| A lot of the coals were used for power generation in china,and NOx and Hg0 produced by coal combustion have serious harm to human body and environment.It is a potential technology to catalytic oxidation of water-insoluble Hg0 to water-soluble Hg2+.SCR catalysts can oxidize Hg0 to Hg2+.Using the existing SCR pollution control device to simultaneously remove NO and Hg0 is a very promising technology,which is not only simple but also economical.Catalyst is the major factor for simultaneously removing Hg0 and NO.Aiming at solving the problems of the SCR catalysts which showed a poor Hg0 removal efficiency,the Co doped Ce-ZrO2 catalysts were firstly used for Hg0 adsorption and oxidation.After that Mn was loaded on Co0.3-Ce-ZrO2 to improve the SCR activity,according to the separated removal performance of NO and Hg0,the catalyst with excellent performance was selected to simultaneously remove Hg0 and NO.1.The catalysts Cox-Ce-ZrO2 were prepared by co-precipitation method,and the Hg0 adsorption and Hg0 oxidation capacity of the catalysts Cox-Ce-ZrO2 with different Co contents were investigated.The result showed that cobalt addition increased the BET surface area,improved redox activity and increased the amount of surface chemisorbed oxygen resulting in higher adsorption capacity and Hg0 oxidation efficiency.When the molar ratio of Co to Co-Ce-ZrO2 was 0.3,the catalyst Co0.3-Ce-ZrO2 had the highest adsorption and oxidation activity.The Hg0 removal efficiency of Co0.3-Ce-ZrO2 was nearly 100% in the initial 120 h and it still maintained above 80% after 164.5 h reaction,and the Hg0 oxidation efficiency of Co0.3-Ce-ZrO2 was 100% in the temperature range of 100-250 oC.2.The Mn was loaded on Co0.3-Ce-ZrO2 through impregnation method,and the separated capacity of Hg0 oxidation and NO conversion over the catalysts Mnx/Co0.3-Ce-ZrO2 were investigated.The enhanced catalytic activity of Mnx/Co0.3-Ce-ZrO2 for NO reduction was due to the existence of MnO2,and the NO conversion efficiencies of Mn0.1/Co0.3-Ce-ZrO2 and Mn0.2/Co0.3-Ce-ZrO2 both increased from 0 to 96.3% with Mn loading.However,the Hg0 oxidation efficiency was decreased after Mn addition,which was due to the decrease of chemisorbed oxygen,cobalt and Co3+.3.Considering the performance of separated activity of NO conversion and Hg0 oxidarion over the catalysts,Mn0.1/Co0.3-Ce-ZrO2 was determined for simultaneously removing NO and Hg0.The Hg0 oxidation efficiency of 83.6% and NO conversion efficiency of 89.4% were simultaneously obtained in SCR+Hg0 atmosphere under a high GHSV 180,000 h-1.It was found that the promoting effects of NO and O2 on Hg0 oxidation could not offset the inhibitive effect of NH3 on Hg0 oxidation in SCR+Hg0 atmosphere,resulting in the Hg0 oxidation efficiency in the process of simultaneously removing NO and Hg0 was lower than the efficiency of separated Hg0 oxidation;HgO accumulated on the catalyst surface bring about less available active sites,resulting in the NO conversion efficiency in the process of simultaneously removing NO and Hg0 was lower than the efficiency of separated NO conversion.4.The effects of some other gases such as O2,H2 O and SO2 on simultaneous Hg0 oxidation and NO conversion were investigated in SCR+Hg0 atmosphere.O2 could improve the catalytic activity of Mn0.1/Co0.3-Ce-ZrO2 for simultaneous Hg0 oxidation and NO conversion.While,H2 O and SO2 showed prohibitive effects on the simultaneous Hg0 oxidation and NO conversion. |