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49220172JOURNALOFHARBININSTITUTEOFTECHNOLOGYVol.49No.2Feb.2017DOI10.11918/j.issn.0367-6234.2017.02.011Cu2+Ni2+-MBR12221121.1500762.150090-MBRCu2+、Ni2+-MBRDOMs.Cu2+、Ni2+5~20mg/L-MBRCODNH4+-N75%45%.-MBRCu2+、Ni2+20mg/LMBR10mg/L.HPIHPO-A.Cu2+、Ni2+MBRSOUR-MBRSOURMBR5%.-MBREPSMBR.X522A0367-6234201702-0062-08InfluencecharacteristicsofCu2+andNi2+onthetreatmentefficiencyofhydrolysis-MBRprocessHUANGLikun12WANGGuangzhi2LIWei2QUFanqi1WANGJingyuan1ZHAOQingliang21.SchoolofFoodEngineeringHarbinUniversityofCommerceHarbin150076China2.SchoolofMunicipalandEnvironmentalEngineeringHarbinInstituteofTechnologyHarbin150090ChinaAbstractInordertoreducetheimpactofheavymetalsonthebiologicaltreatmentsystemofelectroplatingwastewateralab-scaleprocesscombinedwithhydrolysisreactorandmembranebioreactorMBRwasusedtotreatelectroplatingwastewater.TakingCu2+andNi2+asresearchobjectstheeffectsofdifferentmetalconcentrationsontheelectroplatingwastewatertreatmentwerestudiedandthechangesofDOMsandmicrobialactivityinwaterwereanalysedsimultaneously.TheexperimentalresultsshowedthattheremovalefficienciesofCODandNH4+-Nwereabove75%and45%respectivelywhentheconcentrationofNi2+andCu2+was5-20mg/L.Nitrificationbacteria’sabilitytoresistheavymetalimpactwasweak.ThetoleranceconcentrationofNi2+inhydrolysisreactorcombinedwithMBRwas20mg/Landonly10mg/LinMBR.ThehydrolysisreactorcouldconvertmostofHPIintoHPO-Awhichcouldimprovethebiodegradabilityofrefractoryorganiccompoundsandthecontentofaromaticcompoundswasobviouslydecreased.WiththeincreaseofNi2+andCu2+theSOURvalueofactivatedsludgeinMBRreactorwasgraduallydecreasedbuttheinhibitionrateofSOURinhydrolysisreactorcombinedwithMBRwas5%lowerthanthatinMBR.Duetothehydrolysisthetoxicityofheavymetalsdecreased.InhydrolysisreactorcombinedwithMBRtheactivityofmicroorganismwashigherandthecontentofEPSandtheeffluentconcentrationweresignificantlylowerthanthoseinMBR.Theformationofcolloiddissolvedorganicmatterandsludgecakelayercouldbereducedeffectivelywhichretardedtherateofmembranefouling.KeywordselectroplatingwastewaterhydrolysisacidificationMBRheavymetal2016-02-162013ZX07201-007-0032012M5109651980—1962—hitwgz@126.comCu、Ni、Cr、ZnCd、、1.、、2-6COD、7-9..10COD75.08%.11A/O1∶3COD、NH4+-N83%98%.《》GB21900—2008COD、NH4+-N、TN12.membranebioreactorMBR、、、13-15.MBR.MBRMBR16-18Cu2+Ni2+-MBRdissolvedorganicmatterDOMs.11.11.Cu2+Ni2+、.、、2.5、1、3.5mg/L3Cu2+、Ni2+5、1020mg/L.1Tab.1WaterqualitycharacteristicsCOD/mg·L-1NH4+-N/mg·L-1TP/mg·L-1pH/℃250~44030~403.5~6.06.4~7.610~181.2-MBRMBR1HMBR.MBR20L11.8L.D=150mm670mm11.8LMBRL×B×H=400mm×200mm×250mm20L.MBRhydraulicretentiontimeHRT59h.、.MBR、.PVDF0.2μm0.2m2.transmembranepressuredifferenceTMP0.2MPa.MBR4L.MBR14mL/min.150%.MBRMBR.HMBR.6d.2dCOD85%.!#!!$%&’()!*!!#$!%&$#!’()*$&!+,-./01$$!23456$’!789:;$%!5=?$(!@,A$)!@,&$!*!45&$!!!/BC()*1-MBRFig.1Schematicdiagramofthelab-scalehydrolysisacidification-MBRreactor1.3MBRA/O.COD10dCOD80%.8000mg/LMBR4500mg/L.1.4COD、NH4+-N·36·2Cu2+Ni2+-MBRMLSSMLVSSDOMs19DOMstransphilicneutralTPI-N、hydrophobicacidHPO-A、hydrophobicneutralHPO-N、hydrophilicfractionHPItransphilicacidTPI-A5TOC-VCPNUV254254nm20T6-21Lowry22specificoxygenconsumptionrateSOUR23Oxi-3205SET1TWTscanningelectronmicroscopeSEM28Quanta200FEI.2.、、Cu2+Ni2+-MBR.2.1CODNH4+-NCu2+Ni2+HMBRMBRCOD、NH4+-N2、3.2COD260~426mg/L3COD301.0、323.0、313.0mg/L.MBRCOD37.7、65.5、97.2mg/LCOD87.7%、79.2%、68.9%HMBRCOD31.2、35.6、73.3mg/LCOD89.6%、88.4%、76.3%.Cu2+、Ni2+5mg/LCOD.Cu2+、Ni2+10mg/LMBRCODHMBRCOD.Cu2+、Ni2+20mg/LMBRCODCOD.HMBRCOD75%MBRCOD70%.!#$%&’’(!$&)*+,-./012’3!#,4’&%$#!5(6’’’’&’%’$’#’!’5’($%&’,7()*+,-*+,-!#89:89:!#2HMBRMBRCODFig.2CODremovalefficiencyofHMBRandMBRprocessesindifferentstages!#$%&!#’(!&)%*$+#,!!!!&!)!%!*!$!+!#$%&’’-*%)&!!()*+’(./012!+,-345./01./01!#345!#3HMBRMBRNH4+-NFig.3NH4+-NremovalefficiencyofHMBRandMBRprocessesindifferentstages3NH4+-N29.6~42mg/L3NH4+-N35.7、35.936.5mg/L.MBRNH4+-N15.9、19.623.3mg/LNH4+-N55.3%、46.2%35.8%HMBRNH4+-N6.7、9.611.5mg/LNH4+-N58.1%、52.4%52.3%.NH4+-N.Cu2+、Ni2+10mg/LHMBRNH4+-N50%MBR40%.Cu2+、Ni2+20mg/L20mg/LMBRNH4+-N20%HMBR45%.HMBRNH4+-N.2.2DOMs、·46·49、.DOMs、24-25.4HMBRMBRDOMs.!#!$#!##%##$##’()*+,*+(-./+,-.*+(-0/+,-0/(1234567-!8!#$)9:3;8%&’()1$=*0$=+,-.#4527/?#@##A#$#!##/(1234567-!8’()*+,*+(-./+,-.*+(-0/+,-0#$)9:*)9:3B8%&0()1$=*0$=+,-.$#4527/4HMBRMBRDOMsFig.4DOMsintheeffluentofHMBRandMBRprocesses4aMBRTOC27.9%82.3%COD.TOCHPI29.0%、HPO-A28.1%HPO-N31.2%88.1%.Cu2+、Ni2+0mg/LHPIHPO-AHPO-N50.6%.HPO-Aη=57.7%HPO-Nη=68.5%HPO-AHPO-N.MBRHPI84.6%.Cu2+、Ni2+20mg/LDOMSHPO-A42.1%HPI32%3.HPIHPO-A.MBRHPI、HPO-ATPI-AHPO-NTPI-NHPO-NTPI-N.HMBRDOCMBRCODMBRHPI33.4%HMBRHPO-AHPO-N32.4%.HMBR.MBR.、、HMBR.5HMBRMBRUV254.!##$#%#’#()*+,-+,)./0,-./+,).10,-.1234!#$%56’7&18’7’()*#9:;+2=4!,$%56’7&18’7’()*’#9:;+-../0.*?./0.*?+*?!##$#%#’#()*+,-+,)./0,-./+,).10,-.1@A’B&;C9.!@A’B&;C9.!5HMBRMBRUV254Fig.5UV254intheeffluentofHMBRandMBRprocesses5aUV254HPO-N53.4%HPO-N.36.1%UV254MBRUV2546.6%MBRHMBRUV254.HPIUV25424.5%HPO-N93.61%.5bCu2+、Ni2+0mg/L.MBRTPI-A、HPO-NTPI-NUV254HPITPI-A.MBRTPI-ATPI-A.5bMBR·56·2Cu2+Ni2+-MBRHMBR2HMBR.2.3SOUR26-27SOUR.6SOUR.!!#$%$!’()!#’()
本文标题:Cu2和Ni2对水解MBR工艺处理效能的影响特性黄丽坤
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