Anaerobic bioremediation of RDX by ovine whole rumen fluid and pure culture isolates.

The ability of ruminal microbes to degrade the explosive compound hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX) in ovine whole rumen fluid (WRF) and as 24 bacterial isolates was examined under anaerobic conditions. Compound degradation was monitored by high-performance liquid chromatography analysis, followed by liquid chromatography-tandem mass spectrometry identification of metabolites. Organisms in WRF microcosms degraded 180 µM RDX within 4 h. Nitroso-intermediates hexahydro-1-nitroso-3,5-dinitro-1,3,5-triazine (MNX), hexahydro-1,3-dinitroso-5-nitro-1,3,5-triazine (DNX), and hexahydro-1,3,5-trinitroso-1,3,5-triazine (TNX) were present as early as 0.25 h and were detected throughout the 24-h incubation period, representing one reductive pathway of ring cleavage. Following reduction to MNX, peaks consistent with m/z 193 and 174 were also produced, which were unstable and resulted in rapid ring cleavage to a common metabolite consistent with an m/z of 149. These represent two additional reductive pathways for RDX degradation in ovine WRF, which have not been previously reported. The 24 ruminal isolates degraded RDX with varying efficiencies (0-96 %) over 120 h. Of the most efficient degraders identified, Clostridium polysaccharolyticum and Desulfovibrio desulfuricans subsp. desulfuricans degraded RDX when medium was supplemented with both nitrogen and carbon, while Anaerovibrio lipolyticus, Prevotella ruminicola, and Streptococcus bovis IFO utilized RDX as a sole source of nitrogen. This study showed that organisms in whole rumen fluid, as well as several ruminal isolates, have the ability to degrade RDX in vitro and, for the first time, delineated the metabolic pathway for its biodegradation.

Absorption, tissue distribution, and elimination of residues after 2,4,6-trinitro[14C]toluene administration to sheep.

The compound 2,4,6-trinitrotoluene (TNT) is a persistent contaminant of some industrial and military sites. Biological bioremediation techniques typically rely on the immobilization of TNT reduction products rather than on TNT mineralization. We hypothesized that sheep ruminal microbes would be suitable for TNT destruction after phytoremediation of TNT-contaminated soils by cool-season grasses. Therefore we investigated the fate of [14C]TNT in ruminating sheep to determine the utility of ruminant animals as a portion of the bioremediation process. Three wether sheep were dosed with 35.5 mg each of dietary unlabeled TNT for 21 consecutive days. On day 22 sheep (41.9 +/- 3.0 kg) were orally dosed with 35.5 mg of [14C]TNT (129 microCi; 99.1% radiochemical purity). Blood, urine, and feces were collected at regular intervals for 72 h. At slaughter, tissues were quantitatively collected. Tissues and blood were analyzed for total radioactive residues (TRR); excreta were analyzed for TRR, bound residues, and TNT metabolites. Plasma radioactivity peaked within 1 h of dosing and was essentially depleted within 18 h. Approximately 76% of the radiocarbon was excreted in feces, 17% in urine, with 5% being retained in the gastrointestinal tract and 1% retained in tissues. Parent TNT, dinitroamino metabolites, and diaminonitro metabolites were not detected in excreta. Ruminal and fecal radioactivity was essentially nonextractable using ethyl acetate, acetone, and methanol; covalent binding of fecal radioactive residues was evenly distributed among extractable organic molecules (i.e., soluble organic matter, soluble carbohydrate, protein, lipid, and nucleic acid fractions) and undigested fibers (cellulose, hemicellulose, and lignin). This study demonstrated that TNT reduction within the ruminant gastrointestinal tract leads to substantial immobilization of residues to organic matter, a fate similar to TNT in other strongly reducing environments.

Growth and hepatic in vitro metabolism of ergotamine in mice divergently selected for response to endophyte toxicity.

This study investigated if genetic differences exhibited in endophyte-resistant and -susceptible mouse lines had persisted after 13 generations in which the integrity of lines was maintained yet selection ceased. Experimental groups were mouse lines fed an endophyte-free (E-) or -infected (E+) diet. The in vitro metabolism of the ergot alkaloid ergotamine in mouse liver microsomes was characterized by LC-MS/MS and compared between both lines before and after exposure to E+ feed. No difference in the average daily weight gain of pups between resistant and susceptible mice was observed on the E+ diet. Thus, for the weight gain selection criterion under study, the difference established between the two lines appears not to have persisted over the extended period of relaxed selection. Microsomal incubations produced nine predominate peaks in the HPLC assay. The peaks were confirmed by LC-MS/MS to be ergotamine, ergotamine epimer, monohydroxylated metabolites (M1, M2, M1e, M2e) and dihydroxylated metabolites (M3--5). A gender difference for metabolite formation was observed on the E- diet, in that females produced a greater amount of M1, M1e and M3--5 than males. When challenged with the E+ diet, mice showed differences in concentration of M3 for line (resistant > susceptible) and gender (female > male) and of M4 and M5 for gender (female > male). Gender differences in the metabolism of ergotamine have not been shown before in these lines of mice or other species used to study ergot alkaloid metabolism. This adds a potential source of variation in the susceptibility to fescue toxicity not explored previously and would be of value to investigate further.