First principles and experimental study of NH3 adsorptions on MnOx surface
Graphical abstract
The shorter MnN bonds and the more negative Eads values indicated that NH3 adsorptions took place easily on Mn2O3 (2 2 2) and Mn3O4 (2 1 1) surfaces, which was in line with the NH3-TPD and NH3-SCR performances.
Introduction
The difficulty of nitrogen oxide removal has become a serious concern [1], [2] and selective catalytic reduction (SCR) with NH3 is widely applied to remove NOx [3], [4]. Moreover, MnOx on different supports have excellent catalytic activities in the low-temperature SCR reaction for the removal of NOx from stationary sources [5], [6], [7], [8]. Recently, the MnOx and CeOx supported on carbon nanotubes displayed better NH3-SCR activity, higher SO2-tolerance and improved water-resistance. On the other hand, the catalyst obtained from the pyridine-thermal route presents excellent SO2 resistance, better NH3-SCR activity as well as favorable stability [9], [10]. In addition, the MnOx contains various types of labile oxygen to complete a catalytic cycle [11]. The activity and selectivity of pure manganese oxides in SCR at significantly low temperatures have been studied by many researchers [12], [13], [14]. However, doping metals can enhance NO conversion and N2 selectivity of the manganese oxide-based catalysts in low-temperature SCR with NH3. With a broad operation temperature window, NiMnFe mixed oxides show enhanced performance for the SCR of NO with NH3 [15]. MnOx/ZrO2–CeO2 nanorods show the excellent catalytic activity that should be attributed to the adsorbed surface oxygen and oxygen vacancies [16]. It was widely accepted that the first step in SCR was an oxidative abstraction of hydrogen from adsorbed ammonia [4], [13]. Therefore, NH3 adsorptions played a significant role in the mechanism of SCR with NH3 [13], [17], [18], [19], [20]. NH3 was adsorbed on both Bronsted and Lewis acid sites and amide species were present at the surface, mainly on Mn sites [19], [21]. Most performance and mechanism studies concentrated on the SCR reaction process [5], [7], [18], while little attention was paid to NH3 adsorptions on the MnOx surfaces. In fact, the surface reactivity of the metal oxide was closely connected to the presence of adsorption capacity. The adsorption of gas-phase reagent at surfaces played an important part in many types of heterogeneous catalysis [22]. Consequently the adsorptions of NH3 molecules on metallic oxides surfaces were studied by DFT method in previous researches [23], [24], [25], [26]. Based on the combination of experimental and theoretical investigations, Maitarad found the Mn@CeO2(1 1 0) model in the DFT analysis showed a prominent effect on the NO and NH3 adsorption and the catalysts exhibited a better catalytic performance [27].
In this study, MnOx catalysts were characterized by X-ray diffraction (XRD) and ammonia temperature programmed desorption (NH3-TPD). NH3 adsorptions on the Mn2O3 (2 2 2), Mn3O4 (2 1 1) and MnO2 (1 1 0) surfaces were investigated using a DFT method, systematically. By the means of the NH3-TPD and SCR performance below 433 K, Mn2O3 and Mn3O4 showed significantly higher amount of adsorption of NH3 and NO conversion, except MnO2. At the same time, the adsorptions of NH3 molecules on metallic oxides surfaces were studied by DFT method using the generalized gradient approximation (GGA).
Section snippets
Surface methods
The calculations in this work are performed using the program package CASTEP, which is a DFT code, working in a plane wave basis set. The electron-ion interaction is described using the ultrasoft Vanderbilt-type pseudopotentials, with a plane wave energy cutoff of 340 eV. We used the GGA of PW91 for the exchange-correlation energy. The subatrate is modeled by six layers of MnOx separated by a vacuum layer of 10 Å. The two uppermost substrate layers and the NH3 molecule are allowed to relax. This
XRD patterns
XRD patterns of pure MnOx were shown in Fig. 2, indicating that the peaks attributed to oxidized species of manganese. The diffractions of Mn2O3 [JCPDS No. 89-4836, Cubic, space group: Ia-3 (206)], Mn3O4 [JCPDS No. 75-1560, Tetragonal, space group: I41/amd (141)] and MnO2 [JCPDS No. 24-735, Tetragonal, space group: P42/mnm (136)] were observed. There are some published works on the Mn2O3 (2 2 2), Mn3O4 (2 1 1) and MnO2 (1 1 0) surfaces [28], [29], [30], but few of them are on MnOx/NH3 system. Clear
Conclusion
Density functional theory calculations have been carried out to investigate the NH3 adsorption on Mn2O3 (2 2 2), Mn3O4 (2 1 1) and MnO2 (1 1 0) surfaces. The optimized geometries and adsorption energies showed that Mn2O3 (2 2 2) and Mn3O4 (2 1 1) surfaces were active for NH3 adsorption. However, NH3 adsorption carried out difficultly on the MnO2 (1 1 0) surface. The calculations also suggested that the more negative Eads values of Mn2O3–NH3 and Mn3O4–NH3 were −1.31 eV and −1.44 eV, which led to the easiness
Acknowledgements
This work was financially supported by the National “Twelfth Five-Year” Plan for Science & Technology Support of China (2011BAE29B02). And the tests of XRD were supported by Research and Test Center of Materials, Wuhan University of Technology. TPD tests were supported by State Key Laboratory of Silicate Materials for Architectures, Wuhan University of Technology.
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