A 10 kw class natural gas-pemfc distributed heat and power cogeneration system

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Available online at www.sciencedirect.com Energy Procedia 28 (2012 ) 162 169 Fuel Cells 2012 Science & Technology A Grove Fuel Cell Event A 10 kw class natural gas-pemfc distributed heat and power cogeneration system Wanliang Mi a,b, Qingquan Su *a,b, Cheng Bao a, Li Wang a,b a Department of Thermal Science & Energy Engineering, University of Science & Technology Beijing, Beijing 100083, China b Beijing Engineering Research Center for Energy Saving and Environmental Protection, Beijing 100083, China Abstract A 10 kw class prototype of natural gas-pemfc distributed heat and power cogeneration system has been developed and demonstrated for the first time in China. In this system, fuel processing including steps of natural gas desulfurisation, steam reforming, CO water gas shift, and CO preferential methanation for CO deep removal has been applied. The 10 kw class prototype was developed with design dimensions of 1600 mm (L) 1700 mm (H) 600 mm (W). It mainly comprises natural gas reformer, reformate gas moisturiser, PEMFC stack, heat recovery unit, DC/AC inverter, and controlling computer. At a steady state, the reformate gas obtained through the fuel processor has a composition of higher than 75% H 2, about 21% CO 2, less than 4% CH 4, less than 10 ppm(v/v) CO, and less than 10 ppb(g/v) sulfur in dry base. The prototype could supply about 8 kw AC power and about 10 kw heat. During increasing DC power output from 0.8 kw to 8 kw, DC and AC efficiency were higher than 40% and 35%, respectively, and the reformer efficiency higher than 75% (LHV). The efficiency of heat recovery reached 45%, so the total efficiency for cogeneration was higher than 80%. The efficiency of the inverter was basically higher than 90%. The PEMFC cogeneration system is suitable to be applied in small-scale hotels, community buildings etc. for supplying clean and high-efficiency electricity and hot water at the same time. 2012 2012 Published by by Elsevier Elsevier Ltd. Ltd. Selection Selection and/or and/or peer-review peer-review under under responsibility responsibility of the of Grove the Grove Steering Committee. Steering Committee Keywords: PEMFC; Natural gas; Heat and power cogeneration; 10 kw class; Reforming 1. Introduction For addressing the global energy shortage and environment pollution, much attention has been paid to distributed heat and power cogeneration systems, especially for demands of small and medium size with * Corresponding author. Tel: +86-010-62333542; fax: +86-010-62333542. E-mail address: suqingquan@ustb.edu.cn 1876-6102 2012 Published by Elsevier Ltd. Selection and/or peer-review under responsibility of the Grove Steering Committee. doi:10.1016/j.egypro.2012.08.050

Wanliang Mi et al. / Energy Procedia 28 ( 2012 ) 162 169 163 higher efficiency and quality, and lower environmental impacts [1 4]. The proton exchange membrane fuel cell (PEMFC) using hydrogen as fuel has now been commercialised, but its growth is limited by the hydrogen storage, since the current hydrogen storage technology has not yet reached competitive targets [5]. Natural gas is seen as an ideal hydrogen source for PEMFC systems because of its excellent availability through the urban distribution network, so applying a fuel processor in PEMFC systems should be a promising way to meet the issue of hydrogen storage. Among methods of hydrogen production from natural gas, such as steam reforming, catalytic partial oxidation, and autothermal reforming, the steam reforming method is relatively mature and more efficient. Urban natural gas usually contains some sulfur compounds from safety considerations, and the reformed feed gas always contains some carbon dioxide (CO 2 ), while the trace amount of CO and sulfur could poison the anode catalyst and thus reduce the efficiency of the PEMFC [6]. So, it is important to deeply remove sulfur and CO in the feed gas. This paper aims to present a natural gas reforming process including deep removal methods of sulfur and CO, and the performance of a 10 kw class prototype of a heat and power cogeneration system mainly consisting of a 10 kw natural gas steam reformer and a 10 kw PEMFC stack. 2. Experimental 2.1. Fuel desulfurisation Tetrahydrothiofene of about 5 ppm(g/v) is the main sulfur compound in the natural gas in Beijing City. The sulfur was deeply removed over Cu-Zn/Al 2 O 3 catalyst through chemical reaction and chemisorption in order to prevent poisoning of the following catalyst in this heat and power cogeneration system. As shown in Fig. 1, a sulfur content of below 10 ppb was reached under reaction temperature higher than 280 C, and gas space velocity (SV) lower than 2400 h 1. Fig.1. The effect of reaction temperature on natural gas desulfurisation depth over Cu-Zn/Al 2O 3 catalyst.

164 Wanliang Mi et al. / Energy Procedia 28 ( 2012 ) 162 169 2.2. Natural gas steam reforming Natural gas steam reforming occurred when outlet temperature of the reaction was higher than 700 0 C for keeping high CH 4 conversion with SV of 400 h -1 and H 2 O/C (molar ratio) of 3. In this case, one kind of cheap and fully developed Ni-based catalyst was used in the natural gas reforming process. As shown in Fig. 2, a simulation line of CH 4 conversion according to the thermodynamic equilibrium constants was also given out at the same time. When outlet temperature of the reaction is higher than 700 0 C, CH 4 conversion is higher than 96% nearly to the equilibrium conversion [7]. Fig.2. The effect of reaction temperature on CH 4 conversion over steam reforming Ni/Al 2O 3 catalyst. 2.3. CO water gas shift A CO water gas shift process with substitution of Cu-Zn/Al 2 O 3 catalyst for Fe-Cr/Al 2 O 3 catalyst was suggested at high SV of 4000 h 1 in the high-temperature CO water gas shift (HTS), in which the CO content could be reduced to below 3% from an inlet content of 10% in the temperature range 220 370 C, as shown in Fig. 3 [8]. When the outlet temperature was controlled at 160 260 C with SV of 1000 h 1, the CO outlet content could be lower than 1% on the same Cu-Zn/Al 2 O 3 catalyst in the low-temperature CO water gas shift (LTS). In fact, here the same catalyst Cu-Zn/Al 2 O 3 is used in both the HTS and LTS. The high SV in the HTS could effectively reduce the outlet temperature to avoid the sintering of the Cu- Zn/Al 2 O 3 catalyst to a certain degree. Moreover, although the activity of the Cu-Zn/Al 2 O 3 catalyst decreased quickly to a large degree at high temperature, the sintering experiment showed that the amount of CO chemisorption on Cu-Zn/Al 2 O 3 was still higher than that on Fe-Cr/Al 2 O 3 at 450 C when the activity of the catalyst became to be steady after 500 h. The activity of Cu-Zn/Al 2 O 3 catalyst after sintering is higher than that of Fe-Cr/Al 2 O 3 at high temperature.

Wanliang Mi et al. / Energy Procedia 28 ( 2012 ) 162 169 165 Fig.3. The effect of reaction temperature on CO water gas shift at different space velocity. 2.4. CO deep removal In order to remove CO to a level below 10 ppm (V/V) in the CO deep removal step, a two-stage preferential methanation process was proposed [9 11], in which a CO content below 1 ppm could be reached under a relatively wide operation condition range. The two-stage methanation process applies two kinds of catalysts, one with relatively low activity but high selectivity (LA, Ru/-Al 2 O 3, 0.4 wt%) for the first stage at higher reaction temperature, and another one with high activity but relatively low selectivity (HA, Ru/-Al 2 O 3, 0.8 wt%) for the second stage at lower reaction temperature. The temperature difference between the inlet and the outlet of the first stage was 55 70 C; thus, to keep the lower inlet temperature of the second-stage methanation, an intercooler is necessary after the first-stage methanation. In the first stage the CO content could be reduced from 1% to below 0.1% at 250 300 C, and in the second stage to below 10 ppm at 150 185 C, and CO 2 conversion could be kept less than 5% at the same time, as shown in Fig.4 and Fig. 5. Outlet CO (ppm) 10000 1000 100 10 1 The second stage operation range LA HA The first stage operation range 0 120 160 200 240 280 320 360 Inlet temperature ( o C) Fig.4. Reactor temperature profiles of each stage in the two-stage methanation method.

166 Wanliang Mi et al. / Energy Procedia 28 ( 2012 ) 162 169 CO2 conversion (%) 20 16 12 8 4 The second stage operation range LA HA The first stage operation range Fig.5. CO 2 conversion in the different CO methanation stages. 2.5. Practical run of 10 kw class cogeneration power station 0 120 160 200 240 280 320 360 Inlet temperature ( o C) In the steady state, the reformate gas obtained through the fuel processor has a composition of higher than 75% H 2, about 21% CO 2, less than 4% CH 4, less than 10 ppm CO, and less than 10 ppb sulfur on a dry basis, as shown in Fig. 6. The prototype could supply about 8 kw AC power and about 10 kw heat. While increasing DC power output from 0.8 to 8 kw, DC and AC efficiency were higher than 40% and 35%, respectively, and the reformer H 2 production efficiency higher than 75% (LHV). The efficiency of heat recovery reached 45%, so the total efficiency for cogeneration was higher than 80%, as shown in Fig. 7. The inverter efficiency was basically higher than 90%, as shown in Fig. 8. The 10 kw class prototype was developed with design dimensions of 1600 mm (L) 1700 mm (H) 600 mm (W), as shown in Fig. 9. It mainly comprises a natural gas reformer, reformate gas moisturiser, PEMFC stack, heat recovery unit, controlling computer, DC/AC converter and inverter. Infrared detectors lie on the right side of the prototype for detecting H 2, CO, CO 2, and CH 4 online. The operating data were saved by the computer when the prototype was running in real time. The prototype can be operated by a given computer program or by manual control. Fig.6. At a steady state H 2, CO, CO 2, CH 4 content in the final reformate gases.

Wanliang Mi et al. / Energy Procedia 28 ( 2012 ) 162 169 167 Fig.7. Different efficiency of DC/AC, H 2 production, heat recovery, total heat and electricity when increasing the power of cogeneration prototype from 0.8 kw to 8 kw. Fig.8. Effect of DC/AC power on the efficiency of the inverter.

168 Wanliang Mi et al. / Energy Procedia 28 ( 2012 ) 162 169 Fig.9. Photograph of the 10 kw level natural gas-pemfc distributed heat and power cogeneration system prototype. Fig. 10 shows the effect of the output power of the prototype on the cell voltage and current when adding an electronic load. As the elapsed time increased, the current increased quickly, and the cell voltage decreased slowly. Finally, the voltage and current remained almost constant, showing the prototype has reached its steady state. Fig.10. The effect of output power on PEMFC cell voltage and current.

Wanliang Mi et al. / Energy Procedia 28 ( 2012 ) 162 169 169 3. Conclusions A 10 kw class prototype of a PEMFC heat and power cogeneration system with a natural gas reformer for hydrogen production has been developed and demonstrated. According to the actual run data, the contents of sulfur and CO in the feed gas to the anode were less than 10 ppb and 10 ppm, respectively, through fuel processing including steps of natural gas desulfurisation, steam reforming, CO water gas shift, and two-stage CO preferential methanation. The efficiency of H 2 production was higher than 75%, DC and AC efficiency were higher than 40% and 35%, respectively, and the total efficiency for heat and power was higher than 80% in a steady state. Acknowledgments This work was supported by the National Natural Science Foundation of China (Project Nos. 21006005 and 20776016), and also supported by the Beijing Municipal Natural Science Foundation (No. D0406001040111) as a major science and technology programme. References [1] A. Brunetti, G. Barbieri, E. Drioli, A PEMFC and H 2 membrane purification integrated plant, Chemical Engineering and Processing 2008; 47: 1081 1089. [2] W. Chanpeng, Y. Khunatorn, The effect of the input load current changed to a 1.2 kw PEMFC performance, Energy Procedia 2011; 9: 316 325. [3] R. Beneito, J. Vilaplana, S. Gisbert, Electric toy vehicle powered by a PEMFC stack, Int. J. Hydrogen Energy 2007; 32: 1554 1558. [4] J.G.M. Furtado, G.C. Gatti, E.T. Serra, S.C.A. Almeida, Performance analysis of a 5 kw PEMFC with a natural gas reformer, Int. J. Hydrogen Energy 2010; 35: 9990 9995. [5] M.D. Falco, Ethanol membrane reformer and PEMFC system for automotive application, Fuel 2011; 90: 739 747. [6] W. Shi, B. Yia, M. Hou, Z. Shao, The effect of H 2S and CO mixtures on PEMFC performance, Int. J. Hydrogen Energy 2007; 32: 4412 4417. [7] J. Gong, Q.Q. Su, W.L. Mi et al., Effect of inlet gas composition on working temperature of natural gas steam reforming, Journal of Chemical Industry and Engineering (China) 2008; 59(30): 687 693. [8] W.L. Mi, D.J. Sun, Q.Q. Su, D.M. Jia, CO water gas shift reaction character over Cu-Zn catalyst, Journal of University of Science and Technology Beijing 2010; 32(2): 224 229. [9] Z.Y. Li, W.L. Mi, Q.Q. Su, CO deep removal with a method of two-stage methanation, Int. J. Hydrogen Energy 2010; 35(7): 2820 2823. [10] Z.Y. Li, W.L. Mi, Q. Cheng, Q.Q. Su, Influence of reaction conditions on removal of CO in reformate by methanation method, Journal of Chemical Industry and Engineering (China) 2009; 60(10): 2576 2582. [11] Z.Y. Li, W.L. Mi, Q.Q. Su, Deep removal of CO in reformate, Journal of University of Science and Technology Beijing 2010; 32(1): 100 104.