|
|
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 |
|
|
Abstract 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.
|
Received: 22 July 2016
|
|
|
|
|
[1] |
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.
|
[2] |
朱海霞,陈林海,张大伟,等.活性污泥微生物菌群研究方法进展 [J]. 生态学报, 2007,27(1):314-322.
|
[3] |
王振江,武鹏崐,毕学军.倒置A2/O生物脱氮除磷工艺的生产性试验 [J]. 中国给水排水, 2006,22(19):36-38.
|
[4] |
张 波,高迁耀.倒置A2/O工艺的原理与特点研究 [J]. 中国给水排水, 2000,16(7):11-15.
|
[5] |
李亚静,孙力平.常规A2/O工艺和倒置A2/O工艺处理城市污水比较研究 [J]. 环境工程, 2015,33:967-970.
|
[6] |
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.
|
[8] |
杨 倩,蒋阳月,王小军,等.不同区域污水处理厂活性污泥中微生物菌落结构分析 [J]. 化工进展, 2014,33(12):3329-3336.
|
[9] |
葛 峰,郭 坤,周广灿,等.南京市4个污水处理厂的活性污泥中细菌的分离鉴定和抗生素耐药性分析 [J]. 环境科学, 2012,33(5):1646-1651.
|
[10] |
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.
|
[13] |
刘新春,吴成强,张 昱,等. PCR-DGGE法用于活性污泥系统中微生物群落结构变化的解析 [J]. 生态学报, 2005,25(4): 842-847.
|
[14] |
王海燕,周岳溪,蒋进元.强化生物除磷系统的微生物种群及其表征技术 [J]. 微生物学通报, 2005,32(1):118-122.
|
[15] |
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.
|
[17] |
刘惠军,杨凤林,张捍民,等.炭膜曝气生物膜反应器硝化作用及其微生物群落结构分析 [J]. 环境科学, 2007,28(9):2123-2128.
|
[18] |
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.
|
|
|
|