Propane oxidation by vanadium supported on activated carbon from sugarcane straw Virgílio J. M F. Netoa, Thiago de S. Belana, André L. L. Magalhãesa, Alexandre B. Gaspara, Paulo G. Pries de Oliveiraa, Fabiana M. T. Mendes a*. a Nacional Institute of Technology, Catalysis and Chemical Process Division- DCAP, Rio de Janeiro, 20081-312, Brazil *Corresponding author: [email protected] * Keywords: activated carbon, sugarcane straw, propane oxidation, support acid–base character. 1. Introduction In Brazil, the sugar and alcohol industry generates around 597 million tons of waste per year, such as bagasse and straw from sugarcane [1]. The valuation of these wastes using them as a renewable raw material is extremely important. In a near future, the sugarcane harvest will be completely converted from manual to mechanized, which will increase the amount of this waste [2]. The use of biomass to produce activated carbon and its market is well established and allows its widespread use in the environmental, industrial and other sectors for removing, recovering, separating and modifying a variety of species in liquid- and gas-phase applications. The physicochemical characteristics of the activated carbon material has motivated recent studies involving synthesis and application also in different catalytic processes, especially, in Propane Oxidation Reaction [3, 4]. These researchers used for the first time an activated carbon obtained from orange skin residue to support vanadium active sites and got promising catalyst activity, although little is still known. New efforts, but using sugarcane straw instead to obtain a new activated carbon support has been conducted [5]. Besides, when using an activated carbon as support, several physical chemical properties, such as surface area, pore distribution and surface acidity, out to be investigated. The structure of activated carbon supported vanadia catalyst have not been fully explored, as for alumina support [6] and there are no reports at all, when using it prepared from sugarcane straw. Propane Oxidation Reaction has been studied for many decades [7] and still is a challenge regarding feasible and economic innovation, which goes through the search for a higher yield of propylene or oxy-compounds. Vanadium based catalysts are recognized to provide sites that activate the CH bond, form oxygen intermediates and avoid the formation of CO and CO2. However, the structure and redox properties of VOx surface species can govern the reaction mechanism, being more active at submonolayer coverage [7], where isolated tetrahedral VOx species are present. On the other hand, the acid–base character of the support can control the vanadium catalyst reactivity/selectivity and influence both the reactants and product adsorption/desorption. A support with low acidity, with dominant Brøns andted acid sites, usually facilitate rapid propylene desorption and prevents its further oxidation to COx. As activated carbon surface acid groups, can significantly vary per the biomass source used in its preparation, so, the support acid–base character and strength, must be investigated. The present work aims to evaluate the new prepared activated carbon (from sugarcane straw) as a support for vanadium sites towards propane oxidation reaction. Furthermore, compare some of important properties of the new support with that presented by industrial produced activated carbon. The discussion is conducted in terms of their textural properties and nature of surface functional groups. 2. Experimental Sugar cane straw was chemically activated with a solution 85% (w/w) H3PO4 accordingly with the methodology previously described [5], obtaining ("SAC") activated carbon. A commercial activated carbon purchased from Vetec ("VAC") and other, from Alphacarbo Company, ("AAC"), were also used as support. A solution containing vanadium precursor (NH4VO3) and oxalic acid was used to prepare 3wt% VOx supported catalysts. The materials were calcined under synthetic air flow (40 ml/min) up to 500°C (5°C/min), and kept for 5h. N2 adsorption-desorption experiments ware done with ASAP 2020 equipment (Micromeritics). Boehm titration [8] was performed to verify the activated carbon surface acid groups. Thermal desorption of NH3 was done with He flow (30mL/min) up to 500°C, at 10 °C/min. The total number of acid sites were determined using a thermo conductive detector (TCD). Chemical analysis and micrographs were obtained with a scanning electron microscope with energy dispersive analysis (SEM-EDS- Inspect S50 FEI). Propane oxidation reaction was conducted in a conventional fixed bed reactor at 380 °C, coupled with a gas chromatograph with FID and TCD detectors. Reaction conditions were 13% C3H6, 18% O2, 69% N2, volume), at a total flow of 35 ml/min, with the O/C3 ratio of 1.3. 3. Results and discussion Table 1 shows the activated carbons characterization. The isotherm of all materials exhibits a modified type II isotherm, with a hysteresis loop, suggesting a broad pore size distribution. A high specific surface area activated carbon can be obtained from sugarcane straw (SAC), which has a quite similar surface area than the one from Alphacarbo, both being higher the one from Vetec. SAC and AAC activated carbon materials exhibits comparable surface area and particle size, but SAC with a little greater pore volume than the commercial materials. Vanadium catalyst presents a drop down in surface area (around 800m2/g), but no major changes in pore volume. Bohem titration revels the major presence of carboxylic groups for SAC support, while commercial support have mainly phenolic surface groups. TPD-NH3 analysis, reinforces the higher acidic character of the activated carbon (SAC and AAC) surface. The activated carbon from Vetec is the one with which has the less acid character (nature and quantity). Table 1. Texture properties, Boehm titration and NH3-TPD Boehm NH3-TPD SBET Vp (m Eq/g C) (mmols/g) Carbon 2 3 (m /g) (cm /g) Ph/L/C* SAC 1279 1.3 0.19/0.15/0.97 0,57 AAC 1343 1.0 0.80/0.14/0.36 0,85 VAC 785 0.2 0.34/0.05/0.03 0,24 *Ph: phenolic, L: lactonic, C: carboxylic The low vanadium loading, in present paper, was intended to keep vanadium species far from theoretical monolayer coverage (2.9 Vatoms/nm2) aiming to understand support surface influence on reaction activity/selectivity. Ghamdi et al [6] reports that vanadia species are more selective towards propylene, but less active and upon an increasing amount, polyvanadates dominates the surface species, enhancing activity and decreasing selectivity. Figure 1 shows Propane conversion as a function of time. All catalysts were capable to convert propane molecule to propylene. However, the obtained low propylene and high COx selectivity, can be related to the support surface acidity, as well as the amount and type of surface oxygen available. At a very low vanadium surface density (around 0.1 V atoms/nm2), support acidity plays the main role, controlling the catalyst activity and selectivity. Catalysts with stronger surface acid groups favor propylene further oxidation into combustion products, but these acidic sites are needed to maintain activity. Figure 1 – Propane conversion versus reaction time 4. Conclusions. In this work, for the first time, activated carbon obtained from sugarcane straw is used as vanadium support. The obtained catalysts are active for propane conversion. Surface properties of these activated carbon materials controls selectivity, especially at very low vanadium density. Even though vanadium sites are capable to convert propane into propylene, the strong acid sites from the support surface seems to retain propylene, converting it to fully oxidation COx compounds. Furthermore, activated carbon obtained from sugarcane straw has quite similar texture properties than the industrial one from Alphacarbo, but distinct properties with respect to the one from Vetec, especially surface and surface acidity. All these findings stimulate its application as a catalysts support in oxidation catalysis. The possibility of waste (sugarcane straw) valorization opens a range of opportunities. Acknowledgments We acknowledge the financial support from our sponsors, CNPq-PCI and CIEE and The Alphacarbo Co and Biocatalyis Laboratory (LABIC-DCAP). References [1] Viridiana. S. Ferreira-Leitão, Leda M. Gottschalk, Maria A. Ferrara, Alexandre L. Nepomuceno, Hugo B. C. Molinari, Elba P. S. Bon, Waste Biomass Valor. 2010, 1, 65. [2] Brazilian State of São Paulo Law: Lei nº 11.241/02. http://governo-sp.jusbrasil.com.br/legislacao/94008/lei-1124102 (Last access on November 8th, 2016). [3] M. O. Guerrero-Pérez, J. M. Rosas, R. López-Medina, M. A. Banares, J. Rodríguez-Mirasol, T. Cordero, Catalysis Communications 2011, 12(11), 989. [4] M.J.Valero-Romero, A. Cabrera-Molina, M. O. Guerrero Pérez, J. Rodríguez-Mirasol, T. Cordero, Catalysis Today, 2014, 227, 233. [5] F. M. T. Mendes, A. C. C. Marques, D. L. Mendonça, M. S. Oliveira, R. O. Moutta, V. S. Ferreira-Leitão, Waste and Biomass Valorization, 2015, 433. [6] S. A. Al-Ghamdi, H. I. de Lasa, Fuel, 2014, 128, 120. [7] M. Sun, J. Zhang, P. Putaj, V. Caps, F. Lefebvre, J. Pelletier, J. Basset, Chem. Rev., 2014, 114, 981. [8] H. P. Boehm. Carbon. 2002, 40, 145-149.
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