不同污泥负荷下SBR处理游泳馆污水的微生物群落的演变赵双红

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811Vol.8No.11201411ChineseJournalofEnvironmentalEngineeringNov.2014SBR11*2111.3000722.300221。SBR-PCR-DGGESBR。MBRSBRSBR、γ-。。16SrDNAPCR-DGGEX703A1673-9108201411-4813-07SuccessionofmicrobialcommunityinSBRtreatingnatatoriumwastewaterunderdifferentsludgeloadingshocksZhaoShuanghong1SunBaosheng1YuFengqing2ZhangXiaoxue1QiGengshen11.SchoolofEnvironmentalScienceandTechnologyTianjinUniversityTianjin300072China2.TianjinCaringTechnologyDevelopmentCo.Ltd.Tianjin300221ChinaAbstractSludgeloadingcouldaffectthegrowthpatternofmicroorganismdirectlywhenthesludgeload-ingchangedmicrobialcommunitystructurewouldchangeobviouslyinashortperiodoftime.Inordertoinvesti-gatetheeffectsofsludgeloadingshockonmicrobialcommunityconstructureinSBRactivatedsludgePCR-dena-turinggradientgelelectrophoresisPCR-DGGEwasusedtoanalyzethemicrobialcommunitystructureofaSBRtreatingnatatoriumwastewaterunderthedifferentshocksofsludgeloading.TheresultsindicatedthatmicrobialcommunitystructurehadobvioussuccessioninSBRtreatingnatatoriumwastewatercultivatedofMBRunderthedifferentshocksofsludgeloading.Thediversityindexincreasedandtendedtostabilizewiththesludgeloadingshockincreasingbutthediversityindexdropedundertheexcessivesludgeloading.ThedominantbacteriainSBRsludgewereunculturedbacteriumEnterobacteriaceaeTolumonassp.andGammaproteobacteriumbacteri-aect.Duetotheself-modulationofthemicroorganismstheactivatedsludgeformsthecommunitystructurewhichadaptstothedifferentsludgeloads.Keywordssludgeloadingshock16SrDNAPCR-DGGEactivatedsludgemicrobialcommunitystruc-ture2013-10-222013-11-291990—。E-mailzhaoshuanghong927@126.com*E-mailbaosheng_sun@sina.com。。、1。Ns-2。NS。8。。。PCR-DGGEDNARNA3456。PCR-DGGEMBRSBRSBR。。11.1SBR1112mm、106mm、500mm400mm4L。6∶4。。。MBR25d。1Fig.1SchematicdiagramoftheprocessCODBOD。、、。7。Ns0.2~0.5kgBOD5/kgMLSS·dNs0.05~0.15kgBOD5/kgMLSS·dNs0.03~0.08kgBOD5/kgMLSS·dNs1.5~3kgBOD5/kgMLSS·d871。2dPCR-DGGE。1Table1OperationconditionsMLSS-CODmg/LkgCOD/kgMLSS·dmg/L/hNS1NS22506~18571860~21390.02~0.030.10~0.2338~39287~2948844NS3Ns42254~29183106~45970.37~0.480.55~0.73481~497762~8536422NS5NS6NS75132~58732160~30472072~30891.08~1.381.45~1.841.91~2.561585~1681885~985885~985332111418411SBR1.2DNA1.2.110mL8mL3000×g4min。14min。DNA。1.2.2DNADNA-\\-9。1.3PCR16SrDNAV3F357-GC5'-CGCCCGC-CGCGCCCCGCGCCCGGCCCGCCGCCCCCGCCCCCCTACGGGAGGCAGCAG-3'R5185'-ATTACCGCG-GCTGCTGG-3'“GC”240bp10。PCRPCR94℃5min2094℃1min65~55℃1min72℃1min0.5℃1094℃1min55℃1min72℃1min72℃8min11。50μL10~100ngDNA25μL2×TaqPCRMasterMix1μL25μmol/LF357-GC1μL25μmol/LR51850μL。1.416SrDNADGGEC.B.S.SCIENTIFICDGGE-2001PCR1213。1.5DGGE1.5mL50μL60~100℃20min4℃DNA。5000r/min5min6μLPCR。PCR1.5%PCRDNA。1.6DGGEBio-RadQuantityOne4.26DGGE。Shannon-Wiener。Cs。DGGE。HH=-∑si=1PilogPi=-∑si=1ni/Nlogni/N1Pi=ni/NniiN。Cs=2j/a+b2jABabAB。22.1DGGESBR7PCRDGGE2。2SBR。Ns1、Ns2。Ns3、Ns4。Ns5、Ns6Ns7。2SBRUnculturedbacteri-um14。15。SBR51848γ-Gammaproteobacterium、TolumonasEnterobacteriaceaebacterium。2NsPCRDGGEFig.2DGGEprofileofbacteriaunderdifferentsludgeloadingshocksSBRBanda、b、c、e。BandaEnterobacteriaceaebacterium16Enter-obactercloscae17。BandeTolumonas。216SrDNATable2SequencinganalysisofpartofmicrobialcommunityofdominantbacteriaNCBIaAB714459DHL-1399%bGU738449F1Q32TO03DCNL0100%cGU905013SINI91197%dJN125355FJ790139MBfR_Br-195%γ-S14-196%eJF808898R15-1898%fHQ609675AS-11100%gHQ482732Pohang_WWTP_December.2005_395994%hJQ480506Transfer_2C0698%。Bandd、hm。Banddγ-Gammaproteobacteri-umγ-Gammaproteobacterium。。14MBRγ-。Kapley18γ-。proteobacterium。、。BanddAzoarcus19。BandfNs3、Ns4Ns5Ns。618411SBR。BandgNs1Ns4、Ns5、Ns6Ns7。2Ns3、Ns4、Ns5、Ns6Ns7NS。NsNs。2.2QuanlityoneDGGEShannonSBR3。3ShannonFig.3Shannon-wienerindexofsamplesundersludgeloadingshock3Ns1SBR0.57。0.89。。SBR。Ns6Ns7。2.3NS4Ns1Ns1。4Ns6、Ns7Ns150%SBR。Ns1SBR。4Fig.4SimilarityindexofdominantbacteriaundersludgeloadingshockUPGMA5。5。Ns6、Ns7Ns1、Ns2Ns3、Ns5。Ns6、Ns7。Ns1、Ns2、Ns3Ns580%、71848。5DGGEFig.5ClusteranalysisofbacterialDGGEundersludgeloadingshock31SBR。。SBR。2SBR。。733。3SBRγ-GammaproteobacteriumEnterobacteriaceaeSBR。1..2009361023-1028ChenYiSunBaoshengHuangXingetal.Studyofmi-crobialpopulationsuccessioninMBRatdifferentstages.ChineseJournalofEnvironmentalEngineering2009361023-1028inChinese2..20023.PCR-DGGE.2010304729-734MouJieSunBaoshengChenYi.MicrobialcommunitystructureinamembranebioreactordeterminedusingPCR-DGGE.ActaScientiaeCircumstantiae2010304729-734inChinese4..2004106826-830LuLiqongXuYatongLiangJun.Perspectiveofmolecu-larbiologicaltechniquesappliedinmicrobiologicaldiversityandmicrobiologicalecology.ChineseJournalofApplied&EnvironmentalBiology2004106826-830inChi-nese5NambaA.ShigenobuY.KobayashiM.etal.Anewprimerfor16SrDNAanalysisofmicrobialcommunitiesas-sociatedwithPorphyrayezoensis.FisheriesScience2010765873-8786SanzJ.L.KochlingT.MolecularbiologytechniquesusedinwastewatertreatmentAnoverview.ProcessBiochemis-try2007422119-1337FangH.H.P.ChuiH.K.MaximumCODloadingca-pacityinUASBreactorsat37℃.JournalofEnvironmentalEngineering19931191103-1198..20059RosenbergerS.LaabsC.LesjeanB.etal.Impactofcolloidalandsolubleorganicmaterialonmembraneper-formanceinmembranebioreactorsformunicipalwaste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