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MANGANESE OXIDES PURE CATALYSTS SYNTHESIZED WITH SOLUTION COMBUSTION SYNTHESIS FOR LT NH3

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MANGANESE OXIDES PURE CATALYSTS SYNTHESIZED WITH SOLUTION COMBUSTION SYNTHESIS FOR LT NH3-SCR

S. Andreoli, F.A. Deorsola, B. Bonelli, R. Pirone

Dipartimento di Scienza Applicata e Tecnologia, Politecnico di Torino, corso Duca degli Abruzzi, 24;

10124 Torino

Manganese oxides based catalysts have been investigated in recent years for low temperature applications because of their eco-compatibility, versatility and the presence of a certain degree of labile oxygen. Moreover their redox properties, due to the existence of many manganese oxidation states and oxides (MnO, Mn2O3, Mn3O4, Mn5O8 and MnO2), helped to make the catalysts interesting for SCR process (Selective Catalytic Reduction with ammonia) in the

“low temperature region” (120-300 °C) for the abatement of nitrogen oxides in both stationary and automotive fields [1].

Such a technology is under revision in recent years to perform the abatement of nitrogen oxides in mobile sources too, since especially for diesel engines no solution seems to be viable with non-specific reductants (CO, HCs), with the consequent necessity to develop active catalysts for the reduction of NOx with NH3 in a significantly lower temperature range.

Nitrogen oxides (NO, N2O and NO2) are, in fact, well-known atmospheric pollutants, by- produced during combustion at high temperature from stationary and mobile sources.

The aim of this work was the synthesis of pure manganese oxides through the Solution Combustion Synthesis (SCS) method and investigate on the ultimate properties of Mn to be performant in the process.

Two parameters were modified during the synthesis procedure: the oven temperature (400 and 600 °C) and the ratio glycine/nitrate (1:2 in samples G1N2 and 2:1 in samples G2N1) in order to obtain different effects on the structure, the crystallinity, the morphology and the SSA of the MnOx catalysts.

The samples have been characterized by XRD, BET, H2-TPR, NH3-TPD, XPS, FESEM and their catalytic activity tested for NOx removal in a NH3/NOx gas mixture.

It is important to notice that the average Mn oxidation state (calculated through H2-TPR tests and verified through XPS analysis), the specific surface area, the degree of crystallinity, the morphology and the presence of both BrØnsted and Lewis acids sites influenced the catalytic activity and the selectivity to N2.

Furthermore, in order to investigate the role of ammonia, particularly its attitude to be oxidized and its influence on the catalyst surface, NH3-TPD (temperature programmed desorption) analyses were performed with the scope to determine the real mechanism of NOx

reduction during the LT-SCR. In such a way, it was possible to study the catalyst surfaces deepening the binding states and the interaction between NH3 and unsupported MnOx.

The XRD analysis showed that the samples obtained in sub-stoichiometric conditions (G1N2) were mainly constituted by the Mn2O3 phase, whereas the over-stoichiometric ones (G2N1) by the Mn3O4 phase. These results were also confirmed by the calculation of the Mn average oxidation state in the H2-TPR analysis [2]. The samples G1N2 were characterized by sharper and more intense peaks with respect to the G2N1 samples, resulting in a more crystallized structure. Furthermore, the samples synthesized at lower temperature (400 °C) presented a weaker crystallinity rather than the samples synthesized at higher temperature.

It has been reported that the catalytic reduction of NOx is strictly correlated with the concentration of reactive surface oxygen because a high concentration of surface oxygen favours the formation of the (-NH2) specie that reacts with NO to form N2. The samples

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containing Mn2O3 as main phase showed a very similar amount of Oα, while the ones with Mn3O4 as main phase featured a higher content of surface oxygen due to the more marked amorphous character. The G2N1 samples were also characterized by a Mn3+/Mn2+ ratio that was close to unity, since Mn3O4 was the main phase and it consists of a solid solution of MnO and Mn2O3.

The H2-TPR results are illustrated in the Table below, completed with the results of the chemical-physical properties of the catalysts. It is possible to summarize that for the samples G1N2 the oxidation state decreased by increasing the temperature of synthesis due to the decreased cristallinity of the samples, meaning a high availability of surface defects and labile oxygen.

The MnOx phase, and the Mn oxidation state, significantly affected the catalytic performances, as depicted in the Figure below. It is worth to highlight that the Mn3O4 phase could give benefits to the SCR activity at low temperature (120-305 °C) with respect to the other MnOx phases synthesized.

Moreover, in order to understand the origin of the products in the selective reduction of NOx, in particular N2O, the analysis of the oxidation of ammonia was performed, obtaining that the samples synthesized at 600 °C presented longer adsorption time of ammonia and this explained the fact that these curves reached the total conversion slowly than the samples obtained at 400 °C.[3]

References:

[1] Marbàan, G.; Valdès-Solìs, T.; Fuertes, A.B.; Journal of Catalysis 226(2004)138-155.

[2] Stobbe, E.R.; de Boer, B.A.; Geus, J.W.; Catal. Today 47 (1999 ) 161-167 [3] Fang, D.; He, F.; Li, D.; Xie J.; Appl. Surf. Sci. 285B (2013) 215-219

Sample H2 (µmol/g) Theoretical amount of Mn

Average oxidation

state

H2/Mn BET specific area[m2/g]

G1N2_600 6113 69,6% 2,97 0,48 50

G2N1_600 4285 72,0% 2,65 0,33 31

G1N2_400 7970 69,7% 3,26 0,65 40

G2N1_400 4424 72,0% 2,67 0,34 80

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