These results indicate that induction of appropriate biodegradative pathways in strain JS150 permits the biodegradation of complex mixtures of aromatic compounds.     

Biodegradation of 2-nitrotoluene by Pseudomonas sp. strain JS42.

A strain of Pseudomonas sp. was isolated from nitrobenzene-contaminated soil and groundwater on 2-nitrotoluene as the sole source of carbon, energy, and nitrogen. Bacterial cells growing on 2-nitrotoluene released nitrite into the growth medium. The isolate also grew on 3-methylcatechol, 4-methylcatechol, and catechol. 2-Nitrotoluene, 3-methylcatechol, and catechol stimulated oxygen consumption by intact cells regardless of the growth substrate. Crude extracts from the isolate contained catechol 2,3-dioxygenase and 2-hydroxy-6-oxohepta-2,4-dienoate hydrolase activity. The results suggest that 2-nitrotoluene is subject to initial attack by a dioxygenase enzyme that forms 3-methylcatechol with concomitant release of nitrite. The 3-methylcatechol is subsequently degraded via the meta ring fission pathway.     

Oxidation of substituted phenols by Pseudomonas putida F1 and Pseudomonas sp. strain JS6

The biodegradation of benzene, toluene, and chlorobenzenes by Pseudomonas putida involves the initial conversion of the parent molecules to cis-dihydrodiols by dioxygenase enzyme systems. The cis-dihydrodiols are then converted to the corresponding catechols by dihydrodiol dehydrogenase enzymes. Pseudomonas sp. strain JS6 uses a similar system for growth on toluene or dichlorobenzenes. We tested the wild-type organisms and a series of mutants for their ability to transform substituted phenols after induction with toluene. When grown on toluene, both wild-type organisms converted methyl-, chloro-, and nitro-substituted phenols to the corresponding catechols. Mutant strains deficient in dihydrodiol dehydrogenase or catechol oxygenase activities also transformed the phenols. Oxidation of phenols was closely correlated with the induction and activity of the toluene dioxygenase enzyme system.     

Oxidation of substituted phenols by Pseudomonas putida F1 and Pseudomonas sp. strain JS6.

The biodegradation of benzene, toluene, and chlorobenzenes by Pseudomonas putida involves the initial conversion of the parent molecules to cis-dihydrodiols by dioxygenase enzyme systems. The cis-dihydrodiols are then converted to the corresponding catechols by dihydrodiol dehydrogenase enzymes. Pseudomonas sp. strain JS6 uses a similar system for growth on toluene or dichlorobenzenes. We tested the wild-type organisms and a series of mutants for their ability to transform substituted phenols after induction with toluene. When grown on toluene, both wild-type organisms converted methyl-, chloro-, and nitro-substituted phenols to the corresponding catechols. Mutant strains deficient in dihydrodiol dehydrogenase or catechol oxygenase activities also transformed the phenols. Oxidation of phenols was closely correlated with the induction and activity of the toluene dioxygenase enzyme system.     

Lack of Capsular Exopolymer Effects on the Biodegradation of Organic Compounds by Pseudomonas sp. Strains JS1 and JS150

Abstract Due to the increasing interest in the effects of exopolymers on microbial activities, two Pseudomonas sp. strains, JS1 (possesses capsular exopolymer) and JS150 (unencapsulated), were compared for their ability to degrade a variety of organic compounds under a number of different conditions. Degradation kinetics for citrate, salicylate, phenol, toluene, and 2,4,6-trinitrotoluene were identical for both strains in liquid media, regardless of cell density. JS1 and JS150 grew on citrate at the same rate in sand, sterile surface soil, and sterile subsurface sediments. The biodegradation curves for toluene by cells pregrown on citrate in any of the above matrices were indistinguishable. Twofold differences in water content and carbon-to-nitrogen ratios of 0.032 or 320 did not result in any apparent differences in phenol degradation by either encapsulated or unencapsulated cells in sand. These results indicate that generalizations about the effects of exopolymers on microbial processes may not be possible without further research. Received: 14 August 1996; Accepted: 19 November 1996     

Biodegradation of chlorinated alkanes and their commercial mixtures by Pseudomonas sp. strain 273

The biodegradation of chlorinated alkanes was studied under oxic conditions with the objective of identifying favorable and unfavorable intramolecular chlorination sequences with respect to the enzymes studied. Several dehalogenating bacterial strains were screened for their ability to degrade middle-chain polychlorinated alkanes as well as a commercial mixture. Of the organisms tested, the most promising was Pseudomonas sp. strain 273, which possesses an oxygenolytic dehalogenase. The effects of carbon chain length (C₆–C₁₆), halogen position, and overall chlorine content (14–61% w/w) were examined using both commercially available compounds and molecules synthesized in our laboratory. The effects of co-substrates, solvents, and inducing agents were also studied. The results with pure chlorinated alkanes showed that the relative positions of the chlorine atoms strongly influenced the total amount of dehalogenation achieved. The greatest dehalogenation yields were associated with terminally chlorinated alkanes. The α- and α,ω-chlorinated compounds yielded similar results. Vicinal chlorination had the most dramatic impact on degradation. When present on both ends or at the center of the molecule, no dehalogenation was detected. Although partial dehalogenation of 1,2-dichlorodecane was observed, it was likely due to a combination of β-oxidation and an abiotic mechanism. Cereclor S52 was appreciably dehalogenated in shake flasks only when 1,10-dichlorodecane was present as a co-substrate and after increasing the oil surface area through mechanical emulsification, demonstrating the importance of abiotic factors in degrading commercial polychlorinated alkane mixtures.     

Biodegradation of 3-nitrotyrosine by Burkholderia sp. strain JS165 and Variovorax paradoxus JS171

The cascade of reactive nitrogen species generated from nitric oxide causes modification of proteins, lipids, and nucleic acids in a wide range of organisms. 3-Nitrotyrosine is one of the most common products of the action of reactive nitrogen species on proteins. Although a great deal is known about the formation of 3-nitrotyrosine, the subsequent metabolism of this compound is a mystery. Variovorax paradoxus JS171 and Burkholderia sp. strain JS165 were isolated from soil slurries when 3-nitrotyrosine was provided as the sole carbon, nitrogen, and energy source. During growth on 3-nitrotyrosine stoichiometric amounts of nitrite were released along with approximately one-half of the theoretically available ammonia. The catabolic pathway involving oxidative denitration is distinct from the pathway for tyrosine metabolism. The facile isolation and the specific, regulated pathway for 3-nitrotyrosine degradation in natural ecosystems suggest that there is a significant flux of 3-nitrotyrosine in such environments.     

Biodegradation of substituted benzenes

The ability of an association of micro-organisms to degrade a range of substituted aromatic compounds was assessed. Compounds were provided as sources of carbon and energy, and degradation rates monitored. The effect of the presence of other aromatic compounds and of rapidly metabolizable substrates was also investigated. The significance of bioaugmentation of waste-treatment processes with such an inoculum is discussed.     

Biodegradation of substituted benzenes

The ability of an association of micro-organisms to degrade a range of substituted aromatic compounds was assessed. Compounds were provided as sources of carbon and energy, and degradation rates monitored. The effect of the presence of other aromatic compounds and of rapidly metabolizable substrates was also investigated. The significance of bioaugmentation of waste-treatment processes with such an inoculum is discussed.     

Enhancement of phenol degradation by soil bioaugmentation with Pseudomonas sp. JS150

Aims: To test whether bioaugmentation with genetically modified Pseudomonas sp. JS150 strain could be used to enhance phenol degradation in contaminated soils. Methods and Results: The efficiency of phenol removal, content of humic carbon, survival of inoculant, number of total culturable autochthonous bacteria and changes in fatty acid methyl esters (FAME) profiling obtained directly from soils were examined. Bioaugmentation significantly accelerated phenol biodegradation rate in tested soils. Phenol applied at the highest concentration (5·0 mg g^?1 soil) was completely degraded in clay soil (FC) within 65 days, whereas in sand soil (FS) within 72 days. In comparison, phenol biodegradation proceeded for 68 and 96 days in nonbioaugmented FC and FS soils, respectively. The content of humic carbon remained at the same level at the beginning and the end of incubation time in all soil treatments. The number of introduced bacteria (2·50 × 10⁹ g^?1 soil) markedly decreased during the first 4 or 8 days depending on contamination level and type of soil; however, inoculant survived over the experimental period of time. Analysis of FAME patterns indicated that changes in the percentages of cyclopropane fatty acids 17:0 cy and 19:0 cyω10c and branched fatty acids might be useful markers for monitoring the progress of phenol removal from soil. Conclusions: It was confirmed that soil bioaugmentation with Pseudomonas sp. JS150 significantly enhanced soil activity towards phenol degradation. Cyclopropane and branched fatty acids were sensitive probes for degree of phenol utilization. Significance and Impact of the Study: In future, genetically modified Pseudomonas sp. JS150 strain could be of use in the bioaugmentation of phenol‐contaminated areas.     

Degradation of p-chlorotoluene by a mutant of Pseudomonas sp. strain JS6

Pseudomonas sp. strain JS6 grows on chlorobenzene, p-dichlorobenzene, or toluene as a sole source of carbon and energy. It does not grow on p-chlorotoluene (p-CT). Growth on glucose in the presence of p-CT resulted in the accumulation of 4-chloro-2,3-dihydroxy-1-methylbenzene (3-chloro-6-methylcatechol), 4-chloro-2,3-dihydroxy-1-methylcyclohexa-4,6-diene (p-CT dihydrodiol), and 2-methyl-4-carboxymethylenebut-2-en-4-olide (2-methyl dienelactone). Strain JS21, a spontaneous mutant capable of growth on p-CT, was isolated from cultures of strain JS6 after extended exposure to p-CT. In addition to growing on p-CT, JS21 grew on all of the substrates that supported growth of the parent strain, including p-dichlorobenzene, chlorobenzene, benzene, toluene, benzoate, p-hydroxybenzoate, phenol, and ethylbenzene. The pathway for degradation of p-CT by JS21 was investigated by respirometry, isolation of intermediates, and assay of enzymes in cell extracts. p-CT was converted to 3-chloro-6-methylcatechol by dioxygenase and dihydrodiol dehydrogenase enzymes. 3-Chloro-6-methylcatechol underwent ortho ring cleavage catalyzed by a catechol 1,2-dioxygenase to form 2-chloro-5-methyl-cis,cis-muconate, which was converted to 2-methyl dienelactone. A dienelactone hydrolase converted 2-methyl dienelactone to 2-methylmaleylacetic acid. Preliminary results indicate that a change in wild-type induction patterns allows JS21 to grow on p-CT.     

Degradation of p-chlorotoluene by a mutant of Pseudomonas sp. strain JS6.

Pseudomonas sp. strain JS6 grows on chlorobenzene, p-dichlorobenzene, or toluene as a sole source of carbon and energy. It does not grow on p-chlorotoluene (p-CT). Growth on glucose in the presence of p-CT resulted in the accumulation of 4-chloro-2,3-dihydroxy-1-methylbenzene (3-chloro-6-methylcatechol), 4-chloro-2,3-dihydroxy-1-methylcyclohexa-4,6-diene (p-CT dihydrodiol), and 2-methyl-4-carboxymethylenebut-2-en-4-olide (2-methyl dienelactone). Strain JS21, a spontaneous mutant capable of growth on p-CT, was isolated from cultures of strain JS6 after extended exposure to p-CT. In addition to growing on p-CT, JS21 grew on all of the substrates that supported growth of the parent strain, including p-dichlorobenzene, chlorobenzene, benzene, toluene, benzoate, p-hydroxybenzoate, phenol, and ethylbenzene. The pathway for degradation of p-CT by JS21 was investigated by respirometry, isolation of intermediates, and assay of enzymes in cell extracts. p-CT was converted to 3-chloro-6-methylcatechol by dioxygenase and dihydrodiol dehydrogenase enzymes. 3-Chloro-6-methylcatechol underwent ortho ring cleavage catalyzed by a catechol 1,2-dioxygenase to form 2-chloro-5-methyl-cis,cis-muconate, which was converted to 2-methyl dienelactone. A dienelactone hydrolase converted 2-methyl dienelactone to 2-methylmaleylacetic acid. Preliminary results indicate that a change in wild-type induction patterns allows JS21 to grow on p-CT.     

Biodegradation of 4-nitrotoluene by Pseudomonas sp. strain 4NT.

A strain of Pseudomonas spp. was isolated from nitrobenzene-contaminated soil on 4-nitrotoluene as the sole source of carbon, nitrogen, and energy. The organism also grew on 4-nitrobenzaldehyde, and 4-nitrobenzoate. 4-Nitrobenzoate and ammonia were detected in the culture fluid of glucose-grown cells after induction with 4-nitrotoluene. Washed suspensions of 4-nitrotoluene- or 4-nitrobenzoate-grown cells oxidized 4-nitrotoluene, 4-nitrobenzaldehyde, 4-nitrobenzyl alcohol, and protocatechuate. Extracts from induced cells contained 4-nitrobenzaldehyde dehydrogenase, 4-nitrobenzyl alcohol dehydrogenase, and protocatechuate 4,5-dioxygenase activities. Under anaerobic conditions, cell extracts converted 4-nitrobenzoate or 4-hydroxylaminobenzoate to protocatechuate. Conversion of 4-nitrobenzoate to protocatechuate required NADPH. These results indicate that 4-nitrotoluene was degraded by an initial oxidation of the methyl group to form 4-nitrobenzyl alcohol, which was converted to 4-nitrobenzoate via 4-nitrobenzaldehyde. The 4-nitrobenzoate was reduced to 4-hydroxylaminobenzoate, which was converted to protocatechuate. A protocatechuate 4,5-dioxygenase catalyzed meta-ring fission of the protocatechuate. The detection of 4-nitrobenzaldehyde and 4-nitrobenzyl alcohol dehydrogenase and 4-nitrotoluene oxygenase activities in 4-nitrobenzoate-grown cells suggests that 4-nitrobenzoate is an inducer of the 4-nitrotoluene degradative pathway.     

Multiple pathways for toluene degradation in Burkholderia sp. strain JS150.

Burkholderia (Pseudomonas) sp. strain JS150 uses multiple pathways for the metabolism of catechols that result from degradation of aromatic compounds. This suggests that the strain also uses multiple upstream pathways for the initial hydroxylation of aromatic substrates. Two distinct DNA fragments that allowed Pseudomonas aeruginosa PAO1c to grow with benzene as a sole carbon source were cloned from strain JS150. One of the recombinant plasmids containing the initial steps for the degradative pathway contained a 14-kb DNA insert and was designated pRO2016. We have previously shown that the DNA insert originated from a plasmid carried by strain JS150 and contained genes encoding a multicomponent toluene-2-monooxygenase (tbmABCDEF) as well as the cognate regulatory protein (tbmR) that controls expression of the 2-monooxygenase (G. R. Johnson and R. H. Olsen, Appl. Environ. Microbiol. 61:3336-3346, 1995). Subsequently, we have identified an additional region on this DNA fragment that encodes toluene-4-monooxygenase activity. The toluene-4-monooxygenase activity was also regulated by the tbmR gene product. A second DNA fragment that allowed P. aeruginosa to grow with benzene was obtained as a 20-kb insert on a recombinant plasmid designated pRO2015. The DNA insert contained genes encoding toluene-4-monooxygenase activity but no toluene-2-monooxygenase activity. The pRO2015 insert originated from the chromosome of strain JS150, unlike the region cloned in pRO2016. Southern blots and restriction map comparisons showed that the genes for the individual 4-monooxygenases were distinct from one another. Thus, strain JS150 has been shown to have at least three toluene/benzene monooxygenases to initiate toluene metabolism in addition to the toluene dioxygenase reported previously by others.     

Nucleotide sequence analysis of genes encoding a toluene/benzene-2-monooxygenase from Pseudomonas sp. strain JS150.

It was previously shown by others that Pseudomonas sp. strain JS150 metabolizes benzene and alkyl- and chloro-substituted benzenes by using dioxygenase-initiated pathways coupled with multiple downstream metabolic pathways to accommodate catechol metabolism. By cloning genes encoding benzene-degradative enzymes, we found that strain JS150 also carries genes for a toluene/benzene-2-monooxygenase. The gene cluster encoding a 2-monooxygenase and its cognate regulator was cloned from a plasmid carried by strain JS150. Oxygen (18O2) incorporation experiments using Pseudomonas aeruginosa strains that carried the cloned genes confirmed that toluene hydroxylation was catalyzed through an authentic monooxygenase reaction to yield ortho-cresol. Regions encoding the toluene-2-monooxygenase and regulatory gene product were localized in two regions of the cloned fragment. The nucleotide sequence of the toluene/benzene-2-monooxygenase locus was determined. Analysis of this sequence revealed six open reading frames that were then designated tbmA, tbmB, tbmC, tbmD, tbmE, and tbmF. The deduced amino acid sequences for these genes showed the presence of motifs similar to well-conserved functional domains of multicomponent oxygenases. This analysis allowed the tentative identification of two terminal oxygenase subunits (TbmB and TbmD) and an electron transport protein (TbmF) for the monooxygenase enzyme. In addition to these gene products, all the tbm polypeptides shared significant homology with protein components from other bacterial multicomponent monooxygenases. Overall, the tbm gene products shared greater similarity with polypeptides from the phenol hydroxylases of Pseudomonas putida CF600, P35X, and BH than with those from the toluene monooxygenases of Pseudomonas mendocina KR1 and Burkholderia (Pseudomonas) pickettii PKO1. The relationship found between the phenol hydroxylases and a toluene-2-monooxygenase, characterized in this study for the first time at the nucleotide sequence level, suggested that DNA probes used for surveys of environmental populations should be carefully selected to reflect DNA sequences corresponding to the metabolic pathway of interest.     

Biodegradation of 4-methyl-5-nitrocatechol by Pseudomonas sp. strain DNT.

Pseudomonas sp. strain DNT degrades 2,4-dinitrotoluene (DNT) by a dioxygenase attack at the 4,5 position with concomitant removal of the nitro group to yield 4-methyl-5-nitrocatechol (MNC). Here we describe the mechanism of removal of the nitro group from MNC and subsequent reactions leading to ring fission. Washed suspensions of DNT-grown cells oxidized MNC and 2,4,5-trihydroxytoluene (THT). Extracts prepared from DNT-induced cells catalyzed the disappearance of MNC in the presence of oxygen and NADPH. Partially purified MNC oxygenase oxidized MNC in a reaction requiring 1 mol of NADPH and 1 mol of oxygen per mol of substrate. The enzyme converted MNC to 2-hydroxy-5-methylquinone (HMQ), which was identified by gas chromatography-mass spectrometry. HMQ was also detected transiently in culture fluids of cells grown on DNT. A quinone reductase was partially purified and shown to convert HMQ to THT in a reaction requiring NADH. A partially purified THT oxygenase catalyzed ring fission of THT and accumulation of a compound tentatively identified as 3-hydroxy-5-(1-formylethylidene)-2-furanone. Preliminary results indicate that this compound is an artifact of the isolation procedure and suggest that 2,4-dihydroxy-5-methyl-6-oxo-2,4-hexadienoic acid is the actual ring fission product.     

Biodegradation of p-toluenesulphonamide by a Pseudomonas sp.

A bacterium capable of utilising p-toluenesulphonamide was isolated from activated sludge. The isolated strain designated PTSA was identified as a Pseudomonas sp. using chemotaxonomic and genetic studies. Pseudomonas PTSA grew on p-toluenesulphonamide in a chemostat with approximately 90% release of sulphate and 80% release of ammonium. The isolate was also able to grow on 4-carboxybenzenesulphonamide and 3,4-dihydroxybenzoate but did not grow on p-toluenesulphonate. The transient appearance of 4-hydroxymethylbenzenesulphonamide and 4-carboxybenzenesulphonamide during p-toluenesulphonamide degradation proves oxidation of the methyl group is the initial attack in the biodegradation pathway. Both metabolites of p-toluenesulphonamide degradation were identified by high-performance liquid chromatography-mass spectrometry. 4-Carboxybenzenesulphonamide is probably converted into 3,4-dihydroxybenzoate and amidosulphurous acid. The latter is a chemically unstable compound in aqueous solutions and immediately converted into sulphite and ammonium. Both sulphite and ammonium were formed during degradation of 4-carboxybenzenesulphonamide.     

Biodegradation of the sulfonylurea herbicide chlorimuron-ethyl by the strain Pseudomonas sp. LW3

Eleven carbazole (CAR)-degrading bacterial strains were isolated from seawater collected off the coast of Japan using two different media. Seven isolates were shown to be most closely related to the genera Erythrobacter, Hyphomonas, Sphingosinicella, Caulobacter , and Lysobacter . Meanwhile, strains OC3, OC6S, OC9, and OC11S showed low similarity to known bacteria, the closest relative being Kordiimonas gwangyangensis GW14-5 (90% similarity). Southern hybridization analysis revealed that only five isolates carried car genes similar to those reported in Pseudomonas resinovorans CA10 ( car _CA10) or Sphingomonas sp. strain KA1 ( car _KA1). The isolates were subjected to GC-MS and the results indicated that these strains degrade CAR to anthranilic acid.     

Biodegradation of 3-Nitrotyrosine by Burkholderia sp. Strain JS165 and Variovorax paradoxus JS171

The cascade of reactive nitrogen species generated from nitric oxide causes modification of proteins, lipids, and nucleic acids in a wide range of organisms. 3-Nitrotyrosine is one of the most common products of the action of reactive nitrogen species on proteins. Although a great deal is known about the formation of 3-nitrotyrosine, the subsequent metabolism of this compound is a mystery. Variovorax paradoxus JS171 and Burkholderia sp. strain JS165 were isolated from soil slurries when 3-nitrotyrosine was provided as the sole carbon, nitrogen, and energy source. During growth on 3-nitrotyrosine stoichiometric amounts of nitrite were released along with approximately one-half of the theoretically available ammonia. The catabolic pathway involving oxidative denitration is distinct from the pathway for tyrosine metabolism. The facile isolation and the specific, regulated pathway for 3-nitrotyrosine degradation in natural ecosystems suggest that there is a significant flux of 3-nitrotyrosine in such environments.     

Aerobic Biodegradation of 2,4-Dinitroanisole by Nocardioides sp. Strain JS1661

2,4-Dinitroanisole (DNAN) is an insensitive munition ingredient used in explosive formulations as a replacement for 2,4,6-trinitrotoluene (TNT). Little is known about the environmental behavior of DNAN. There are reports of microbial transformation to dead-end products, but no bacteria with complete biodegradation capability have been reported. Nocardioides sp. strain JS1661 was isolated from activated sludge based on its ability to grow on DNAN as the sole source of carbon and energy. Enzyme assays indicated that the first reaction involves hydrolytic release of methanol to form 2,4-dinitrophenol (2,4-DNP). Growth yield and enzyme assays indicated that 2,4-DNP underwent subsequent degradation by a previously established pathway involving formation of a hydride-Meisenheimer complex and release of nitrite. Identification of the genes encoding the key enzymes suggested recent evolution of the pathway by recruitment of a novel hydrolase to extend the well-characterized 2,4-DNP pathway.