高浓度氨氮污泥脱滤液的半硝化实验研究徐珊

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58Vol.5No.820118ChineseJournalofEnvironmentalEngineeringAug.201111*11111KenjiFurukawa21.5410042.860-8555。402mg/L、HRT=5.5h、22~31℃、DO<1.0mg/L、pH7.4~8.2NO-2-N/NH3-N1.13~1.321.76kgN/m3·dNO-2-N/NO-x-N100%。X703A1673-9108201108-1768-05StudyofsludgeliquorwithhighconcentrationammoniumviapartialnitrificationprocessXuShan1ChengGuanwen1WeiWenyuan1WeiRongrong1LuoJiejun1LuGuodan1FuHongyuan1KenjiFurukawa21.DepartmentofResourcesandEnvironmentalEngineeringGuilinUniversityofTechnologyGuilin541004China2.GraduateSchoolofScienceandTechnologyKumamotoUniversityKumamoto860-8555JapanAbstractRejectwastewaterwithhighconcentrationsofammoniaandlowC/Nratiopartialnitrificationprocesswasinvestigated.Theexperimentalresultsshowedthatunderthetemperature22~31℃andDO<1.0mg/LtheeffluentratioofnitritetoammoniumofthePNreactorcouldbeadjustedtomeetinfluentsubstratedemandoftheanaerobicammoniumoxidationAnammoxreactorbycontrollinginfluentammoniaconcentration402mg/LpH7.4~8.2andhydraulicretentiontimeHRT=5.5h.Moreoverthenitrogenloadingratewasachieved1.76kgN/m3·dtheeffluentratioofnitritetoammoniumofPNreactorwasmaintained1.13~1.32withnearly100%ofnitriteaccumulationefficiency.Keywordshighconcentrationammoniapartialnitrificationsludgeliquorammoniaoxidizingbacteriaandnitriteoxidizingbacteria200910596R012010-06-222010-07-271985~。E-mailxushan1111@163.com*E-mailchenggw@glite.edu.cnC/N、NH+4-NTN25%1。、、。DelftanaerobicammoniaoxidationAnammoxAnammox1∶1~1∶1.322。Anammox50%。11.11a5.3L、8。。Biofringe1b。100%。、。1Fig.1Partialnitrificationreactorandbiofringecarrier1.2KenjiFurukawa3MLSS800mg/L。。1.3BOD5150.1~200.8mg/LCOD178.1~274.3mg/LNH+4-N428.0~1012.5mg/LSS3.0~6.0mg/LpH8.16~9.37。1.4NH+4-NOPP4NO-2-N5NO-3-N5SS5DOHORIBADOmeterOM-55pHpHB-211HoribaJa-panTOCTOCShimadzuTOC-5050A5LA-920HoribaCo.Ltd.Japan。22.1NH+4-N、C/N、NH+4-NTN25%30℃、DO<1.0mg/L、pH7.4~8.2。50%6。250~280mg/LNO-2-N81mg/LNO-3-N40mg/LAOBNOBNO-2-NNO-3-NNO-3-NNO-2-N26.59%。Anthonisen7FAAOBNOB10~150mg/L0.1~1.0mg/L。FANOBAOB。42L/hAOBNOBNOBAOB。232NO-3-N40mg/L0NO-2-N128mg/L59.26%>50%NO-2-NNO-3-N1.32∶1。2.22.2.1。20℃AOBNOB20℃AOBNOB8。22~31℃3。967152PNFig..2TimecourseofPNperformanceNPR0.1kgN/m3·dAOB30℃400mg/L0.93kgN/m3·d0AOBNOB0。5931.5℃22.1℃976NPR。AOBNOB25~31℃。3Fig.3Effectoftemperatureonnitriteconcentration2.2.2DO42L/hDO<1.0mg/LAOBNOB10NOBNOBAOBAOB“”NOBAOBNOB。2.2.3FAFAAOB、NOBFA0.6mg/LFANO-240mg/L11。4FA3~10mg/LpH7.4~7.9FA10~16mg/LpH7.9~8.1。112FA、pH。FA=1714×NH3×10pHKb/Kw+10pH1FAKbKb=10-9.2420℃KwKw=0.69×10-1420℃Kb/Kw=e6.344/273+T。AOBpH7.4~7.9FA10mg/LNO-2NO-2。4FApHFig.4ChangesinFAandpHduringexperimentalperiod2.2.4HRT18h。pH7.4~8.3DO<1mg/LHRT。5HRT18h14h0.380.6307718NO-2-NNH3-N165mg/L138mg/LNO-2-N/NH3-N1.3NO-3-N0。HRT5.5h1.76NO-2-N/NH3-N1.13NO-3-N0。HRT18h5.5h1.76NO-2-N/NH3-N1.13~1.3NO-3-N0。AOB0。5HRTNLRFig.5ChangesinHRTandNLRduringexperimentalperiod2.3NO-2-N/NO-x-N6。615128mg/LNO-2-N/NO-x-N66.9%95.2%。16~831.3∶1NO-2-N/NO-x-N100%Anammox。6Fig.6Effluentratioofammoniatonitriteduringexperimentalperiod2.4MLSS800mg/LSVI118mL/g。80dMLSS3130mg/LSVI83.2mL/g7180μm280μmPN。100%。7Fig.7Changesofparticlesizeduringexperimentalperiod3130℃、DO<1mg/L、pH7.4~8.223NO-3-N40mg/L0NO-2-N59.26%>50%NH+4∶NO-2≈1∶1~1∶1.32。225~31℃、DO<1mg/L、FA<10mg/L、HRT5.5h1∶1.321.76kgN/m3·dNO-2-N/NO-x-N100%。。3SVI83.2mg/L280μm17715。Biofringe。。1..2006261135-38ZhouQiYangDianhaietal.Short-cutnitrificationanddenitrificationoflowC/Nratiomunicipalwastewaterinapilot-scaleresearch.IndustrialWaterTreatment2006261135-38inChinese2HellingaC.SchellenA.A.J.C.etal.TheSHARONprocessAninnovativemethodfornitrogenremovalfromammonium-richwastewater.WaterScienceandTechnolo-gy1998379135-1423KenjiFurukawa..200935s172-764KandaJ.Determinationofammoniuminseawaterbasedontheindophenolreactionwitho-phenylphenolopp.WaterResearch199529122746-27505AndrewD.E.LenoreS.C.ArnoldE.G.StandardMeth-odsfortheExaminationofWaterandWastewater19thEd.AmericanPublicHealthAssociationWashingtonD.C.19956..200218629-31ZhangYingjieHuYaocheng.WaytocontrolofnitrificationatNitrosificationphase.ChinaWater&Wastewater200218629-31inChinese7AnthonisenA.C.Inhibitionofnitrificationbyammoniaandnitrousacid.JWPCF1976485835-8528HyungseokYoo.Nitrogenremovalfromsyntheticwastewaterbysimultaneousnitrificationanddenitrificationvianitriteinanintermittently-aeratedreactor.WaterRe-search1999331146-1499VanDongenU.JettenM.S.M.VanLoosdrechtM.C.M.etal.TheSHARONR-AnammoxRprocessfortreatmentammoniumrichwastewater.WaterScienceandTechnology2001441153-16010.AOBNOB.20093051430-1436ZengWeiZhangYueLiLeietal.Competitionandopti-mizationofAOBandNOBfordomesticwastewatertreat-mentatnormaltemperatures.EnvironmentalScience20093051430-1436inChinese11.-.20053615-8YongmingLiXiaomingZengGuangmingetal.AstudyofmechanismofSHARON-ANAMMOX.IndustrialWater&Wastewater20053615-8inChinese12SenQiaoNorikoMatsumotoTakehikoShinoharaetal.High-ratepartialnitrificationperformanceofhighammoni-umcontaingwastewaterunderlowtemperatures.Biore-sourceTechnology20101011111-1172771

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