催化臭氧氧化有机废气处理技术研究进展陆建海

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20149229INDUSTRIALCATALYSISSept.2014Vol.22No.92014-03-102014-04-262012C210961982。。*310005。、、、SBA-16、、MnOx/γ-Al2O3。。、、、。O*2。、。doi10.3969/j.issn.1008-1143.2014.09.002X701A1008-1143201409-0654-06ProgressincatalyticoxidationtreatmenttechnologyoforganicwastegasbyozoneLUJianhai*ZHUHongGUZhenyuEnvironmentalScienceResearch&DesignInstituteofZhejiangProvinceHangzhou310005ZhejiangChinaAbstractGasphasecatalyticoxidationoforganicwastegasbyozoneisatechnologyofadvancedcatalyticoxidationatlowtemperatures.ThecarriersofthecatalystsforgasphasecatalyticozoneoxidationmainlyincludealuminasilicatitaniumdioxidezeolitesandSBA-16molecularsievesetc.andtheactivecom-ponentsloadedonthecarriersaremetallicoxidesofcoppercobaltmanganesenickelandsoon.MoreresearchisfocusedonMnOx/Al2O3.Theresearchadvanceincatalyticoxidationtreatmenttechnologyoforganicwastegasbyozoneathomeandabroadwasreviewedandtheresearchprospectsofthetechnologywereoutlined.Themaininfluencialfactorsofcatalyticoxidationincludedtheactivecomponentsandtheirloadingsreactiontemperaturesrunningtimebyproductshumidityandsoon.Accordingtothemecha-nismofthereactionprocessthereactionconsistedoftwopartsozonedecompositionandoxidationoforganicwastegas.ActiveoxygenorperoxidespeciesO*2producedbythecatalyticdecompositionofozonewasthekeytotheoxidationoforganicwastegas.Inthefutureresearchtheproblemsneededtobesolvedaretheadsorptioneffectsofcatalystcarriersoptimalreactiontemperaturestoavoiddeactivationofthecatalystsandcompletereactionmechanismsforgasphasecatalyticoxidation.Keywordsenvironmentalprotectionengineeringgasphasecatalyticoxidationozoneorganicwastegasdoi10.3969/j.issn.1008-1143.2014.09.002CLCnumberX701DocumentcodeAArticleID1008-1143201409-0654-0620149655E0=+2.07V1。CO2H2O2-4。、5。6。。1。DimitarMehandjiev7γ-Al2O3Cu-CrCo-CrAlCuCrⅠ、AlCuCrⅡ、AlCoCrⅠAlCoCrⅡ。8.5%~10%CuCoCr4∶1。XRDAlCuCrCuO、CuCr2O4Cu2Cr2O4AlCoCrCo3O4CoCr2O4。AlCoCrAlCuCr。HisahiroEinagaa8MnOx/SiO2、MnOx/Al2O3、MnOx/TiO2MnOx/ZrO3。Al2O3SiO2Al2O3TiO2ZrO3Al2O320%40%。LiMaoshuai9CuCoMCM-41。CoCuMCM-41。CoCuCo。JongHwaPark10SBA-16Al-SBA-16SiAl2015%Al-SBA-16-MN15%Al-SBA-16-MA15%。Al-SBA-16-MA15%Al-SBA-16-MN15%。XPSAl-SBA-16-MA15%Al-SBA-16-MA15%。80minAl-SBA-16-MA15%Al-SBA-16-MN15%5%。EbrahimRezaei11MnOx/γ-Al2O3Mn1%、5%、10%20%。MnMn2O3MnMnO2Mn2O3MnO2MnMn。22~100℃Mn。12MnOx/γ-Al2O3PtPd1%Pt-MnOx/γ-Al2O3Pd-MnOx/γ-Al2O3PdPt。X65620149Pd-MnOx/γ-Al2O3PdMnPt-MnOx/γ-Al2O3PtMnPtMnMn—O—PtMnPt-MnOx/γ-Al2O33d。2、、、。DimitarMehandjiev7CO。AlCoCrⅡ50%360℃90℃100℃80%。HisahiroEinagaa8COx。22℃CO2CO。。、、、25-。300℃450℃。13Mn-Y、Mn-b、Mn-MORMn-ZSM-5Y70℃CO2。StoyanovaM14NiOx/Al2O3CO-50~250℃-45℃。12Ni4+OOH2。HsuShengLiang1510%MnOx/SiO2。120℃、300000h-1900×10-690.4%COCO2。96h12-450℃76.2%77.1%。HisahiroEinaga16SiAl1805%~15%Mn/SiO2。5%Mn/USY。313KCO2CO。HisahiroEinagaa17MnOx/γ-Al2O3。。。ZhaoDezhi18CO2。80%CO20%CO2RH≥55%100%CO2。。19MnOx/Al2O3Mn5%。70×10-615mg·m-3、75%、84%88%。20149657、。20Al2O35。5MnOxNiO、CoOMnOx666mg·m-3193mg·m-3965mg·m-315.2%46.7%0.57%。21MnOx137mg·m-3642mg·m-3、56%25℃200000-1CO2150minCO2100%。3∶12∶3100%58%CO2100%MnOxCO2MnOx。322。GolodetsGI23MnO2/Al2O324。LiWei25-26O*2。RakeshRadhaKrishnan27O*。Kroger1932GrasselliRK28Mars-vanKrevelen29-30。NaydenovA31MnO2。HisahiroEinaga32O*2。EbrahimRezaei33MnOx/γ-Al2O3EXAFS、--3。20。/、O3/TiO2/UV34-35。4CO2H2O。、。1。2。。3。。。1.65820149//2006C.、2006.2OyamaSTZhangWHeisigC.Decompositionofozoneusingcarbon-supportedmetaloxidecatalysisJ.AppliedCatalysisBEnvironmental199714117-129.3EinagaHFutamuraS.Oxidationbehaviorofcyclohexaneonalumina-supportedmanganeseoxideswithozoneJ.AppliedCatalysisBEnvironmental20056049-55.4.J.200427143-145.ChenLinLiuGuoguangLüWenying.ProspectiveofozoneoxidationtethnologyJ.EnvironmentalScienceandTech-nology200427z1143-145.5.-J.200123124-26.HaoZhengpingChengDaiyunHeYing.Preliminarystudyondegradationoflowconcentrationgaseouspollutantsbyozono-catalytictechnologyJ.EnvironmentalPollution&Control200123124-26.6.J.20092611-15.MaJunLiuZhengqianYuQiyietal.Advancesinhetero-geneouscatalyzedozonationinwatertreatmentJ.JournalofNaturalScienceofHeilongjiangUniversity20092611-15.7DimitarMehandjievKatinkaCheshkovaAntonNaydenovetal.CatalyticoxidationofCOandC6H6onalumina-sup-portedCu-CrandCo-CroxidecatalystsinthepresenceofozoneJ.ReactionKineticsMechanismsandCatalysis2002762287-293.8HisahiroEinagaaShigeruFutamuraa.Catalyticoxidationofbenzenewithozoneoveralumina-supportedmanganeseoxidesJ.JournalofCatalysis20042272304-312.9LiMaoshuaiHuiKNHuiKSetal.Influenceofmodifica-tionmethodandtransitionmetaltypeonthephysicochemicalpropertiesofMCM-41catalystsandtheirperformancesinthecatalyticozonationoftolueneJ.AppliedCatalysisBEnvi-ronmental2011107245-252.10JongHwaParkJiManKimMingshiJinetal.CatalyticozoneoxidationofbenzeneatlowtemperatureoverMnOx/Al-SBA-16catalystJ.NanoscaleResearchLetters20127114-17.11EbrahimRezaeiJafarSoltanaNingChen.Catalyticoxida-tionoftoluenebyozoneoveraluminasupportedmanganeseoxideseffectofcatalystloadingJ.AppliedCatalysisBEnvironmental2013136239-247.12EbrahimRezaeiJafarSoltanNingChenetal.EffectofnoblemetalsonactivityofMnOx/γ-aluminacatalystincatalyticozonationoftolueneJ.Chemi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