Sequestration of a fluorinated analog of 2,4-dichlorophenol and metabolic products by L. minor as evidenced by 19F NMR.

Fate of halogenated phenols in plants was investigated using nuclear magnetic resonance (NMR) to identify and quantify contaminants and their metabolites. Metabolites of 4-chloro-2-fluorophenol (4-Cl-2-FP), as well as the parent compound, were detected in acetonitrile extracts using 19F NMR after various exposure periods. Several fluorinated metabolites with chemical shifts approximately 3.5 ppm from the parent compound were present in plant extracts. Metabolites isolated in extracts were tentatively identified as fluorinated-chlorophenol conjugates through examination of signal-splitting patterns and relative chemical shifts. Signal intensity was used to quantify contaminant and metabolite accumulation within plant tissues. The quantity of 4-Cl-2-F metabolites increased with time and mass balance closures of 90-110% were achieved. In addition, solid phase 19F NMR was used to identify 4-Cl-2-FP which was chemically bound to plant material. This work used 19F NMR for developing a time series description of contaminant accumulation and transformation in aquatic plant systems.

Activity of Desulfitobacterium sp. strain Viet1 demonstrates bioavailability of 2,4-dichlorophenol previously sequestered by the aquatic plant Lemna minor.

Aquatic plants take up and sequester organic contaminants such as chlorophenols through incorporation in cell wall materials and storage in vacuoles. The ultimate fate of plant-sequestered chlorophenols, however, remains unclear. This research investigated 2,4-dichlorophenol (2,4-DCP) sequestration by the aquatic plant Lemna minor and evaluated contaminant release and bioavailability after plant death and cellular disruption. 14C-labeled 2,4-DCP was used to establish that contaminant removed from the aqueous phase was retained internal to L. minor. An assay with Desulfitobacterium sp. strain Viet1 was used to assess the readily bioavailable fraction of plant-sequestered 2,4-DCP and plant metabolites of 2,4-DCP. In plant-free systems, strain Viet1 dechlorinated 2,4-DCP to stoichiometric amounts of 4-chlorophenol (4-CP) as a stable and quantifiable end product. Anaerobic microcosms containing inactivated L. minor, which had accumulated 3.8 micromol of 2,4-DCP equivalents/g of plant material (fresh weight) during a preceding aerobic exposure, were inoculated with strain Viet1. After 118 d of incubation with strain Viet1, 43.5% (+/-1.4%) of the contaminant was recovered as 4-CP, indicating a large portion of plant-sequestered 2,4-DCP was bioavailable for dechlorination by strain Viet1. In contrast, 4-CP formation was not observed in autoclaved microcosms, and only 26.1% (+/-1.0%) of plant-sequestered 2,4-DCP was recovered in the aqueous phase. These findings demonstrate contaminant cycling between plants and microorganisms, and emphasize that understanding the mechanisms and pathways of contaminant sequestration by plants is critical for predicting long-term contaminant fate.

Oxidative microbial degradation of 2,4,6-trinitrotoluene via 3-methyl-4,6-dinitrocatechol.

A novel pathway for biodegradation of 2,4,6-trinitrotoluene (TNT) was investigated where TNT was the sole carbon, nitrogen, and energy source. Results showed the ability of microorganismsto metabolize TNT through removal of a nitro-group, oxygenation of the aromatic ring, and production of a metabolite that is typically a precursor to oxygenolytic ring cleavage. Nitrite production was observed in active systems, and TNT degradation activity was repeatable and transferable. The metabolic intermediate, 3-methyl-4,6-dinitrocatechol, was positively identified through stable isotope mass spectrometry and tandem mass spectrometry. Experimentation with 14C-TNT showed >3% 14C-labeled CO2 in active systems after 30 d exposure to microorganisms. An increasing fraction of 14C-labeled material was associated with biomass with time, where 11.41 +/- 2.91% and 17.09 +/- 1.49% of 14C was associated with biomass in active systems after 20 and 30 d, respectively, as compared with 5.68 +/- 1.33% and 6.08 +/- 1.27% in inactive systems. Parallel degradation of TNT and production of organic metabolites and nitrite were observed in shake flasks constructed with soil from historically contaminated sites, indicating that the novel pathway identified herein is disturbed in the environment. Therefore, results presented provide evidence of a previously unreported pathway for oxidative degradation of TNT.