Selective catalytic reduction (SCR) units can be exploited to reduce Hg emissions from coal-based power plants; hereby, Hg 0 is oxidized into Hg 2+ , which has a higher solubility than the former and can therefore be scrubbed before leaving the stacks. With the purpose of examining the effect of the surface composition and surface coverage on the reactivity of a commercial SCR catalyst (V 2 O 5 −WO 3 −TiO 2 ) toward Hg oxidation, two models were used to represent TiO 2 -supported systems with low and high loading of the two active phases (i.e., V 2 O 5 and WO 3 ). The reactivities of these systems were compared through the analysis of the adsorption energies of Hg, Cl• , HgCl, and HCl, which are likely involved in the Hg oxidation mechanism. These adsorption energies were complemented by results from both the Bader charge and projected density of states (PDOS) analyses, thus providing an increased understanding of the effects of surface coverage and composition on the electronic structure of these materials. An enhanced reactivity of the SCR catalyst is observed with increasing loadings of both V 2 O 5 and WO 3 phases. Binary systems (i.e., V 2 O 5 −TiO 2 or WO 3 −TiO 2 ) were compared against ternary systems (V 2 O 5 −WO 3 −TiO 2 with different V 2 O 5 /WO 3 ratios) and indicate a higher reactivity of the latter.
■ INTRODUCTIONThe annual estimation of Hg emission from natural and coalfired power plants in the United States corresponds to 48 tons, about one-third of the total amount of mercury released by anthropogenic sources of this country.1 As the environmental and health problems associated with the mercury emissions from stationary sources become an obvious problem, the U.S. Environment Protection Agency set in 2011 a series of emission standards to limit these emissions. These standards state that the U.S. natural gas and coal-fired power plants are forced to install air pollution control devices to prevent 91% of the Hg present in flue gas from being released.
2The insolubility and inertness of Hg 0 make its capture difficult. Promoting its oxidation along the path of the flue gas from the boiler to the stack is the best removal strategy using current emission control technologies. Mercury oxidation has been observed across the selective catalytic reduction (SCR) unit with a primary purpose of controlling NO x emissions by reducing them to N 2 and water vapor using ammonia (NH 3 ). Employing an already existing air pollution control device such as the SCR unit to tackle the Hg problem is an attractive approach due to the lower economic invesment and the environmental and heath benefits of reducing Hg emissions.Commercial SCR catalysts employ the anatase phase of TiO 2 as a support material for the active phases which consists of vanadium and tungsten oxides.3,4 The vanadia phase V 2 O 5 not only catalyzes NO x reduction 5 and Hg 0 oxidation 6 but also the undesired SO 2 to SO 3 oxidation reaction.7 It has been proven experimentally that higher catalytic activities are reached with increasing V ...