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32920129ActaScientiaeCircumstantiaeVol.32No.9Sep.2012No.07JCZDJC02100SupportedbytheNaturalScienceFoundationofTianjinNo.07JCZDJC021001984—E-mailyuyu943@163.com*E-mailBaosheng_sun@sina.comBiographyYUFengqing1984—maleE-mailyuyu943@163.com*CorrespondingauthorE-mailBaosheng_sun@sina.com.2012.MBRJ.3292084-2090YuFQSunBSChenYetal.2012.StudyonbiologicaldiversityoftheMBRactivesludgecultivationprocessJ.ActaScientiaeCircumstantiae3292084-2090MBR11*12111.3000722.3151032011-11-172011-12-142011-12-19MBRConventionalactivatedsludgeCASMBR.DNAPCR-DGGE.CASMBRMBR.MBRPCR-DGGE0253-2468201209-2084-07X703AStudyonbiologicaldiversityoftheMBRactivesludgecultivationprocessYUFengqing1SUNBaosheng1*CHENYi12DUJiang1ZHOUQiangjian11.SchoolofEnvironmentScienceandTechnologyTianjinUniversityTianjin3000722.SinopecNingboEngineeringCompanyLimitedNingbo315103Received17November2011receivedinrevisedform14December2011accepted19December2011AbstractToinvestigatethesuccessionofthestructureofmicrobialcommunityandthemicrobialdiversityofMBRintheentirecultivationprocessthesludgeinthetrainingdomesticatedstageofanMBRreactorwasstudiedbyusingtheconventionalactivatesludgemethod.BasedontheconventionalwastewatersludgeindexestotalbacterialgenomicDNAindifferentstageswasextractedfromtheMBRsludgeandthePCR-DGGEandsimilarityanalysiswereapplied.ItwasshownthatintheprocessofcultivationofCASintheMBRreactorthechangeofdiversityandsuccessionprocedureofbacteriawereobviousandthesimilarityindexofbacteriaineachstageshowedthesuccession.Thecultivationofsludgewasasequencingprocesswhichwasduetotheself-modulationofthemicroorgannismstotheenvironmentchangesindifferentperiodoftimeformingthecommunitystructurethatwasbestfortheMBRprocess.KeywordsMBRsludgedomesticatedPCR-DGGEbiodiversity1Introduction、.———2008..PCR-DGGEWagneretal.2002.MBR、F/MCASDOI:10.13671/j.hjkxxb.2012.09.0299MBRYukietal.2007CASMBR.MBRWitzigetal.20022008a2008.MBR.CASMBRMBR.2Materialsandmethods2.1MBR1.5m3·d-1.MBR5h7h-.MBR360.2μm15L·m-2·h-120∶1.2.2MBRA2/O.MLSS5798mg·L-1SV23%.MBRMLSS650mg·L-1.、NH4Cl、KH2PO4MBRC∶N∶P=100∶5∶1250mg·L-1COD.20d400m3.40dMBR3000mg·L-1600m360d2000m3.MBR1.1MBRTable1ThefeedingwaterqualityoftheMBRofareclaimedwastewatertreatmentplantmg·L-1CODCrNH+4-NTNTPSS260~40020~3520~403~5160~2202.3MBR23d6d110.、、MBR2.CODCr、NH+4-N、SS、MLSSGB11914—89HJ535—2009GB11901—89.2MBRTable2OperationconditionsandtreatmenteffectforvariousstagesofthecultivationanddomesticationprocessesDO/mg·L-1CODCrSSC1C2C33d9d15d4.54.74.520∶1~22∶145%~70%--C4C521d27d3.93.819∶1~21∶160%~80%--C6C733d39d3.23.120∶1~21∶170%~85%--C8C9C1051d57d63d3.02.92.820∶1~23∶189%93%95%90%92%91%93%94%93%5802322.4DNA500mL30min50mL50mL6~10℃、9165g10min30mL10min30mLTE10min15mL5mLDNA.-\\-DNA2008.2.5DNAPCRDNAPCR.16SrRNAV3F357-GCR518240bpMuyzeretal.1993.50μL10~100ng5μL10×PCRbuffer20mmolMgCl210mmol·L-1dNTPs1μL0.5μmol·L-10.5μL2.5U·L-1Taq1μL50μL.PCR94℃5min2094℃1min65~55℃1min72℃1min0.5℃1094℃1min55℃1min72℃1min72℃8min.1.5%.2.6PCRDGGE6%~12%35%55%100%7mol·L-140%30min.10%PCR20μL.1×TAE6.5h150V、60℃.2.7DGGEDGGE16SrDNA1.5mL50μLTE4℃DNA3μLPCR.PCR1.5%.PCRDGGE.2.82.8.1Shannon-WienerQuantityOneV4.25DGGEShannon-Wiener.ShannonHH=-∑Si=1PilogPi=-∑Si=1ni/Nlogni/NPi=ni/NniNS.2.8.2UPGMAMBR10QuantityOneDGGE.3Resultsanddiscussion3.1MLSS、SVIMBR390mg·L-1MLSS、SVI、SVShannon1.1aMLSS350mg·L-1SVI42.1mL·g-126.3mL·g-1.7dMLSS650mg·L-1MLSS24d455mg·L-1SVI..20d24dMLSSSVI27d117.2mL·g-168029MBR.Shannon1bC421d0.91.2010MBR.40d3000mg·L-1.MBRShannon27dCASMBA.50d5000mg·L-1SVI120mL·g-1MBR.1MBRMLSS、SVI、SV、ShannonFig.1ThechangeofMLSSSVISVandShannondiversityindexesatdifferentstagesofthecultivationanddomesticationprocesses3.2253.Bandb、c、d、eBandb、cAeromonasBandd、ePseudomonas4.MBR.Bandm、n、o.BandnComamonasMBR7802322MBRDGGEFig.2DGGEpatternsofdominantbacteriainthecultivationanddomesticationprocesses.Comamonasslime-EPScapsular-EPSBalaetal.2006.ZetaMBR2008a..C1~C42BandA、B、CDGGE.DGGEDNADNA1.5%Muyzeretal19932008a.BandD、F、G.MBRMBR.MBRMBRMBRMBR.MBR“”MBRStamperetal.2003.BandDCitrobacter、MBRMBR.BandFBacillus.、2008b.BandbEC6.MBRF/M.2005EPS.3DGGETable3TheclassificationofthebacteriathroughDGGEpatternsinthecultivationanddomesticationprocessesBandabcdefBandmnoBandABCBandDFGBandbE88029MBRUnculturedbacterium、UnculturedPseudomonas、UnculturedammoniaAmann1995.416SrDNATable4Sequencinganalysisofpartofthemicrobialcommunityofthedominantbacteria/bpNCBIGenbankBanda157FJ973478FJ372598UnculturedbacteriumisolateDGGEgelbandWA1797%Bandb152FJ973479DQ059496Aeromonassp.HPC1379100%Bandc172FJ973480FJ005059Aeromonassp.enrichmentculturecloneGuo599%Bandd158FJ973481FJ755909Pseudomonasputida98%Bande155FJ973482EU909141UnculturedPseudomonassp.Cloneccmr00299%Bandf150FJ973483AB239734Unculturedammonia-oxidizingbacterium97%Bandn150FJ973484FJ824117ComamonastestosteronistrainLMCB01498%Bando157FJ973485AM711886UnculturedPseudomonassp.90%BandD153FJ973486DQ279752Citrobactersp.AzoR-599%BandF146FJ973487FJ820330Bacillussp.VKMK-3698%3C1~C10Fig.3ThesimilarityindexofthedominantbacteriafromC1toC103.3DGGE3C10.3MBRC10C135.6%MBR.MBR.10C1010.MBR.4DGGEFig.4TheClusteranalysisofDGGEpatternsofdominantba
本文标题:MBR活性污泥培养驯化过程中生物多样性研究于凤庆
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