Microbial diversity in activated sludges of conventional and reversed A2/O processes
LI Peng1,2, BI Xue-jun3, WANG Jun2, RU Shao-guo2
1. Shandong Academy of Environmental Science, Jinan 250013, China;
2. Marine Life Science College, Ocean University of China, Qingdao 266003, China;
3. School of Environmental and Municipal Engineering, Qingdao Technological University, Qingdao 266033, China
To explore the reason why removal efficiency of nitrogen and phosphorus in reversed anoxic-anaerobic-oxic (A2/O) process is higher than that in conventional A2/O process, bacterial community compositions of activated sludges from the two procedures were investigated by PCR-DGGE (polymerase chain reaction-denaturing gradient gel electrophoresis) technique and cultivation method. Betaproteobacteria and Gammaproteobacteria were detected as dominant bacteria in activated sludge from both processes. In the activated sludge of the reversed A2/O process, a large amount of Nitrosospira sp., Rhodocyclus sp., and four uncultured bacteroidetes bacterium were detected by PCR-DGGE technique, while less of these bacteria were found in the conventional A2/O process. Shewanella algae sp., Klebsiella sp., and Rhodobacter sphaeroides of Gammaproteobacteria were separated from the activated sludge of reversed A2/O process by cultivation method, while they were absent from the conventional A2/O process. The diversity of these above-mentioned bacteria species could account for the higher removal efficiency of nitrogen and phosphorus in the reversed A2/O process. Additionally, scanning electron microscopy showed that the activated sludge of reversed A2/O process was relatively loose, with less Filamentous bacteria and no Nostoc.
李鹏, 毕学军, 王军, 汝少国. 常规和倒置A2/O工艺活性污泥微生物群落结构的比较[J]. 中国环境科学, 2017, 37(3): 1137-1145.
LI Peng, BI Xue-jun, WANG Jun, RU Shao-guo. Microbial diversity in activated sludges of conventional and reversed A2/O processes. CHINA ENVIRONMENTAL SCIENCECE, 2017, 37(3): 1137-1145.
Liu C X, Zhang Y, Yang M, et al. Analysis of bacterial community structures in two sewage treatment plants with different sludge properties and treatment performance by nested PCR-DGGE method [J]. Journal of Environmental Sciences, 2007,19(1):60-66.
Zhou J, Bruns M A, Tiedje J M. DNA recovery from soils of diverse composition [J]. Applied and environmental microbiology, 1996,62(2):316-322.
[7]
Bosshard P P, Santini Y, Grüter D, et al. Bacterial diversity and community composition in the chemocline of the meromictic alpine Lake Cadagno as revealed by 16S rDNA analysis [J]. FEMS Microbiology Ecology, 2000,31(2):173-182.
Bourrain M, Achouak W, Urbain V, et al. DNA extraction from activated sludges [J]. Current microbiology, 1999,38(6):315-319.
[11]
Dar S A, Kuenen J G, Muyzer G. Nested PCR-denaturing gradient gel electrophoresis approach to determine the diversity of sulfate-reducing bacteria in complex microbial communities [J]. Applied and environmental microbiology, 2005,71(5):2325-2330.
[12]
Chen Y, Ren C G, Yang B, et al. Priming effects of the endophytic fungus Phomopsis liquidambari on soil mineral N transformations [J]. Microbial ecology, 2013,65(1):161-170.
Buchan L. Possible biological mechanism of phosphorus removal [J]. Water Science and Technology, 1983,15(3/4):87-103.
[16]
Laanbroek H J, Gerards S. Competition for limiting amounts of oxygen between Nitrosomonas europaea and Nitrobacter winogradskyi grown in mixed continuous cultures [J]. Archives of Microbiology, 1993,159(5):453-459.
Hesselmann R P X, Werlen C, Hahn D, et al. Enrichment, phylogenetic analysis and detection of a bacterium that performs enhanced biological phosphate removal in activated sludge [J]. Systematic and Applied Microbiology, 1999,22(3):454-465.
[19]
Bond P L, Keller J, Blackall L L. Characterisation of enhanced biological phosphorus removal activated sludges with dissimilar phosphorus removal performances [J]. Water Science and Technology, 1998,37(4):567-571.
[20]
Zilles J L, Hung C H, Noguera D R. Presence of Rhodocyclus in a full-scale wastewater treatment plant and their participation in enhanced biological phosphorus removal [J]. Water Science and Technology, 2002,46(1/2):123-128.
[21]
Van Houten R, Evenblij H, Keijmel M. Membrane bioreactors hit the big time: ten years of research in The Netherlands [J]. H2O MBR Special, 2001:26-31.
[22]
Guo F, Zhang T. Profiling bulking and foaming bacteria in activated sludge by high throughput sequencing [J]. Water research, 2012,46(8):2772-2782.
[23]
Fuhs G W, Chen M. Microbiological basis of phosphate removal in the activated sludge process for the treatment of wastewater [J]. Microbial Ecology, 1975,2(2):119-138.
[24]
Suresh N, Warburg R, Timmerman M, et al. New strategies for the isolation of microorganisms responsible for phosphate accumulation [J]. Water science and technology, 1985,17(11/12): 99-111.
[25]
Liu P, Liu K, He J. A novel analysis to the ridged cylinder TEM transmission line [J]. International journal of infrared and millimeter waves, 1995,16(6):1083-1090.
[26]
Gieseke A, Arnz P, Amann R, et al. Simultaneous P and N removal in a sequencing batch biofilm reactor: insights from reactor-and microscale investigations [J]. Water Research, 2002, 36(2):501-509.