臭氧化处理含溴水时溴酸盐的生成特性

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4212201012JOURNALOFHARBININSTITUTEOFTECHNOLOGYVol.42No.12Dec.20101121111.150090mei18@hit.edu.cn2.450000.10minpH8pH710μg/L.40mg/L10μg/L.TU991A0367-6234201012-1883-04StudyonformationCharacteristicsofbromateinbromidewatertreatmentbyozoneLIUdong-mei1YUming-xue12CUIfu-yi1ZHUqi1ZHAOzhi-wei11.StateKeyLaboratoryofUrbanWaterResourceandEnvironmentHarbinInstituteofTechnologyHarbin150090Chinamei18@hit.edu.cn2.InstituteofCityManagementPlanning&Designco.ltdZhengzhou450000ChinaAbstractTocontroltheformationofbromateinthetreatmentofdrinkingwaterwithbromidebyozonetheinfluencingfactorsonbromateformationwerestudiedindetail.Resultsofpilottestandpilotscaletestshowthatmostofbromatearegeneratedinthefirst10minutesofozonationandwhenpH>8thebromatefor-mationisincreasedevidentlywhenpH<7thebromateformationislimitedunder10μg/L.TheexistenceofNH3-NandNOMcouldinhibitthegenerationofbromate.WhentheconcentrationofNOMgetsto40mg/Ltheamountofbromatewillbeunder10μg/L.Keywordsozonationbromatebromideformation2009-05-25.508080522010TS08E201007.1973—1958—.1.USEPA10μg/L2.2004《》25μg/L10μg/L3.2005CJ/T206-2005《》0.01mg/L4.56.pH7、89、H2O21011、7、12...11.1.10~20min5L3L21.280mm3.5m2.5m20~40μm35.4m3/d1.50m3/h15min.3571015min..0.5m.5.463280791105300200100081—进臭氧管(硅胶管);2—出水龙头;3—有机玻璃柱(外径10cm,内径8cm);4—出臭氧管(硅胶管);5—穿孔布气板;6—盖板(有机玻璃板,要求密封,可开启);7—石英砂粒(粒径约2mm);8—进水弯头(带阀门);9—放空管(带阀门);10—曝气头.11234551—2—3—4—5—21℃NTUpHCODMnmg·L-1TOCmg·L-1ρmg·L-1UV254cm-1ρCaCO3mg·L-13.0~7.00.3~0.57.10~7.454.2~4.63.0~3.50.8~1.00.06856~641.2BrO3-DIONEXDX-30002μg/LTOCTOC-VCPHUV254T6751G.22.1pH3Br-=200μg/L、4mg/L、10min、pH6~9pH.pHO3O3pH.pHpH.pH6.510μg/LpH8.pH7.2pH·4881·42pH.9.08.07.06.05.0臭氧氧化前调节pH臭氧氧化后调节pH有机物含量不同时020406080100120籽(溴酸盐)/(滋g·L-1)pH403020100籽(腐殖酸)/(mg·L-1)Br-=200μg/Lt=10min3pH2.23Br-=200μg/L、4mg/L、10min、pH7.23.20mg/L.20mg/L.2.3Br-=200μg/L、4mg/L、pH7.23410min10min10min.pH7.3Br-=200μg/L、4mg/L40~15min、.6min10μg/L.161412108642020406080100籽(溴酸盐)/(滋g·L-1)小试,不同臭氧氧化时间中试,不同臭氧氧化时间中试,不同溴离子浓度小试,不同溴离子浓度6005004003002001000籽(溴离子)/(滋g·L-1)臭氧氧化时间/min42.410min、4mg/L、pH7.23418.3%.pH7.34mg/L49.8%400μg/L400μg/L400μg/L400μg/L.100μg/L10μg/L.2.5pH5Br-=200μg/L、·5881·124mg/L、10min、pH.1.00.5mg/L.pH..5pH.30252015105NH3-N∶0.5mg/LNH3-N∶1mg/L6.56.97.37.78.18.5pH籽(溴酸盐)/(滋g·L-1)Br-=200μg/Lt=10min531Br-50~500μg/LBrO3-Br-.Br-100μg/LBrO3-10μg/LBr-.2pH5.5~9.0BrO3-pH.pH710μg/LpH8pH8.56.557.83%.310min.4.40mg/L10μg/L.5.1KUROKAWAYMAEKAWAA.CarcinogenicityofpotassiumbromateadministeredorallytoF334ratsJ.JounaloftheNationalCancerInstitute198371965-972.2BONACQUISTITP.Adrinkingwaterutility’sper-spectiveonbromidebromateandozonationJ.Toxicology2006221125-148.3.J.2006166677-678.4.CJ/T206-2005J.2005.5GUNTENvonU.OzonationofdrinkingwaterPartIIDisinfectionandby-productformationinpresenceofbromideiodideorchlorineJ.WaterResearch2003371469-1487.6.J.200829199-103.7SIDDIQUIMSAMYGLRICERG.BromateionformationAcriticalreviewJ.AWWA1995871058-70.8GUNTENvonUHOIGNJ.Bromateformationduringozonationofbromide-contaniningwatersInteractionofozoneandhydroxylradicalreactionsJ.EnvironSciTec19942871234-1235.9SIDDIQUIMSAMYGL.FactorsaffectingDBPfor-amtionduringozone-bromidereactionsJ.AWWA199385163-72.10.J.200018341-45.11WESTERHOFFPSONGRAMYGLetal.NOMsroleinbromideandbromateformationduringozonationJ.AWWA1998891182-94.12.J.20052141-4.·6881·42

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