单级好氧除磷工艺与厌氧好氧除磷工艺的对比研究杨帆

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3211201111ENVIRONMENTALSCIENCEVol.32No.11Nov.2011/1313123*131313131341.4100822.5300043.4100824.410015A/O2SBRA/OSBR1SBR2.32SBR91.72%3.23mg·g-1SBR171.70%2.91mg·g-1SBR2.SBR1PHASBR2PHAPHA2SBRSBR22.6mg·L-113.28mg·L-1.SBR1SBR22SBR.A/OSBRX703.1A0250-3301201111-3379-072010-12-192011-05-2851078128CX2009B0791986~E-mailyfqihang@163.com*E-mailxmli@hnu.cnComparisonStudyonPhosphorusRemovalBetweenSingle-stageOxicProcessandAnaerobic/AerobicProcessYANGFan13WANGDong-bo13LIXiao-ming123YANGQi13DENGYing13LUOKun13ZOUZheng-jun13ZENGTian-jing13DENGPin41.CollegeofEnvironmentalScienceandEngineeringHunanUniversityChangsha410082China2.CollegeofEnvironmentGuangxiUniversityNanning530004China3.KeyLaboratoryofEnvironmentalBiologyandPollutionControlHunanUniversityMinistryofEducationChangsha410082China4.ResearchInstituteofHunanNonferrousMetalsChangsha410015ChinaAbstractTocomparetheefficiencyofphosphorusremovalbetweenanaerobic/aerobicprocessSBR1andsingle-stageoxicprocessSBR2twoSBRswereconductedusingacetateasthesolecarbonsourcewhichisthemostextensivesubstrateinmunicipalwastewater.TheresultsobtainedfromthreemonthsexperimentshowedthatthephosphorusremovalefficiencyandtheTPremovedonaunitMLSSwere91.72%3.23mg·g-1SBR1and71.70%2.91mg·g-1SBR2respectivelyduringsteadyoperation.ThefurtherstudyfoundthatasignificantincreaseofPHAassociatedwithandecreaseofglycogeninSBR1whileasignificantsynthesisofPHAincreasedwiththeaccumulationofglycogeninSBR2indicatingglycogenwasnotessentialforthesynthesisofPHAinsingle-stageoxicprocess.FurthermoreobviousphosphorusreleasewasobservedinbothSBRsduringidleperiodbutthecontentofphosphorusreleasedinSBR213.28mg·L-1wassignificantlyhigherthanthatinSBR12.6mg·L-1.ThepossiblereasonforSBR1andSBR2exhibiteddifferentphosphorusremovalefficiencieswasthatmicroorganismsinbothSBRshaddifferentcyclicstorageandconsumptionprocessofenergystoragesduringmetabolicprocess.KeywordsSingle-stageoxicprocessA/OprocesssimulatedmunicipalwastewaterSBRglycogenpoly-phosphate1~4.EBPR5~8310.EBPR/A/O“”PAOs210.A/O.81285%4DOI:10.13227/j.hjkx.2011.11.041321a22a1a.EBPRPAOs、pH235.EBPR..EBPR11121314.2005SBR95.6%19~25.A/OPHA2021.EBPR.A/O.3A/O.11.122LSBRSBR1、SBR2.MLSS4000mg·L-1.2SBR38h..SBR1→2h→4h→2h→SBR2→4h→4h→SBR1SBR2SBR.1L2SBR1.8L.SBR1.2SBR23L·min-1.100mLMSRT18d.1LHRT14h.1.2.2SBR1.26.0.5mL1Table1ComponentsofthesyntheticwastewaterC/mmol·L-1P/mg·L-1/mg·L-1/mg·L-1/mg·L-1/mL1512401050.6.1.3DO27pH27TP27MLVSS27COD27-20~24PHA20~246890N.22.1SBRCOD、VFA、、、pH、DOpHEBPR5.SBR1SBR212SBR.pHA/OPAOs23525pH.SBR1SBR2pH083311/.EBPRpH28.1SBR1SBR240d70dDOpH2.2SBRDOpH.SBR1SBR2pH=7.4±0.08SBR1pH0.257.128.6028.SBR2pH7.378.54SBR1SBR27.897.87.SBR1SBR228DO0≤0.5mg·L-1.SBR1SBR2pHDOA/O.1SBR1SBR240d70dpHDOFig.1ProfilesofpHandDOintwoSBRsduringonecycleofday40andday70experiments2.2SBR1SBR22SBR3.2SBRTPSBR1SBR235d.PAOs12..SBR1SBR22MSRT.SBR1SBR246.2%38.9%25dP81.1%68.1%.26~35d41.3%34.9%.2SBR.2SBR.2SBR91.72%1.06mg·L-1SBR171.70%3.62mg·L-1SBR2.A/OSBR28.38mg·L-1.10mg·L-15mg·L-18.2.3.3A/O1833322SBR1SBR290dTPFig.2RemovalofTPinSBR1andSBR2during90daysoperation.2SBRA/O22SBRSRTA/O2h..A/O“”.EBPR、2SBR1SBR2Table2SummaryofperformanceparametersintwoSBRsduringsteady-stateoperation/%/%/mg·L-1/mg·L-1/%/mg·L-1SBR194.890.01.280.6791.721.06SBR274.668.14.083.271.703.623A/OTable3EconomicalandtechnicalanalysesbetweenA/Oandsingle-stageoxicprocessA/OSBR1SBR2/%91.7271.70HRT/h14142.25mg3.6L30%185A/O.A/O.A/OUCT、DEPHANOXBardenpho.A/O3.Wang2190%..332SBR55~80dMLSSMLVSS/MLSS.MLSS3309mg·L-1SBR13243mg·L-1SBR2.59d2SBR11.5mg·L-18.8mg·L-1MLSS3574mg·L-13024mg·L-1MLSSSBR1P3.23mg·g-1SBR2P2.91mg·g-132SBRMLVSS/MLSSSBR1SBR2SBR1SBR229.SBR1SBR2EBPRA/OPAOsPHAPAOsPHA“”1~3.TCA283311/355~80dMLSSMLVSS/MLSSFig.3ChangesofMLSSandMLVSSinSBR1andSBR2betweenday55andday80experimentPHA16.PAOsTCAPHAPHA“”2324.40d、59d80d2SBRTP、COD、PHA.4559d22.A/OSBR14TP16.02mg·L-190min96.2%90~120mimChen633.30mg·L-1TP49.32mg·L-1PHAC8.7mmol·L-1、C3.52mmol·L-1COD81%.SBR1TP48.87mg·L-1、PHA9.35mmol·L-1、6.15mmol·L-1COD19%.5SBR2TP26.8mg·L-14.5mg·L-122.3mg·L-1PHA5.2mmol·L-17.6mmol·L-1COD60min93%1.7mmol·L-1.A/OPAOs459dSBR1TP、COD、PHAFig.4VariationsofTPCODandsludgeglycogenaswellassludgePHAsduringonecycleinSBR1ofday59experiment559dSBR2TP、COD、PHAFig.5VariationsofTPCODandsludgeglycogenaswellassludgePHAsduringonecycleinSBR2ofday59experimentEBPRPAOsPHA310PHA30%15SBR2PHA.SBR2SBR1A/O.SBR2SBR12PAOsEBPRPAOs38333224.2SBRSBR213.28mg·L-13.32mg·h-1SBR12.6mg·L-11.3mg·h-1.SBR2.45SBR130.SBR2SBR1.SBR2TPSBR1TP.、PHA8.PAOs8.TP.SBR1SBR232SBR.SBR1SBR2A/O90%..EBPR.42SBRA/O.A/OSBR191.72%71.70%.SBR28.60mg·L-1A/O.SBR1SBR22SBR.1YangSYangFLFuZMetal.SimultaneousnitrogenandphosphorusremovalbyanovelsequencingbatchmovingbedmembranebioreactorforwastewatertreatmentJ.JournalofHazardousMaterials20101751-3551-557.2De-BashanLEBashanY.Recentadvancesinremovingphosphorusfromwastewateranditsfutureuseasfertilizer1997-2003J.WaterResearch200438194222-4246.3OehmenALemosPCCarvalhoGetal.AdvancesinenhancedbiologicalphosphorusremovalfrommicrotomacroscaleJ.WaterResearch200741112271-2300.4XieLQXiePLiSXetal.ThelowTNTPratioacauseoraresultofMicrocystisblooms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