| Nitrogen oxides(NOx),as the main pollutants of industrial flue gas,is not only the main precursor of acid rain and photochemical smog,which will cause serious harm to the environment,but also cause great harm to human health.In this paper,low temperature plasma co-catalytic reduction(NTP-SCR)was used to remove NOx.α-Mn O2 catalyst was prepared and Ce metal was doped to improve the NOx removal rate.The effects of different gas components and discharge reactor structure parameters on the removal of NO and the effects of different loading methods and carriers on the removal of NOx by low temperature plasma co-catalytic reduction were discussed.(1)The discharge conditions of N2/O2,N2/O2/NO,N2/O2/NH3 and N2/O2/SO2 under empty tube,V2O5-WO3/Ti O2 and Mn-based catalysts were compared.The presence of a time-space tube in O2 and the discharge of vanadium-tungsten-titanium catalysts can generate O3 oxide N2 or NO to generate NOx,while the filling of Mn-based catalysts will decompose O3 on the catalyst surface and enhance the REDOX capacity of the catalysts.When the catalyst is filled,NOx can be removed by adding NH3.(2)In N2/NH3/O2/NO atmosphere,the denitrification effect of catalysts with different Mn/Ce ratios is stronger than that ofα-Mn O2 catalyst,and the best effect is achieved when Mn/Ce ratio is 1,which can maintain the above 95%NOx removal rate in the range of 200~400J/L.XRD and BET results show that the specific surface area of Mn-Ce catalyst is 6.3 times that ofα-Mn O2 after doping Ce,and the crystal type of the catalyst is amorphous.H2-TPR results show that the reduction temperature is reduced,which provides favorable conditions for low temperature plasma co-catalytic reduction and denitrification.(3)The effects of reactor parameters and gas component content on NTP-SCR were studied.With the increase of discharge length,the NOx removal rate decreased and the discharge mode changed.With the increase of discharge gap,NOx removal increases first and then decreases;The addition of O2 can improve the denitration effect,but with the increase of O2 content will produce a certain inhibitory effect;The best denitration effect can be obtained when the ammonia-nitrogen ratio is 1.(4)Ce metal doping can effectively improve the water and sulfur resistance of Mn-based catalyst.The addition of SO2 will be oxidized by plasma and first consume NH3,thus hindering the occurrence of SCR reaction.The doping of Ce can reduce the formation of sulfate,change the crystal shape and microstructure of catalyst,increase the number of active sites,and thus improve the water and sulfur resistance(5)The preparation method of supported catalyst and its influence on the catalyst,the Mn-Ce catalyst prepared by hydrothermal deposition method,coprecipitate method and impregnation method reached the maximum NOxremoval rate at 189J/L,216J/L and 313J/L,respectively.Ti O2 and Al2O3supported catalysts can improve the sulfur resistance of Mn O2.The tolerance degree of Mn O2/Al2O3 to SO2 is slightly lower than that of Mn O2/Ti O2.Compared with the catalyst prepared by impregnation method,the denitrification and sulfur resistance of MN-based catalyst prepared by hydrothermal deposition method are better,and the performance of Ti O2supported catalyst is better than that of Al2O3 supported catalyst. |