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117Vol.11No.720177ChineseJournalofEnvironmentalEngineeringJuly20172016-05-272016-07-081992—。E-maila5130751@126.com*E-mailchenlj@tsinghua.edu.cnAnMBR/A/OMBR1112*1.1000842.314006//AnMBR/A/OMBR。OMBRpHNH3-N。An-MBR/A/OMBRHRT61.3hTP2.3±0.3mg·L-1OMBRpH7.5±0.2、DO4~6mg·L-12∶1。COD、TOC、NH3-NTN1790±17mg·L-1、447.3±9.1mg·L-1、107.3±5.2mg·L-1221.9±5.6mg·L-1254±76mg·L-1、53.8±3.2mg·L-1、3.9±1.1mg·L-170.0±8.8mg·L-185.7±0.9%、88.0±0.7%、96.4±1.1%68.5±3.7%。Ⅰ、ⅡⅣ88.5%Ⅱ40%。AnMBR/A/OMBRX703.1A1673-9108201707-4043-08DOI10.12030/j.cjee.201605225OperatingconditionsoptimizationandcharacteristicsstudyofanAnMBR/A/OMBRProcessforcokingwastewatertreatmentZHUJiadi1LIFeifei1CHENLyujun12*1.SchoolofEnvironmentTsinghuaUniversityBeijing100084China2.ZhejiangProvincialKeyLaboratoryofWaterScienceandTechnologyZhejiangJiaxing314006ChinaAbstractAlaboratoryscaleanaerobicmembranebioreactor/anoxic/aerobicmembranebioreactorAnMBR/A/OMBRwasdevelopedandtheoperatingconditionsoptimizedfortreatmentofcokingwastewater.Itsperform-anceunderoptimumoperatingconditionswasinvestigated.Theresultsindicatedthattheadditionofaphosphorussourceintheinfluentcouldmeetthegrowthneedofmicroorganismsandpromotethedenitrificationprocess.ThecontrolofpHintheOMBRensuredsteadyammonia-nitrogenremovalintheAnMBR/A/OMBRsystem.ThebestperformancewasobtainedattotalHRT61.3hinfluentTP2.3±0.3mg·L-1pH7.5±0.2andDO4—6mg·L-1ofOMBRwithrefluxratio2∶1.UndertheseoperatingconditionsandwiththeinfluentconditionsofCOD1790±17mg·L-1TOC447.3±9.1mg·L-1NH3-N107.3±5.2mg·L-1andTN221.9±5.6mg·L-1theeffluentCODTOCNH3-NandTNwere254±76mg·L-153.8±3.2mg·L-13.9±1.1mg·L-1and70.0±8.8mg·L-1.Theremovalrateswere85.7±0.9%88.0±0.7%96.4±1.1%and68.5±3.7%respectively.ThetotalproportionofRegionⅠandⅡaro-maticproteinanaloguesandRegionⅣsolublemicrobialby-productsintheinfluentwas88.5%.ThecontentofRegionⅡaromaticproteinanalogueswashighestintheAnMBR/A/OMBRsystemeffluentandaccountedfor40%.KeywordscokingwastewateranaerobicmembranebioreactorAnMBR/A/OMBRprocessoperatingcharacteris-tic11。、。A/O2、A2/O、A/O。membranebioreactorMBR1-3。4-5COD。、、、、6、。。anaerobicmembranebioreactorAnMBR7-10、11-12、13-1415。//AnMBR/A/OMBRAnMBR/A/OMBR。11.1AnMBR/A/OMBRAnMBRV=4.9L、AV=4.5LOMBRV=9L1。。AnMBR、37℃AOMBR。PVDF0.02μm3.24L·m2·h-1OMBR。AnMBRAnMBR。AnMBRAOMBR。OMBR2∶1A。1.2、1。pH3~4NaOHpH7.0~8.0。。AnMBR3。AnMBR、AOMBRMLSS15、104g·L-1。1Table1EffluentqualityofcokingplantregulationpoolCODTOCTNTPpH1927~1683522~50792~73226~218<0.39.5~9.0pHmg·L-1。44047AnMBR/A/OMBR1AnMBR/A/OMBRFig.1SchematicdiagramofAnMBR/A/OMBRsystem1.3AnMBR/A/OMBRAnMBR、3。AnMBR94d95~320dHRT、TPpH。AnMBR、AOMBRDO0.01~0.2、0.1~0.54.0~6.0mg·L-1AnMBR37℃25~33℃。OMBRpHNa2CO3。。。、10%NaClO3。。AnMBR/A/OMBRCOD16HachDR890USANH3-N17TN-17。TOCTOCShimadzuTOV-VCPHJapan。HitachiF-7000。2Fig.2Pollutantsremovalperformanceduringstart-upperiod22.1AnMBR/A/OMBRAnMBRAnMBR、95d160d。2。AnMBRCODCODTOC。NH3-NTN。95dAnMBRHRT49hCODTOC1482mg·L-1、1106mg·L-1330.2mg·L-1、240.9mg·L-120.3%26.5%。AnMBR。AnMBRNH3-NTN。160dAnMBR/A/OMBRHRT184h。10dCODTOC。2.2COD、NH3-NTNHRT、TPpH540411。3HRTFig.3EffectoftotalHRTonorganicpollutantsremoval2.2.1HRTHRT122.7、92、80、73.6、61.352.5hHRTHRT34。3HRTCODAnMBR/A/OMBRCODHRT。HRT122.792hCOD242238mg·L-187.3%87.0%。HRT83h52.6hCOD224mg·L-1267mg·L-187.8%85.7%。4AnMBRHRT。HRT122h61.3hAnMBRHRT32.7h16.3hOLR0.1980.013kgCOD·kgMLSS·d-10.4580.032kgCOD·kgMLSS·d-1。4HRTFig.4EffectofsingleHRTonOLRandsludgeloadingofeachprocessinguniHRT52.6hAnMBRHRT14hOLR。AOMBROLRHRT。HRTHRT。HRT。An-MBRHRT61.3hAnMBR、A、OMBRHRT64047AnMBR/A/OMBR16.3、1530h。5TPpHFig.5EffectofTPandpHonnitrogenremoval2.2.2TPTP5。TP8mg·L-1OMBRNH3-NTN。TP2mg·L-1NH3-NTN。250TP2mg·L-1320NH3-NTN。TP0.5mg·L-1。6AnMBR/A/OMBRFig.6MainpollutantsremovalduringstableoperatingperiodofAnMBR/A/OMBRsystem2.2.3pHOMBR。ZHAO18A2/O-MBRMBRpH7.0~7.2NH3-N0.8±0.9mg·L-199.4±0.3%。19A1/A2/ZB-MBRMBRpH7.0~8.5MBRNH3-N5.6±4.1mg·L-1。OMBRpHpH5。300OMBRpH7.3TNNH3-N。pH≈7.5320。335OMBRpH7.7。pH≈7.5345。NH3-NpHpHpHNH3-N>95%。MBRpH7.5±0.2NH3-NTN。AnMBR/A/OMBRCOD、NH3-NTNHRT61.3hTP2.3±0.3mg·L-1OMBRpH7.5±0.2。2.32.3.1AnMBR/A/OMBR80dCOD、TOC、NH3-NTN6。7404116COD、TOC、NH3-NTN1790±17mg·L-1、447.3±9.1mg·L-1、107.3±5.2mg·L-1221.9±5.6mg·L-1254±76mg·L-1、53.8±3.2mg·L-1、3.9±1.1mg·L-170.0±8.8mg·L-185.7±0.9%、88.0±0.7%、96.4±1.1%68.5±3.7%。《》GB16171-2012。AnMBR/A/OMBR2。AnMBR15.3±1.7g·L-1CODTOC15%17%。AnMBRNH3-NAnMBRNH3-N。50%。OMBRNH3-N40%。2AnMBR/A/OMBRTable2ContributionofeachstagetopollutantremovalinAnMBR/A/OMBRsystem/%CODTOCNH3-NTNAnMBR15.2±4.517.4±3.1-9.2±4.51.0±2.7A53.4±4.951.0±2.564.5±5.557.0±4.2OMBR17.2±2.619.6±1.941.1±3.711.4±4.185.7±0.988.0±0.796.4±1.168.5±3.72.3.272000。CHEN205Ⅰ~Ⅴ、、、。7Ⅰ、Ⅱ、Ⅳ21-22。7Fig.7ThreeDimensionFluorescencespectraofeachstageeffluent3。AnMBR585615%CODΣFICOD。AOMBROMBRΣFI。OMBRⅠ、Ⅳ17%21%Ⅱ57.5%OMBR。TOC8。Ⅰ、ⅡⅣ88.5%Ⅱ40%Ⅱ84047AnMBR/A/OMBR23。3Table3FluorescencepeaksandintensitychangeofeachstageeffluentAnMBRAOMBR58568385Ex/EmFIEx/EmFIEx/EmFIEx/EmFI220/2953497220/2952842220/3051013220/295596.1230/3603020230/3502597230/3501951230/3501736270/2956524270/2955617270/2951863270/2951367∑FI40751431244668234092Ex/Em/nm/nmFIAU。8Fig.8Relativecontentandabsolutecontentofdissolvedorganicmatter
本文标题:OMBR处理焦化废水的运行条件优化与运行效果
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