期刊文献+

连续流A/O/A工艺中反硝化聚磷菌的富集及种群跟踪 被引量:2

Enrichment of Denitrifying Phosphate Accumulating Bacteria (DPB) and Population Tracking in the Continuous A/O/A Technology
下载PDF
导出
摘要 [目的]为反硝化除磷工艺的实际应用提供依据。[方法]利用连续流A/O/A工艺富集反硝化聚磷菌,并采用平板计数法和PCR-DGGE法对功能菌群进行跟踪和鉴定。[结果]活性污泥中的反硝化菌、聚磷菌和反硝化聚磷菌分别增加了7.1×102、8.1×104和8.0×105倍;稳定运行时活性污泥中存在3种优势菌种,a菌群与产碱杆菌属的同源性高达96%,为反硝化聚磷菌;b菌群与副球菌属的同源性高达94%,同样为反硝化聚磷菌;c菌群与紫色杆菌属的同源性高达96%,既是一种反硝化菌,也是一种酵解菌。其中副球菌具有反硝化聚磷功能尚未见报道;稳定运行出水指标为:COD47.0mg/L、PO34--P0.2mg/L、NH4+-N2.6mg/L和NO3--N3.5mg/L。[结论]采用先启动膜法硝化池、后启动泥法反硝化除磷池(厌氧和缺氧)的功能菌富集方式是可行的,且A/O/A工艺是可达到《城镇污水处理厂污染物排放标准》(GB18918-2002)一级A标准的要求。 [ Objection] The research aimed to provide the basis for the practical application of the denitrifying phosphorus removal technology. [ Method] The continuous A/O/A technology was used to enrich denitrifying phosphate accumulating bacteria. Plate count and DGGE-PCR methods were adopted to track and identify the functional bacteria. [ Result ] The amount of denitrifying bacteria/phosphate accumulating bacteria and DPB increased 7.1 ×10^2 ,8.1 ×10^4 and 8.0×10^5 times in the activated sludge. Under stable operation conditions there were three types of dominant bacteria in the activated sludge, a had 96% homology with Alcaligenes sp. and was a kind of DPB. b had 94% homology with Paracoccus sp. and also was a kind of DPB. c has 96% homology with Janthinobacterium sp. and was a kind of denitrifying bacteria and glycolysis bacteria. Paracoccus sp. had the function of denitrifying and phosphate accumulating and was first reported. During the stable operation the related indicators of the secondary sedimentation tank were COD 47mg/L, pO3^4- -P 0.2 mg/L, NH4 -N 2.6 mg/L and NO3- -N 3.5 mg/L . [ Conclusion] First start up membrane nitrification tank, then start up denitrifying phosphorus removal tank( anaerobic and anoxic), enrichment approach of functional bacterial is feasible. The A/O/A technology can reach the first standard value(A) of Discharge Standard of Pollutants for Municipal Waste'water Treatment Plant ( GB 18918-2002 ).
出处 《安徽农业科学》 CAS 北大核心 2010年第24期13329-13332,共4页 Journal of Anhui Agricultural Sciences
基金 广东自然科学基金项目(06022869 07003251) 广州市海珠区科技计划项目(2007-Z-023) 广东省教育厅资助项目(LYM08067)
关键词 反硝化聚磷 反硝化聚磷菌(DPB) PCR—DGGE 生物除磷 Denitrifying phosphate accumulating Dcnitrifying phosphate accumulating bacteria PCR-DGGE Biological phosphate removal
  • 相关文献

参考文献13

  • 1刘晖,孙彦富,崔英德,周康群,顾雪婷,陈仪萍.一株短程反硝化除磷菌的鉴定与生物学利用[J].化工学报,2009,60(7):1758-1766. 被引量:18
  • 2周康群,刘晖,孙彦富,王宝娥,周遗品.反硝化聚磷菌的SBR反应器中微生物种群与浓度变化[J].中南大学学报(自然科学版),2008,39(4):705-711. 被引量:19
  • 3张波,高廷耀.生物脱氮除磷工艺厌氧/缺氧环境倒置效应[J].中国给水排水,1997,13(3):7-10. 被引量:82
  • 4罗宁,罗固源,吉方英,张德纯.新型双泥生物反硝化除磷脱氮系统中微生物的组成[J].给水排水,2003,29(8):33-35. 被引量:51
  • 5HU J Y,ONG S L,NG W J,et al.A new method for characterizing denitritying phosphorus removal bacterial by using three different types of electron acceptors[J].Water Research,2003,37(14):3463-3471.
  • 6隋军.反硝化聚磷除磷脱氮新工艺研究[C]//中国环境保护产业协会水污染治理委员会.中国水污染防治技术装备论文集.天津,2005.
  • 7KIRSTEN S J,ANNELI S L P.Polyphosphae accumulation among denitrilying bacteria in activated ludge[J].Anaerobe,1995(1):161-168.
  • 8YEATES C,GILLING M R.Methods for microbial DNA extraction from soil for PCR amplification[J].Biological Procedures Online,1998(1):40-47.
  • 9WACHTMEISTER A,KUBA T,VAN LOOSDRECHT M C M,et al.A sludge characterization for aerobic and denitrifying phosphate removing sludge[J].Wat Res,1997,31(3):471-478.
  • 10MEINHOLD J,FILIPE C D M,DAGGER G T,et a1.Characterization of the denitrifying fraction of phosphate accumulating organisms in biological phosphate removal praeess[J].Wat Sci Tech,1999,39(1):31-42.

二级参考文献49

共引文献165

同被引文献21

  • 1刘新春,吴成强,张昱,杨敏,李红岩.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. 被引量:77
  • 2代文臣,张捍民,肖景霓,杨凤林,张兴文,张新宇.序批式膜生物反应器中反硝化聚磷菌的富集[J].环境科学,2007,28(3):517-521. 被引量:13
  • 3王春丽,马放,王立立,王强.耐低温聚磷菌的研究[J].哈尔滨工业大学学报,2007,39(8):1327-1330. 被引量:8
  • 4Kuba T, van Loosdrecht M C M, Heijnen J J. Phosphorus and nitrogen removal with minimal COD requirement by integration of denitrifying dephosphatation and nitrification in a two-sludge system. Water Research, 1996,30(7) : 1702-1710.
  • 5Muyzer G,Smalla K. Application of denaturing gradient gel e lectrophoresis (DGGE) and temperature gradient gel electro- phoresis (TGGE) in microbial ecology. Antonie van Leeuwen- hoek, 1998,73(1) : 127-141.
  • 6Choi J H,Zee S H,Fukushi K. Comparison of sludge character- istics and PCR DGGE based microbial diversity of nanofiltra- tion and mierofiltration membrane bioreactors. Chemosphere, 2007,67(8) .. 1543- 1550.
  • 7Khemkhao M, Nuntakumjorn B, Techkarnjanaruk S. UASB per formance and microbial adaptation during a transition from me- sophilic to thermophilic treatment of palm oil mill effluent. Jour- nal of Environmental Management,2012,103(30) - 74-82.
  • 8Taheri E, Khiadani M H. Treatment of saline wastewater by a sequencing batch reactor with emphasis on aerobic granule for- mation. Bioresource Technology, 2012,111(5) .. 21-26.
  • 9Jurelevicius D, Elisa K, Renata C, et al. Polyphasic analysis of the bacterial community in the rhizosphere and roots of Cyperus rotundusL, grown in a petroleum- contaminated soil. Journal of Microbiological Biotechnology,2010, 20(5) :862-870.
  • 10赵璐,傅金祥,池福强.NO3^-、NO2^-作为反硝化除磷最终电子受体的研究初探[J].水处理技术,2009,35(5):31-34. 被引量:9

引证文献2

二级引证文献18

相关作者

内容加载中请稍等...

相关机构

内容加载中请稍等...

相关主题

内容加载中请稍等...

浏览历史

内容加载中请稍等...
;
使用帮助 返回顶部