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Biomedical subjects

R J Spanggord

Publications and source records attributed to R J Spanggord.

8 recordsLinked to original sources

Biodegradation of 2,4-dinitrotoluene by a Pseudomonas sp.

Previous studies of the biodegradation of nonpolar nitroaromatic compounds have suggested that microorganisms can reduce the nitro groups but cannot cleave the aromatic ring. We report here the initial steps in a pathway for complete biodegradation of 2,4-dinitrotoluene (DNT) by a Pseudomonas sp. isolated from a four-member consortium enriched with DNT. The Pseudomonas sp. degraded DNT as the sole source of carbon and energy under aerobic conditions with stoichiometric release of nitrite. During induction of the enzymes required for growth on DNT, 4-methyl-5-nitrocatechol (MNC) accumulated transiently in the culture fluid when cells grown on acetate were transferred to medium containing DNT as the sole carbon and energy source. Conversion of DNT to MNC in the presence of 18O2 revealed the simultaneous incorporation of two atoms of molecular oxygen, which demonstrated that the reaction was catalyzed by a dioxygenase. Fully induced cells degraded MNC rapidly with stoichiometric release of nitrite. The results indicate an initial dioxygenase attack at the 4,5 position of DNT with the concomitant release of nitrite. Subsequent reactions lead to complete biodegradation and removal of the second nitro group as nitrite.

Biodegradation, Environmental

N-formyliminodiacetic acid, a new compound from the reaction of nitrilotriacetic acid and chlorine.

It has been proposed that nitrilotriacetic acid be substituted for trisodium polyphosphates in detergents as a way to reduce the rate of eutrophication in the Great Lake Basin. The reaction of nitrilotriacetic acid with chlorine-containing solutions produces a hitherto unknown degradation production, N-formyliminodiacetic acid, in high yield. The toxicological and environmental implications of this reaction are unclear.

Acetates

Cometabolism of DDT analogs by a Pseudomonas sp.

A Pseudomonas sp. capable of growth on several nonchlorinated and mono-p-chloro-substituted analogs of DDT as a sole carbon source degraded bis(p-chlorophenyl)methane and 1,1-bis(p-chlorophenyl)ethane only in the presence of diphenylethane. The products p-chlorophenylacetic acid and 2-(p-chlorophenyl)-propionic acid were not further metabolized by the bacterium. Other chlorinated analogs of DDT were found to be recalcitrant to cometabolic degradation with diphenylethane.

Benzene Derivatives

Some observations on biodegradation of pollutants in aquatic systems.

The biodegradability of pollutants introduced into aquatic environments is subject to many variabilities characteristic of microbial processes. Some observations have been reported on studies with p-cresol, methyl parathion, benzo[b]thiophene, dibenzothiophene, 9H-carbazole, quinoline, benzo[f]quinoline, benz[a]anthracene, benzo[a]pyrene, 7H-dibenzo[c,g]carbazole, Mirex, 2,4-dichlorophenoxyacetic acid, Lindane and 1,1-bis(p-chlorophenyl)-2,2,2-trichloroethane analogs. Water reservoirs included a eutrophic stream, a eutrophic pond, an oligotrophic lake and effluents from waste-water treatment plants. The first ten of the above compounds were studied only in aerobic mixed-culture systems, and Mirex was studied with mixed cultures under both aerobic and anaerobic conditions. Examples were presented of the significance of cometabolism, diauxic processes, film fermentations and microbial interactions in biodegradation studies. Caution is advised in protocols regarding biodegradability of pollutants in aquatic environments.

Bacteria

Metabolism of DDT analogues by a Pseudomonas sp.

A Pseudomonas sp. rapidly metabolized several nonchlorinated analogues of DDT, with the exception of 2,2-diphenylethanol, as the sole carbon source. Several of the mono-p-chloro-substituted diphenyl analogues were also metabolized as the sole carbon source by the bacterium. The resulting chlorinated aromatic acid metabolites were not further metabolized. The isolate was unable to metabolize p,p'-dichlorodiphenyl analogues as the sole carbon source.

Biodegradation, Environmental

Degradation of lindane by Escherichia coli.

Lindane was degraded by Escherichia coli isolated from rat feces. About 10% of the added lindane was metabolized by the bacterium in Trypticase soy broth containing the pesticide. A single metabolite, 2,3,4,5,6-pentachloro-1-cyclohexene, was detected and identified by gas chromatography and mass spectrometry.

Aerobiosis

Structure-activity relationship for the intrinsic hepatotoxicity of dinitrotoluenes.

The relation of various structural parameters to hepatotoxic potential was investigated by using six dinitrotoluene (DNT) isomers and isolated rat hepatocyte suspensions as the biological test system. DNT-induced hepatotoxicity was found to correlate with an inhibition of protein synthesis and an increase in lactate dehydrogenase (LDH) release but not with lipid peroxidation. With each isomer, protein synthesis inhibition was the most sensitive indicator of cytotoxicity. Regardless of the indicator, ortho- and para-substituted isomers were more hepatotoxic at the same concentration than meta-substituted isomers. High-performance liquid chromatograms (HPLC) on samples at 4 h revealed significant quantities of reduced metabolites in the medium. However, increased lipid peroxidation (formation of thiobarbituric acid reactants or evolution of ethane) in the cells was not consistently demonstrated. log EC50 for protein synthesis inhibition and log EC20 for LDH release were linearly correlated with the C atomic charge on the ring carbons bearing the nitro substituents by using molecular orbital (MNDO calculations) theory. The relation was used to predict the hepatotoxic potentials of untested nitrotoluenes, and the predictions were verified to a first approximation by using three trinitrotoluene isomers.

Animals