Author
Listed:
- Jian Tian
(Shenzhen Key Laboratory of Marine Bioresource and Eco-environmental Science, Shenzhen Engineering Laboratory of Marine Algal Biotechnology, College of Life Science, Shenzhen University, Shenzhen 518060, China)
- Jun Lu
(Shenzhen Key Laboratory of Marine Bioresource and Eco-environmental Science, Shenzhen Engineering Laboratory of Marine Algal Biotechnology, College of Life Science, Shenzhen University, Shenzhen 518060, China
Faculty of Health & Environmental Sciences, and Institute of Biomedical Technology, Auckland University of Technology, Auckland 1142, New Zealand)
- Yu Zhang
(Shenzhen Key Laboratory of Marine Bioresource and Eco-environmental Science, Shenzhen Engineering Laboratory of Marine Algal Biotechnology, College of Life Science, Shenzhen University, Shenzhen 518060, China)
- Jian-Cheng Li
(Shenzhen Key Laboratory of Marine Bioresource and Eco-environmental Science, Shenzhen Engineering Laboratory of Marine Algal Biotechnology, College of Life Science, Shenzhen University, Shenzhen 518060, China)
- Li-Chen Sun
(Shenzhen Key Laboratory of Marine Bioresource and Eco-environmental Science, Shenzhen Engineering Laboratory of Marine Algal Biotechnology, College of Life Science, Shenzhen University, Shenzhen 518060, China
Trainee from the Division of Life Science, Sun Yat-Sen University, Guangzhou 510275, China)
- Zhang-Li Hu
(Shenzhen Key Laboratory of Marine Bioresource and Eco-environmental Science, Shenzhen Engineering Laboratory of Marine Algal Biotechnology, College of Life Science, Shenzhen University, Shenzhen 518060, China)
Abstract
Effectiveness of drinking water treatment, in particular pathogen control during the water treatment process, is always a major public health concern. In this investigation, the application of PCR-DGGE technology to the analysis of microbial community structures and dynamics in the drinking water treatment process revealed several dominant microbial populations including: α-Proteobacteria , β-Proteobacteria , γ-Proteobacteria, Bacteroidetes , Actinobacteria Firmicutes and Cyanobacteria . α-Proteobacteria and β-Proteobacteria were the dominant bacteria during the whole process. Bacteroidetes and Firmicutes were the dominant bacteria before and after treatment, respectively. Firmicutes showed season-dependent changes in population dynamics. Importantly, γ-Proteobacteria , which is a class of medically important bacteria, was well controlled by the O 3 /biological activated carbon (BAC) treatment, resulting in improved effluent water bio-safety.
Suggested Citation
Jian Tian & Jun Lu & Yu Zhang & Jian-Cheng Li & Li-Chen Sun & Zhang-Li Hu, 2014.
"Microbial Community Structures and Dynamics in the O 3 /BAC Drinking Water Treatment Process,"
IJERPH, MDPI, vol. 11(6), pages 1-10, June.
Handle:
RePEc:gam:jijerp:v:11:y:2014:i:6:p:6281-6290:d:37100
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Citations
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Cited by:
- Sheng Dong & Lijun Liu & Yuxiu Zhang & Fajun Jiang, 2019.
"Occurrence and Succession of Bacterial Community in O 3 /BAC Process of Drinking Water Treatment,"
IJERPH, MDPI, vol. 16(17), pages 1-12, August.
- Jiancheng Li & Cheng Chen & Jun Lu & Anping Lei & Zhangli Hu, 2016.
"Temporal Patterns in Bacterioplankton Community Composition in Three Reservoirs of Similar Trophic Status in Shenzhen, China,"
IJERPH, MDPI, vol. 13(6), pages 1-14, June.
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