24 research outputs found

    Impact of Ammonium on Syntrophic Organohalide-Respiring and Fermenting Microbial Communities

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    Citation: Delgado, A. G., Fajardo-Williams, D., Kegerreis, K. L., Parameswaran, P., & Krajmalnik-Brown, R. (2016). Impact of Ammonium on Syntrophic Organohalide-Respiring and Fermenting Microbial Communities. Msphere, 1(2), 10. doi:10.1128/mSphere.00053-16Syntrophic interactions between organohalide-respiring and fermentative microorganisms are critical for effective bioremediation of halogenated compounds. This work investigated the effect of ammonium concentration (up to 4 g liter(-1) NH4+-N) on trichloroethene-reducing Dehalococcoides mccartyi and Geobacteraceae in microbial communities fed lactate and methanol. We found that production of ethene by D. mccartyi occurred in mineral medium containing = 1 g liter(-1) NH4+-N, organohalide-respiring dynamics shifted from D. mccartyi and Geobacteraceae to mainly D. mccartyi. An increasing concentration of ammonium was coupled to lower metabolic rates, longer lag times, and lower gene abundances for all microbial processes studied. The methanol fermentation pathway to acetate and H-2 was conserved, regardless of the ammonium concentration provided. However, lactate fermentation shifted from propionic to acetogenic at concentrations of >= 2 g liter(-1) NH4+-N. Our study findings strongly support a tolerance of D. mccartyi to high ammonium concentrations, highlighting the feasibility of organohalide respiration in ammonium-contaminated subsurface environments. IMPORTANCE Contamination with ammonium and chlorinated solvents has been reported in numerous subsurface environments, and these chemicals bring significant challenges for in situ bioremediation. Dehalococcoides mccartyi is able to reduce the chlorinated solvent trichloroethene to the nontoxic end product ethene. Fermentative bacteria are of central importance for organohalide respiration and bioremediation to provide D. mccartyi with H2, their electron donor, acetate, their carbon source, and other micronutrients. In this study, we found that high concentrations of ammonium negatively correlated with rates of trichloroethene reductive dehalogenation and fermentation. However, detoxification of trichloroethene to nontoxic ethene occurred even at ammonium concentrations typical of those found in animal waste (up to >= 2 g liter(-1) NH4+-N). To date, hundreds of subsurface environments have been bioremediated through the unique metabolic capability of D. mccartyi. These findings extend our knowledge of D. mccartyi and provide insight for bioremediation of sites contaminated with chlorinated solvents and ammonium

    Dopamine Transporter and Reward Anticipation in a Dimensional Perspective : A Multimodal Brain Imaging Study

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    We would like to thank Christine Baron, Vincent Brulon, Stéphane LeHelleix, Stéphane Demphel, Claude Comtat, Frédéric Dollé, Philippe Gervais, and Renaud Maroy from the Service Hospitalier Frédéric Joliot for their efficient technical support and 11C radioligand preparation. They thank Marie Prat, Audrey Pepin, and Audrey Mabondo for their help in PET processing and Pr. Maria-Joao Santiago-Ribeiro and Dr Renaud de Beaurepaire for their involvement in the recruitment of participants.Peer reviewedPostprin

    Role of bicarbonate as a pH buffer and electron sink in microbial dechlorination of chloroethenes

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    <p>Abstract</p> <p>Background</p> <p>Buffering to achieve pH control is crucial for successful trichloroethene (TCE) anaerobic bioremediation. Bicarbonate (HCO<sub>3</sub><sup>−</sup>) is the natural buffer in groundwater and the buffer of choice in the laboratory and at contaminated sites undergoing biological treatment with organohalide respiring microorganisms. However, HCO<sub>3</sub><sup>−</sup> also serves as the electron acceptor for hydrogenotrophic methanogens and hydrogenotrophic homoacetogens, two microbial groups competing with organohalide respirers for hydrogen (H<sub>2</sub>). We studied the effect of HCO<sub>3</sub><sup>−</sup> as a buffering agent and the effect of HCO<sub>3</sub><sup>−</sup>-consuming reactions in a range of concentrations (2.5-30 mM) with an initial pH of 7.5 in H<sub>2</sub>-fed TCE reductively dechlorinating communities containing <it>Dehalococcoides</it>, hydrogenotrophic methanogens, and hydrogenotrophic homoacetogens.</p> <p>Results</p> <p>Rate differences in TCE dechlorination were observed as a result of added varying HCO<sub>3</sub><sup>−</sup> concentrations due to H<sub>2</sub>-fed electrons channeled towards methanogenesis and homoacetogenesis and pH increases (up to 8.7) from biological HCO<sub>3</sub><sup>−</sup> consumption. Significantly faster dechlorination rates were noted at all HCO<sub>3</sub><sup>−</sup> concentrations tested when the pH buffering was improved by providing 4-(2-hydroxyethyl)-1-piperazineethanesulfonic acid (HEPES) as an additional buffer. Electron balances and quantitative PCR revealed that methanogenesis was the main electron sink when the initial HCO<sub>3</sub><sup>−</sup> concentrations were 2.5 and 5 mM, while homoacetogenesis was the dominant process and sink when 10 and 30 mM HCO<sub>3</sub><sup>−</sup> were provided initially.</p> <p>Conclusions</p> <p>Our study reveals that HCO<sub>3</sub><sup>−</sup> is an important variable for bioremediation of chloroethenes as it has a prominent role as an electron acceptor for methanogenesis and homoacetogenesis. It also illustrates the changes in rates and extent of reductive dechlorination resulting from the combined effect of electron donor competition stimulated by HCO<sub>3</sub><sup>−</sup> and the changes in pH exerted by methanogens and homoacetogens.</p

    Coupling Bioflocculation of <i>Dehalococcoides mccartyi</i> to High-Rate Reductive Dehalogenation of Chlorinated Ethenes

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    Continuous bioreactors operated at low hydraulic retention times have rarely been explored for reductive dehalogenation of chlorinated ethenes. The inability to consistently develop such bioreactors affects the way growth approaches for <i>Dehalococcoides mccartyi</i> bioaugmentation cultures are envisioned. It also affects interpretation of results from in situ continuous treatment processes. We report bioreactor performance and dehalogenation kinetics of a <i>D. mccartyi</i>-containing consortium in an upflow bioreactor. When fed synthetic groundwater at 11–3.6 h HRT, the upflow bioreactor removed >99.7% of the influent trichloroethene (1.5–2.8 mM) and produced ethene as the main product. A trichloroethene removal rate of 98.51 ± 0.05 me<sup>–</sup> equiv L<sup>–1</sup> d<sup>–1</sup> was achieved at 3.6 h HRT. <i>D. mccartyi</i> cell densities were 10<sup>13</sup> and 10<sup>12</sup> 16S rRNA gene copies L<sup>–1</sup> in the bioflocs and planktonic culture, respectively. When challenged with a feed of natural groundwater containing various competing electron acceptors and 0.3–0.4 mM trichloroethene, trichloroethene removal was sustained at >99.6%. Electron micrographs revealed that <i>D. mccartyi</i> were abundant within the bioflocs, not only in multispecies structures, but also as self-aggregated microcolonies. This study provides fundamental evidence toward the feasibility of upflow bioreactors containing <i>D. mccartyi</i> as high-density culture production tools or as a high-rate, real-time remediation biotechnology

    Biostimulation of chlorinated ethene-respiring communities containing <i>Dehalococcoides</i>.

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    <p>Dechlorination of TCE in microcosms (left panels), first transfers from microcosms (middle panels), and enriched soil/sediment-free cultures (right panels). The microcosms (left panels) were setup with (A) uncontaminated garden soil, (B) uncontaminated mangrove sediment, and (C) PCE-contaminated groundwater sediment. A total of 26 microcosms were established. (A)–(B) (left panels) Cuzdrioara and Carolina microcosm replicates exhibited the same pattern for reductive dechlorination product formation and one replicate is shown. Eight Parris Island replicate microcosms from different core depths formed VC and ethene within 30 days after microcosms were established. (C) (left panel) One representative VC and ethene-producing microcosm is presented. The dashed arrows represent an additional transfer not shown. The time-course experiments from the right panels (A–C) are from the third consecutive addition of 0.5 mmol L<sup>−1</sup> TCE. The error bars in the right panels show standard deviation of triplicate cultures. Note the time scale differences between left, middle, and right panels.</p
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