短程硝化厌氧氨氧化组合工艺深度处理垃圾渗滤液吴莉娜

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29420164ResearchofEnvironmentalSciencesVol.29No.4Apr.2016.-J.2016294587-593.WULinaXUYingyingSHIXiaoetal.AdvancedtreatmentoflandfillleachatebycombinedprocessofpartialnitrificationandanaerobicammoniumoxidationJ.ResearchofEnvironmentalSciences2016294587-593.2015-02-052016-01-05512080402013M5413822015J000501978-wlncyj@sina.com.*1949-pyz@bjut.edu.cn-1222314*11.1500902.1026173.1000124.100124、UASB-AO-ANAMMOXR-ANAMMOX1∶10ρCODCr、ρNH4+-NρTN750±30290±10300±10mgL90d.CODCr、NH4+-NTN88%±1%、95%±1%91%±1%67±515±235±5mgLGB16889—2008《》.AOρFAFA0.21~1.38mgLNOBAOBNO2--N70%~96%ANAMMOXRANAMMOXNH4+-NNO2--N.-X7031001-6929201604-0587-07ADOI10.13198j.issn.1001-6929.2016.04.17AdvancedTreatmentofLandfillLeachatebyCombinedProcessofPartialNitrificationandAnaerobicAmmoniumOxidationWULina12XUYingying2SHIXiao2YANGTianxue3PENGYongzhen14*ZHANGJie11.StateKeyLaboratoryofUrbanWaterResourceandEnvironmentSchoolofMunicipalandEnvironmentalEngineeringHarbinInstituteofTechnologyHarbin150090China2.BeijingInstituteofPetrochemicalTechnologyBeijing102617China3.LaboratoryofWaterSystemsEngineeringChineseResearchAcademyofEnvironmentalSciencesBeijing100012China4.KeyLaboratoryofBeijingforWaterQualityScienceandWaterEnvironmentRecoveryEngineeringBeijingUniversityofTechnologyBeijing100124ChinaAbstractInthisstudyanin-linesystemwithacombinedupflowanaerobicsludgebedUASB-anaerobicaerobicAO-anaerobicammoniaoxidationreactorANAMMOXRwasusedfortheadvancedtreatmentofamixtureofmunicipallandfillleachateanddomesticwastewater.Partialnitrification-anaerobicammoniaoxidationwasemployedinthesystemtoachieveadvancednitrogenremoval.Thesystemsolvestheproblemsassociatedwithbiologicaltreatmentoflandfillleachatesuchashightoxicityofleachatetomicroorganismsunsatisfactoryorganicandnitrogenremovalandhighcostofadditionalcarbonsourcesupplemented.Theexperimentwasoperatedfor90dayswithaninfluentofa1∶10mixturevolumeratioofrawleachateanddomesticsewage.ThecorrespondingconcentrationsofρCODCrρNH4+-NandρTNwere750±30290±10and300±10mgLrespectively.TheresultsshowedthatthefinaleffluentsofρCODCrρNH4+-NandρTNwere67±515±2and35±5mgLwithremovalratesof88%±1%95%±1%and91%±1%respectively.Theeffluentqualitycompliedwiththedischargerequirementsofthe29StandardforPollutionControlontheLandfillSitesofMunicipalSolidWasteGB16889-2008.InadditionwhenthefreeammoniaFAconcentrationwas0.21-1.38mgLFAcouldinhibitnitrite-oxidizingbacteriaNOBbutnotammonia-oxidizingbacteriaAOBAOBwasthedominantbacteriaintheAOreactor.Moreoverpartialnitrificationwith70%-96%nitritenitrogenaccumulationratewasachievedintheAOreactorwhichwasfollowedbyANAMMOXRtocompletelyremoveresidualammoniaandnitrite.KeywordslandfillleachatepartialnitrificationanammoxUASBAOreactor、NH4+-N.1-3ρNH4+-N4.GB16889—2008《》TN5.6-10.〔UASBup-flowanaerobicsludgeblanket〕11〔SBRsequencingbatchreactor、、、12-15〕NH4+-NNOx--NTN16-17.NOx--N.40%、25%30%18-20.ANAMMOXanaerobicammoniumoxidation.ANAMMOXANAMMOXNO2--NNH4+-NN212.ANAMMOX、.ANAMMOXNO2--N.2223FA、pHρDO-ANAMMOXCN〔ρCODCrρTN〕.24.UASB-AO-ANAMMOXR-ANAMMOXNH4+-NTN、.11.1UASB+AO+ANAMMOXR1.-ANAMMOXNH4+-NTN.UASBNOx--N.AO.UASBAOAOANAMMOXNH4+-NNO2--N.AOANAMMOXRANAMMOXRANAMMOXNH4+-NNO2--NANAMMOXRANAMMOXNO3--NTN.UASBANAMMOXR8.254.25L.AO15.00L101.1∶101.1.290d4.50LdUASBANAMMOXRHRT1.830.94dAOHRT3.33d.8854-1UASB-AO-ANAMMOXRFig.1FlowdiagramoftheUASB-AO-ANAMMOXRsystem1Table1CharacteristicsofleachateρmgLCODCrNH4+-NTPNOx--NTNCNpH5500±5002900±10012.00±3.0010±53000±1001.8~2.08.00±0.50340±4035±55.00±0.9043±3750±30290±105.63±1.015±1300±102.5~2.67.09±0.20UASB-AO-ANAMMOXR1a.UASB100%AO.UASBANAMMOXR35℃AO20~22℃ρDO0.30~1.00mgLρMLSS3000~4500mgL.raw、u1eUASB、A1AO、O2~O10AO、s1、u2iANAMMOXRu2eANAMMOXR.1.3ρCODCr、ρNH4+-N、ρNO2--NρNO3--N25ρTNTNTOCMultiNC3000ρDOWTWDO330iWTWpH、pHWTWpH340iWTW.PCRANAMMOX26ABI7300Real-TimePCRSystemAppliedBiosystemsCAUSAPCRSYBRGREEN.HSBeta396FHSBeta742RhzsB27-28ARGGHTGGGGHAGYTGGAAGGTYCCHACRTCATGVGTCTG①95℃3min②95℃、30s59℃、30s72℃、30s4028-29.20μLSYBRPremixExTaqTakara10μLROX50Takara0.4μL10mmolL1μL10DNA2μL20μL.GeneJetPlasmidMiniprepKitFermentasMBILithuaniaANAMMOXhzsB.NanoDrop2000ThermoFisherScientificWilmingtonDEUSADNAhzsB10.798529.3.PCR7300SDSSystemANAMMOX.90%~110%0.98DNA.22.1CN2.5~2.6.NO3--NCN4.0NO2--NCN>2.530.31ANAMMOXρTN.32.2rawρCODCr740mgLu1e200mgLUASBρCODCr200mgLAOρCODCr90±10mgL.ANAMMOXρCODCr120mgLANAMMOX33.UASBρCODCr740mgL33UASBANAMMOX1.35×108g-1.AOANAMMOXRρCODCrAOANAMMOXANAMMOX2ANAMMOX109g-1.ρCODCrρNOx--NρNH4+-N2、4NOx--N.ANAMMOXR.2ANAMMOXR、ρCODCrANAMMOXR.ANAMMOXRANAMMOXNH4+-NNO2--NANAMMOX.34———CANONcompletelyautotrophicammoniumremovalovernitriteANAMMOX108g-1ANAMMOX.3ANAMMOX5.43×109g-1ANAMMOX.35ρCODCr120mgLANAMMOX.ANAMMOXANAMMOXRρNH4+-N、ρNO2--NρNO3--N15、155mgLρTN34mgL.2UASB-AO-ANAMMOXRρCODCrFig.2VariationofρCODCrintheUASB-AO-ANAMMOXRsystem1—UASB2—O13—O54—O105—ANAMMOXR.3ANAMMOXFig.3Analysisaboutvariationofthecopynumbersofgeneofanammoxbacteriainthesystem2.2ρNH4+-N290mgLUASBρNH4+-N106mgL.UASBNOx--N.AO.ρDO1mgL.0954-4AOO1ρNH4+-N58mgLO2~O10ρNH4+-N.AOO10ρNH4+-N30mgLρNO2--NρNO3--N351mgLNO2--N96%AON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