Chloromethylmuconolactones as critical metabolites in the degradation of chloromethylcatechols: recalcitrance of 2-chlorotoluene

Three chlorotoluene-degrading bacterial strains: Differences in biodegradation potential and cell surface properties

Pollution of the environment with chlorinated aromatic compounds is a problem of increasing importance, which has stimulated the search for efficient methods for the remediation of contaminated soil and water. Additionally, for better understanding of the significance of bioavailability to biodegradation, investigation of the cell surface properties is necessary. Hence, this study concerns the properties and possible application, in chlorotoluene removal, of three newly isolated environmental bacterial strains from the genera Pseudomonas, Raoultella and Rahnella. The results show the differences in the biochemical profiles of the isolated strains, their cellular fatty acid composition and their hemolytic properties. However, all three strains exhibit high biodegradation potential, degrading not less than 60% of each monochlorotoluene isomer in 21-day experiments. What is more, observations of changes in the cell surface properties indicate the possible adaptation mechanisms of the strains that enable efficient biodegradation of hydrophobic pollutants such as monochlorotoluenes.

Biodegradation of gaseous emissions of 2-chlorotoluene by strains of Rhodococcus sp. in polyurethane foam packed biotrickling filters

About 60,000-70,000 tons of 2-chlorotoluene, which shows high toxicity in aquatic ecosystems, are produced worldwide and used in a tremendous field of applications. However, clear proofs of biodegradation were only presented for Comamonas testosteroni KT5 and Rhodococcus sp. OCT10. Hence, this study aims on the isolation of additional strains and their characterization in pilot-scale biotrickling filters. Three strains named OCT2, OCT9, and OCT14 of the genus Rhodococcus were isolated, able to mineralize gaseous 2-chlorotoluene like the previously isolated strain Rhodococcus sp. OCT10. The performance levels of these strains were tested in four biotrickling filters each containing 18.8 L of polyurethane foam package, showing elimination capacities of carbon (C) of 30.9 (OCT2), 30.1 (OCT9), 32.2 (OCT10), and 3.9 g C·m^-3·h^-1 (OCT14) at an average crude gas level of 397.6 mg C·m^-3 and an empty bed residence time (EBRT) of 22.6 s. Since OCT10 showed the highest performance levels, this strain was characterized in a second biotrickling filter configuration at long-term conditions of 985 days, varying crude gas levels, EBRT and nutrient supply. Chloride balancing showed a recovery of 94.4% of 2-chlorotoluene eliminated out of the gas phase, pointing out mineralization of 2-chlorotoluene. German emission limit values were met at crude gas levels up to 750 mg C·m^-3 at EBRTs of 120 s or higher. The maximum elimination capacity was 51.2 g C·m^-3·h^-1 at a specific freight of 51.9 g C·m^-3·h^-1 and an EBRT of 254 s. Performance levels were strongly boosted by addition of ammonia as nutrient and stabilized at efficiency levels higher than 90% at a feed rate of 4 g ammonium sulfate per week and 100 L of package volume. Repetitive monitoring of the established 2-chlorotoluene degrading community by BOX-PCR fingerprinting revealed a high long-term stability of OCT10, underlining its suitability in this kind of application.

Computer-assisted engineering of the synthetic pathway for biodegradation of a toxic persistent pollutant

Anthropogenic halogenated compounds were unknown to nature until the industrial revolution, and microorganisms have not had sufficient time to evolve enzymes for their degradation. The lack of efficient enzymes and natural pathways can be addressed through a combination of protein and metabolic engineering. We have assembled a synthetic route for conversion of the highly toxic and recalcitrant 1,2,3-trichloropropane to glycerol in Escherichia coli, and used it for a systematic study of pathway bottlenecks. Optimal ratios of enzymes for the maximal production of glycerol, and minimal toxicity of metabolites were predicted using a mathematical model. The strains containing the expected optimal ratios of enzymes were constructed and characterized for their viability and degradation efficiency. Excellent agreement between predicted and experimental data was observed. The validated model was used to quantitatively describe the kinetic limitations of currently available enzyme variants and predict improvements required for further pathway optimization. This highlights the potential of forward engineering of microorganisms for the degradation of toxic anthropogenic compounds.

Recombinant expression of a unique chloromuconolactone dehalogenase ClcF from Rhodococcus opacus 1CP and identification of catalytically relevant residues by mutational analysis

Chloromuconolactone dehalogenase ClcF plays a unique role in 3-chlorocatechol degradation by Rhodococcus opacus 1CP by compensating the inability of its chloromuconate cycloisomerase ClcB2 to dechlorinate the chemically stable cycloisomerization product (4R,5S)-5-chloromuconolactone (5CML). High sequence similarities showed relatedness of ClcF to muconolactone isomerases (MLIs, EC 5.3.3.4) of the 3-oxoadipate pathway. Although both enzyme types share the ability to dechlorinate 5CML, comparison of kcat/Km indicated a significant extent of specialization of ClcF for dechlorination. This assumption was substantiated by an almost complete inability of ClcF to convert (4S)-muconolactone and the exclusive formation of cis-dienelactone from 5CML. Mutational analysis of ClcF by means of variants E27D, E27Q, Y50A, N52A, and A89S indicated relevance of some highly conserved residues for substrate binding and catalysis. Based on the putative isomerization mechanism of MLI, evidence was provided for a role of E27 in initial proton abstraction as well as of Y50 and N52 in substrate binding. In case of N52 substrate binding is likely to occur to the carboxylic group of 5CML as indicated by a significant change of product specificity. Expression in Escherichia coli BL21-CP(DE)-RIL followed by a three-step purification procedure with heat treatment is a convenient strategy to obtain recombinant ClcF and variants thereof.

Degradation of 2-chlorotoluene by Rhodococcus sp. OCT 10

A strain Rhodococcus sp. OCT 10 DSM 45596(T), exhibiting 99.9% of 16S rDNA identity with Rhodococcus wratislaviensis NCIMB 13082, was isolated from a soil sample. The strain completely mineralised 2-chlorotoluene, 2-bromotoluene, o-xylene, benzyl alcohol and benzoate. In contrast, 2-fluorotoluene was only partially mineralised. By GC-MS and (1)H-NMR analyses, 4-chloro-3-methylcatechol was identified as the central intermediate in the degradation pathway of 2-chlorotoluene. It was further degraded by enzymes of the meta cleavage pathway. Catechol 1,2-dioxygenase and chlorocatechol 1,2-dioxygenase as the initial enzymes of the ortho cleavage pathways were not detectable under these conditions. Furthermore, neither formation nor oxidation of 2-chlorobenzylic alcohol, 2-chlorobenzaldehyde, or 2-chlorobenzoate was observed, thereby excluding side chain oxidation activity.

Comparative studies on the degradation of three aromatic compounds by Pseudomonas sp. and Staphylococcus xylosus

Biological methods of wastewater treatment have been proved very effective for bioremediation of polluted sites. In this study, the degrading abilities of two bacteria Pseudomonas sp. and Staphylococcus xylosus, towards 1,2-dichlorobenzene (1,2-DCB), 2,4-dichlorophenol (2,4-DCP) and 4-Cl-m-cresol, are compared. Culture history and the presence of glucose as carbon source have been used for the optimization of cell's performance. 1,2-DCB showed the higher values of effective concentration (EC(50)), 1.04 and 0.84 mM with Pseudomonas sp. and S. xylosus respectively, whereas no substrate-inhibition appeared, in contrary to 4-Cl-m-cresol, that was more persistent in biodegradation by both bacteria. 2,4-DCP was less assimilated compared to 1,2-DCB, whereas bacterial specificity was higher, as it was found by the estimation of the half-saturation constant of 0.36 and 0.26 mM with Pseudomonas sp. and S. xylosus, respectively.

Co-metabolism of 2,4-dichlorophenol and 4-Cl-m-cresol in the presence of glucose as an easily assimilated carbon source by Staphylococcus xylosus

Comparison of the ability of Staphylococcus xylosus to degrade 2,4-dichlorophenol and 4-Cl-m-cresol in separate cultures is reported. Bacterial adaptation and the continuous presence of glucose, as a conventional carbon source, were found to stimulate the degrading efficiency of S. xylosus. 4-Cl-m-cresol exhibited higher substrate-induced toxicity with K(ig) value at 0.25 mM, comparing to 2,4-dichlorophenol (K(ig) value at 0.90 mM) at initial concentration ranging from 0.1 to 0.5 mM. Degradation rate of 4-Cl-m-cresol was found to decrease only, revealing lower value of inhibition degradation constant (K(i) at 0.019 mM) comparing to that of 2,4-dichlorophenol (K(i) at 0.41 mM). Both glucose and each one of the chloro-aromatic compounds tested were simultaneously consumed and an increase of chloride ions in the medium appeared, during the exponential phase of growth. The chloride ions increase was nearly stoichiometric in the presence of 2,4-dichlorophenol and one of its several intermediate products identified was 2-Cl-maleylacetic acid. In the case of 4-Cl-m-cresol, only one metabolic product was found and identified as 3-methyl-4-oxo-pentanoic acid.

Ex-situ bioremediation of chlorobenzenes in soil

Chlorinated benzenes, including chlorobenzene (CB) and 1,2-dichlorobenzene (DCB) are widely used as chemical intermediates and solvents across industry. Soil contaminated with these compounds was treated in a pilot-scale trial in 6 m3 cells. Air was drawn through each cell and exhausted via an activated carbon (GAC) filter system. The trial objective was to stimulate native microflora with nutrients and varying levels of organic amendments (0%, 12% and 35%). Initial soil DCB concentrations varied from <1 to 6 mg/kg in the three cells with an average of 2 mg/kg. Approximately 90% of the DCB mass present in the soil was removed over a period of 2-3 weeks. Up to 100-fold increases in total heterotrophs (THP), CB+ and DCB+ degraders were observed. Residual concentrations of chlorinated benzenes were generally below detection limits (0.2 mg/kg). Adding organic matter did not enhance the removal of CB and DCB under the trial conditions, which were set up to minimize losses from volatilization. Biodegradation estimation calculations indicated that <5% of the chlorinated benzenes were removed by volatilization and 90% removed by biodegradation. Laboratory shake flask trials confirmed that the soils in the pilot-scale treatment contained a microbial consortium capable of mineralizing CB and DCB. This consortium was capable of mineralizing both CB and DCB with up to 50% of carbon added as chlorinated benzene substrate being recovered as CO2 and up to 44% of organic chlorine being released as chloride ion in mineralization tests, further confirming these chlorinated benzenes were biodegraded. The study confirms that vented ex-situ biotreatment processes for chlorinated benzenes can be achieved without excessive losses from volatilization and that naturally occurring microflora can be readily stimulated with aeration and nutrients.

Specificity of catechol ortho-cleavage during para-toluate degradation by Rhodococcus opacus 1cp

Degradation of para-toluate by Rhodococcus opacus 1cp was investigated. Activities of the key enzymes of this process, catechol 1,2-dioxygenase and muconate cycloisomerase, are detected in this microorganism. Growth on p-toluate was accompanied by induction of two catechol 1,2-dioxygenases. The substrate specificity and physicochemical properties of one enzyme are identical to those of chlorocatechol 1,2-dioxygenase; induction of the latter enzyme was observed during R. opacus 1cp growth on 4-chlorophenol. The other enzyme isolated from the biomass grown on p-toluate exhibited lower rate of chlorinated substrate cleavage compared to the catechol substrate. However, this enzyme is not identical to the catechol 1,2-dioxygenase cloned in this strain within the benzoate catabolism operon. This supports the hypothesis on the existence of multiple forms of dioxygenases as adaptive reactions of microorganisms in response to environmental stress.

Recent advances in oxygenase-catalyzed biotransformations

Oxygenases continue to be widely studied for selective biooxidation of organic compounds. Protein engineering has resulted in heme and flavin monooxygenases with widely altered substrate specificities, and attempts have been reported to scale-up reactions catalyzed by these enzymes. Cofactor regeneration is still a key issue in these developments. Protein engineering contributed to understanding of structure versus function in dioxygenases.