(402e) Syngas Production By Biogas Steam and Oxy Steam Reforming Processes on Rh/CeO2 Catalyst Coated on Ceramics Monolith and Open Foams
AIChE Annual Meeting
2015
2015 AIChE Annual Meeting Proceedings
Advances in Fossil Energy R&D
Fuel Processing for Hydrogen Production I
Tuesday, November 10, 2015 - 4:35pm to 4:55pm
Today there is a worldwide interest in the use of biofuel as an environmental friendly renewable energy source [1]. Biogas can be considered as one of the most widespread renewable fuel obtained from biomass produced from a variety of organic raw materials in various sectors ranging from zootechnical to agro-industrial [2-3]. Biogas, basically, it is constituted by 50-75% CH4, 25-45% CO2, 2-7% H2O (at 20-40 °C), 2% N2, less than 1% H2/H2S and traces of O2, NH3, halides and siloxanes [4]. The utilization of biogas to produce syngas/hydrogen by reforming processes [5] to feed fuel cells represents an alternative route to the traditional utilization of this renewable fuel in less efficient and polluting engines to produce energy and heat. Among the possible reforming reactions, steam reforming (SR) is widely used for hydrogen production. It is the largest and generally most economical route especially for industrial applications [6]. However, SR is strongly endothermic, and large amount of heat supply is required. Another option can be represented by the oxy steam reforming (OSR) process. The simultaneous occurrence of the reactions due to the presence of O2 and H2O can help to overcome critical factors as the deactivation by coke deposition reducing at the same time the overall endothermicity of the process [7]. One of the central issue of reforming processes is the development of efficient, stable and low cost catalysts. The most used catalysts in reforming processes are based on transition metals supported on oxides. Noble metals (Pt, Rh, Ru, Pd, Ir) are normally, more active and tolerant to coke formation [8] with respect to other transition metals as Ni. However, an excessive use of these elements increases the total cost of the catalyst. Another important challenge is the development of more compact and lightweight fuel processors, especially to achieve the targets for small-scale applications such as for distributed hydrogen production [9]. In this respect different catalyst configurations (foams, honeycombs, gauze, microchannels) were proposed as alternative to traditional packed-bed reactors for the realization of compact reactors [10]. The advantages of structured catalysts are related especially to the large surface-to-volume ratio that leads to good heat and mass transfer properties and low pressure drop. In this work, the performances of structured catalysts, based on Rh (1.5 wt.%), supported on CeO2, coated on cordierite monoliths (400 cpsi, diameter 1 cm, length 1.5 cm) and alumina foams (20, 30, 40 ppi) were investigated and compared. The structured support was lined by combining the solution combustion synthesis with the impregnation technique [11-13]. The deposition process was repeated several times until reaching the desired amount of catalytic layer over the supports (6.5 mg cm–2 referred as weight of active metal plus oxide carrier on the bare support geometric surface). In addition to the preparation of the coated monoliths, the corresponding catalyst at powder level was prepared and used for the chemical-physical characterization of the supported catalyst (XRD, TEM, SEM and chemisorption analyses). The pressure drop and the porosity across the bare ceramics supports and the structured catalysts were determined at different superficial velocities and compared. In addition the adherence between the catalytic layer and the support walls was evaluated via sonication treatment [12,13]. Biogas OSR and SR experiments were conducted in a fixed-bed quartz reactor with inner diameter of 1 cm at atmospheric pressure. The structured catalysts were placed between two quartz wool plugs in the center of the quartz tube, inserted into a furnace heated at the reaction temperature TSET and controlled through a PID temperature controller. Instead, the influence of temperature and of the WSV was assessed on all the prepared structured catalysts varying the temperature (TSET) between 700–900 °C and the WSV between 34,000 and 18,000,000 Nml gcat–1 h–1 at fixed S/C =1 for the SR reaction, and the temperature (TSET) between 700–900 °C and the WSV between 36,000 and 24,0000,00 Nml gcat–1 h–1 at fixed S/C =1 and O/C = 0.2 for the OSR reaction. Model biogas containing 60% CH4 and 40% CO2, was prepared from high purity CH4, O2 and N2 gas cylinders. Steam was added to the feed by using an isocratic pump and a specially designed evaporator. The feed and reaction products were analyzed using an Agilent 6890 Plus gas chromatograph equipped with thermal conductivity (TCD) and flame ionization (FID) detectors. Before testing the catalytic performance of the prepared monoliths, each coated support was reduced under hydrogen-rich atmosphere directly in the quartz reactor of the test rig. All the structured catalysts showed a uniform thin coating with thickness between 20–30 µm, high mechanical strength and low pressure drop. In detail the monolith based catalyst has shown a negligible weight loss (0.4%) of the catalytic layers after two sanction baths (1 h overall) in a mixture of water and acetone (50–50 wt.%), instead the foam based samples have shown a higher loss of catalytic layer. This different behaviour is probably due to the different surface morphology of bare supports, the bare monolith is characterized by the presence of a more intense macro-porosity over the walls respect the surface of the foams supports, this can help to obtain a more stable layer of CeO2 during the first step of coating procedure. Also, regarding the pressure drop measurement there are differences between the foam and monoliths. The monolith based catalysts show a lower pressure drop respect that of the foam catalysts, in addition the values increase increasing the ppi. Both monolith an foam catalysts have shown good performances during SR and OSR processes at all the WSV investigated in terms of high CH4 conversion (99.9–98% for SR and 99.9–96% for OSR), high H2 concentration (64-62% for SR and ≈58% for OSR, in dry basis and nitrogen free), the H2/CO ratio changed from about 2.8 for the SR to 1.9 for the OSR. The utilization of CO2 contained in the biogas in both reforming processes was also registered, the results have shown that the CO2 conversion can be regulated principally tuning the S/C and the O/C molar ratio. In SR reforming condition, increasing the WSV, the CO2 conversion decreased from 10 to 3%, instead in OSR condition it decreased from 49 to 42%. The presence of O2 and lower amount of steam in the OSR process probably leads to convert more CO2 trough the dry reforming reaction that is disadvantaged in SR condition by the large presence of steam.
[1] E. Shafiei, B. Davidsdottir, J. Leaver, H. Stefansson, E. I. Asgeirsson. Comparative analysis of hydrogen, biofuels and electricity transitional pathways to sustainable transport in a renewable-based energy system. Energy 83,2015,614–627.
[2] W. Edelmann Biogas production and usage. In: Kaltschmitt M, Hartmann H, editors. Energy from biomass: basic principles, technologies and processes. Leipzig, Germany: Springer; 2001.
[3] G. Alkanok, B. Demirel, T.T. Onay. Determination of biogas generation potential as a renewable energy source from supermarket wastes. Waste Manag. 34,2014,134-140.
[4] I. Wheeldon, C. Caners, K. Karan, Brant Peppleyd, Utilization of biogas generated from Ontario wastewater treatment plants in solid oxide fuel cell systems: A process modeling study. Int. J. Green Energy 4,2007,221–231.
[5] J. Xuan, M.K.H. Leung, D.Y.C. Leung, M. Ni, A review of biomass-derived fuel processors for fuel cell systems, Renew. Sust. Energy Reviews 13,2009,1301–1313.
[6] M. Ashrafi, T. Proll, C. Pfeifer, H. Hofbauer. Experimental study of model biogas catalytic steam reforming: 1. thermodynamic optimization. Energy Fuels 22,2008,4182–4189.
[7] U. Amjad, A.Vita, C. Galletti, L. Pino, S. Specchia. Comparative study on steam and oxidative steam reforming of methane with noble metal catalysts. Ind. Eng. Chem. Res. 52,2013,15428−15436.
[8] L. Pino, A.Vita, F. Cipitì, M. Laganà, V. Recupero, Catalytic performance of Ce1-xNixO2 catalysts for propane oxidative steam reforming. Catal. Lett. 122, 2008, 121–130.
[9] S. Specchia, Fuel processing activities at European level: A panoramic overview. Int. J. Hydrogen Energy 39,2014,17953–17968.
[10] G. Kolb, T. Baier, J. Schürer, D.Tiemanna, A. Ziogas, H. Ehwald, P. Alphonse, A micro-structured 5 kW complete fuel processor for iso-octane as hydrogen supply system for mobile auxiliary power units: Part I. Development of autothermal reforming catalyst and reactor. Chem. Eng. J. 137,2008,653–663.
[11] S. Specchia, E. Finocchio, G. Busca, V. Specchia, Combustion synthesis, Lackner M, Winter F and Agarwal AK, Handobook of combustion, Wiley-VCH Verlag GmbH & Co. KGaA, Volume 5, Chapter 17, Weinheim (Germany), 2011, 439–472.
[12] A.Vita, G. Cristiano, C. Italiano, S. Specchia, F. Cipitì, V. Specchia, Methane oxy-steam reforming reaction: performances of Ru/γ-Al2O3 catalysts loaded on structured cordierite monoliths. Int. J. Hydrogen Energy 39,2014,18592–18603.
[13] A.Vita, G. Cristiano, C. Italiano, L. Pino, S. Specchia, Syngas production by methane oxy-steam reforming on Me/CeO2 (Me = Rh,Pt,Ni) catalyst lined on cordierite monoliths. Appl. Catal. B: Environ. 162,2015,551–563.
Acknowledgements
This work was funded by the Italian Ministry of Education, University and Research (MIUR, PRIN 2010–2011) within the project IFOAMS (“Intensification of catalytic processes for clean energy, low-emission transport and sustainable chemistry using open-cell FOAMS as novel advanced structured materials”, protocol no.2010XFT2BB).