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Biodegradation of tetrabromobisphenol A in the sewage sludge process

Biodegradation of tetrabromobisphenol A in the sewage sludge process
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摘要 Anaerobic sewage sludge capable of rapidly degrading tetrabromobisphenol A(TBBPA) was successfully acclimated in an anaerobic reactor over 280 days. During the period from 0 to 280 days, the TBBPA degradation rate(DR), utilization of glucose, and VSS were monitored continuously. After 280 days of acclimation, the TBBPA DR of active sludge reached 96.0% after 20 days of treatment in batch experiments. Based on scanning electron microscopy(SEM) observations and denaturing gradient gel electrophoresis(DGGE) determinations,the diversity of the microorganisms after 0 and 280 days in the acclimated anaerobic sewage sludge was compared. Furthermore, eleven metabolites, including 2-bromophenol,3-bromophenol, 2,4-dibromophenol, 2,6-dibromophenol, tribromophenol and bisphenol A,were identified by gas chromatography–mass spectrometry(GC–MS). Moreover, the six primary intermediary metabolites were also well-degraded by the acclimated anaerobic sewage sludge to varying degrees. Among the six target metabolites, tribromophenol was the most preferred substrate for biodegradation via debromination. These metabolites degraded more rapidly than monobromide and bisphenol A. The biodegradation data of the intermediary metabolites exhibited a good fit to a pseudo-first-order model.Finally, based on the metabolites, metabolic pathways were proposed. In conclusion, the acclimated microbial consortia degraded TBBPA and its metabolites well under anaerobic conditions. Anaerobic sewage sludge capable of rapidly degrading tetrabromobisphenol A(TBBPA) was successfully acclimated in an anaerobic reactor over 280 days. During the period from 0 to 280 days, the TBBPA degradation rate(DR), utilization of glucose, and VSS were monitored continuously. After 280 days of acclimation, the TBBPA DR of active sludge reached 96.0% after 20 days of treatment in batch experiments. Based on scanning electron microscopy(SEM) observations and denaturing gradient gel electrophoresis(DGGE) determinations,the diversity of the microorganisms after 0 and 280 days in the acclimated anaerobic sewage sludge was compared. Furthermore, eleven metabolites, including 2-bromophenol,3-bromophenol, 2,4-dibromophenol, 2,6-dibromophenol, tribromophenol and bisphenol A,were identified by gas chromatography–mass spectrometry(GC–MS). Moreover, the six primary intermediary metabolites were also well-degraded by the acclimated anaerobic sewage sludge to varying degrees. Among the six target metabolites, tribromophenol was the most preferred substrate for biodegradation via debromination. These metabolites degraded more rapidly than monobromide and bisphenol A. The biodegradation data of the intermediary metabolites exhibited a good fit to a pseudo-first-order model.Finally, based on the metabolites, metabolic pathways were proposed. In conclusion, the acclimated microbial consortia degraded TBBPA and its metabolites well under anaerobic conditions.
出处 《Journal of Environmental Sciences》 SCIE EI CAS CSCD 2017年第11期39-48,共10页 环境科学学报(英文版)
基金 supported in part by the Grant from Guangdong Province Scientific and Technological Project (2016A050503029) Fundamental Research Funds for the Universities (161gpy27) Research Fund Program of Guangdong Provincial Key Laboratory of Environmental Pollution Control and Remediation Technology (2016K0008)
关键词 Tetrabromobisphenol A BIODEGRADATION METABOLITES Anaerobic sewage sludge PATHWAYS Tetrabromobisphenol A Biodegradation Metabolites Anaerobic sewage sludge Pathways
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  • 1Baath E,1989.Effects of heavy metals in soil on microbial processes and populations[J].Water Air Soil Pollut,47:335-379.
  • 2Berg B,Ekbohm G,Staaf H et al.,1991.Reduction of decomposition rates of Scots pine needle litter due to heavy-metal pollution[J].Water Air Soil Pollut,59:165-177.
  • 3Chander K,Brookes P C,Harding S A,1995.Microbial biomass dynamics following addition of metal-enriched sewage sluges to a sandy loam soil[J].Soil Biol Biochem,27:1409-1421.
  • 4Filiz B D,Celal F G,1996.Microbiology of activated sludge treating wastewater containing Ni(II) and Cr(VI)[J].Water Science and Technology,34:183-191.
  • 5Friedrich V,Wintzingerode U B,Gobel E S,1997.Determination of microbial diversity in environmental samples:pitfalls of PCR-based rRNA analysis[J].FEMS Microbiol Rev,21:213-229.
  • 6Fritze H,Niini S,Mikkola K et al.,1989.Soil microbial effects of a Cu-Ni smelter in southwestern Finland[J].Biol Fertil Soils,8:87-94.
  • 7Kunito T,Oyaizu H,Matsumoto S et al.,1998.Ecology of soil heavy metal-resistant bacteria and perspective of bioremediation of heavy metal-contaminated soils[J].Recent Res Devel Agric Biol Chem,2:185-206.
  • 8Kunito T,Sacki K,Oyaizu H et al.,1999.Influences of copper forms on the toxicity to microorganisms in soils[J].Ecotoxicol Environ Saf,44:174-181.
  • 9Luca C,Daniele A,Marisa M et al.,2002.An application of PCR-DGGE analysis to profile the yeast population in raw milk[J].Int Dairy J,12:407-411.
  • 10Mette H N,Neils B R,2002.Denaturing gradient gel electrophoresis (DGGE) approaches to study the diversity of ammonia-oxidizing bacteria[J].J Microbiol Methods,50:189-203.

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