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檲檲檲檲檲檲檲檲檲檲檲檲檲檲檲檲檲檲檲檲檲檲殘殘殘殘112341.3003842.3000403.1300214.1500903FeCl3、PACAS。FeCl3PAC12mg/L0.380.30NTUASUV254UV254PAC>AS>FeCl312mg/L59%57%52%FeCl3PAC20~30minAS40min。PACUV254。TU991.2A1673-9353201401-0001-06doi10.3969/j.issn.1673-9353.2014.01.00111ZCKFSF017002012ZX07404-002OptimalselectionofcoagulantsfortreatinglowtemperatureandlowturbidityDanjiangkouReserviorwaterSunYunkai1HeWenjie12SunYing3TanHaoqiang41.SchoolofEnvironmentalandMunicipalEngineeringTianjinChengjianUniversityTianjin300384China2.TianjinWaterworksGroupCo.Ltd.Tianjin300040China3.ChinaNortheastMunicipalEngineeringDesignandResearchInstituteChangchun130021China4.HarbinInstituteofTechnologyHarbin150090ChinaAbstractAimedatthelowtemperatureandlowturbidityDanjiangkouReserviorwatertheoptimalselectionwasconductedonthedosageandsedimentationtimeofferricchlorideFeCl3polyaluminumchloridePACandaluminumsulfateASbycoagulationsedimentationbeakertest.TheresultsindicatedthatthedosageofFeCl3andPAChadstrongnegativecorrelationwithresidualturbidityamongtestscope.Theminimumresidualturbiditywasobtainedin12mg/Lwhichwas0.38NTUand0.30NTUrespectively.ItwassuperiortoASobviously.ThecoagulantdosagehadpositivecorrelationwithremovaleffectofUV254theremovaleffectofUV254wasPAC>AS>FeCl3.Themaximumremovalratewasobtainedin12mg/Lwhichwas59%57%and52%respectively.TheflocsedimentationvelocitywasfastwhichformedbyFeCl3andPAC.Thecompletesedimentationcouldgetin20to30min·1·8120142WATERTECHNOLOGYVol.8No.1Feb.2014andthesedimentationtimeofdosingASwasmorethan40min.TheadaptabletestwasconductedintherelationofoptimaldosageofPACturbidityandUV254inpilotsystemandtheresultsweregood.KeywordslowtemperatureandlowturbiditywaterDanjiangkouReservoircoagulant、、、《》GB3838—2002Ⅰ、Ⅱ。12310℃3NTU。、、、1-2。。3、。11.11.1.1HACH2100QZR4-6JA2003B0.001gSP-19000.45μmHACHHQ40d。6m3/h110r/min60s332518r/min5~8m3/m2·h1.8mm/s9.6min。1.1.2PACAl2O330%FeCl3AS。30.5g/LPACASAl2O3FeCl3Fe。1.2。1。1Tab.1Indexofrawwaterquality/℃/NTUUV254/cm-1CODMn/mg·L-1pH6.8~9.91.01~2.910.0312~0.05321.32~1.868.10~8.318.41.890.04291.538.231.33。UV254CCCO3。UV254。61L2。10min4cm0.45μmUV254。2030min。57mg/L2。PACUV254。2Tab.2Stirringconditions/r·min-1/s1/r·min-11/min2/r·min-12/min3/r·min-13/min400501205805405·2·812014222.1102030min31~3。10min3UV2544投加量/(mg·L-1)23.02.52.01.51.00.5余浊/NTU100806040200去除率/%04681012FeCl3AsPACFeCl3AsPAC余浊:去除率:110minFig.1Relationofcoagulantdosagewithresidualturbidityandremovalrateofturbidityfor10min投加量/(mg·L-1)2046810123.02.52.01.51.00.5余浊/NTU100806040200-20去除率/%FeCl3AsPAC余浊:FeCl3AsPAC去除率:220minFig.2Relationofcoagulantdosagewithresidualturbidityandremovalrateofturbidityfor20min24681012投加量/(mg·L-1)3.02.52.01.51.00.5余浊/NTU0100806040200-20去除率/%FeCl3AsPAC余浊:FeCl3AsPAC去除率:330minFig.3Relationofcoagulantdosagewithresidualturbidityandremovalrateofturbidityfor30min24681012投加量/(mg·L-1)00.0600.0550.0500.0450.0400.0350.0300.0250.020出水UV254/cm-1100806040200去除率/%FeCl3AsPACUV254:FeCl3AsPAC去除率:410minUV254Fig.4RelationofcoagulantdosagewithsedimentationoutflowUV254andremovalratefor10min2.1.1FeCl31~3FeCl3。1mg/L。1mg/L4mg/LFeCl3。FeCl34mg/L102030min53.4%63.7%66.7%。4mg/LFeCl3FeCl3。30.600.380.38NTU。12mg/L370%FeCl33。10min2030min。FeCl3。33Tab.3CorrelationbetweenthreecoagulantsdosageandresidualturbidityFeCl3PACAS10min-0.862646-0.712236-0.68600620min-0.857451-0.788453-0.21595330min-0.855267-0.787165-0.224678FeCl3·3·20142814。2.1.2PACPACFeCl3。PAC4mg/L。3PAC4mg/L61%65%69%12mg/L55%69%75%0.650.560.30NTU。PAC3。PAC、FeCl35-6。2.1.3AS1~3AS0mg/L5mg/L5mg/L0.74NTU50%~60%。8mg/L。。AS。ASFeCl3PACAS7。AS3。3。3FeCl3>PAC>AS。2.1.43UV254UV2544。43UV254UV254UV254。3UV254UV254。3UV254PAC>AS>FeCl3。12mg/L3UV25459%57%52%。UV2544。UV254。43UV254Tab.4CorrelationcoefficientbetweenthreecoagulantsdosageandoutflowUV254FeCl3PACAS-0.950296-0.962200-0.9357072.257mg/L。5~7。。FeCl320min25min0.560.47NTU70%76%。PAC25min25min30min0.470.37NTU76%81%。AS20min50min0.600.48NTU75%80%30min0.850.86NTU65%64%。·4·8120142余浊/NTU1520253035沉淀时间/min101.00.80.60.40.29080706050去除率/%5mg/L投加量7mg/L投加量5mg/L投加量7mg/L投加量余浊:去除率:5FeCl3Fig.5RelationbetweensedimentationtimeresidualturbidityandremovalrateofturbidityundertwodosageconditionsofFeCl35mg/L投加量7mg/L投加量5mg/L投加量7mg/L投加量去除率/%1520253035沉淀时间/min10余浊/NTU1.00.80.60.40.29080706050余浊:去除率:6PACFig.6RelationbetweensedimentationtimeresidualturbidityandremovalrateofturbidityundertwodosageconditionsofPAC5mg/L投加量7mg/L投加量5mg/L投加量7mg/L投加量余浊:去除率:去除率/%余浊/NTU2030405060沉淀时间/min102.01.61.20.80.40100806040207ASFig.7RelationbetweensedimentationtimeresidualturbidityandremovalrateofturbidityundertwodosageconditionsofAS30minPAC。FeCl3PAC20~30min。FeCl3PAC。AS。2.31NTU1NTU。3PAC1500/Al2O330%FeCl3850/38%~40%AS960/Al2O316.5%。1NTU20min35。5Tab.5CostanalysisFeCl3PACAS/mg·L-12.1Fe2.5Al2O33.5Al2O3/kg15.638.3321.2/13.2912.5020.35PACFeCl3AS5.9%38.6%。2.4。PAC1.5~4.0mg/L。UV25489。89PAC1.5mg/L4.0mg/L。4.0mg/L0.83NTU47.6%。PACUV254。PAC1.5mg/L4.0mg/LUV254·5·201428124.3%43%。去除率/%2025303540投加量/(mg·L-1)15浊度/NTU2.01.51.00.5050403020100原水浊度沉后水浊度沉后水去除率8PACFig.8RelationbetweenPACdosageturbidityandremovalrateinpilotsystem去除率/%UV254/cm-12.02.53.03.54.0投加量/(mg·L-1)1
本文标题:丹江口水库水低温低浊期混凝剂优选
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