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September 3, 2004 Chemistry of SO2 on Ce1-xZrxO2 Nanoparticles and Ce1-xZrxO2(111) SurfacesJ.A. Rodriguez1, X. Wang1, G. Liu1, J. Hanson1, J. Hrbek1, C.H.F. Peden2, A. Iglesias-Juez3, and M. Fernandez-Garcia3 A major effort in environmental cleanup is controlling the emission of toxic pollutants produced during the combustion of fuels in factories, power plants, and automotive engines. Cerium oxide (CeO2) -based materials are utilized as catalysts for the destruction of one of these pollutants, sulfur dioxide (SO2), and are also used to prevent acid rain. High-resolution photoemission, time-resolved x-ray diffraction (TR-XRD), and x-ray absorption near-edge spectroscopy (XANES) were used to investigate the chemistry of SO2 on cerium oxide-zirconium (Ce1-xZrxO2) nanoparticles and Ce1-xZrxO2(111) surfaces (x ≤ 0.5). S K-edge XANES spectra pointed to sulfate (SO4) as the main product of the adsorption of SO2 on these mixed-metal oxides. Full SO2 dissociation was seen on the nanoparticles, but not on the Ce1-xZrxO2(111) surfaces. The metal cations at corner or edge sites of the Ce1-xZrxO2 nanoparticles probably play a very important role in interactions with the SO2 molecules.
Figure 1 shows the structure of an ideal Ce1-xZrxO2(111) surface (x < 0.4). The top layer consists of O atoms, but within this layer there are holes that expose the Ce or Zr cations in the second layer. This well-defined surface allows the detailed study of O↔SO2 and Ce,Zr↔SO2 interactions. For the Ce1-xZrxO2 nanoparticles, the results of transmission electron microscopy show rough surfaces that can be O or cation-terminated and have a high density of edge or corner sites. These different structural properties affect the chemical reactivity of these mixed-metal oxides.
The top of Figure 2 shows S K-edge XANES spectra for the adsorption of SO2 on CeO2(111) and Ce0.7Zr0.3O2(111) surfaces at room temperature. A comparison to the corresponding peak positions for sulfates and sulfites indicates that SO4 is the main species formed on the oxide surfaces, with a minor concentration of SO3 (SO2,gas + nOlattice → SO3,ads or SO4,ads). The cations in the second layer have all of their O neighbors (eight in total), and interact very weakly with an adsorbed SO2 molecule. One must introduce O vacancies in CeO2(111) and Ce0.7Zr0.3O2(111) to see the interaction of SO2 with the metal cations and the subsequent dissociation of the molecule.
Figure 2 also shows S K-edge XANES spectra taken after exposing nanoparticles of CeO2, Ce0.66Zr0.33O2 and Ce0.66Ca0.33O2-y to SO2 at 25 °C. Again, we found that SO4 is the main sulfur-containing species present on the oxides, but, in addition, we saw features at photon energies between 2470 and 2472 eV that denote the existence of metal-S bonds as a consequence of full SO2 dissociation. Thus, the nanoparticles have metal cations at corner or edge sites that can interact well with the SO2 molecule. In addition, there may be O vacancies in the surface of the Ce0.66Zr0.33O2 and Ce0.66Ca0.33O2-y nanoparticles that facilitate S-O bond cleavage.
Figure 3 shows the effect of temperature on the SO4 signal for the CeO2 and Ce1-xZrxO2 systems in Figure 2. As the temperature is raised, SO4 decomposes. The SO4 adsorbed on the nanoparticles is somewhat more stable than that present on the (111) surfaces. For both types of systems, the presence of Zr seems to induce an increase in the thermal stability of the adsorbed sulfate. BEAMLINE FUNDING PUBLICATION FOR MORE INFORMATION |