Degradation of 2-methylaniline and chlorinated isomers of 2-methylaniline by Rhodococcus rhodochrous strain CTM

Rhodococcus rhodochrous strain CTM co-metabolized 2-methylaniline and some of its chlorinated isomers in the presence of ethanol as additional carbon source. Degradation of 2-methylaniline proceeded via 3-methylcatechol, which was metabolized mainly by meta-cleavage. In the case of 3-chloro-2-methylaniline, however, only a small proportion (about 10%) was subjected to meta-cleavage; the chlorinated meta-cleavage product was accumulated in the culture fluid as a dead-end metabolite. In contrast, 4-chloro-2-methylaniline was degraded via ortho-cleavage exclusively. Enzyme assays showed the presence of catechol 1,2-dioxygenase and catechol 2,3-dioxygenase as inducible enzymes in strain CTM. Extended cultivation of strain CTM with 2-methylaniline and 3-chloro-2-methylaniline yielded mutants, including R. rhodochrous strain CTM2, that had lost catechol 2,3-dioxygenase activity; these mutants degraded the aromatic amines exclusively via the ortho-cleavage pathway. DNA hybridization experiments using a gene probe revealed the loss of the catechol 2,3-dioxygenase gene from strain CTM2.     

Degradation of p-toluidine by Pseudomonas testosteroni

Abstract A bacterium, which utilizes p -toluidine as sole source of carbon and energy was isolated from soil. The bacterium was identified as Pseudomonas testosteroni .
From enzymatic studies we propose the following pathway for the degradation of p -toluidine: p -toluidine is oxidatively converted to 4-methyl-catechol, which is then cleaved by a meta -pyrocatechase to 2-hydroxy-5-methyl- cis-cis -muconate semialdehyde.     

Degradation of 1,4-naphthoquinones by Pseudomonas putida

Pseudomonas putida J1 and J2, enriched from soil with juglone, are capable of a total degradation of 1,4-naphthoquinone, 2-hydroxy-1,4-naphthoquinone, and 2-chloro-1,4-naphthoquinone. Naphthazerin and plumbagin are only converted into the hydroxyderivatives 2-hydroxynaphthazerin and 3-hydroxyplumbagin, respectively, whereas 2-amino-1,4-naphthoquinone is not attacked at all. The degradation of 1,4-naphthoquinone begins with a hydroxylation of the quinoid ring, yielding 2-hydroxy-1,4-naphthoquinone (lawsone). Lawsone is reduced to 1,2,4-trihydroxynaphthalene with consumption of NADH. The fission product of the quinol could not be detected by direct means because of its instability. However, the presence of 2-chromonecarboxylic acid, a secondary product of lawsone degradation, leads to the conclusion, that the cleavage of the quinol takes place in the meta-position. The resulting ring fission product is converted into salicylic acid by removal of the side chain, presumably as pyruvate. Further degradation of salicyclic acid leads to the formation of catechol, which is then cleaved in the ortho-position and then metabolized via the 3-oxoadipate pathway. The initial steps in the degradation of 2-chloro-1,4-naphthoquinone, namely, the hydroxylation of the quinone to 2-chloro-3-hydroxy-1,4-naphthoquinone, followed by the elimination of the chlorine substituent lead to lawsone, which is further degraded through the pathway described. The degradation steps could be verified by the accumulation products of mutant strains blocked in different steps of lawsone metabolism. Generation of mutants was carried out by chemical and by transposon mutagenesis. The regulation of the first steps of the pathway catalysed by juglone hydroxylase and lawsone reductase, was investigated by induction experiments.     

Degradation of 2-methylaniline in Rhodococcus rhodochrous: cloning and expression of two clustered catechol 2,3-dioxygenase genes from strain CTM

Rhodococcus rhodochrous strain CTM degrades 2-methylaniline mainly via the meta-cleavage pathway. Conversion of the metabolite 3-methylcatechol was catalysed by an Mr 156,000 catechol 2,3-dioxygenase (C23OI) comprising four identical subunits of Mr 39,000. The corresponding gene was detected by using an oligonucleotide as a gene probe. This oligonucleotide was synthesized on the basis of a partial amino acid sequence obtained from the purified enzyme from R. rhodochrous. The structural gene of C23OI was located on a 3.5 kb BglII restriction fragment of plasmid pTC1. On the same restriction fragment the gene for a second catechol 2,3-dioxygenase, designated C23OII, was found. This gene coded for the synthesis of the Mr 40,000 polypeptide of the Mr 158,000 tetrameric C23OII. More precise mapping of the structural genes showed that the C23OI gene was located on a 1.2 kb BglII-SmaI fragment and the C23OII gene on the adjacent 1.15 kb SmaI fragment. Comprehensive substrate range analysis showed that C23OII accepted all the substrates that C23OI did, but additionally cleaved 2,3-dihydroxybiphenyl and catechols derived from phenylcarboxylic acids. C23OI exhibited highest activity towards methylcatechols, whereas C23OII cleaved unsubstituted catechol preferentially.     

Transformation of 2-chloroquinoline to 2-chloro-cis-7,8-dihydro-7,8-dihydroxyquinoline by quinoline-grown resting cells of Pseudomonas putida 86

Abstract Resting cells of Pseudononas putida strain 86 were grown on quinoline transformed 2-chloroquinoline to 2-chloro- cis -7,8-dihydro-7,8-dihydroxyquinoline which was not converted further. 7,8-Dioxygenating activity was present when the enzymes of quinoline catabolism were induced. Quinoline-grown cells of strain 86 treated simultaneously with 2-chloroquinoline and D-(-)- threo -chloramphenicol to prevent protein biosynthesis also formed the cis -7,8-dihydrodiol of 2-chloroquinoline. Succinate-grown resting cells did not oxidize 2-chloroquinoline. Acid-catalyzed decomposition of 2-chloro- cis -7,8-dihydro-7,8-dihydroxyquinoline predominantly yielded 2-chloro-8-hydroxyquinoline. By analogy, accumulation of the putative dead-end metabolite 1 H -8-hydroxy-2-oxoquinoline during growth of P. putida 86 on quinoline is suggested to likewise result from dehydration of the 7,8-dihydrodiol of 1 H -2-oxoquinoline.