多级好氧缺氧生物膜反应器脱氮及污泥减量特性王永磊

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39920139JOURNALOFBEIJINGUNIVERSITYOFTECHNOLOGYVol.39No.9Sep.201312111121.1001242.250101ρC/ρN、.3∶4∶3HRT11hρDO4.0mg/L25℃R=1.0.ρTN、ρNH+4-N、ρCOD80~130、75~100、260~400mg/LρTN20mg/LρNH+4-N、ρCOD5.0、30mg/LTN、NH+4-N、COD80%、95%、91%.0.10.X703A0254-0037201309-1405-082012-04-12.510780080040005466120108122005KZ201110005008.1977—E-mailwyl1016@sina.com.1964—E-mailjglijun@bjut.edu.cn.NitrogenRemovalPerformanceandSludgeReductionbyUsingaMulti-aerobic-anoxicBio-filmReactorWANGYong-lei12LIJun1ZHANGXue-song1WANGChang-wen1WANGZhao-zhao1YINMeng-meng21.KeyLaboratoryofBeijingforWaterQualityScienceandWaterEnvironmentRecoveryEngineeringCollegeofArchitectureandCivilEngineeringBeijingUniversityofTechnologyBeijing100124China2.CollegeofEnvironmentalandMunicipalEngineeringShandongJianzhuUniversityJinan250101ChinaAbstractInordertosolveproblemsofinsufficientcarbonsourcesduringbiologicaldenitrificationandtoomuchsurplussludgeinwastewatertreatmentplantamulti-aerobic-anoxicbio-filmreactorwasbuilttotreatlowρC/ρNratiowastewaterinacommunity.Thereactorcouldachieveitsoptimalresultswhenflowdistributionratiowas3∶4∶3HRTwas11hρDOwas4.0mg/Ltemperaturewasat25℃andrefluxratioR=1.0.UnderaboveconditionswhenρTNρNH+4-NandρCODinrawwaterwas80~13075~100and260~400mg/LrespectivelyremovalefficiencyofTNNH+4-NandCODreached80%95%and91%respectivelyρTNineffluentwasabout20mg/LρNH+4-NandρCODineffluentwasdroppedtobelow5.0mg/Land30mg/Lrespectively.Theresultsalsoshowedthatthesludgeproductionratewasonly0.10whichwassuperiortootherbio-filmprocesses.Sotheeffectsludgereductionwassignificant.Keywordsaerobicanoxicbio-filmnitrogenremovalsludgereduction2013COD、ρC/ρN.1-3.、4-5.、6-7--.、、、.、、.ρC/ρN.11.11270cm×20cm×60cmL×B×H240L.1Fig.1Experimentdevice9、O-1、A-1、O-2、A-2、O-3、A-3、O-4、.2∶1、50%、100%.28cm1.5cm0.90.2Fig.2CompositedisplacementballporousQ=15L/h5∶3∶2、4∶2∶4、3.3∶3.3∶3.3、3∶4∶3、2∶3∶5、HRT14h、11h、9h、ρDO2.0、3.0、4.0、5.0mg/L、13℃、25℃、R2.0、1.5、1.01a.1.21ρNH+4-N75~100mg/L90mg/LρTN110mg/LρBOD5/ρCOD0.65ρC/ρN2.5~3.0..1.32.、ρMLSSρCODcr.604191Table1Rawwaterqualitymg·L-1ρCODρBOD5ρNH+4-NρSSρTNρTP260~400125~26575~10090~17080~1304.6~6.52Table2TestitemsandmethodsCODCrTOCJenapHN-1---22.1、、Q=15L/hO-1、A-1、A-2R1=5∶3∶2、R2=4∶2∶4、R3=3.3∶3.3∶3.3、R4=3∶4∶3、R5=2∶3∶5.3R1.R3R4R496.4%ρNH+4-N3.2mg/LR1O-2R4.3ρNH+4-N、ρNO-x-NFig.3VariationofρNH+4-NandρNO-x-NatdifferentinfluentflowratedistributionratiosR52222ρNH+4-N.R2R5.3R1A-1、A-2A-3.2NO-x-NA-3NO-x-N.R2R5A-2A-3.R3R4A-1、A-2NO-x-NρNO-x-N.R3、R4TN.4R4TN78.38%ρTN22.7mg/L.2.2HRT、.9、11、14h.704120134ρTNFig.4RemovalefficiencyofρTNatdifferentinfluentflowratedistributionratios.5HRT14、11、9h96.1%、94.2%、89.5%..5HRTρNH+4-N、ρNO-x-NFig.5VariationofρNH+4-NandρNO-x-NatdifferentHRTρNO-x-N5A-1、A-2ρNO-x-N3mg/LA-1、A-2A-3A-1、A-2ρNO-x-N1A-3A-1、A-2COD3A-3.TN6ρTNTN84.2%、79.3%、64.1%.8-9HRT、.、NO-x-N14h、11hρTN11h.6HRTρTNFig.6VariationofρTNatdifferentHRT2.3ρDO.A/O、.ρDOρDOTN.ρDO10-11.ρDOTN.ρDO2.0、3.0、4.05.0mg/L.ρDOρNH+4-N7ρDO78.4%、84.8%、95.3%、96.4%.ρDOρDOρNH+4-N.ρDO.ρDO4.0mg/L5.0mg/L1.1%ρNH+4-N4.3mg/L3.2mg/L.7ρDO..7ρNO-x-NρDOρDO.804197ρDOρNH+4-N、ρNO-x-NFig.7VariationofρNH+4-NandρNO-x-NatdifferentρDO8ρDOTN65.8%、72.2%、80.2%、76.4%ρDOρDOρDO.8ρDO=4.0mg/LρDO=5.0mg/LTN67.8%ρDO=4.0mg/L71.3%ρDO.ρDO、、.8ρDOTNFig.8RemovalefficiencyofTNatdifferentρDO2.49NH+4-NCOD13℃COD、NH+4-N84.9%、63.8%25℃COD、NH+4-N90.9%、93.2%.NH+4-NCOD.20~30℃15℃5℃12.9ρCOD、ρNH+4-NFig.9RemovalefficiencyofρCODandρNH+4-Natdifferenttemperatures2.5..R=1.0、1.5、2.0.10R=1.0、1.5、2.0COD91.4%、92.9%、93.5%COD.R=1.0、1.5、2.0TN81.8%、75.5%、70.4%11R=1.010ρCODFig.10RemovalefficiencyofρCODatdifferentrefluxratios11ρTNFig.11RemovalefficiencyofρTNatdifferentrefluxratios90412013TN71.3%TN..2.6CODTN3∶4∶3、HRT=11h、ρDO=4.0mg/L、R=1.0ρTNρCOD12ρCODρCOD30mg/LCOD90%.ρTN20mg/LTN80%.ρTNρCODTN.12TN、ρDOρDO、.、、、SNDsimultaneousnitrificationanddenitrification.、.12ρTN、ρCODFig.12VariationofρTNandρCODatoptimalconditions2.7TPρTP4.6~6.5mg/LρTP3.5~5.0mg/L..FeSO435mg/LTP93%ρTP0.45mg/L.2.8.HRT=11h、3∶4∶3、ρDO4.0mg/L、25℃、1.00.100.40~0.551/4~1/5.13-163.3Table3SludgeyieldcomparisonofsimilarprocessesUASB+MBBR0.32SBBR0.17A2/O0.14~0.42SBR0.210.151、、、、、172、、18-20..10×4001419、、、13..13Fig.13Microscopephotographsofmicro-organismsonthecarrier313∶4∶3HRT11hρDO4.0mg/L25℃R=1.0.2ρTN、ρNH+4-N、ρCOD80~130、75~100、260~400mg/LρTN20mg/LρNH+4-N、ρCOD5.0mg/L、30mg/LTN、NH+4-N、COD80%、95%、91%.3、.0.10.1deBABRADRILOCCARRIOLMAHONEYKetal.PracticalconsiderationfordesignofastepfeedbiologicalnutrientremovalsystemJ.FloridaWaterResourcesJournal20024021803-823.2.J.2011327-30.HUIJinWANGBing-songZHANGFeng-jun.StudyonthecarrierascarbonsourceanditsapplicationonthetreatmentoflowC/NwastewaterJ.EnvironmentalProtectionScience2011327-30.inChinese3.J.200935101396-1401.LIJunRENJianYANGXiao-dongetal.Thechemical-aidphosphorusremovalfrommunicipalwastewaterwithlimitedcarbonsourceJ.JournalofBeijingUniversityofTechnology200935101396-1401.inChinese4ROXBURGHRSIEGERRJOHNSONBetal.Sludgeminimizationtechnologies-doingmoretogetlessJ.ProceedingsoftheWaterEnviromentFederation2006111506-525.5.J.2007331050-53.MAJian-liZHAOYou-caiZHANGHuaetal.Researchonmethodsofsludgedisp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