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38420174ENVIRONMENTALSCIENCEVol.38No.4Apr.2017SRT-SBR*315211SRTSRT.SRTSBRSRT5、10、20、40d、EPS、PCR-DGGE.SRT5~10dSRTCODEPSEPSEPS5~40dSRTSVISRT>20d、SRT3.SRT.SRT-SBRX703.1A0250-3301201704-1513-07DOI10.13227/j.hjkx.2016071752016-07-262016-11-02LY12E08007/Y201121195/XKl15D2291974~E-mailwenzhoulv@yahoo.com*E-mailliuying1@nbu.edu.cnEffectofSRTonStabilityofYeast-SBRinTreatingOil-containingWastewaterLWen-zhouZHANGShu-linQIAOYu-xiangLIUYing*CollegeofArchitecturalCivilEngineeringandEnvironmentNingboUniversityNingbo315211ChinaAbstractSludgeretentiontimeSRTisacrucialparametertoinfluencethestabilityofbiologicalwastewatertreatmentsystems.EspeciallytheeffectsofSRTonyeast-wastewatertreatmentremainunclear.Inthisstudymixturesofyeaststrainswereappliedtotreatoil-containingwastewaterinsequencingbatchreactorsSBRandtheeffectsofsludgeretentiontimeSRTas5102040dontheremovalefficiencyofpollutantscontentsandcompositionofextracellularpolymericsubstancesEPSyeastcellssettleabilityandyeastcommunitieswereinvestigated.TheresultsshowedthattherecommendedSRTwas5-10dfortheyeast-SBRsystemHigherSRTledtodecreaseofCODremovalrateandcontentofEPSthetightly-boundedEPSwasthemajoronewhichconsistedofpolysaccharides.SRTof5-40dhadnosignificanteffectsontheSVIofyeastcellshoweverlongerSRT>20dresultedintheincreaseofmycelialcellsandatendencytoproducethefilamentousbulking.InthecontinuousoperationofSBRthreeextraneousyeaststrainscapableofutilizingordegradingoilwereidentifiedinthesystemsundertheshortandlongSRT.ToconcludeshorterSRTwasfavorableforthesystemstabilityintreatingoil-containingwastewaterbyyeasts.KeywordssludgeretentiontimeSRTyeast-SBRextracellularpolymericsubstancesEPSmycelialcellssystemstability、、12.SRT、、、34EPS56.EPS7~10.EPSEPS11..SRTEPSEPS.SBRSRTEPS、EPSEPSPCR-DGGE、SRTSRT.11.13O2Candidatropidalis、G1Candidalipolytica、W1Candidahalophila.12.38COD20000mg·L-1.COD6500~8500mg·L-1TN3.4~5.8mg·L-1TP32.4~45.4mg·L-1BOD51950~3200mg·L-11817~2258mg·L-1pH6.5~8.8.1.242LSBR.BOD5NH42SO4、KH2PO4BOD5∶N∶P100∶5∶1.9h3h1/2.pH5.0~5.528℃0.5~1.5mg·L-1.1.310LCOD3000~4000mg·L-1、BOD∶N∶P100∶5∶1pH5.0~5.5.4dCOD7500mg·L-1MLSS5.3g·L-1SBR.MLVSS/MLSS90.93%MLSS4.5g·L-1.SRTSRT5、10、20、40d.SBRSRTSRT=40dSVI13.1.4CODDRB200DR1010CODHACH5000r·min-15minCODOIL480BOD5BODTrakHACHpHHM-30PpHDKK-TOAMLSSMLVSS.TBEPSTBEPSLBEPS2LBEPS.LBEPS148000r·min-110min.0.9%NaCl5min12000r·min-115minLBEPS.TBEPS14LBEPS80℃30min12000r·min-115minTBEPS.-.1.51.5.1DNASBR1.5mL2mL8000r·min-12minFastDNASPINKitforSoilMpbioDNA.DNA-20℃.1.5.2PCR-DGGEPCRGC1-NL15'-GCATATCAATAAGCGGAGGAAAAG-3'LS25'-ATTCCCAAACAACTCGACTC-3'..50μLPCR1μLDNA1μL0.5μL23μLRNAFreewater25μLPremixTakaraTaqVersion2.0plusdye.PCR95℃5min3095℃60s52℃45s72℃60s72℃7min.PCR1.0%.DGGEBio-Rad.8%30%~50%.PCR50μL6×loadingbuffer10μL35μL.60℃、120V6~8h0.01%SYBRBiotium20min25minGelDocXRBio-RadUSA15.1.5.316SrRNADGGEPMD19-TTakara16℃16h-80℃EscherichiacoliDH5αTakara10μL42℃90s1~2minLB890μL37℃170r·min-11h./IPTG/X-GalLB37℃16h.41514SRT-SBR.GenBankhttp//.ncbi.nlm.nih.gov/BLAST/.22.1SRTCODSRTCOD1.SRT20dCOD5dSRT5dCODSRT10d20d.SRTF/MSRT20dSRTSRT=5dSRT.SRT40d30dSRT40d.SRTSRT40dSRT.1SRTCODFig.1EffectofSRTontheCODandoilremovalrate2.2SRTEPSEPS161718.Ravella19EPS.TBEPSLBEPSTBEPS、.EPSEPS70%~80%17.SRTEPS20.SRTLBEPS2LBEPSEPSSRT.-1/θC=Y×Nrs-KdSRT.Batstone21、22EPSSRTSRTF/MEPS23.2SRT5d、10d4~5dLBEPSSRTLBEPS.SRT40d30d241bEPS515138.MatlabSRT5、10、20、40dX1LBEPSX2α=0.000α<0.01SRTLBEPSSRTLBEPS.2SRTLBEPSFig.2EffectofSRToncompositionandcontentofLBEPS3SRTTBEPSFig.3EffectofSRToncompositionandcontentofTBEPS3TBEPS.TBEPS2TBEPSLBEPS1013.TBEPSLBEPSSRT.SRT5、10、20d5dTBEPS.SRT40dTB20dTBEPS.SRT5、10、20、40dX1LBEPSX2α=0.00α<0.05SRTTBEPSSRTTBEPS.2.3SRTSVISRT4SVI4.20dSVISVISRTSRTSVI13.18d30dSVISRT.SRTMLSSSVISV30SRTMLSSSVISRT.30dSRT40dSVISRTEPS2361514SRT-SBRMLSS.SRT20dSVI5SRTFig.5MicroscopyimagesofyeastcellswithdifferentSRTinSBRs.5SRT.SRT5dSRT10、20、40dSRT40d.MatlabSRTSVIα=0.45SRTSVISRTSVI.SRTSRTSRT.2.4SRT5dSRT40dPCR-DGGE6.DGGE3O2、G1、W1315.22d3.10dSRT34SRTSBRSVIFig.4VariationofSVIofyeastcellswithdifferentSRTinSBRs1、2、3SRT40d3.、GenBank1.Candidacylindracea100%2.Candidaintermedia99%3.Yarrowialipolytica99%1.3325~27.SRT40d715138SRTSRT.Candidaalbicans28.SRT.6SRTDGGEFig.6DGGEimageofyeastcommunitywithdifferentSRTinSBRs116SrRNATable1Comparisonofextraneousyeaststrainsby16SrRNAsequences/%1DQ377633100CandidacylindraceastrainVTTC-045292AB27859999Candidaintermedia3EU23937999YarrowialipolyticastrainTJY18b31SRT5~10dCODSRTCOD.2EPSTBEPSEPSSRTEPSSVI.3SRT5~40dSRTSVISRT.4.1JarbouiRBaatiHFetouiFetal.YeastperformanceinwastewatertreatmentcasestudyofRhodotorulamucilaginosaJ.EnvironmentalTechnology2012338951-960.2DavereyAPakshirajanK.Treatmentofdairywastewatercontaininghighamountoffatsandoilsusingayeast-bioreactorsystemunderbatchfed-batchandcontinuousoperationJ.DesalinationandWaterTreatment201657125473-5479.3.J.2015283453-459.TianYDuanLSongYHetal.CharacteristicsofmicrobialcommunitystructureinmembranereactorsunderdifferentsolidretentiontimesJ.ResearchofEnvironmentalSciences2015283453-459.4SilvaAFAntunesSSaundersAetal.Impactofsludgeretentiontimeonthefinecompositionofth
本文标题:SRT对酵母SBR处理油脂废水稳定性的影响吕文洲
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