A Synergistic Platform for Continuous Co-removal of 1,1,1-Trichloroethane, Trichloroethene, and 1,4-Dioxane via Catalytic Dechlorination Followed by Biodegradation.
Yi-Hao LuoXiangxing LongBoya WangChen ZhouYouneng TangRosa Krajmalnik-BrownBruce E RittmannPublished in: Environmental science & technology (2021)
Groundwater co-contaminated with 1,4-dioxane, 1,1,1-trichloroethane (TCA), and trichloroethene (TCE) is among the most urgent environmental concerns of the U.S. Department of Defense (DoD), U.S. Environmental Protection Agency (EPA), and industries related to chlorinated solvents. Inspired by the pressing need to remove all three contaminants at many sites, we tested a synergistic platform: catalytic reduction of 1,1,1-TCA and TCE to ethane in a H2-based membrane palladium-film reactor (H2-MPfR), followed by aerobic biodegradation of ethane and 1,4-dioxane in an O2-based membrane biofilm reactor (O2-MBfR). During 130 days of continuous operation, 1,1,1-TCA and TCE were 95-98% reductively dechlorinated to ethane in the H2-MPfR, and ethane served as the endogenous primary electron donor for promoting 98.5% aerobic biodegradation of 1,4-dioxane in the O2-MBfR. In addition, the small concentrations of the chlorinated intermediate from the H2-MPfR, dichloroethane (DCA) and monochloroethane (MCA), were fully biodegraded through aerobic biodegradation in the O2-MBfR. The biofilms in the O2-MBfR were enriched in phylotypes closely related to the genera Pseudonocardia known to biodegrade 1,4-dioxane.
Keyphrases
- drinking water
- high intensity
- human health
- heavy metals
- candida albicans
- wastewater treatment
- high throughput
- staphylococcus aureus
- cancer therapy
- reduced graphene oxide
- risk assessment
- escherichia coli
- polycyclic aromatic hydrocarbons
- health risk
- room temperature
- life cycle
- high resolution
- crystal structure
- water quality
- cystic fibrosis
- simultaneous determination
- innate immune
- mass spectrometry