Showing papers on "Dehalococcoides published in 2001"
TL;DR: "Dehalococcoides ethenogenes" strain 195 is the first isolate capable of dechlorinating chloroethenes past cis-DCE, and chloroform was found to be inhibitory to chloroethene utilization by strain 195 and at least partially accounts for the inhibitory activity of the synthetic cis- DCE.
Abstract: cis-Dichloroethene (DCE) and vinyl chloride (VC) often accumulate in contaminated aquifers in which tetrachloroethene (PCE) or trichloroethene (TCE) undergo reductive dechlorination. "Dehalococcoides ethenogenes" strain 195 is the first isolate capable of dechlorinating chloroethenes past cis-DCE. Strain 195 could utilize commercially synthesized cis-DCE as an electron acceptor, but doses greater than 0.2 mmol/L were inhibitory, especially to PCE utilization. To test whether the cis-DCE itself was toxic, or whether the toxicity was due to impurities in the commercial preparation (97% nominal purity), we produced cis-DCE biologically from PCE using a Desulfitobacterium sp. culture. The biogenic cis-DCE was readily utilized at high concentrations by strain 195 indicating that cis-DCE was not intrinsically inhibitory. Analysis of the commercially synthesized cis-DCE by GC/mass spectrometry indicated the presence of approximately 0.4% mol/mol chloroform. Chloroform was found to be inhibitory to chloroethene utilization by strain 195 and at least partially accounts for the inhibitory activity of the synthetic cis-DCE. VC, a human carcinogen that accumulates to a large extent in cultures of strain 195, was not utilized as a growth substrate, and cultures inoculated into medium with VC required a growth substrate, such as PCE, for substantial VC dechlorination. However, high concentrations of PCE or TCE inhibited VC dechlorination. Use of a hexadecane phase to keep the aqueous PCE concentration low in cultures allowed simultaneous utilization of PCE and VC. At contaminated sites in which "D. ethenogenes" or similar organisms are present, biogenic cis-DCE should be readily dechlorinated, chloroform as a co-contaminant may be inhibitory, and concentrations of PCE and TCE, except perhaps those near the source zone, should allow substantial VC dechlorination.
269 citations
TL;DR: Assessment of the indigenous reductive dechlorinating potential in a trichloroethene-contaminated aquifer at Cape Canaveral Air Station, Florida suggests molecular-probing can provide a relatively quick and facile method for investigating spatial distributions of dechlorinators on-site.
Abstract: A combination of microcosm studies, polymerase chain reaction (PCR) analysis, and site data was used to assess the indigenous reductive dechlorinating potential in a trichloroethene (TCE)-contaminated aquifer at Cape Canaveral Air Station, Florida. Sediment and groundwater were obtained from two distinct locations approximately 10 m apart. Microcosm studies were performed to assess dechlorinating activity under a variety of nutrient and electron donor amendment conditions. Most live microcosms constructed using material from the first location, near well 9 (W09), were negative for dechlorination. All live microcosms constructed using material from the second location (W06) exhibited dechlorination of TCE to vinyl chloride (VC) and ethene (ETH). DNA encoding 16S ribosomal RNA (rDNA) with a sequence nearly identical with that from Dehalococcoides ethenogenes strain 195 was detected in the active microcosms and in the sediment from W06 with polymerase chain reaction (PCR) using primers targeted to unique regions of Dehalococcoides 16S rDNA. Dehalococcoides was not detected in the autoclaved microcosms from W06, nor in sediment and most microcosms from W09. The results of the microcosm studies and PCR analysis were supported by field data, which indicated significant accumulation of cis-1,2-dichloroethene (cisDCE) and VC at W06, but not at W09. The different microcosm results obtained for the two locations and the spatial variation of positive PCR results indicates heterogeneous distribution of dechlorinating activity and a specific dechlorinating organism, Dehalococcoides, at the site. As both Dehalococcoides and dechlorination activity were similarly, heterogeneously distributed, this suggests that molecular-probing (which could and should be extended in the future to include virtually all known dechlorinators and/or dehalogenases) can provide a relatively quick and facile method for investigating spatial distributions of dechlorinators on-site.
204 citations
TL;DR: Amplified Ribosomal DNA Restriction Analysis of the microbial populations in well waters indicated that a relatively low diversity, sulfur-transforming community outside the plume was shifted toward a high diversity community including Dehalococcoides ethenogenes-type microorganisms inside the zone of contamination.
Abstract: A recent article presented geochemical and microbial evidence establishing metabolic adaptation to and in-situ reductive dechlorination of trichloroethene (TCE) in a fractured dolomite aquifer. This study was designed to further explore site conditions and microbial populations and to explain previously reported enhancement of reductive dechlorination by the addition of pulverized dolomite to laboratory microcosms. A survey of groundwater geochemical parameters (chlorinated ethenes, ethene, H2, CH4, DIC, DOC, and delta13C values for CH4, DIC, and DOC) indicated that in situ reductive dechlorination was ongoing and that an unidentified pool of organic carbon was contributing, likely via microbial respiration, to the large and relatively light on-site DIC pool. Petroleum hydrocarbons associated with the dolomite rock were analyzed by GC/MS and featured a characteristically low delta13C value. Straight chain hydrocarbons were extracted from the dolomite previously found to stimulate reductive dechlorination; these were particularly depleted in hexadecane (HD). Thus, we hypothesized that HD and related hydrocarbons might be anaerobically respired and serve both as the source of on-site DIC and support reductive dechlorination of TCE. Microcosms amended with pulverized dolomite demonstrated reductive dechlorination, whereas a combusted dolomite amendment did not. HD-amended microcosms were also inactive. Therefore, the stimulatory factor in the pulverized dolomite was heat labile, but that component was not HD. Amplified Ribosomal DNA Restriction Analysis (ARDRA) of the microbial populations in well waters indicated that a relatively low diversity, sulfur-transforming community outside the plume was shifted toward a high diversity community including Dehalococcoides ethenogenes-type microorganisms inside the zone of contamination. These observations illustrate biogeochemical intricacies of in situ reductive dechlorination reactions.
48 citations
TL;DR: In this article, a microbial mixed culture capable of dechlorinating tetrachloroethene (PCE) to ethylene and ethane was enriched in a fluidized-bed reactor using soil sediments, anaerobic sludges and activated sludgeges as inocula.
Abstract: Chlorinated solvents such as tetrachloroethene(PCE) and trichloroethene(TCE) are common groundwater contaminants. A microbial mixed culture capable of dechlorinating PCE to ethylene and ethane was enriched in a fluidized-bed reactor using soil sediments, anaerobic sludges and activated sludges as inocula. DNA sequence analyses of 16S rDNA clones obtained from the mixed culture showed the existence of clones which have high similarity to 16S rDNA of Dehalococcoides ethenogenes 195. This result indicated a high possibility that a bacterium phylogenetically close to D. ethenogenes was responsible for complete dechlorination. Soil columns were inoculated with the enrichment culture and continuously fed with PCE and organic compounds. PCE(4 mg/L) was completely dechlorinated to ethylene within 5 h of HRT with 30 mg/L of ethanol, 30 mg/L of lactate, 60 mg/L of propionate or 50 mg/L of sucrose. Although dechlorination was slightly inhibited in the presence of sulfate(64 mg/L), complete dechlorination occurred at 12 h of HRT. KEYWORDS; tetrachloroethene, dechlorination, electron donor, sulfate, 16S rDNA, Dehalococcoides