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38520175ENVIRONMENTALSCIENCEVol.38No.5May2017SCAR1212121212121.2016202.201620SCAR、.HRT6hCOD75%.F420SMAEPSEPSTB-EPS.HRT.SCARX172X703.1A0250-3301201705-2021-09DOI10.13227/j.hjkx.2016090242016-09-042016-10-2413ZR14010001973~E-mailyangbo@dhu.edu.cnAnalysisonPerformanceandMicrobialCommunityDynamicsofaStrengthenCirculationAnaerobicReactorTreatingMunicipalWastewaterYANGBo12XUHui12FENGXiu-ping12LIFang12TIANQing12MAChun-yan121.StateEnvironmentalProtectionEngineeringCenterforPollutionTreatmentandControlinTextileIndustryShanghai201620China2.CollegeofEnvironmentalScienceandEngineeringDonghuaUniversityShanghai201620ChinaAbstractAstrengthencirculationanaerobicreactorSCARtreatingartificialmunicipalwastewaterwasinvestigatedunderdifferentvolumetricloadingrateVLRandthereactorperformancecharacteristicsofgranularsludgeandmicrobialcommunitystructurewerealsotestedinthisexperiment.TheresultsoftheexperimentdemonstratedthatthehydraulicretentiontimeHRTof6hcouldberegardedasthekeyparameterdominatingtheefficientoperationofSCARreactorinwhichconditiontheCODremovalefficiencywasabove75%.ThecoenzymeF420andthemaximumspecificmethanogenicactivitySMAofgranularsludgeincreasedwithincreasingVLRandtheEPScontentsespeciallyTB-EPSinthegranulesludgealsoincreasedobviously.ConsistentlythecharacteristicsofanaerobicgranularsludgeandtheremovalefficiencyofthereactorwereinfluencedbybothsludgeloadingandHRT.Themicrobialcommunitystructureanditsspatialdistributioninthereactorwerealsoaffectedbysludgeloadingwhiletherelativeabundanceofthemicrobialcommunitywithdifferentmetaboliccharacteristicsindifferentspatialpositionschangedwiththeadjustmentofthesludgeloading.KeywordsstrengthencirculationanaerobicreactorSCARmunicipalwastewaterparticlesizedistributionactivityofsludgeEPSmicrobialcommunity1~3.、、4.5.6~8.910.SCAR38Vup.SCAR.HRT、SMAF420EPS.、、.11.1COD450mg·L-128mg·L-1、57mg·L-15mg·L-1mg·L-1111122001003010010305NH4Cl100K2HPO420CaCl25FeSO4·7H2O5.8MgSO4·7H2O6.pHNaHCO3.1.2IC.2.19mmMLSS48.45g·L-1MLVSS/MLSS0.79.28L2/5.1.31.1SCARFig.1SchematicdiagramoftheSCARsystemtreatingmunicipalwastewaterSCAR0.2m2.0m70L.525、60、100、140170cmA、B、C、D、E.30℃±1℃.120d100d20d.Vup4m·h-1HRT451213.22025SCAR1.4COD、MLSS、MLVSS14F42015SMA1216VFASgc789015m×0.53mmFFAPpH<2EPS17-18BCA19..E.Z.N.ATMMag-BindSoilDNAKitOMEGADNA.Qubit2.0DNALifeDNAPCRDNA.16SrDNAV3-V4.PCR341F-805RPCRM-349FGU1ST-1000RPCR349F-806R.PCR.Qubit2.0DNA1∶1.Barcode.97%OTUOTURDP..22.1SCARSCARHRT=15h、0.7kg·m3·d-1.20d20dCOD75%VFAsSCAR.HRTSCAR40.7kg·m3·d-10.89、1.18、1.772.7kg·m3·d-1HRT12、9、64h.2aHRT12、96h1~3dCODCOD.HRTCODCOD75%.HRT4h20dCOD107mg·L-1209mg·L-1COD75.3%50.8%VFAsHRT.HRT12hCOD75%.SCARHRT=6hSCAR.VFAs、HRT20.2bHRTVFAsHRT15、12、96hHRT4hVFAs.HRT21.2bHRTHRT6h.CO2、22.2.2SCAR2.2.1320238aCOD、COD、b2SCARHRTFig.2PerformanceofSCARunderdifferentHRTconditions3SCARHRT3.>1mm90%>2mm60%HRT=12h>1mm80%>2mm47%HRT=6h>1mm81%1~2mm30%44%HRT=4h>1mm86%1~2mm52%<1mm5%.<1mm>2mm1~2mm.Vup.>1mm.42025SCAR3SCARFig.3ParticlessizedistributionandsludgeconcentrationoftheSCARsystemduringtheoperationprocess52.19g·L-110d45.34g·L-1HRT=9h39.29g·L-1.HRT=6h46.15g·L-1.HRT=6hSCAR.2.2.2SMAF420F420SMA1523HRTADF420SMA4.4ADF420SMA.HRTF420SMAHRT6h4hF420F420.4F420Fig.4VariationofspecificmethanogenicactivityandcoenzymeF420ofgranularsludgewithHRT.4DSMAA.2.2.3EPSEPSPS、PN、.EPS24.520238HRTEPSEPSS-EPS、EPSLB-EPS、EPSTB-EPS5.5EPSEPSTB-EPS.HRT=15h3EPSEPSTB-EPS4.48mg·g-1EPS.S-EPS、LB-EPS、TB-EPSEPS.5HRTEPSFig.5EPScontentintheinoculumandgranulesofSCARatdifferentHRTTB-EPS25.TB-EPSHRT=15h4.48mg·g-1HRT=4h10.19mg·g-1.EPSPNPS24~264HRT15、12、96hEPSPN/PS4HRT=4hEPSPN/PSTB-EPSPN/PSHRT=6h4.361.27.HRT=4hLB-EPSHRT=6h2.07mg·g-15.38mg·g-1EPSLB-EPS2526.2.3HRT=12hHRT=6h6、78HRT=12hHRT=6h.6Chloroflexi、Bacteroidetes、Firmicutes、Proteobacteria.Ambuchi27EGSBexpandedgranularsludgebedChloroflexiFirmicutesLiao28EGSBProteobacteria.HRT12h6h6Chloroflexi28.89%16.49%Proteobacteria17.96%26.43%.ChloroflexiChloroflexi29ProteobacteriaChloroflexi.Methanosaetasp.36.2%、Methanolineasp.29.1%、Methanosarcinasp.9.7%、Methanomassiliicoccus4.2%、Methanobacterium4.9%.Methanosaetasp.Methanolinea62025SCARA1HRT=12hAD1HRT=12hDA2HRT=6hAD2HRT=6hD6Fig.6RelativeabundanceofbacterialphylaA1HRT=12hAD1HRT=12hDA2HRT=6hAD2HRT=6hD7Fig.7Relativeabundanceofarchaealgenerasp.50%80%.Chelliapan210.86~1.86kg·m3·d-1.Methanosaeta130~33.HRT=12hMethanosaeta16.08%HRT=6hMethanosaeta75.58%.Siggins34EGSBVFAMethanosaeta.8SCAR80mg·L-1Methanosaeta2m、HRT=12h157202388SCARFig.8VariationsofaceticacidalongtheheightofSCARmg·L-1HRT=6h40mg·L-1Methanosaeta15mg·L-1Methanosaeta.Wang35EGSB10kg·m3·d-1.Methanolinea30Methanosaeta.、364SMAF420.31SCAR4m·h-130℃.SMAF420.HRT=6h、1.77kg·m3·d-1COD75%HRT4hVFAs.21~2mm.EPSTB-EPSEPSPN.3.ChloroflexiProteobacteriaMethanolineasp.Methanosaetasp..1OzgunHGimenezJBErsahinMEetal.ImpactofmembraneadditionforeffluentextractionontheperformanceandsludgecharacteristicsofupflowanaerobicsludgeblanketreactorstreatingmunicipalwastewaterJ.JournalofMembraneScience201547995-104.2HahnMJFigueroaLA.Pilotscaleapplicationofanaerobicbaffledreactorforbiologicallyenhancedprimarytreat
本文标题:SCAR处理城市生活污水的效能及其微生物群落动态分析杨波
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