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W Reineke

Publications and source records attributed to W Reineke.

46 records · Page 3Linked to original sources
PubMed1980

Critical Reactions in Fluorobenzoic Acid Degradation by Pseudomonas sp. B13.

3-Chlorobenzoate-grown cells of Pseudomonas sp. B13 readily cometabolized monofluorobenzoates. A catabolic pathway for the isomeric fluorobenzoates is proposed on the basis of key metabolites isolated. Only 4-fluorobenzoate was utilized and totally degraded after a short period of adaptation. The isoenzymes for total degradation of chlorocatechols, being found during growth with 3-chlorobenzoate or 4-chlorophenol, were not induced in the presence of fluorobenzoates. Correspondingly, only the ordinary enzymes of the benzoate pathway were detected in 4-fluorobenzoate-grown cells. Ring cleavage of 3-fluorocatechol was recognized as a critical step in 3-fluorobenzoate degradation. 2-Fluoro-cis,cis-muconic acid was identified as a dead-end metabolite from 2- and 3-fluorobenzoate catabolism. During 2-fluorobenzoate cometabolism, fluoride is eliminated by the initial dioxygenation.

Journal Article↗
PubMed1980

Hybrid pathway for chlorobenzoate metabolism in Pseudomonas sp. B13 derivatives.

Derivatives of Pseudomonas sp. B13 which had acquired the capability to utilize 4-chloro- and 3,5-dichlorobenzoate as a consequence of the introduction of genes of the TOL plasmid of Pseudomonas putida mt-2 were studied. The utilization of these substrates, a property not shared by the parent strains, was shown to depend upon the combined activities of enzymes from the donor and from the recipient. During growth on 3-chloro-, 4-chloro-, and 3,5-dichlorobenzoate, predominantly the toluate 1,2-deoxygenase and both dihydrodihydroxybenzoate dehydrogenases of the parent strains were induced. On the other hand, no catechol 2,3-dioxygenase from P. putida mt-2 was detectable, so that degradation of chlorocatechols by the nonproductive meta-cleavage pathway was avoided. Instead of that, chlorocatechols were subject to ortho cleavage and totally degraded by the preexisting enzymes of Pseudomonas sp. B13.

Catechol 1,2-Dioxygenase↗
PubMed1979

Metabolism of 3-chloro-, 4-chloro-, and 3,5-dichlorobenzoate by a pseudomonad.

Pseudomonas sp. WR912 was isolated by continuous enrichment in three steps with 3-chloro-, 4-chloro-, and finally 3,5-dichlorobenzoate as sole source of carbon and energy. The doubling times of the pure culture with these growth substrates were 2.6, 3.3, and 5.2 h, respectively. Stoichiometric amounts of chloride were eliminated during growth. Oxygen uptake rates with chlorinated benzoates revealed low stereospecificity of the initial benzoate 1,2-dioxygenation. Dihydrodi-hydroxybenzoate dehydrogenase, catechol 1,2-dixoygenase, and muconate cycloisomerase activities were found in cell-free extracts. The ortho cleavage activity for catechols appeared to involve induction of isoenzymes with different stereospecificity towards chlorocatechols. A catabolic pathway for chlorocatechols was proposed on the basis of similarity to chlorophenoxyacetate catabolism, and cometabolism of 3,5-dimethylbenzoate by chlorobenzoate-induced cells yielded 2,5-dihydro-2,4-dimethyl-5-oxo-furan-2-acetic acid.

Biodegradation, Environmental↗
PubMed1978

Chemical structure and biodegradability of halogenate aromatic compounds. Substituent effects on 1,2-dioxygenation of benzoic acid.

Dioxygenation of substituted benzoic acids by whole cells of 3-chlorobenzoate-utilizing Pseudomonas sp. B 13, benzoate-induced cells of Alcaligenes eutrophus B 9 and toluate-grown cells of Pseudomonas putida mt-2 was examined. Electron-attracting substituents like halogen decreased the reaction rates of benzoate 1,2-dioxygenation. Dioxygenation of substituted benzoic acids by P. putida mt-2 was mostly undisturbed by steric effects of the substituents. Good correlation resulted between the log Vrel values and the Hammett substituent constant sigma. In contrast the reaction rates of dioxygenation by Pseudomonas sp. B 13 and A. eutrophus were decreased predominantly by steric effects of substituents. A non-polar reaction mechanism of benzoate 1,2-dioxygenation is discussed. Results from inhibition studies demonstrate high stereospecificities for the 1,2-dioxygenation by Pseudomonas sp. B 13 of benzoic acids with substituents in ortho- or para-position. In the case of P. putida mt-2 steric handrance by substituents was observed only with orth-substituted benzoic acids. Stereospecificities of the benzoate 1,2-dioxygenation by Pseudomonas sp. B 13 and P. putida mt-2 are illustrated schematically.

Bacteria↗
PubMed1978

Chemical structure and biodegradability of halogenated aromatic compounds. Substituent effects on dehydrogenation of 3,5-cyclohexadiene-1,2-diol-1-carboxylic acid.

The dehydrogenation of substituted 3,5-cyclohexadiene-1,2-diol-1-carboxylic acids by dihydrodihydroxybenzoic acid dehydrogenases from benzoate grown cells of Alcaligenes eutrophus and Pseudomonas sp. B 13 and 3-chlorobenzoate grown cells of the latter organism was examined. No significant differences (Km and Vrel values) were detected for the enzymes from both organisms. The same dihydrodihydroxybenzoic acid dehydrogenase is formed in Pseudomonas sp. B13 during growth on benzoate as well as on 3-chlorobenzoate. The lower turnover rates of 3- and 5-chlorodrodihydroxybenzoic acid compared to dihydrodihydroxybenzoic acid are counterbalanced by an increase in specific activity. With the exception of 4-substituted dihydrodihydroxybenzoic acids exhibiting relative high Km values, only slight sterical and electronic substituent effects are evident. Reaction rates were never reduced to a critical level.

Alcaligenes↗
PubMed1976

[On the mechanism of the biological persistence of halogenated and sulfonated aromatic hydrocarbons (author's transl)].

Aromatic compounds with unphysiological substituents like halogen or SO2H-groups are mainly degraded by cometabolism. Investigations with model compounds show, that the negative inductive effect (-I-effect) of the halogen substituents impede the electrophilic attack of the oxygenases, particularly the pyrocatechases. Although the "affinity" of the enzyme for the substrate increases with the number of halogen substituents, the rate of ring cleavage decreases by the presence of halogen substituents. Benzoate oxygenation shows that in certain positions of substitution the -I-effect can be weakened by the + M-effect of the halogen. As soon as aromaticity is lost by the action of dioxygenases, halide can be eliminated with greater ease and total mineralization is possible. When naphthalene-2-sulfonic acid is degraded by a naphthalene utilizing Pseudomonas strain the sulfonic acid group appears to be eliminated oxygenolytically and the carbon skeleton is channelled into the naphthalene pathway.

Alcaligenes↗
PubMedDate not supplied

Aerobic degradation of polychlorinated biphenyls by Alcaligenes sp. JB1: metabolites and enzymes.

In contrast to the degradation of penta- and hexachlorobiphenyls in chemostat cultures, the metabolism of PCBs by Alcaligenes sp. JB1 was shown to be restricted to PCBs with up to four chlorine substituents in resting-cell assays. Among these, the PCB congeners containing ortho chlorine substituents on both phenyl rings were found to be least degraded. Monochloro-benzoates and dichlorobenzoates were detected as metabolites. Resting cell assays with chlorobenzoates showed that JB1 could metabolize all three monochlorobenzoates and dichlorobenzoates containing only meta and para chlorine substituents, but not dichlorobenzoates possessing an ortho chlorine substituent. In enzyme activity assays, meta cleaving 2,3-dihydroxybiphenyl 1,2-dioxygenase and catechol 2,3-dioxygenase activities were constitutive, whereas benzoate dioxygenase and ortho cleaving catechol 1,2-dioxygenase activities were induced by their substrates. No activity was found for pyrocatechase II, the enzyme that is specific for chlorocatechols. The data suggest that complete mineralization of PCBs with three or more chlorine substituents by Alcaligenes sp. JB1 is unlikely.

Aerobiosis↗
PubMedDate not supplied

Toxicity of chlorobenzene on Pseudomonas sp. strain RHO1, a chlorobenzene-degrading strain.

Pseudomonas sp. strain RHO1 able to use chloro- and 1,4-dichlorobenzene as growth substrates was tested towards sensitivity against chlorobenzene. Concentrations of chlorobenzene higher than 3.5 mM were found to be toxic to cells independent of pregrowth with chlorobenzene or nutrient broth. Below this concentration, sensitivity towards chlorobenzene depended on the precultivation of the cells, i.e. type of growth substrate (chlorobenzene or nutrient broth) and the concentration of chlorobenzene as the growth substrate. Cells grown in continuous culture were especially sensitive with a threshold concentration of 2.5 mM chlorobenzene. In addition to chlorobenzene, metabolites also seem to function as toxic compounds. 2-Chlorophenol and 3-chlorocatechol were isolated from cell extracts. Cleavage of 3-chlorocatechol by catechol 1,2-dioxygenase seems to be the critical step in the metabolism of chlorobenzene.

Biodegradation, Environmental↗