采用ASBR快速培养颗粒污泥及其菌群分析邵享文

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ASBR350108ASBR、ASBR。ASBR。VFA93mg/L54mg/LCa2+EPS3。80dCOD150d0.5~4.0mm15.0~38.5m/h。MLSS7.8g/LCOD97%~99%。TU992A1000-4602201819-0030-07510080802015J01199RapidGranulationofSludgeinAnaerobicSequencingBatchReactorStrategyMechanismandPopulationStructureSHAOXiang-wenZHANGTing-tingAICui-lingLIUDa-xinCHENQi-youCollegeofCivilEngineeringFuzhouUniversityFuzhou350108ChinaAbstractAnaerobicsequencingbatchreactorASBRhasreceivedmuchattentionduetoitslowinvestmentsimpleoperationandflexiblecontrol.Howevertheproblemssuchasthedifficultytoformgranuleslimititsapplication.ThereforerapidcultureofanaerobicgranularsludgewasinvestigatedinASBRfedwithglucose.ToenhancethegrowthofgranularsludgeASBRwasoperatedwithlongfeedingtimeandCa2+wasdosed.TheresultsshowedthatprolongingthefeedingtimeanddosingCa2+couldac-celeratetheformationofanaerobicgranulesinASBR.MeanwhileextensionoffeedingtimecouldreducetheaccumulationofVFAanddecreasetheconcentrationofaceticacid.Thepeakconcentrationofaceticaciddecreasedfrom93mg/Lto54mg/LinacyclethusboostedthegrowthofMethanosaetawhichwasinfavorofthegranulationofsludge.AddingsomeamountofCa2+couldpromotethebacteriacellstose-cretemorePNandPSinEPSinwhichthecontentsofPNandPSwerenearlytripledandobviouslyplayedanimportantroleforthestructureandmaintenanceofgranules.After80daysofoperationgran-uleswithfilamentousmicroorganismswerethedominantformofmicrobialaggregatesinthereactor.Fur-therthefeedingtimewasdecreasedfrom120minto30minandinfluentCODgraduallyincreasedwithgradientresultingintheformationofsphericalbacteriamaturedinthegranularsludgein150dayswith·03·3419201810CHINAWATER&WASTEWATERVol.34No.19Oct.2018adiameterfrom0.5-4.0mmandsettlingrateof15.0-38.5m/h.TheMLSSwas7.8g/LinreactorandtheremovalefficiencyofCODreached97%-99%.KeywordsASBRgranularsludgefeedingtimeaceticacidEPSASBR1SSVSS2~4。2090Dague300d1mm5VFA6。UASB7、EGSB8150d、。910、、、。ASBR。EPS。1112~14。EPS、、、。ASBREPSASBRASBR。11.1ASBR4.5L150mm375mm33±1℃5min30s50r/min。1.2COD∶N∶P=300∶5∶1。1500mg/LCaCO3。NaCl120mg/LMgCl2·6H2O49mg/LNa2SO443mg/LFeSO4·7H2O5.53mg/LMnCl2·4H2O2.02mg/LZnCl20.67mg/LNiCl2·6H2O0.65mg/LCaCl2·H2O0.59mg/LCoCl2·6H2O0.48mg/LCuCl2·6H2O0.16mg/LH3BO30.063mg/LNa2MoO4·2H2O0.0045mg/L。1.3。MLSS、MLVSS26.14、19.77g/L2L。1.4、。38h1/3HRT24h。30min、410min、30min、10min。CaCl2COD。30d。31~80d120min、330min、20min、10min100mg/LCaCl2。81~180d30min、400min、40min、10min100mg/LCaCl2。1.5CODpHVFA-3.0、2.5、2.0、1.5、1.0、0.5、0.2mm·13·.watergasheat.comASBR3419、、、1200mg/L2~4gVSS/L33±1℃。22.1ASBR180dCODVFA。12COD、CODVFA。COD1000mg/L21000mg/L30dCOD3000mg/LCOD85%VFA265mg/LpH6.8SS100mg/LASBR。进水COD出水COD去除率80007000600050004000300020001000COD/(mg·L-1)0180t/d160140120100806040201009080706050403020100去除率/%1CODFig.1VariationofCODandCODremovalwithtime40035030025020015010050出水VFA/(mg·L-1)0180t/d160140120100806040202VFAFig.2VariationofVFAineffluentwithtimeSS750mg/LCOD2500mg/L。COD500mg/LCOD90%VFA100mg/L。2.22.2.13VFA。700600500400300200100VFA/(mg·L-1)012345678t/h启动阶段形成阶段成熟阶段a.试验组VFA700600500400300200100VFA/(mg·L-1)012345678t/h启动阶段形成阶段成熟阶段b.对照组VFA16014012010080604020乙酸/(mg·L-1)012345678t/h启动阶段形成阶段成熟阶段c.试验组乙酸16014012010080604020乙酸/(mg·L-1)012345678t/h启动阶段形成阶段成熟阶段d.对照组乙酸3VFAFig.3VariationofVFAandaceticacidinacycleatdifferentstagesVFA·23·3419.watergasheat.com。VFA30min120minVFA445mg/L218mg/L93mg/L54mg/L。4。30min20min。a.形成阶段颗粒污泥外表面b.形成阶段颗粒污泥内部c.成熟阶段颗粒污泥外表面d.成熟阶段颗粒污泥内部4Fig.4SEMphotographsofsludgeatdifferentstages80d30minVFA0.5h645mg/L140mg/L。。20min40min。150dVFA。。180d>0.5mm80%COD6500mg/LCOD95%。。MethanosaetaMethano-sarcina。MethanosarcinaMethanosaeta1516。MethanosaetaMethanosarcinaMonodS*70mg/L70mg/LMethanosaetaMethanosarcina。VFAMethanosaeta。120min30min2.3hMethano-sarcinaMethanosarcina。MethanosarcinaMethanosaeta17。2.2.2EPSCa2+EPSEPS。EPS5。PNPS100mg/LCa2+EPSPS6.13mg/gMLSS24.14mg/gMLSSCa2+PN11.02mg/gMLSS39.83mg/gMLSS。0.5~1.5mm1.5mm15%6。PNPS1.5mm。PNPS。EPS·33·.watergasheat.comASBR341918。6050403020100EPS含量/(mg·g-1MLSS)启动形成成熟启动形成成熟蛋白质多糖试验组对照组5EPSFig.5VariationofEPSduringgranulationprocess65d95d125d155d180d50403020100分布比例/%粒径/mm0.2~0.50.5~11~1.51.5~22~2.52.5~46Fig.6SizedistributionofgranulesduringprocessofgranulationEPSPNPN。19EPS。Ca2+EPSZeta20。2.32.3.1。665d50%0.2~0.5mm155d0.5~1.5mm52%1.5~2.5mm23%4.0mm。、。21。2.3.27。<1.5mm>1.5mm38.5m/h。。Schmidt22。45403530252015/(m·h-1)0.5/mm01.01.52.02.57Fig.7Variationofsettlingrateofgranularsludge2.3.38。1.61.41.21.00.80.60.40.20/(gCOD·g-1VSS·d-1)3040128150t/d8Fig.8VariationofspecificmethanogenicactivitiesSMAduringexperiment·43·3419.watergasheat.com40d、、0.122、0.641、0.3710.142gCOD/gVSS·d。150d0.723、0.973、0.8240.635gCOD/gVSS·d。2.4、EPS。、。Methanosaeta、、。。Ca2+EPSEPSEPS。。Metha-nosaetaMethanosarcina。EPSPN。EPS。3ASBR180d30d、COD。1TauseefSMAbbasiTAbbasiSA.Energyrecoveryfromwastewaterswithhigh-rateanaerobicdigestersJ.Renewable&SustainableEnergyReviews2013191704-741.2MasséDIMasseLVervilleAetal.Thestart-upofanaerobicsequencingbatchreactorsat20℃and25℃forthetreatmentofslaughterhousewastewaterJ.Jour-nalofChemicalTechnology&Biotechnology2010764393-400.3IntanooPSuttikulTLeethochawalitMetal.Hydrogenproductionfromalcoholwastewaterwit

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