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811Vol.8No.11201411ChineseJournalofEnvironmentalEngineeringNov.2014MBR、、11*221.1000242.100124、2MBRTHMs。25mJ/cm23mg/L、6mg/L4mg/L2《》GB/T18920-2002。THMs。THMs4mg/LTHMs14.11μg/L37.19%。X703A1673-9108201411-4681-06DisinfectionofMBReffluentsbychlorinationultravioletirradiationozonationandcombinationtechnologiesLiXinwei1LiKuixiao1ZhengXiaoying2WangJianlong21.ResearchandDevelopmentCenterBeijingDrainageGroupCompanyLimitedBeijing100024China2.KeyLaboratoryofBeijingforWaterQualityScienceandWaterEnvironmentRecoveryEngineeringBeijingUniversityofTechnologyBeijing100124ChinaAbstractTheobjectiveofthisworkwastoinvestigatethedisinfectioneffectivenessofseveraltechnolo-giesi.e.chlorinationultravioletUVirradiationozonationandthecombinationchlorinationwithUVirra-diationorozonationontheremovalofindicatormicroorganismsandtheformationoftrihalomethanesTHMsrelatedtoavailablechlorinedosagefromapilot-scaleMBReffluents.Thecombinationtechnologiesexhibitedmuchhigherdisinfectioneffectivenessthanthatofsingleone.ThetotalcoliformofdisinfectedMBReffluentsdis-infectedinbothUV-chlorinationcombinationprocessatanUVdoseof25mJ/cm2andanavailablechlorinedoseof3mg/Landozonation-chlorinationcombinationprocessatanozonedoseof6mg/Landanavailablechlorinedoseof4mg/LcouldmeettherequirementofReuseofUrbanRecyclingWater-WaterQualityastandardforUrbanMiscellaneousWaterConsumptionGB/T18920-2002.TheconcentrationofTHMsincreasedwiththeincreaseofavailablechlorinedosage.IncomparisonwithUV-chlorinationcombinationprocessozona-tion-chlorinationcombinationprocesscouldeffectivelyreducetheTHMformation..TheconcentrationofTHMswas14.11μg/Latanavailabledoseof4mg/Lwhichdecreasedby37.19%comparedwithchlorinationdisin-fection.Keywordschlorineultravioletozonationtrihalomethanes5117824220120953-32013-10-272014-02-281981~。E-maillixinwei@bdc.cn*E-mailkuixiao_li@163.comMBR、1。MBR、。THMs。8、2、3。。THMs、4。5。MBR、2THMsMBR。11.1、1AtlanticMP13AUV1.97L。3.7WUV20mW/cm2D=I·tDmJ/cm2ImW/cm2ts15、20、25、3035mJ/cm2。250L10min8~60g/m3HareEG-600Jit-sugyoD=Q·cDmg/LQm3/hcg/m32、4、6、810mg/L。10%1、2、3、45mg/L。0.5h、。=log10NN。3。1.2MBR20~300.24~0.42NTUUV2540.11~0.13/cmDOC4.85~7.77mg/L22~109×103CFU/mL100~900×103CFU/L100~560×103CFU/L。1.3、。1、Fig.1SchematicdiagramofchlorinationUVandO3disinfectiontestdevice286411MBR、、THMsEPAstandardmethods6232BLLE-GC/MS。HP-5。200℃70eV。He1ml/min。40℃3min10℃/min95℃25℃/min200℃3min。230℃。150℃。EI。SIM∑SIM83、85、87、∑SIM83、85、87、129、47、∑SIM127、129、131、48、79、∑SIM171、173、175THMs。22.1HOClHOCl。2a。5mg/L、3.06×107CFU/L、1.7×105CFU/L4×105CFU/L1800CFU/L、78CFU/L52CFU/L4。5mg/L、50CFU/L。CUV-C254nmDNADNARNADNA。RNA。、。2b35mJ/cm2、1.28×108CFU/L、3.28×105CFU/L2.15×105CFU/L1550CFU/L、271CFU/L80CFU/L534。2、Fig.2RemovalofdifferentchlorineUVandO3dosagealoneonmicroorganismMBR、UVUV6。。2cCOD、NO-2-N、7。6mg/L10mg/L、2.15×107CFU/L、1.48×105CFU/L2×105CFU/L350CFU/38648L、350CFU/L145CFU/L3。、8。MBR、、。、3。2.229。25mJ/cm21、2、34mg/L。10。6mg/L1、2、34mg/L23。32Fig.3Removaloftwokindsofcombinationprocessonmicroorganism3a。、3.8×106CFU/L、5.5×105CFU/L2.2×105CFU/L5050CFU/L、508CFU/L415CFU/L3mg/L、2CFU/L3CFU/L《》GB/T18920-20024mg/L。。。11。3b。。、7.5×106CFU/L、6.1×105CFU/L3.05×105CFU/L5.35×105CFU/L、7600CFU/L6050CFU/L4mg/L、2CFU/L1CFU/L《》B/T18920-2002。。23mg/L、4mg/L2《》GB/T18920-2002。2.3THMsMBRTHMs12。486411MBR、、1314。42THMs。42THMsFig.4InfluenceofdifferentavailablechlorinedosageonformationofTHMsinchlorinealoneandtwokindsofcombinationprocess4aTHMs5mg/LTHMs30.79μg/LTCM23.62μg/LTHMs76.71%THMs15BDCM4.07μg/LDBCM3.10μg/LTBM2μg/LTHMs。4bTHMsTHMs。THMs。7cTHMs。。THMsTHMs。4mg/LTHMs14.11μg/LTHMs37.19%。MBR。DBPs4THMsTCM、DBCM、BDCMTBM60、60、100100μg/L16。2THMs。31、、。2、。25mJ/cm23mg/L、2CFU/L3CFU/L、6mg/L4mg/L、2CFU/L3CFU/L2《》GB/T18920-2002。3THMs5mg/L58648THMs30.79μg/L。THMs4mg/LTHMs14.11μg/LTHMs37.19%。1·.—.2003232196-200MoLiHuangXiaDilibaerS.Operationcharacterofmembranebioreactorintreatingthewaterofmicro-pollutedwatersource.ChinaEnvironmentalScience2003232196-200inChinese2HaiderT.SommerR.KnasmullerS.etal.GenotoxicresponseofAustriangroundwatersamplestreatedunderstandardizedUV254nm-disinfectionconditionsinacombinationofthreedifferentbioassays.WaterResearch200236125-323..2006221746-49ZhangYongjiLiuWenjun.InfluencesofUVDisinfectiononE.coliactivityduringphotoreactivation.ChinaWater&Wastewater2006221746-49inChinese4..2013772414-2418LiFangLuSaoming.Influenceofdifferentdisinfectingmodesondisinfectionefficiencyofoutletwaterfromsandfilter.ChineseJournalofEnvironmentandEngineering2013772414-2418inChinese5..201228782-84GongFeitengLiXinweiZhangJinghuietal.Optimiza-tionofreclaimedwaterdisinfectionprocess.ChinaWater&Wastewater201228782-84inChinese6.MBR.200723547-49YuDandanZhangGuanghuiZhangFengetal.StudyondisinfectionofMBReffluentbyultraviolet.ChinaWater&Wastewater200723547-49inChinese7..201036419-23WangXiangyongChenHongbinRuanJiuli.Progressonwastewaterandreusedwaterdisinfectionbyozone.Technol-ogyofWaterTreatment201036419-23inChinese8..20082116-18JiangYiyuanKeZhenshanZhangYuetal.Studyondisinfectionproblemsinmunicipalwastewaterreclamationtreatmentprocess.ChineseJournalofEnvironmentandEn-gineering20082116-18inChinese9..200723
本文标题:MBR出水氯-紫外-臭氧单独与组合消毒
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