Molecular characterization and substrate specificity of nitrobenzene dioxygenase from Comamonas sp. strain JS765

Comamonas sp. strain JS765 can grow with nitrobenzene as the sole source of carbon, nitrogen, and energy. We report here the sequence of the genes encoding nitrobenzene dioxygenase (NBDO), which catalyzes the first step in the degradation of nitrobenzene by strain JS765. The components of NBDO were designated Reductase(NBZ), Ferredoxin(NBZ), Oxygenase(NBZalpha), and Oxygenase(NBZbeta), with the gene designations nbzAa, nbzAb, nbzAc, and nbzAd, respectively. Sequence analysis showed that the components of NBDO have a high level of homology with the naphthalene family of Rieske nonheme iron oxygenases, in particular, 2-nitrotoluene dioxygenase from Pseudomonas sp. strain JS42. The enzyme oxidizes a wide range of substrates, and relative reaction rates with partially purified Oxygenase(NBZ) revealed a preference for 3-nitrotoluene, which was shown to be a growth substrate for JS765. NBDO is the first member of the naphthalene family of Rieske nonheme iron oxygenases reported to oxidize all of the isomers of mono- and dinitrotoluenes with the concomitant release of nitrite.     

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 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.     

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.     

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.     

Three types of taxis used in the response of Acidovorax sp. strain JS42 to 2-nitrotoluene

Acidovorax sp. strain JS42 is able to utilize 2-nitrotoluene (2NT) as its sole carbon, nitrogen, and energy source. We report here that strain JS42 is chemotactic to 2NT and that the response is increased when cells are grown on compounds such as 2NT that are known to induce the first step of 2NT degradation. Assays with JS42 mutants unable to oxidize 2NT showed that the first step of 2NT metabolism was required for the induced response, but not for a portion of the constitutive response, indicating that 2NT itself is an attractant. The 2NT metabolite nitrite was shown to be a strong attractant for strain JS42, and sufficient nitrite was produced during the taxis assay to account for a large part of the induced response. A mutant with an inactivated ntdY gene, which is located adjacent to the 2NT degradation genes and codes for a putative methyl-accepting chemotaxis protein, showed a defect in taxis toward 2NT that may involve a reduced response to nitrite. Responses of a mutant defective for the energy-taxis receptor, Aer, indicated that a functional aer gene is required for a substantial part of the wild-type induced response to 2NT. In summary, strain JS42 utilizes three types of taxis to sense and respond to 2NT: constitutive 2NT-specific chemotaxis to directly sense 2NT, metabolism-dependent nitrite-specific chemotaxis that may be mediated by NtdY, and energy taxis mediated by Aer.     

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.     

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.     

Molecular Characterization and Substrate Specificity of Nitrobenzene Dioxygenase from Comamonas sp. Strain JS765

Comamonas sp. strain JS765 can grow with nitrobenzene as the sole source of carbon, nitrogen, and energy. We report here the sequence of the genes encoding nitrobenzene dioxygenase (NBDO), which catalyzes the first step in the degradation of nitrobenzene by strain JS765. The components of NBDO were designated Reductase_NBZ, Ferredoxin_NBZ, Oxygenase_NBZα, and Oxygenase_NBZβ, with the gene designations nbzAa, nbzAb, nbzAc, and nbzAd, respectively. Sequence analysis showed that the components of NBDO have a high level of homology with the naphthalene family of Rieske nonheme iron oxygenases, in particular, 2-nitrotoluene dioxygenase from Pseudomonas sp. strain JS42. The enzyme oxidizes a wide range of substrates, and relative reaction rates with partially purified Oxygenase_NBZ revealed a preference for 3-nitrotoluene, which was shown to be a growth substrate for JS765. NBDO is the first member of the naphthalene family of Rieske nonheme iron oxygenases reported to oxidize all of the isomers of mono- and dinitrotoluenes with the concomitant release of nitrite.     

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     

Genome Sequence of the ethene- and vinyl chloride-oxidizing actinomycete Nocardioides sp. strain JS614

Nocardioides sp. strain JS614 grows on ethene and vinyl chloride (VC) as sole carbon and energy sources and is of interest for bioremediation and biocatalysis. Sequencing of the complete genome of JS614 provides insight into the genetic basis of alkene oxidation, supports ongoing research into the physiology and biochemistry of growth on ethene and VC, and provides biomarkers to facilitate detection of VC/ethene oxidizers in the environment. This is the first genome sequence from the genus Nocardioides and the first genome of a VC/ethene-oxidizing bacterium.     

Selection for Growth on 3-Nitrotoluene by 2-Nitrotoluene-Utilizing Acidovorax sp. Strain JS42 Identifies Nitroarene Dioxygenases with Altered Specificities

Acidovorax sp. strain JS42 uses 2-nitrotoluene as a sole source of carbon and energy. The first enzyme of the degradation pathway, 2-nitrotoluene 2,3-dioxygenase, adds both atoms of molecular oxygen to 2-nitrotoluene, forming nitrite and 3-methylcatechol. All three mononitrotoluene isomers serve as substrates for 2-nitrotoluene dioxygenase, but strain JS42 is unable to grow on 3- or 4-nitrotoluene. Using both long- and short-term selections, we obtained spontaneous mutants of strain JS42 that grew on 3-nitrotoluene. All of the strains obtained by short-term selection had mutations in the gene encoding the α subunit of 2-nitrotoluene dioxygenase that changed isoleucine 204 at the active site to valine. Those strains obtained by long-term selections had mutations that changed the same residue to valine, alanine, or threonine or changed the alanine at position 405, which is just outside the active site, to glycine. All of these changes altered the regiospecificity of the enzymes with 3-nitrotoluene such that 4-methylcatechol was the primary product rather than 3-methylcatechol. Kinetic analyses indicated that the evolved enzymes had enhanced affinities for 3-nitrotoluene and were more catalytically efficient with 3-nitrotoluene than the wild-type enzyme. In contrast, the corresponding amino acid substitutions in the closely related enzyme nitrobenzene 1,2-dioxygenase were detrimental to enzyme activity. When cloned genes encoding the evolved dioxygenases were introduced into a JS42 mutant lacking a functional dioxygenase, the strains acquired the ability to grow on 3-nitrotoluene but with significantly longer doubling times than the evolved strains, suggesting that additional beneficial mutations occurred elsewhere in the genome.     

Simultaneous production of hydrogen and bioflocculant by Enterobacter sp. BY-29

Hydrogen and a bioflocculant could be produced simultaneously by anaerobic culture of Enterobacter sp. BY-29. For production of hydrogen and the bioflocculant by cell culture of the bacterium in batch cultures, cultivation at 37 °C in a medium containing glucose as a carbon source and Polypepton as a nitrogen source was found to be suitable. In continuous production of hydrogen and the bioflocculant by cell culture or immobilized cells of the bacterium, the hydrogen production rate and hydrogen yield by the immobilized cells on porous glass beads in stirred and column reactors were higher than those by the cell culture in a stirred reactor. However, production of the bioflocculant by the cell culture was superior to that by the immobilized cells in continuous production.     

Isolation and identification of a carbazole degradation gene cluster from Sphingomonas sp.JS1

The carbazole degrading bacterium JS1 was isolated from carbazole polluted soil and identified as Sphingomonas sp. bacterium based on its 16S rDNA gene. The car gene cluster located in the genome of JS1 was isolated by PCR and its presence verified by Southern hybridization. Sequence analysis of the car gene cluster showed that the arrangement of elements in JS1 was different from that of Pseudomons sp. CA10 and Nocardioides aromaticivorans IC177, but car gene cluster and neighboring regions were nearly identical to that of Sphingomonas sp. KA1 and Sphingomonas sp.GTIN11. Each element of the car gene cluster was expressed in E. coli upon IPTG induction. The amount of CaBb protein expressed was higher than CarBa and the ratio of these two proteins was 1:1.5. CarC expression level was detected using anti-CarC antibody. The result showed that carbazole degrading proteins were induced by the substrate carbazole. The quantity of CarC at 0.5 mg/ml carbazole was five times more than that at 0.1 mg/ml. Meiying Yang and Wenming Li have the equal contribution for this work.     

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.     

A Nag-like dioxygenase initiates 3,4-dichloronitrobenzene degradation via 4,5-dichlorocatechol in Diaphorobacter sp. strain JS3050

The chemical synthesis intermediate 3,4-dichloronitrobenzene (3,4-DCNB) is an environmental pollutant. Diaphorobacter sp. strain JS3050 utilizes 3,4-DCNB as a sole source of carbon, nitrogen and energy. However, the molecular determinants of its catabolism are poorly understood. Here, the complete genome of strain JS3050 was sequenced and key genes were expressed heterologously to establish the details of its degradation pathway. A chromosome-encoded three-component nitroarene dioxygenase (DcnAaAbAcAd) converted 3,4-DCNB stoichiometrically to 4,5-dichlorocatechol, which was transformed to 3,4-dichloromuconate by a plasmid-borne ring-cleavage chlorocatechol 1,2-dioxygenase (DcnC). On the chromosome, there are also genes encoding enzymes (DcnDEF) responsible for the subsequent transformation of 3,4-dichloromuconate to β-ketoadipic acid. The fact that the genes responsible for the catabolic pathway are separately located on plasmid and chromosome indicates that recent assembly and ongoing evolution of the genes encoding the pathway is likely. The regiospecificity of 4,5-dichlorocatechol formation from 3,4-DCNB by DcnAaAbAcAd represents a sophisticated evolution of the nitroarene dioxygenase that avoids misrouting of toxic intermediates. The findings enhance the understanding of microbial catabolic diversity during adaptive evolution in response to xenobiotics released into the environment.     

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.