Orthric Rieske dioxygenases for degrading mixtures of 2,4-dinitrotoluene/naphthalene and 2-amino-4,6-dinitrotoluene/4-amino-2,6-dinitrotoluene

Pollutants are frequently found as mixtures yet it is difficult to engineer enzymes with broad substrate ranges on aromatics. Inspired by the archetypal nitroarene dioxygenase, which shares its electron transport with a salicylate monooxygenase, we have created an innovative and general approach to expand the substrate range of dioxygenase enzymes in a single cell. We have developed here a series of novel, hybrid dioxygenase enzymes that function with a single ferredoxin reductase and ferredoxin that are used to transport two electrons from nicotinamide adenine dinucleotide to the two independent terminal oxygenases. Each independent alpha-oxygenase may then be used simultaneously to create orthric enzymes that degrade mixtures of environmental pollutants. Specifically, we created a hybrid dioxygenase system consisting of naphthalene dioxygenase/dinitrotoluene dioxygenase to simultaneously degrade 2,4-dinitrotoluene and naphthalene (neither enzyme alone had significant activity on both compounds) and dinitrotoluene dioxygenase/nitrobenzene dioxygenase to simultaneously degrade the frequently encountered 2,4,6-trinitrotoluene reduction products 2-amino-4,6-dinitrotoluene and 4-amino-2,6-dinitrotoluene.     

Evolution of catabolic pathways for synthetic compounds: bacterial pathways for degradation of 2,4-dinitrotoluene and nitrobenzene

The pathways for 2,4-dinitrotoluene (2,4-DNT) and nitrobenzene offer fine illustrations of how the ability to assimilate new carbon sources evolves in bacteria. Studies of the degradation pathways provide insight about two principal strategies for overcoming the metabolic block imposed by nitro- substituents on aromatic compounds. The 2,4-DNT pathway uses novel oxygenases for oxidative denitration and subsequent ring-fission. The nitrobenzene pathway links facile reduction of the nitro- substituent, a novel mutase enzyme, and a conserved operon encoding aminophenol degradation for mineralization of nitrobenzene. Molecular genetic analysis with comparative biochemistry reveals how the pathways were assembled in response to the recent appearance of the two synthetic chemicals in the biosphere.     

Aerobic biodegradation of dinitrotoluenes in batch systems by pure and mixed cultures

Biodegradation characteristics of 2,4- and 2,6-dinitrotoluenes (DNTs) individually by pure strains and defined mixed cultures obtained from a mixed culture isolated from a slate packed bed bioreactor is described. Batch degradation experiments were carried out with free cells in submerged cultivations. The degradation rate and efficiency of five best individual bacterial strains, bacterial consortia comprising three and five of these strains, and the complete mixed culture were evaluated and compared. All the strains showed ability to degrade both the DNTs. All but one strain degraded both DNTs at the same rate. The degradation rate as well as the degradation efficiency by the mixed cultures was higher than that by the individual strains. The complete mixed culture showed 15-20x higher degradation rate than the individual bacterial strains.     

Stability of hydroxylamino- and amino-intermediates from reduction of 2,4,6-trinitrotoluene, 2,4-dinitrotoluene, and 2,6-dinitrotoluene

Hydroxylamines, produced as intermediates in the reductive metabolism of 2,4,6-trinitrotoluene, 2,4-dinitrotoluene, and 2,6-dinitrotoluene between nitroaromatic parent compounds and corresponding amines, were unstable in aqueous solution in the presence of O₂. Reactions of hydroxylamines to compounds other than amines may be the major cause of poor mass balance observations in bioremediation systems where only aminated products are monitored. Results demonstrate the formation of azoxy compounds as products of abiotic aryl-hydroxylamine reactions.     

Evolution of a new bacterial pathway for 4-nitrotoluene degradation

Bacteria that assimilate synthetic nitroarene compounds represent unique evolutionary models, as their metabolic pathways are in the process of adaptation and optimization for the consumption of these toxic chemicals. We used Acidovorax sp. strain JS42, which is capable of growth on nitrobenzene and 2-nitrotoluene, in experiments to examine how a nitroarene degradation pathway evolves when its host strain is challenged with direct selective pressure to assimilate non-native substrates. Although the same enzyme that initiates the degradation of nitrobenzene and 2-nitrotoluene also oxidizes 4-nitrotoluene to 4-methylcatechol, which is a growth substrate for JS42, the strain is incapable of growth on 4-nitrotoluene. Using long-term laboratory evolution experiments, we obtained JS42 mutants that gained the ability to grow on 4-nitrotoluene via a new degradation pathway. The underlying basis for this new activity resulted from the accumulation of specific mutations in the gene encoding the dioxygenase that catalyses the initial oxidation of nitroarene substrates, but at positions distal to the active site and previously unknown to affect activity in this or related enzymes. We constructed additional mutant dioxygenases to identify the order of mutations that led to the improved enzymes. Biochemical analyses revealed a defined, step-wise pathway for the evolution of the improved dioxygenases.     

Comparison of DNA binding between the carcinogen 2,6-dinitrotoluene and its noncarcinogenic analog 2,6-diaminotoluene

We used ³²P-postlabelling to compare DNA binding between the potent hepatocarcinogen 2,6-dinitrotoluene and its noncarcinogenic analog 2,6-diaminotoluene. The two compounds were compared to determine whether differences in DNA binding could partly explain the differences in their carcinogenicity. Fischer-344 rats were administered 1.2 mmol/kg of a compound by single i.p. injection and examined for DNA adduct formation in the liver. Four adducts were detected following administration of 2,6-dinitrotoluene, with a total adduct yield of 13.5 adducted nucleotides per 10⁷ nucleotides. Qualitatively identical adducts were also detected after treatment with the derivative 2-amino-6-nitrotoluene. Adduct yields from 2,6-dinitrotoluene were 30 times greater than from 2-amino-6-nitrotoluene. No adducts were observed following treatment with 2,6-diaminotoluene. 2,6-Dinitrotoluene and 2,6-diaminotoluene were also compared for qualitative differences in hepatotoxicity. 2,6-Dinitrotoluene produced extensive hemorrhagic necrosis in the liver, whereas no evidence of hepatocellular necrosis was detected following administration of the latter. The differences between the two compounds in both DNA binding and cytotoxicity were consistent with the differences in their carcinogenicity.     

Aerobic tryptophan degradation pathway in bacteria: novel kynurenine formamidase

While a variety of chemical transformations related to the aerobic degradation of L-tryptophan (kynurenine pathway), and most of the genes and corresponding enzymes involved therein have been predominantly characterized in eukaryotes, relatively little was known about this pathway in bacteria. Using genome comparative analysis techniques we have predicted the existence of the three-step pathway of aerobic L-tryptophan degradation to anthranilate (anthranilate pathway) in several bacteria. Based on the chromosomal gene clustering analysis, we have identified a previously unknown gene encoding for kynurenine formamidase (EC 3.5.1.19) involved with the second step of the anthranilate pathway. This functional prediction was experimentally verified by cloning, expression and enzymatic characterization of recombinant kynurenine formamidase orthologs from Bacillus cereus, Pseudomonas aeruginosa and Ralstonia metallidurans. Experimental verification of the inferred anthranilate pathway was achieved by functional expression in Escherichia coli of the R. metallidurans putative kynBAU operon encoding three required enzymes: tryptophan 2,3-dioxygenase (gene kynA), kynurenine formamidase (gene kynB), and kynureninase (gene kynU). Our data provide the first experimental evidence of the connection between these genes (only one of which, kynU, was previously characterized) and L-tryptophan aerobic degradation pathway in bacteria.     

Aerobic degradation of choline by Proteus mirabilis: enzymatic requirements and pathway

Cleavage of choline to trimethylamine and acetaldehyde by extracts of Proteus mirabilis requires both particulate and soluble protein fractions, K+, and a bound divalent metal cation. The reaction shows a long lag period, abolished only by preincubation of the particulate fraction in the complete reaction system. The two-carbon fragment produced is acetaldehyde; choline cleavage appears to be tightly coupled to dismutation of the acetaldehyde to ethanol and acetate, as indicated by stimulation by NAD+, ADP, and Fe2+ and inhibition by reagents reacting with acetaldehyde. The system is thus similar to that previously described in anaerobes (Desulfovibrio, Clostridium). Attempts to demonstrate a cobamide coenzyme requirement (as in the similar ethanolamine ammonia-lyase reaction) were unsuccessful; the reaction was carried out by fractions devoid of vitamin B12 activity (not supporting growth of Lactobacillus leichmannii) and insensitive to light.     

Evidence for a new pathway in the bacterial degradation of 4-fluorobenzoate

Six bacterial strains able to use 4-fluorobenzoic acid as their sole source of carbon and energy were isolated by selective enrichment from various water and soil samples from the Stuttgart area. According to their responses in biochemical and morphological tests, the organisms were assigned to the genera Alcaligenes, Pseudomonas, and Aureobacterium. To elucidate the degradation pathway of 4-fluorobenzoate, metabolic intermediates were identified. Five gram-negative isolates degraded this substrate via 4-fluorocatechol, as described in previous studies. In growth experiments, these strains excreted 50 to 90% of the fluoride from fluorobenzoate. Alcaligenes sp. strains RHO21 and RHO22 used all three isomers of monofluorobenzoate. Alcaligenes sp. strain RHO22 also grew on 4-chlorobenzoate. Aureobacterium sp. strain RHO25 transiently excreted 4-hydroxybenzoate into the culture medium during growth on 4-fluorobenzoate, and stoichiometric amounts of fluoride were released. In cell extracts from this strain, the enzymes for the conversion of 4-fluorobenzoate, 4-hydroxybenzoate, and 3,4-dihydroxybenzoate could be detected. All these enzymes were inducible by 4-fluorobenzoate. These data suggest a new pathway for the degradation of 4-fluorobenzoate by Aureobacterium sp. strain RHO25 via 4-hydroxybenzoate and 3,4-dihydroxybenzoate.     

Aerobic bacterial degradation of polycyclic aromatic hydrocarbons (PAHs) and its kinetic aspects

Aerobic bacterial degradation of PAHs is reviewed. Particular attention is paid to its kinetic aspects (rate and specificity). The general concepts of PAH biodegradation in nature and the role of aerobic bacteria in this process are described. The problem of PAH bioavailability and the mechanism of PAH penetration through bacterial cell wall are discussed. The key role of the reaction of PAH hydroxylation in controlling the rate and specificity of PAH biodegradation process is substantiated. The effects of competitive inhibition, intermediate inhibition, cross induction, and cometabolism are considered. The importance of microbial communities for PAH biodegradation in natural ecosystems is shown. The review contains the list of 138 references.     

Evidence for a new pathway in the bacterial degradation of 4-fluorobenzoate.

Six bacterial strains able to use 4-fluorobenzoic acid as their sole source of carbon and energy were isolated by selective enrichment from various water and soil samples from the Stuttgart area. According to their responses in biochemical and morphological tests, the organisms were assigned to the genera Alcaligenes, Pseudomonas, and Aureobacterium. To elucidate the degradation pathway of 4-fluorobenzoate, metabolic intermediates were identified. Five gram-negative isolates degraded this substrate via 4-fluorocatechol, as described in previous studies. In growth experiments, these strains excreted 50 to 90% of the fluoride from fluorobenzoate. Alcaligenes sp. strains RHO21 and RHO22 used all three isomers of monofluorobenzoate. Alcaligenes sp. strain RHO22 also grew on 4-chlorobenzoate. Aureobacterium sp. strain RHO25 transiently excreted 4-hydroxybenzoate into the culture medium during growth on 4-fluorobenzoate, and stoichiometric amounts of fluoride were released. In cell extracts from this strain, the enzymes for the conversion of 4-fluorobenzoate, 4-hydroxybenzoate, and 3,4-dihydroxybenzoate could be detected. All these enzymes were inducible by 4-fluorobenzoate. These data suggest a new pathway for the degradation of 4-fluorobenzoate by Aureobacterium sp. strain RHO25 via 4-hydroxybenzoate and 3,4-dihydroxybenzoate.     

Aerobic Degradation of Dinitrotoluenes and Pathway for Bacterial Degradation of 2,6-Dinitrotoluene

An oxidative pathway for the mineralization of 2,4-dinitrotoluene (2,4-DNT) by Burkholderia sp. strain DNT has been reported previously. We report here the isolation of additional strains with the ability to mineralize 2,4-DNT by the same pathway and the isolation and characterization of bacterial strains that mineralize 2,6-dinitrotoluene (2,6-DNT) by a different pathway. Burkholderia cepacia strain JS850 and Hydrogenophaga palleronii strain JS863 grew on 2,6-DNT as the sole source of carbon and nitrogen. The initial steps in the pathway for degradation of 2,6-DNT were determined by simultaneous induction, enzyme assays, and identification of metabolites through mass spectroscopy and nuclear magnetic resonance. 2,6-DNT was converted to 3-methyl-4-nitrocatechol by a dioxygenation reaction accompanied by the release of nitrite. 3-Methyl-4-nitrocatechol was the substrate for extradiol ring cleavage yielding 2-hydroxy-5-nitro-6-oxohepta-2,4-dienoic acid, which was converted to 2-hydroxy-5-nitropenta-2,4-dienoic acid. 2,4-DNT-degrading strains also converted 2,6-DNT to 3-methyl-4-nitrocatechol but did not metabolize the 3-methyl-4-nitrocatechol. Although 2,6-DNT prevented the degradation of 2,4-DNT by 2,4-DNT-degrading strains, the effect was not the result of inhibition of 2,4-DNT dioxygenase by 2,6-DNT or of 4-methyl-5-nitrocatechol monooxygenase by 3-methyl-4-nitrocatechol.     

Aerobic degradation of polychlorinated biphenyls

The microbial degradation of polychlorinated biphenyls (PCBs) has been extensively studied in recent years. The genetic organization of biphenyl catabolic genes has been elucidated in various groups of microorganisms, their structures have been analyzed with respect to their evolutionary relationships, and new information on mobile elements has become available. Key enzymes, specifically biphenyl 2,3-dioxygenases, have been intensively characterized, structure/sequence relationships have been determined and enzymes optimized for PCB transformation. However, due to the complex metabolic network responsible for PCB degradation, optimizing degradation by single bacterial species is necessarily limited. As PCBs are usually not mineralized by biphenyl-degrading organisms, and cometabolism can result in the formation of toxic metabolites, the degradation of chlorobenzoates has received special attention. A broad set of bacterial strategies to degrade chlorobenzoates has recently been elucidated, including new pathways for the degradation of chlorocatechols as central intermediates of various chloroaromatic catabolic pathways. To optimize PCB degradation in the environment beyond these metabolic limitations, enhancing degradation in the rhizosphere has been suggested, in addition to the application of surfactants to overcome bioavailability barriers. However, further research is necessary to understand the complex interactions between soil/sediment, pollutant, surfactant and microorganisms in different environments.     

Aerobic degradation of aromatic compounds

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Highlights► Metabolic and regulatory networks are finely tuned for biodegradation of aromatics. ► New pathways and widespread bacterial biodegradation capabilities revealed by omics. ► Full characterization of hybrid pathways expands the scope of aromatic biodegradation. ► The metabolism of aromatics plays a pivotal role in cell to cell communication. ► Computational and synthetic biology approaches design novel biodegradation pathways.     

Mutagenicity of 2,6-dinitrotoluene and its metabolites, and their related compounds in Salmonella typhimurium

The mutagenic activities of 2,6-dinitrotoluene (2,6-DNT) and its 6 metabolites, and their 8 related compounds were examined using Salmonella typhimurium strains TA98 and TA100 in the absence or presence of S9 mix. 2,6-DNT itself showed no mutagenicity toward either strain, but 2,6-dinitrobenzaldehyde (2,6-DNBAl), one of the metabolites of 2,6-DNT, showed the highest mutagenic activity in strain TA100. 2,6-DNBAl was a direct-acting mutagen, not requiring metabolic activation. The other compounds containing nitro groups showed weak or no mutagenic activity. This result suggests that the direct-acting mutagenicity of 2,6-DNBAl is mainly due to the aldehyde group of the 2,6-DNBAl molecule.     

Cloning and characterization of Pseudomonas sp. strain DNT genes for 2,4-dinitrotoluene degradation.

The degradation of 2,4-dinitrotoluene (DNT) by Pseudomonas sp. strain DNT is initiated by a dioxygenase attack to yield 4-methyl-5-nitrocatechol (MNC) and nitrite. Subsequent oxidation of MNC by a monooxygenase results in the removal of the second molecule of nitrite, and further enzymatic reactions lead to ring fission. Initial studies on the molecular basis of DNT degradation in this strain revealed the presence of three plasmids. Mitomycin-derived mutants deficient in either DNT dioxygenase only or DNT dioxygenase and MNC monooxygenase were isolated. Plasmid profiles of mutant strains suggested that the mutations resulted from deletions in the largest plasmid. Total plasmid DNA partially digested by EcoRI was cloned into a broad-host-range cosmid vector, pCP13. Recombinant clones containing genes encoding DNT dioxygenase, MNC monooxygenase, and 2,4,5-trihydroxytoluene oxygenase were characterized by identification of reaction products and the ability to complement mutants. Subcloning analysis suggests that the DNT dioxygenase is a multicomponent enzyme system and that the genes for the DNT pathway are organized in at least three different operons.     

Aerobic degradation of olive mill wastewaters

The degradation of olive mill wastewater by aerobic microorganisms has been investigated in a batch reactor, by conducting experiments where the initial concentration of organic matter, quantified by the chemical oxygen demand, and the initial biomass were varied. The evolution of the chemical oxygen demand, biomass and the total contents of phenolic and aromatic compounds were followed through each experiment. According to the Contois model, a kinetic expression for the substrate utilization rate is derived, and its biokinetic constants are evaluated. This final predicted equation agrees well with all the experimental data. Received: 12 June 1996 / Received revision: 11 September 1996 / Accepted: 13 September 1996