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当前位置:首页 > 商业/管理/HR > 质量控制/管理 > 短程硝化反硝化AOOA工艺处理老龄垃圾渗滤液王永庆
AOOA1112111.5100062.510006///AOOADO0.1~0.5mg/L。O1NO-2-N90%NH+4-NTN95%66.5%。0.3~0.5mg/LO1AHRT13.9h。A1O1AOB。O1/O2NO-2-NSND。AOOATU992A1000-4602201821-0018-0720152015B0202350132016201610010069E-mailcexjwang@scut.edu.cnPartialNitrificationandDenitrificationofMatureLandfillLeachateUsingPilot-scaleAnaerobic/Oxic/Oxic/AnaerobicProcessWANGYong-qing1CHENZhen-guo1WANGXiao-jun1JIANLei2CHENJing1CHENXiao-kun11.CollegeofEnvironmentandEnergySouthChinaUniversityofTechnologyGuangzhou510006China2.GuangzhouHualuEnvironmentalTechnologyCo.Ltd.Guangzhou510006ChinaAbstractApilot-scaleanaerobic/oxic/oxic/anaerobicAOOAprocesswasappliedfortreat-mentofmaturelandfillleachateandpartialnitrificationanddenitrificationwasachievedbycontrollingthedissolvedoxygenDOtoalowvalueof0.1-0.5mg/L.Undertheconditionoflowdissolvedoxy-genandsufficientalkalinitythenitriteaccumulationrateinthefirstaerobicreactorO1wasstablya-bove90%andtheremovalrateofammoniumandtotalnitrogenofthewholeprocesswashigherthan95%and66.5%respectivelywhichindicatedthatAOOAprocesscouldeffectivelysolvethedifficultproblemofnitrogenremovalinlandfillleachate.ThelimitingfactorofpartialnitrificationofO1wastheactualhydraulicretentiontimeAHRTandshouldbecontrolledabove13.9hundertheconditionofDOof0.3-0.5mg/L.InthenormaloperationstagethedominantbacteriainthefirstanaerobicreactorA1weredenitrifyingbacteriawhilethedominantbacteriaintheO1wereammonia-oxidizingbacteriaAOB.InadditionnitriteaccumulationwasrealizedinO1/O2andsimultaneouspartialnitrification·81·3421201811CHINAWATER&WASTEWATERVol.34No.21Nov.2018anddenitrificationSNDwasformedtoacertainextent.KeywordsnitrosationshortcutdenitrificationmaturelandfillleachateAOOAprocess。。、1。pH、MLSS、FA、、DOHRT2。pHNOBAOB3。AOBNOB0.3~0.5、0.7~1.8mg/LDO4。AOOA0.1~0.5mg/L、、HRTC/N。、CODAOOA。11.1pH8.78COD、NH+4-N、TN、3144、1425、1512、6684mg/L。1.2AOOA1PVC4720L。1Fig.1FlowchartofAOOAprocessA1A2A12∶1。A2。10L/d。DOA1、O1、O2、A2DO0、0.1~0.5、0.1~0.5、0mg/LO1DO。O1DO0.3~0.5mg/L。24h。1。1AOOATab.1Operationplanofpilot-scaleAOOAprocess/L·d-1/mg·L-1HRT/dO1HRT/hO1DO/mg·L-1Ⅰ60400→6001222.70.1~0.3Ⅱ—————Ⅲ606001222.70.1~0.3Ⅳ60600→15001222.70.1~0.3Ⅴ60728490100110120130012108.687.26.6622.719.116.515.413.912.711.70.3~0.5Ⅰ~Ⅴ1~58、59~69、70~80、81~132、133~188dⅡⅢⅤ7。·91·.watergasheat.comAOOA34211.3CODNH+4-NNO-2-NN-1--NO-3-NTNpHpHs-25DOHACHHQ30dMLSSSV30。22.12。①Ⅰ~Ⅲ≥95%60L/d2∶1400mg/L。②Ⅳ3~4dCOD/TN2.2。Ⅳ。③Ⅴ1300mg/L60L/d120L/dHRT12d6dO10.1~0.3mg/L0.3~0.5mg/L。2Ⅳ、ⅤFig.2DataofinfluentandeffluentqualityofphaseⅣandⅤ2.2AOOA2100L/dHRT7.2dAOOANH+4-N、CODTN92%、74%70%NAR97%。120L/dHRT6d。ⅣA1O1100mg/L480mg/L97%。435mg/LHRT<7.2d174d。0.15kg/dO10.11kg/dDO0.1~0.5mg/LO10.688kgNH+4-N/m3·dNH+4-NNO-2-NNAR90%。174dO1NAR3。100~174dCOD/TN2.2CODTN70%C/N。HRT6.6d175~188dNARTNCOD/TN2.2HRT≥6.6dQ≤110L/d。HRTO1A1。·02·3421.watergasheat.com3NH+4-NAOOAFig.3TreatmentperformanceofAOOAsystemunderdifferenttotalinfluentamountofNH+4-N3O1TN174dO1。174dO1TN。O1A1O1。O1NO-2-NNO-3-N0.15kg/dO1。O1。NH+4-NTN。A2A1A14。4ⅤAOOAFig.4MonitoringdataofeachpartofAOOAprocessinphaseⅤ。4A160%O1。HRTNH+4-N。HRTNO-2-NDO。。NAR97%90%。TNTN60L/dTN73%100L/d。HRT7.2dCOD、NH+4-NTN730、9390mg/L。GB16889—2008。2.3A1NO-2-N215mg/LNO-3-N10.5mg/LA1COD1327mg/L882mg/L。COD/NO-2-N=2.141.53。A1。O1COD224mg/L398mg/LNO-2-N325.6mg/LNO-3-N4.9mg/L1790mg/LCaCO3。O1TNCOD。O2COD、、TNNO-2-NNO-3-N。O2、、、。A2A2COD、、TN、、NO-2-NNO-3-NA2。A2TN。·12·.watergasheat.comAOOA34213A1O1。O1O1SND。。A1NO-2-NCOD。A1NO-2-N174~188d。O1AOBNOBO2NO-2-NDONOB。AHRT、DOpH。3.1O1AHRTO1AHRTNAR、NS、SVI5。5O1AHRTFig.5SludgeindexandeffluentqualityofthefirstoxicreactorunderdifferentAHRTNAR90%NAR。AHRT0.170kgNH+4-N/kgMLVSS·dAHRT≥13.9hO1AHRT≤12.7h。。SVI50~200mL/g。SVIMLVSSSVI5MLVSS。ⅤO1MLVSS4200mg/L。SVI169~214mL/g。5O1O1。6。3.2DOSND。、、O1SND7。O。O1、、COD、NO-2-N、。DO、。DO、SND8。AOOAO1、O2DO0.1~0.5mg/L。OTN10.4%SND。3.3pHpHpH。pH·22·3421.watergasheat.compHpHFA。pH6.0~7.5pH7.0~8.59。O1100mg/LpH7.0~8.5O1FA10mg/L。NOBAOBFAAOB25mg/LNOB1~5mg/L10。AOBNOB。A1pH。O1、O2pH7~7.8AOBO1600mg/LCaCO3。4①AOOAO1、O2DO。②AOOA2∶110L/dO1O2DO0.3~0.5mg/L100L/d1300mg/LCOD3100mg/L。COD、NH+4-NTN730、9390mg/LHRT7.2d。③CODTNA1NH+4-NO1NO-2-N。A1CODTN75%73%O199%95%。④A1O1AOBNO-2-NSND。AHRT、DOpHAOOAO1SND。1ZhangCZhangSZhangLetal.EffectsofconstantpHandunsteadypHatdifferentfreeammoniaconcentra-tionsonshortcutnitrificationforlandfillleachatetreat-mentJ.ApplMicrobiolBiotechnol20159981-7.2.A/OJ.2006265703-709.MaYongWangShuyingZengWeietal.A/Opilot-scalenitrogenremovalprocesstreatingdomesticwastewaterⅠ.Thestudyofshort-cutnitrificationanddenitrificationJ.ActaScientiaeCircumstantiae2006265703-709inChinese.3.UASB-A/OJ.200929101059-1064.SunHongweiPengYongzhenShiXiaoningetal.A-chievingnitrogenremovalfromlandfillleachateviaUASB-A/OprocessJ.ChinaEnvironmentalScience200929101059-1064inChinese.4GuisasolaAJubanyIBaezaJAetal.RespirometricestimationoftheoxygenaffinityconstantsforbiologicalammoniumandnitriteoxidationJ.JChemTechnolBiotechnol2005804388-396.5.A2/O2J.2011371290-93.GaoJianleiZhangXiaojingLiuHanghang.Researchonshort-cutnitrificationanddenitrificationinA2/O2processfortreatmentofnitrogenousfertilizerwastewaterJ.TechnologyofWaterTreatm
本文标题:短程硝化反硝化AOOA工艺处理老龄垃圾渗滤液王永庆
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