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97Vol.9No.720157ChineseJournalofEnvironmentalEngineeringJul.2015--518059---MBR。pH6.050mA/cm2、2hCOD71.5%Cu86%0.110.30。pH531.28g/kg。6BV/h298min884mL。15%96.4%。-MBR。---MBRCOD250mg/L0.5mg/L《DB44/6-2001》COD。MBRX703.1A1673-9108201507-3355-06Treatmentofcopper-platingwastewaterbyelectrocoagulationionexchangeandbiochemicalprocessPengJuanZhaoChendongFengFanrangZhangQingxiZhengShuaifeiShenzhenHazardousWasteTreatmentStationCo.Ltd.Shenzhen518049ChinaAbstractTheelectrolesscopperplatingwastewaterwastreatedbythecombinedprocessofelectrocoagula-tion-ionexchange-anaerobichydrolysis-aerobicmembranebioreactionMBRtechnology.Theexperimentalre-sultsshowthattheremovalratesofCODandCu2+canreach71.5%and86%respectivelywhenpHvalueis6.0thecurrentdensityis50mA/cm2andtheelectrolyzingtimeis2h.Additonallythebiodegradabilityindexofwastewaterincreasesfrom0.11to0.30.Intheion-exchangeprocessingwhenthepHvalueis5thehighestremovalrateofCu2+bymacroporousstyrenechelatingresincanbereached.Furthermorethepenetrationtimeis298minandthetreatmentcapacityis884mLwhentheflowrateis6BV/h.When15%HClusesasthedesor-bentthedesorptionrateisupto96.4%.TheconcentrationsofCODandCu2+inwastewaterarelowerthan250mg/Land0.5mg/Lrespectivelywhichcanmeetthethird-gradestandardfordischargeofwaterpollutantsinGuangdongProvinceDB44/26-2001.Keywordselectrocoagulationion-exchangeresinanaerobichydrolysisacidificationmembranebioreactorMBRcopper-platingwastewater2014-05-122014-06-071982—。E-mailpjshwt@163.comprintedcircuitboardPCB1。2、EDTA。3。4。5。-Fenton-6、7、8、9、1011。、、12。。911.1EC-10、、、、、100V、20A。。-50%~60%0.35~0.55mm256mm×62mm×2mm、、。1.2pHCOD18136mg/LBOD5985mg/LpH=3.51680mg/LEDTA4300mg/L。CODBOD5pHpHS-3CAA7000EDTA-。1.313。Fe2+H14。15。。MBR16。1.4--MBR1。1pH=6。pH8~9。。MBR。2。2.1、pH、。2.1.1pHpH、17。10V20A120minpHCOD2。2pH。pH6pHCOD。pH=6COD77.82%74.45%。pH8.0~11.0COD。pH。pH4.0COD。Cu2+pH1Fig.1Flowchartoftreatmentofwastewatertreatmentprocess65337--2pHCODFig.2InfluenceofpHonCuandCODremovalefficiencypH18。pH6~719。pH6.0pH7~8。2.1.220。pH=610V2hCOD3。3CODFig.3InfluenceofcurrentdensityonCuandCODremovalefficiency3COD。50mA/cm2。。50mA/cm2。2.1.321。pH=610V50mA/cm2COD。4CODFig.4InfluenceofelectrolyzingtimeonCuandCODremovalefficiency4COD2hCOD75.12%98.76%。2h。2.1.46m2。20t/d50mA/cm2pH6.02hpH7~8pH8~91。1Table1SiteexperimentofelectrocoagulationCu2+CODBOD5EDTABOD5/COD1mg/L168518236198540580.11mg/L281495815372830.31%83.3272.6722.693.022mg/L8359367112421320.12mg/L11326768011450.30%86.4771.4328.793.23mg/L127013542203136520.15mg/L139382511051630.29%89.171.7645.695.5175339CODCu71.5%86%EDTA93%。BOD5/COD0.110.30。2.2H。2.2.1100mL1g150r/min24h。pH5。5pHFig.5InfluenceofpHonCuremovalefficiency5pHpH5。pHH+NpHCu2+pHCu2+OH-Cu2+22。pH5。5g400mL281mg/LpH=5.0。6。300min31.28g/kg。6Fig.6Relationshipbetweentimeandadsorption2.2.230mLpH=52、4、68BV/h1mg/L7。7Fig.7Influenceofflowvelocityonpenetrationtime72、4、68BV/h1055、557、298162min3805、1886、884453.0mL。6BV/h884mL。2.2.342mL3%、5%、10%15%HCl24h。HCl3%43.2%5%85337--78.5%HCl10%85.3%HCl15%96.4%。。HCl15%。HCl20040mg/L。。2.3。COD2700mg/L1600mg/LCOD40%BOD5/COD0.35MBR。MBR7000~18000mg/L、20~24h、0.59kgCOD/kgMLSS·d、DO3~4mg/LCOD1600mg/L250mg/LMBRCOD90%COD100~250mg/L0.5mg/LCOD。31---MBRCOD250mg/L0.5mg/L《DB44/26-2001》COD≤500mg/LCu≤2.0mg/LCOD。2pH、pH6.050mA/cm2、2hCOD71.5%86%。0.110.30。3pH5。6BV/h298min884mL。15%96.4%。4、。1..201263860-864WangJianfangLiuZhigangShenYaoliangetal.Optimiza-tionexperimentoncopperremovalofcomprehensivewastewaterfromprintedcircuitboardindustrialparkbyal-kalinemethod.ChineseJournalofEnvironmentalEngineer-ing201263860-864inChinese2..201131138-39ZhaoDaweiZhangPeng.Technologyanddevelopmentofelectrolesscopperplating.HeilongjiangMetallurgy201131138-39inChinese3..20137124719-4723LiuPengLiChaolinKongXianghanetal.TreatmentofelectrolesscopperplatingwasteliquidbyUV-catalyticwetperoxideoxidation.ChineseJournalofEnvironmentalEngi-neering20137124719-4723inChinese4..20115MolinariR.PoerioT.ArgurioP.ChemicalandoperationalaspectsinrunningthepolymerassistedultrafiltrationforseparationofcopperⅡ-citratecomplexesfromaqueousmedia.JournalofMembraneScience20072951-2139-1476LanShanhongJuFengWuXiuwen.TreatmentofwastewatercontainingEDTA-CuIIusingthecombinedprocessofinteriormicroelectrolysisandFentonoxidation-coagulation.SeparationandPurificationTechnology201289117-1247.DTC.2011561246-1250LingYulinDaiYouzhiLiuLihuaetal.SynthesisofaheavymetalchelatingagentwithDTCgroupanditsper-formanceoftreatmentofcopper-containingwastewater.Chi-neseJournalofEnvironmentalEngineering2011561246-1250inChinese8SeshadriH.ChitraS.ParamasivanK.etal.Photocatalyt-icdegradationofliquidwastecontainingEDTA.Desalina-tion20082321-3139-1449..2006170-17110..2011342129-135LiZhihongWangMingyu.Experimentonpurificationeffi-cienciesofcopper-contaminatedwaterusingmulti-media95339constructedfloatingislands.EnvironmentalScience&Technology2011342129-135inChinese11..200934695-698LiYanlinWuLiboWangWeietal.Removalofcopperi-onsfromaqueoussolutionsusingpolymerenhancedultra-filtration.ChineseJournalofEnvironmentalEngineering200934695-698inChinese12VoleskyB.Detoxificationofmetal-bearingeffluentsBio-sorp
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