高分子絮凝剂对水厂排泥水的调质效果与絮凝形态学特性黄辉

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28220116JournalofGuangdongUniversityofTechnologyVol.28No.2June20112010-12-312010Z5242010B0309000011986-.510006APAPpHAP.10.3mg/LAPr2~3v20.3mg/L20.395%0.1~0.3mg/L3DV>2DV<24pHpH.TU991.23A1007-7162201102-0012-064%~7%1...、、、、.、.、、2-55.“”、.、.11.1AN910SHSNFFLOERG-ERAPC3H5NOn1.5×107.APAP10mg/L0.5mol/LNaOH0.2mol/LH2SO4150mm.1.2wNaCl=0.5%NaCl2100PDHG-9145AA2O4FE-210OlympusSMZ-T2、.1.3、..0.5mol/LNaOH0.2mol/LH2SO4pH.0.395%.1.41LpH=7AP.1AP5s200r/min30s290s60r/min.700.5mm7cm20mL/min.、.Coackley690mm150mm0.0355MPa400mm0.5%NaCl.DADV、.15min.1.122.1APpH=7AP0、0.05、0.1、0.3、0.5、1.0mg/L、、、.2.2AP2.1.12AP..AP2a.AP0.05mg/L.2b.AP1~52c、d7s.10sAP-“”-7..AP2e12s.4s14s10cmAP2s“”.AP2f19s10cm.2.1.2AP1.3AP.AP.StokesdSTσ3121.4AP.APσ.AP0.1~0.3g/Lσ45、6RL-CAReaction-limitedColloidAggregation.AP“”.DLCADiffusion-limitedColloidAggregation8-9.3AP20×4AP5AP6AP1APAP/mg·L-1StokesdST/μmσm/gt/sv/mm·s-1r/1012m·kg-115min/NTU0.0066.6315.924.4421063.5729.3748250.0578.4221.334.476594.7111.7231790.1085.8817.694.664385.488.00152.00.3086.8117.964.762346.158.79447.50.50103.0044.794.833395.567.22461.91.00114.0432.414.941405.697.11156.11AP.AP0.3mg/L5、6.1AP..2.ρe10.ρe4128dST711-12lgρe=3-DVlgdST+b.APDV.8APDV.DV>2.80.052.2778.DV>20.1mg/L、0.05mg/L.0.1mg/L.DV<2、“”..Re>0.17StokesdST8APDv2.1.3APStokesdSTσAP0.1~0.3mg/Lσ.0.1~0.3mg/L.1APr、t、ρe、m、StokesdST0~0.3mg/L.2.1.22DV.DVDV=2AP0.1~0.3mg/L.XDV=20.1~Xmg/L.DV<2AP8.APAP.APAPAPPAM.0.395%0.1~0.3mg/L0.3mg/L.2.2pHAP0.1mg/LpH.2.2.19pH.pH=4.5~6.0.pH=5、pH=79a、10.pH6.5~7.8AP.“”.pHOH-OH-9c.、10.10pHpH.5129pH10pH2.2.21.11pH.pH=715min.11pH2.pHDV2.pHDV>2vDV.pHDV<2v.2pH9DV2DVpHpHDV52.381971.971191.8348pH7DVDV.31AP2~3.2、10.395%AP0.1~0.3mg/L.2pHAP.3DV>2DV<2.1.D.2001.2PeterScales.DewateringofwatertreatmentplantsludgesJ.InterfaceScienceandTechnology200610225-243.3.J.2009222-2.4.M.2006.5DavidI.VerrelliPeterJ.Scales.Assessingdewateringperform-anceofdrinkingwatertreatmentsludgesJ.Wa-terResearch20104451542-1552.6SmithaPGCoackleyaP.Amethodfordeterminingspecif-icsurfaceareaofactivatedsludgebydyeadsorptionJ.WaterResearch1983175595-598.7.M.1999.8TangSPreeceJM.FractalmorphologyandbreakageofDLCAandRLCAaggregatesJ.JournalofColloidandIn-terfaceScience2000221114-123.9.J.20061922A97-98.10.J.200561A74.216128ResearchonBendingMomentsandPunchingCalculationsofTriangleCapswithThree-PileFoundationsYangXue-qiangYangRuiZhangJian-longFaultyofCivilandTransportationEngineeringGuangdongUniversityofTechnologyGuangzhou510006ChinaAbstractIncombinationwithprojectionsofreinforcementindifferentdirectionsbendingmomentcalculatingmethodsoftrianglecapswiththree-pilefoundationsaregivenindetailandatthesametimebasedonexperimen-talresultsandtheoreticalformulaofconcreteslabpunchingbearingcapacitypublishedinliteraturesomecom-mentsaboutcornerpilepunchingcodeformulaarefurtherpresentedinthispaper.Theresearchservesasafurtherexplanationofcorrespondingcodespecificationsoftrianglecapswiththree-pilefoundationsandhelpstopromotethedesignofthistypeoffoundations.Keywordscapswiththree-pilefoundationscornerpilebendingmoment櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆櫆punchingbearingcapacity1611CloverSharnaMYao-DeYanetal.Bridgingfloccula-tionstudiedbylightscatteringandsettlingJ.ChemicalEngineeringJournal20008033-12.12TangPGreenwoodJRaperJA.AModeltoDescribetheSettlingBehaviorofFractalAggregatesJ.JournalofColloidandInterfaceScience.20022471210-219.TheConditioningEffectoftheSludgefromWaterPlantwithPolymerFlocculantAPandMorphologicPropertiesHuangHuiLiDong-meiRuanCai-qunHeNaRenYiLiuChun-liuFacultyofCivilandTransportationEngineeringConstructionGuangdongUniversityofTechnologyGuangzhou510006ChinaAbstractTakingthemiscellaneouswaterplantsludgeintheGuangzhouUniversitiesTownCampusasresearchingobjectexperimentbyanionicpolymersshortenedformAPwithbridgingflocculationsettlementwithonlinemi-croscopecameratechnologyandimageanalysistechnologystudyontheconditioningeffectandthecoagulationmorphologicpropertiesofthesludgeunderdifferentdosageofAPanddifferentpHvalue.Theresultsshowedthat1Adding0.3mg/LdosageofAPthespecificresistanceoffiltrationSRFrdrceases2~3timesandthesedi-mentationratevincreasesabout2timesWhenthedosageofAPisgreaterthan0.3mg/Ltheconditioningeffectwilltendtomild2TheoptimaldoseofAPtothesludgewhichsolidrateis0.395percentis0.1~0.3mg/LdosageofAP3WhenthefractaldimensionDV>2thedimensionwillincreasewiththeincreasingofthedos-agetheflocwillbedenserthefluidresistancewilldeclineandfinallythesinkvelocitywillincrease.MoreeverDV<2thedimensionwilldeclinewiththeincreasingofthedosagetheinterstitialratewilldeclineandfinallythesinkvelocitywillincrease4ThewateronneutralpHforconditioningsludgeislowerqualitythanthewateronAciditypHandAlkalinepHvalue.Keywordswaterplantsludgeconditioningsludgesettlingbehaviorsflocculationcoagulationmorphologicproperties122

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