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当前位置:首页 > 商业/管理/HR > 公司方案 > 不同温度对SBBR同步短程硝化反硝化处理炼油催化剂废水的影响周戈
96Vol.9No.620156ChineseJournalofEnvironmentalEngineeringJun.2015SBBR12112*1.1500402.150090SBBR1.0mg/L。SBBRSND。SND40%。33、3028℃90%。pHORPpHORP。SBBRSNDX703A1673-9108201506-2869-06Effectsofdifferenttemperaturesontreatmentofcatalystwastewaterwithsimultaneousshortcutnitrification-denitrificationinasequencingbatchbiofilmreactorZhouGe1ZhaoXiaojing2LiangHong1GaoDawen121.SchoolofForestryNortheastForestryUniversityHarbin150040China2.SchoolofMunicipal&EnvironmentalEngineeringHarbinInstituteofTechnologyHarbin150090ChinaAbstractWestudiedtheeffectsofdifferenttemperaturesonnitrogenremovalofrefinerycrackingcatalystproductionwastewaterinSBBRsystemwithDOat1.0mg/L.TheresultsshowedthatvolumeloadandnitrogenremovalpercentageviasimultaneousnitrificationanddenitrificationSNDwerepositivelyassociatedwiththein-fluentammoniaconcentration.Atdifferentinfluentammoniaconcentrationsthemaximumnitrogenremovalper-centagethroughSNDprocesscouldreach40%.Nitriteaccumulationratecouldbestablyhigherthan90%attemperaturesof3330and28℃.ThetrendsofpHandORPvaluecurvewerealmostidentical.Byadjustingre-actiontimethroughpHandORPonlinecontrolatdifferentinfluentammoniaconcentrationsitcouldachievemaximumguaranteeofstabilityofshortcutnitrificationanddenitrification.KeywordsSBBRshortcutnitrification-denitrificationsimultaneousnitrificationanddenitrificationSNDcrackingcatalystwastewater2014-04-182014-06-181989—。E-mail272457802@qq.com*E-mailgaodw@hit.edu.cn。、12。。、/3。、、3-5。pH、、6-8。SBR。SBBR、。/SND9。SB-BR-9。11.1MLSS9755mg/L、MLVSS6945mg/LVSS/SS0.712。2L3560mg/L。1。1Table1Maincomponentsofcatalystwastewater℃28~35CODmg/L130~210pH6.7~8.0NH+4-Nmg/L60~230mS/cm13~20NO-2-Nmg/L0.2~18Cl-mg/L980~1750NO-3-Nmg/L0.4~31F-mg/L30~85K、Ca、Na、Mg、Si、Sr、Li。1.2SBR400mm190mm8mm11L9L1。。WTWpH/Oxi3430ipH、DOORP。SBRK345%。SBBR、、、。pHORP7h。COD、NH+4-N、NO-2-N、NO-3-N、MLSS、SVI、《》10。30℃、28℃33℃33、3028℃。3、。1SBBRFig.1DiagramofexperimentalequipmentandcontrolsysteminSBBRprocess、。22.12.1.13SBBR2。2SBBRFig.2AmmoniaremovalpercentageofSBBRatdifferenttemperatures260~150mg/L。33℃、85mg/L70%。80~8490mg/L150mg/LSBBR35%。07826SBBR120mg/L。90~11330℃。33℃30℃。3。105~11370mg/L90%。113~13428℃。1~2。。2.1.2SBBR3。3Fig.3Variationofreactionvolumeloadatdifferenttemperatures。33、3028℃SBBR0.178kgNH3-N/m3·d、0.173kgNH3-N/m3·d0.231kgNH3-N/m3·d。2390mg/L30.170kgNH3-N/m3·d120mg/L。2.1.333℃89、30℃11328℃1324。4Fig.4Concentrtionvariationofammonianitriteandnitrateinoneperiodatdifferenttemperatures。433℃114.8mg/L10h。。33、3028℃114.6、68.972.1mg/L。30℃28℃45h。33℃5h114.6mg/L58.6mg/L56mg/L33℃10h22。3140mg/L79.6mg/L、89.4mg/L69.5mg/L、75.9mg/L57.5mg/L42.7%、22.3%24.0%。30℃28℃SND33℃2SND。43。2.2。AOB17829NOB11AOBNOB1213。3SBBR5。5Fig.5Nitriteaccumulationrateatdifferenttemperatures33℃95%。33℃30℃90%SND。。28℃595%。28℃13。2.3。SND1415。SND。6SND。6333、3028℃20%~40%SBBRSND。33℃80~1606SNDFig.6Totalremovalrateofammonianitriteandnitratethroughsimultaneouslynitrificationanddenitrificationatdifferenttemperaturesmg/LSND10%~45%。SND。30℃、28℃SND20%~40%。333℃30℃28℃3SBBR30.3%、26.8%27.3%。2.4。13。16ORPpH、ORP、pH。ORPpHpH、ORPpHORP、17。7pHORP。3pHORP。33、3028℃pH9.114、9.2419.0362hpH0.387、0.7410.333。2.1.33114.6、68.972.1mg/L33℃27826SBBR7ORPpHFig.7VariationcurvesofORPandpHinonereactionperiodatdifferenttemperaturesAOB。730℃28℃pH33℃。3pH“”17SBBR。。7pH30min0pH8.9。3ORP-100mV。。733℃600min、30℃28℃300minORP“”17ORP。4。ORP30minORP。pHORP。312AOB。。2。33、3028℃90%、。SNDSND40%。3pHORP。pHORP。1..201217793-98ShiJiangongLiuZhijianZhangMinhongetal.Ad-vancesintechnologyfortreatingwastewaterfrompetro-chemicalcatalystproduction.Sino-GlobalEnergy201217793-98inChinese2..2008161173-75GaoHuijieLiYuansheng.Bio-treatmentofammonia-con-tainingwastewaterfromcatalystmanufacture.IndustrialCa-talysis2008161173-75inChinese3ZhuGuibingPengYongzhenLiBaikunetal.Biologicalremovalofnitrogenfromwastewater.ReviewsofEnviron-mentalContaminationandToxicology2008192159-1954HellingaC.SchellenA.A.J.C.MulderJ.W.etal.ThesharonprocessAninnovativemethodfornitrogenre-movalfromammonium-richwastewater.WaterScienceandTechnology1998379135-1425..20001611-19ZhouShaoqiZhouJilin.Theadvancesininvestigationof37829newtechnologiesonbiologicalnitrogenremoval.Tech-niquesandEquipmentforEnvironmentalPollutionControl20001611-19inChinese6.pH.200537121664-1666GaoDawenPengYongzhenWangShuying.Nitrogenre-movalfromwastewaterviashortcutnitrification-denitrifica-tionachievedbycontrollingpH.JournalofHarbinInstituteofTechmology200537121664-1666inChinese7./Ⅰ..2004245761-768GaoDawenPengYongzhenWangShuying.Alternatingoxic-anoxicshortcutnitrification-denitrificationI.Realiza-tionandcontrol.ActaScientiaeCircumstantiae2004245761-768inChinese8VanHulleS.W.HVolckeE.I.P.TeruelJ.L.etal.InfluenceoftemperatureandpHonthekineticsoftheSharonnitritationprocess.JournalofChemicalTechnology&Biotechnology2007825471-4809.MBRDO.200117610-14ZouLianpeiZhangLiqiuWangBaozhenetal.EffectofDOonsimultaneousnitrificationanddenitrificationinMBR.ChinaWater&Wastewater200117610-14inChinese10..1989246-28611..2006264561-566LuoHuaiqingHuYongyou.Mathematicalkineticsmodelevaluationoffactorseffectonnitritificationandnitrafica-tionprocess.ActaScientiaeCirc
本文标题:不同温度对SBBR同步短程硝化反硝化处理炼油催化剂废水的影响周戈
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