| Mercury and its compounds from coal-fired power plants is another major air pollutant after NOx,SO2 and fly ash,and it is the largest source of anthropogenic mercury emissions in China.With the implementation of Minamata Convention,more stringent mercury emission standards will be implemented in China.Existing pollutant control systems for coal-fired power plants can effectively remove mercury species in forms other than elemental mercury(Hg0),which is difficult to capture because of its high volatility and insolubility in water.Catalytic oxidation is a more economical technology to oxidize water-insoluble Hg0 to water-soluble oxidized mercury(Hg2+),which is then removed by the existing wet desulfurization system.The catalytic oxidation capacity of Hg0 is the key role in this technology,and CeO2 catalysts have received wide attention due to oxygen storage capacity which is benefit for the mercury removal.However,the existing CeO2-based catalysts are highly dependent on the HCl in flue gas and also poor sulfur and water resistance at low temperatures.Taking above into consideration,different morphologies of CeO2,supported RuO2/CeO2 catalysts and doped Co/Ce catalysts were used as the research systems to investigate the low temperature activity and the reaction mechanism of Hg0 oxidation.(1)CeO2 nanorods with exposed(110)facets and high oxygen vacancy concentration were developed for low-temperature Hg0 removal.The characterization results illustrate that CeO2 nanorods(CeO2-R)mainly expose(110)facets and CeO2nanoparticles(CeO2-P)mainly expose(111)facets.It is found that CeO2-R with higher oxygen vacancy concentration exhibits higher catalytic activity in the range of 100-300°C,and reaches a maximum mercury removal efficiency of 83%at 200°C.The DFT calculations show that Hg0 oxidation barrier on the surface of CeO2(110)is lower than that on the surface of CeO2(111),and the presence of oxygen vacancies facilitates O2 adsorption,thus generating new active sites for HCl activation.But a higher concentration of oxygen vacancies also leads to the embedding of Cl atoms in oxygen vacancies,leading a higher activation energy to oxidize Hg0 compared to the surface adsorbed Cl.The Hg/Cl/O catalytic cycle on the CeO2 surface can be divided into four parts:(i)HCl activation by lattice oxygen,(ii)Hg0 oxidation at the defect surface,(iii)HCl activation by adsorbed oxygen,and(iv)Hg0 oxidation at the stoichiometric surface.(2)The complete reaction mechanism of Hg/O2/SO2 on CeO2 catalysts was obtained,and the key steps to enhance the efficiency of Hg0 removal under HCl-free conditions on CeO2 nanorods are enhance the adsorption energy of Hg0 and reduce the desorption energy of HgO.It was found that the active temperature of CeO2 oxidation of Hg0 under the condition of O2 needs to reach more than 300°C,and the rate-determining step is HgO desorption.The order of the interaction between mercury species and the surface follows Hg0<HgO<HgSO4,where Hg0 cannot be adsorbed on the surface at the reaction temperature.Combining the results of mechanism analysis and DFT theoretical calculations,the reaction paths of different mechanisms in the Hg/O2 oxidation reaction were proposed,and the main contribution of Hg0 oxidation is from the E-R mechanism.SO2 in flue gas cannot directly oxidize Hg0,and low concentration of SO2 will slightly promote the oxidation of Hg0 by generating HgSO4with HgO,while high concentration of SO2 will occupy the active site and consume the active oxygen lead to a decrease in the efficiency of Hg0 oxidation.(3)Supported RuO2/CeO2 catalysts were investigated for low-temperature Hg0removal,and were found to have a stronger adsorption capacity of Hg0 adsorption and a lower reaction energy barrier for Hg0 oxidation.The results show that the RuO2/CeO2-R has more oxygen vacancies than the RuO2/CeO2-P,and it exhibited higher Hg0 removal efficiency in the range of 100-350°C,and reaching 97.1%at 200°C.Meanwhile,compared with the unloaded CeO2 nanorods,the sulfur resistance was significantly enhanced.The characterization results revealed that it is mainly the catalyst surface Ce3+that are involved in the oxidation of Hg0,while the formation of surface sulfate species(SO42-)is the main reason for the influence of SO2.In addition,Hg0 is chemisorbed on the RuO2 surface and the subsequent oxidation follows the L-H mechanism,and the active oxygen provided by the CeO2-R carrier can accelerate the oxidation of Hg0,indicating the contribution of the carrier oxygen vacancy to the oxidation of Hg0 on the RuO2 surface.(4)Among the metal-doped M/CeO2(110)(M=Co,Cu,Mn,Ni,Ru,V)surface,Co showed the lowest Hg0 adsorption energy and the lowest Hg0 oxidation reaction energy barrier,which is favorable for subsequent Hg0 removal under O2 atmosphere.In order to enhance the efficiency of Hg0 removal at low temperatures,the Hg0 adsorption characteristics of the six transition metals doped CeO2(110)surface were systematically investigated based on the key steps and reaction mechanism of Hg/O2 on the CeO2(110)surface,and the specific pathways of Hg0 oxidation were searched to clarify the changes of the reaction transition state structure and its energy barriers.Theoretical calculations show that the Co-doped catalyst has the strongest affinity for Hg0 among the six doped catalyst surfaces,with the adsorption energy reaching-47.8 k J/mol,while the Co/CeO2(110)surface also possesses the highest catalytic activity for Hg0 oxidation,and the Hg0 oxidation barrier is only 64.1 k J/mol.(5)Co-doped CeO2 nanorods were investigated as an efficient low-temperature and sulfur-resistant material for mercury removal,and the high concentration of oxygen vacancies could both promote Hg0 oxidation and inhibit SO2 adsorption.The Co doping greatly enhanced the reduction ability and oxygen vacancy concentration of the CeO2nanorods.The 0.2Co/Ce catalyst possessed the highest activity among all the catalysts,and the efficiency of mercury removal was higher than 95%in the temperature range from 100 to 200°C.Besides,the DFT results confirmed that the presence of oxygen vacancies are benefit for the oxidation of Hg0.The 0.2Co/Ce showed excellent sulfur resistance,which was found by the electron transfer between Co and Ce inhibit the adsorption and oxidation of SO2 on the surface.However,H2O is easily adsorbed and dissociated on the oxygen vacancy site.On the one hand,the H2O/OH adsorbed on the active site will inhibit the adsorption of Hg0,and on the other hand,the redox cycle of the active site will be broken and the oxidation of Hg0 will be inhibited by the inability to continue to produce surface active oxygen. |