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Study On The Promotion Effects Of Phosphorus-Doped Carbon Aerogels Supports For MnOx-CeO2 Catalysts In Low-Temperature Selective Catalytic Reduction Of NO With NH3

Posted on:2022-06-01Degree:MasterType:Thesis
Country:ChinaCandidate:H WangFull Text:PDF
GTID:2491306722498754Subject:Material Chemical Engineering
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The atmospheric pollutants produced by the combustion of fossil fuels are nitrogen oxides(NOx),and the main components of atmospheric pollutants are nitric oxide(NO)and nitrogen dioxide(NO2 ),which cause serious environmental problems such as acid rain,optical smog and ozone destruction.NH3selective catalytic reduction of NO(NH3-SCR)is a widely used technology to control the emission of NO from fixed sources.In industrial production,V2O5-WO3/Ti O2 is used as commercial catalyst.However,the main active component of the catalyst has disadvantages such as strong toxicity and high price of V2O5,and it is difficult to recycle the waste of V2O5-WO3/Ti O2 catalyst,which is easy to cause secondary pollution to the environment.Therefore,the development of low-cost and environmentally friendly catalysts has become a research hotspotCarbon material carrier has the advantages of large specific surface area,high porosity and easy recovery of metal oxides in deactivated catalyst.There are abundant functional groups on the surface of carbon materials.Carbon itself can also act as a catalyst.The surface chemical properties of carbon materials have an important effect on the catalytic activity of carbon based catalyst for NO reduction.It has been reported that oxygen-containing groups or nitrogen-containing groups are beneficial to the direct catalytic decomposition of NO on carbon.The oxygen-containing functional groups on carbon can improve the surface acidity,Mn4+/Mnx+ratio and the number of adsorbed oxygen species of Mn-Ce Oxcatalyst supported by carbon materials,and thus improve the NH3-SCR activity of Mn-Ce Oxcatalyst supported by carbon materials.I.Phosphorus-doped carbon aerogels(P-CA)was prepared from phenol,m-cresol,furfural and phosphoric acid MnOx-Ce O2 /P-CA catalysts were prepared via incipient wetness impregnation of Mn(NO32·4H2O and Ce(NO33·6H2O over phosphorus-doped carbon aerogels(P-CA)for selective catalytic reduction of NO by NH3(NH3-SCR).The results show that P doping on carbon support significantly promotes the NH3-SCR performance of MnOx-Ce O2 /P-CA catalysts.P modification can improve the hydrophilicity of carbon support and facilitate the dispersion of MnOx-Ce O2 components on carbon surface,which enhances the electronic interactions between MnOxand Ce O2 .The optimal catalyst10%MnOx-Ce O2 /P-CA shows higher surface acidity,more Mn4+and Ce3+,and a larger amount of surface chemisorbed oxygen(Oα)than that of 10%MnOx-Ce O2 /CA catalyst.As a result,even though in the company of SO2 ,more NO can be adsorbed and oxidized over the10%MnOx-Ce O2 /P-CA catalyst to generate more NO complexes,alleviating the suppression of SO2 on the SCR reaction via Langmuir-Hinshelwood(L-H)mechanism,and thus the SO2 resistance is enhanced.II.H3PO4as phosphorus source,phenol,m-cresol and furfural were prepared through a pot of sol-gel and aging to obtain phosphorus-doped wet aerogel,and then phosphorus-doped carbon aerogel(P-CA)was obtained through atmospheric drying and carbonization process.Phosphorus-doped carbon aerogel was ground and used as a metal-free catalyst to remove NOx.The results show that the carbonization temperature of phosphorus doped carbon aerogels and the content of P on the surface of P-CA catalyst are related to the catalytic activity of NH3-SCR.When the carbonization temperature is 800℃,the NOx removal efficiency of p-CA catalyst is the highest,and the NOx removal efficiency of P-CA catalyst is 60.6%at 200 oC.The higher the content of P,the higher the NOxremoval efficiency of phosphorus doped carbon aerogel catalyst.However,the phosphoric acid compound will have thermal decomposition and release at high temperature,and part of the functional groups containing phosphorus will be converted into P2O5particles,resulting in the pore of carbon aerogel catalyst being blocked and covering the surface of the active site at the same time.The P-CA-800 catalyst was subjected to vacuum heat treatment for 8 hours.When P2O5particles were removed,the NOxremoval efficiency of P-CA-800vaccatalyst was increased to 76.8%at 200oC.Through characterization,it was found that phosphorus atom doping on the surface of carbon aerogel material could produce more acid sites and active sites conducive to NH3-SCR reaction.The functional groups of phosphorus on the surface of carbon aerogel materials are C3P,C3-P=O,C-O-P and P2O5.The presence of C3-P=O and C-O-P functional groups is conducive to the NH3-SCR reaction.In addition,the NOx removal efficiency of p-CA-800vaccatalyst is low under the passage of NO or NO+O2 in different atmosphere,indicating that the passage of NH3is very important for NH3-SCR reaction.In-situ DRIFTs test shows that the adsorption peak of NH3disappears after the passage of NO+O2 in p-CA-800vaccatalyst in advance.After NO+O2 is entered in advance,NH3is entered.However,the strength of NO adsorption peak will not disappear with NH3entering.The results showed that Eley-rideal(E-R)mechanism was the main reaction path of NH3-SCR reaction over P-CA-800vaccatalyst.DFT calculation was carried out for the main phosphorus-containing functional groups on the surface of P-CA-800vaccatalyst.The presence of COP was beneficial to the adsorption of NH3.The C3PO site is the most active site for NO molecule adsorption.However,the structure of NO molecule is relatively stable.The COP site is the most active site for O2 molecular dissociation.At the same time,the adsorption of NH3is exothermic reaction,and the adsorption of NO and O2 is endothermic reaction.
Keywords/Search Tags:phosphorus-doped carbon aerogels(P-CA), NH3-SCR, MnOx-CeO2, SO2 resistance
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