Chloroform (CF) can undergo reductive dechlorination to dichloromethane, chloromethane, and methane. However, competition for hydrogen (H ), the electron-donor substrate, may cause poor dechlorination when multiple electron acceptors are present. Common acceptors in anaerobic environments are nitrate (NO ), sulfate (SO ), and bicarbonate (HCO ). We evaluated CF dechlorination in the presence of HCO at 1.56 e Eq/m -day, then NO at 0.04-0.15 e Eq/m -day, and finally NO (0.04 e Eq/m -day) along with SO at 0.33 e Eq/m -day in an H -based membrane biofilm reactor (MBfR). When the biofilm was initiated with CF-dechlorination conditions (no NO or SO ), it yielded a CF flux of 0.14 e Eq/m -day and acetate production via homoacetogenesis up to 0.26 e eq/m -day. Subsequent addition of NO at 0.05 e Eq/m -day maintained full CF dechlorination and homoacetogenesis, but NO input at 0.15 e Eq/m -day caused CF to remain in the reactor's effluent and led to negligible acetate production. The addition of SO did not affect CF reduction, but SO reduction significantly altered the microbial community by introducing sulfate-reducing Desulfovibrio and more sulfur-oxidizing Arcobacter. Dechloromonas appeared to carry out CF dechlorination and denitrification, whereas Acetobacterium (homoacetogen) may have been involved with hydrolytic dechlorination. Modifications to the electron acceptors fed to the MBfR caused the microbial community to undergo changes in structure that reflected changes in the removal fluxes.
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http://dx.doi.org/10.1002/bit.26945 | DOI Listing |
Environ Sci Pollut Res Int
May 2024
Research Center for Low Carbon Technology of Water Environment, School of Environment & Natural Resources, Renmin University of China, Beijing, 100872, China.
Sci Total Environ
November 2021
State Key Laboratory of Pollution Control and Resources Reuse, College of Environmental Science and Engineering, Tongji University, Shanghai 200092, China.
Due to the rapid wastewater treatment plants (WWTPs) development and the China's 2060 goal of carbon neutrality, the contribution of greenhouse gas (GHG) emissions from WWTPs should not be overlooked. Thus, the GHG accounting method, featured with site-specific and real operation data targeting city-level WWTPs, is scientifically and pragmatically called for. In this paper, we compared IPCC (IPCC 2006 and IPCC 2019), optimized IPCC and operational data integrated methods (ODIM) for the direct NO and CH emissions for total 50 WWTPs in Shanghai.
View Article and Find Full Text PDFSci Total Environ
May 2021
Research Group Sustainable Systems Engineering (STEN), Ghent University, Coupure Links 653, 9000 Ghent, Belgium.
Responsible water use and sustainable consumption and production are high on the agenda of multiple stakeholders. Different water supply sources are available, including tap water, bottled water, domestically harvested rainwater and domestically abstracted groundwater. The extent to which each of these water supply sources is used, differs over consumption patterns in various housing types, being detached houses, semi-detached houses, terraced houses and apartments.
View Article and Find Full Text PDFBiotechnol Bioeng
June 2019
School of Sustainable Engineering and the Built Environment, Arizona State University, Biodesign Institute, Tempe, Arizona.
Chloroform (CF) can undergo reductive dechlorination to dichloromethane, chloromethane, and methane. However, competition for hydrogen (H ), the electron-donor substrate, may cause poor dechlorination when multiple electron acceptors are present. Common acceptors in anaerobic environments are nitrate (NO ), sulfate (SO ), and bicarbonate (HCO ).
View Article and Find Full Text PDFSci Total Environ
February 2019
Department of Renewable Resources, University of Alberta, Edmonton, AB T6G 2E3, Canada. Electronic address:
The role of agroforestry systems in mitigating greenhouse gas (GHG) emission from agricultural soils during spring thaw (early April to mid-May) has been poorly studied. Soil CO, CH and NO fluxes were measured from treed areas and adjacent herblands (areas without trees) during spring thaw in 2014 and 2015 at 36 agroforestry sites (12 hedgerow, 12 shelterbelt and 12 silvopasture) in central Alberta, Canada. Fluxes of those GHGs varied with agroforestry systems and land-cover types.
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