CHEMICAL ENGINEERING TRANSACTIONS VOL. 61, 2017 A publication of The Italian Association of Chemical Engineering Online at www.aidic.it/cet Guest Editors: Petar S Varbanov, Rongxin Su, Hon Loong Lam, Xia Liu, Jiří J Klemeš Copyright © 2017, AIDIC Servizi S.r.l. ISBN 978-88-95608-51-8; ISSN 2283-9216 The Development and Research Prospect on Catalytic Coal Gasification Xia Liu*, Yunbao Tu, Xiaoqing Xu, Zhongneng Liu Sinopec Shanghai Research Institute of Petrochemical Technology, Shanghai 201208, China liuxia.sshy@sinopec.com Catalytic coal gasification has attracted much attention in both academic and industrial circles due to that it is considered as a key technology for coal efficient utilization, in terms of lower reaction temperature and higher heat efficiency as compared to the conventional coal gasification. In this paper, the development and the research on catalytic coal gasification are reviewed, including the mechanism, catalysts and applications. Four categories of intensively used catalysts, including alkali metal catalysts (i.e. K, Na), alkaline earth metal catalysts (i.e. Ca), transition metal catalysts (i.e. Fe), and compound metal catalysts as well as their composites are summarized in detail. Furthermore, process conditions, such as coal feed composition, gasification operating conditions, and amount of catalyst are also reviewed. Although catalytic coal gasification as a promising technology can overcome some operation difficulties for efficiently converting coal to target products (H2, CH4), there are still many unsolved problems remained, such as, how to find catalysts more effective, recyclable and cheaper, and how to balance the efficiency and economic cost of gasification process. 1. Introduction In numerous utilization technologies of coal, the gasification is widely considered as an important industrial process for converting raw coal to more useful and cleaner carbon feedstock for power generation and syngas production (Akhlas et al., 2015). Coal gasification reaction involves complex heterogeneous physical and chemical changes that occur between coal and gaseous reactants. However, high temperature and high pressure operating conditions are required in the conventional coal gasification process, eg, 1,300 °C and 3 MPa in GE coal slurry gasification. These requirements increase the plant capital and operating cost considerably. It is necessary to develop more cost-effective coal gasification technology. In last decades, catalytic coal gasification is becoming a more attractive way to produce hydrogen-rich and methane-rich syngas, compared with conventional gasification, which labelled a slow, highly endothermic reaction that requires high temperatures above 900 °C under certain pressure (Yuan et al., 2015). The r temperature of the catalytic gasification can be lowered to 704-815 °C through the utilization of the catalyst, which is more commercially desirable for the process. Furthermore, it can remarkably enhance the gasification reaction rate and elevate the gasification efficiency. Generally, the overall reactions of catalytic coal gasification can be described by elementary Reaction (1)-(4): Water-gas reaction: 22 HCOOHC  +131.3 kJ/mol (1) Boudouard reaction: 2COCOC 2  +162.4 kJ/mol (2) Water-gas shift reaction: 222 HCOOHCO  -41 kJ/mol (3) Methanation reaction: OHCH3HCO 242  -206.3 kJ/mol (4) The main characteristics of catalytic gasification can be described as: (1) With catalysts loading, the activation energy of the gasification decreases and gasification reaction rate increases. The temperature of the steam gasification process can be lowered to 700 °C. (2) H2 and CH4 concentration is improved by taking advantage DOI: 10.3303/CET1761192 Please cite this article as: Liu X., Tu Y., Xu X., Liu Z., 2017, The development and research prospect on catalytic coal gasification, Chemical Engineering Transactions, 61, 1165-1170 DOI:10.3303/CET1761192 1165 of the favourable reaction selectivity of catalysts loading. CH4 could be increased to 20%-30% in the gasified syngas (Jing, 2016). (3) In overall reaction process, besides oxygen and air, the gasification agents could be CO2, H2, water steam, or mixture of H2O and O2, as utilizing CO2 to react with coal is an effective way to realize reduced CO2 emissions in the process. Compared with the conventional entrained bed gasification technology, the catalytic coal gasification has lower reaction temperature, the higher thermal efficiency and selectivity to certain gas products, which is considered as the potential third generation of coal gasification technology. 2. Catalysts for catalytic coal gasification process The catalytic activity is due to their ability to reduce the apparent activation energy. There is a wide acceptance that the presence of catalyst enhances the reactivity of coal gasification by increasing the amount of active intermediates on the carbon surface. The increase in the active surface area can be attributed to the interaction of catalyst with the solid carbon surface and to the resulting newly formed catalytic precursors (Hamilton, 1984). The precursors are capable of dissociating oxygen species containing gases (O2, CO2 and H2O) and producing oxidized intermediates that participate in the redox reaction. The catalytic mechanism involves an oxidation–reduction cycle with the intermediate formation of the hydroxide of the alkali metal (Jiang et al., 2017). As shown in Reaction (5), the alkali metals could be generated from the interaction between alkali carbonate and carbon. The intermediate formation is thought to be a highly reactive compound that acts as an oxygen carrier. It transfers the oxygen atom to the carbon surface where it reacts with the carbon substrate to form CO. For CO2 gasification, the active intermediates are the free alkali metals and the metal oxides, as shown in Reactions Eq(6)-(8). Under this mechanism, the alkali metal carbonate undergoes carbothermal reduction to metal by oxidation due to steam or CO2, which reforms their carbonate. COCO2MCCOOMCCOM 22232  (5) CO32MC2COM 32  (6) COOKCOM 22  (7) 3222 COMCOOM  (8) Another important mechanism is the carbonate decomposed on carbon sites to form surface oxides (Sams and Shadman, 1986). Carbonate decomposed on carbon sites to form surface oxides. The mechanism is suggested in Reaction (9), where (–CO2M)(s), –(COM)(s), (–CM)(s) represent the generalized sites with the fully oxidized, partial reduced, and the completely reduced. The catalytic gasification is aroused by CO2 could be explained by Reaction (9), (10), including the oxidation and reduction reactions. Besides, alkali earth metals, transition metals such as nickel, iron, and other metals have been also used as catalysts to promote the gasification reaction of coal and other carbon-based sources. Recently, special attention has been given to co-feeding biomass. Overall, salts and oxides of alkali metals, and alkaline earth salts, have been widely employed for the gasification of carbon materials due to their superior catalytic properties and relative low cost (Jiang et al., 2017). The types of catalyst used for catalytic coal gasification are shown in Figure.1. COCKCOM)(M)CO(COM (s) C (s)(s)2 C 32  )( (9) COM)COCOCOM)( (s)22(s)  ( (10) 1166 Catalyst Transition metal catalyst Alkaline metal catalyst Alkaline earth metal catlyst iron compounds, cobalt, nickel CaCO3, Ca(OH)2, etc. Binary and ternary alkali metal catalyst Single alkali metal catalyst, eg, Na2CO3, K2CO3 Compound catalyst alkali, alkali-earth, and iron-based compound catalysts Figure 1: Types of catalyst used in catalytic coal gasification 2.1 Alkali metal catalyst The early study on the gasification catalyst is focused on single alkali metal catalysts. When the activated carbon is gasified with CO2, the catalytic activities are followed in order: Cs>Rb>K>Na>Li (Kapteijin, 1984). Li2CO3, Na2CO3, K2CO3 are used as the catalysts of steam gasification on lignite char, and the catalytic activities ranked as Na2CO3>K2CO3> Li2CO3 under same reaction temperatures (700-800 °C) with 3 wt.% catalyst loading (Kwon et al.,1989). Wang et al. (2015) provided the catalytic performance of Na2CO3 for high-aluminum coal gasification, with comparison of that of K2CO3, the catalytic action of Na2CO3 was better since its superior mobility and poorer volatility. As the alkali metal carbonate in the same catalyst loading rates of steam gasification, Vamvuka (2012) tested the effect of different alkali catalysts on the conversion of waste paper, and the efficiency of these alkali metal catalysts found to be in the following order: Li2CO3 > K2CO3 > CaCO3 > Rb2CO3 > CaSO4 > Cs2CO3 > Na2CO3. These alkali metal catalysts increase reaction rates and lower the combustion temperature. Besides, it was found that sodium, potassium, and cesium carbonates were equally effective at typical gasification temperatures. As cheap disposable catalyst, alkali species (K, Na) are more catalytically active than alkaline earth species (Ca, Mg) during gasification. Apart from single alkali salts, the binary and ternary alkali catalysts have been investigated with respect of their catalytic activity. McKee et al. (1985) observed that a Pittsburgh coal char containing a Li2CO3-Na2CO3-K2CO3 eutectic catalyst was at least an order of magnitude more reactive for steam gasification than the sample containing the same total concentration of K2CO3 alone. Similarly, on the same catalyst loading, in the CO2 and char gasification process, Li2CO3-Na2CO3 eutectic catalyst and the Li2CO3-Na2CO3-K2CO3 had higher catalytic activity than single alkali carbonate, and the ternary eutectic catalyst was more effective than the binary one (Yeboah, et al. 2011). 2.2 Alkaline earth metal catalyst Alkaline earth metal is important catalyst for gasification due to its low cost and getting easily from extensive sources, especially Ca-bearing minerals such as CaO, CaCO3, and Ca(OH)2 which have been widely investigated to improve hydrogen yields in last decade. CaO can be used as a sorbent in CO2 adsorption, which is with rapid initiation of the surface CO2-CaO carbonation reaction that followed by the slow diffusion of CO2 through CaCO3 layers formed at the surface (Zhou, 2014). At the presence of steam, CaO reacts with H2O to form Ca(OH)2, which then reacts with CO2 to form CaCO3. These two reactions occur at relatively low temperatures and are not affected by the partial pressure of CO2. Following the decrease in CO2 partial pressure caused by CO2 isolation, the water–gas shift reaction is driven forward, giving high H2 yields in the coal or biomass gasification. Ca(OH)2 is usually produced by the calcinations of CaCO3, followed by the subsequent hydration of the CaO formed. It is desirable to directly use CaCO3 as the catalyst raw material owing its low cost. In the steam gasification of coal with CaCO3 catalyst, TPD and XRD measurements demonstrated that calcium catalyst was initially present in the ion-exchanged form and as finely dispersed calcium species after pyrolysis. CaCO3 was found to be effective as a catalyst raw material in the steam gasification, even at low catalyst loading (Murakami et al, 2014). 1167 2.3 Transition metal catalyst Transition metal is used as gasification catalyst including iron, cobalt, nickel compounds which have good catalytic effect on the steam gasification. In these transition metals, iron compounds catalyst attracted more interest because of their abundance, and low environmental impact compared with other transition metals. The iron catalysts precipitated from aqueous solution of FeCl3 that to catalyse the gasification of brown coal with CO2 could lower the temperature at which the maximum rate of CO formation occurs by 130 - 160°C (Asami et al., 1996). Fe(NO3)3, FeSO4, and FeCO3 are also employed as the iron precursor. Fe(NO3)3 was less active than FeSO4 during pyrolysis of a sub-bituminous coal with the same iron loading at 700 - 800 °C. For FeCO3 used as a catalyst precursor in coal gasification with CO2, the redox cycle is between metallic Fe and FeO catalysed the initial char gasification with CO2. The catalytic iron species changed to FeO and Fe3O4 in the char gasification. 2.4 Compound catalyst Pursuing higher gasification rates at relatively lower reaction temperatures, some alkali, alkali-earth, and iron- based compound catalysts, particularly potassium carbonate (K2CO3) based complex, have been trialled as catalysts for coal gasification. In the steam gasification of coal char, the binary K2CO3-Ca(OH)2 catalyst showed a synergic effect on promoting the gasification rate, whereas the catalytic activities of the Li2CO3-Ca(OH)2 and Na2CO3-Ca(OH)2 were worse than their respective alkali carbonates alone (Tang and Wang, 2015). The gasification characteristics of coal char with CO2 under Cao and Fe(NO3)3 were studied by Chen etal.(2012), and it is found that the optimal mass addition of compound catalyst was 1 % Ca+2 % Fe, the catalytic intensity were 5.71, 1.65 and 2.04 times of raw coal char, single component catalyst of CaO and Fe(NO3)3. In addition, For K2SO4 and Na2CO3, the gasification rate could be enhanced by addition of iron salt. It is reported that the mixtures K2SO4-FeSO4 and K2SO4-Fe(NO3) exhibited better catalytic activity than K2CO3 at 800 °C (Song and Kim, 1993). 3. The influence factors of catalytic gasification In addition to metal catalyst discussed, there are also other factors which could have influence on the gasification efficiency, including quantity of coal, catalyst loading, operating condition of gasification. The mineral components of coal including alkaline metal (K, Na) and alkaline earth metal (Ca) have catalytic activity for gasification. In the coal gasification, the low rank coal usually has higher gasification ratio. For catalyst K2CO3 loaded, the react ratio changes with coal ranks, as shown in Table 1, the higher coal rank, the higher catalytic efficiency in coal-based char gasification. Table 1: Effect of potassium carbonate on carbon gasification by steam Char source Operating temperature (°C) Content K2CO3 (wt%) Ratio of rate Catalysed/uncatalysed Reference Lignite char 700 10 3.8 (Nzihou, et al., 2013) Sub-bituminous char 700 10 7.5 (Nzihou, et al., 2013) Bituminous char 700 10 16 (Nzihou, et al., 2013) Anthracite char 800 10 25 (Nzihou, et al., 2013) Sub-bituminous coal 700 10 20 (Kopyscinski, et al., 2014) The catalyst loading also affects the gasification efficiency. At the low catalyst loading, the more catalyst addition, result in the higher of catalytic activity. However, as the catalyst addition exceeds the optimal amount value, the excess appear low dispersity on the surface, which decreased the active surface of the coal with catalyst. Yang et al. (2013) reported that the reactivity of lignite char increased linearly with catalyst loading up to a loading saturation level which was around 10 %, for both K and Ca. Temperature and pressure of reaction are two main factors affecting gasification efficiency, which obviously influence reactive rate, carbon conversion and the components of the produced syngas. While the operating temperature of entrained bed gasifier is at range of 750 - 1,000 °C, the yield of H2, carbon conversion rate both improved with the temperature increasing, which is confirmed by Popa and Fan (2013) that rate constants of coal char conversion with 900 °C was 3.4 - 3.7 times more than that of 700 °C. 4. Industrial application development Catalytic gasification to synthetic natural gas (SNG) has been done a developmental effort by Exxon in the late 1970s to the early 1980s. Potassium carbonate (K2CO3) was employed in the Exxon pilot-scale coal gasification, which was demonstrated using a fluidized-bed gasifier in the late 1979 (Nahas, 1983). Exxon’s catalytic coal 1168 gasification process was gasified coal with steam to produce a CH4 and hydrogen. There were two steps included in this gasification process. Firstly, the coal underwent rapid devolatilization to yield coal char and numerous volatile products. The resulting char was catalytic gasified with steam and recycle gas to produce a mixture of CH4, H2, and CO2. However, the high operating cost of catalyst recovery and the natural gas market contracted, continued developmental efforts stopped, resulting this technology could not proceed further. In last decade, as the industrial development of coal-to-gas convention has drawn much attention, Great Point Energy from US has expanded on Exxon's developments and completed the 1 t/d pilot catalytic gasification study, the feedstock has extended with petroleum coke and biomass. The flowsheet of Bluegas™ gasification process is shown in Figure 2. The dried coal is mixed with catalyst in feedstock preparation step. The catalyzed coal is then dried and transported to a fluidized-bed gasifier. The catalyst promotes the hydrogasification/WGS/methanation reactions to produce CH4 and CO2 in gasifier. The produced syngas undergoes a series of steps to remove particulates, acid gases to recover the CH4 product gas. The demonstration of their Bluegas™ technology was initially conducted at the Gas Technology Institute’s (GTI) Flex-Fuel Test Facility in 2007. As the next stage of commercial development, Great Point Energy and China Wanxiang already have a $1.25 109 partnership to build a synthetic natural gasification using the Bluegas™ hydro-methanation technology in China (NETL, 2017). CO2 sequestration , enhance oil recovery Ash and char removal Ash removal cyclene Gas cleaning Gas seperation Steam Catalyst recycle Feedstock and catalyst CH4 CO2 Particulates Sulfur, trace metals Gasifier Figure 2: The flowsheet of Bluegas™ gasification process (NETL, 2017) Although catalytic coal gasification has been developing for several decades, it has not been put into industrial application. One major reason is the poor recovery of the gasification catalyst, which is usually considered to be attributed to deactivation of the gasification catalyst resulting from the interaction between the catalyst and the mineral matters in the coal. 5. Conclusions Catalytic gasification has a preference to other conventional gasification techniques due to its improved reaction activity and moderate operating conditions, especially for methane and hydrogen target production. A lot of work has been done to find the cheaper catalysts and improve the gasification scheme application more economically. The catalytic performance of alkali and alkaline earth metal salts on the goal gasification has been extensively investigated technically and in term of applications. With regard to improve the economics of catalytic gasification process and make it environmentally acceptable, recovery of the catalyst need to be used in catalytic gasification. The main process variables of catalyst recycle should to be considered, such as, solvent-to-coal ratio, mixing time, extraction temperature, pH, concentration, which are major factors affect the catalyst recovery efficiency. For further industrial application, the Heat Integration and Total Sites Integration tools (Klemeš, 2013), also should be considered to improve the gasification site energy efficiency. References Akhals J., Ruggeri F., Bertucco A., 2015, Simulation of steam gasification of coal with pre-combustion enabling cleaner coal conversion, Chemical Engineering Transactions, 43, 2017-2022. Asami K., Sears P., Furimsky E., Ohtsuka Y., 1996, Gasification of brown coal and char with carbon dioxide in the presence of finely dispersed iron catalysts, Fuel Process Technology, 47, 139–151. 1169 Hamilton R.T., Sams D.A., Shadman F., 1984, Variation of rate duringpotassium-catalysed CO2 gasification of coal char, Fuel, 63,1008–1012. Jiang L., Hu S., Xu K., Wang Y., Syed-Hassan S.A., Su S., Liu C.Y. Xiang J., 2017, Formation, fates and roles of catalytic precursors generated from the K2CO3-carbon interactions in the K2CO3-catalyzed CO2 gasification of coal char, Journal of Analytical and Applied Pyrolysis, accessed 28,02, 2017. Jing Y.H., 2016, Research progress of catalytic coal gasification technology, Contemporary Chemical Industry, 45(6), 1273-1275 (in Chinese). Kapteijn F., Abbel G., Moulijn J.A., 1984, CO2 gasification of carbon catalysed by alkali metals: reactivity and mechanism, Fuel, 63, 1036–1042. Klemeš J.J. (Ed), 2013. Handbook of Process Integration (PI): Minimisation of Energy and Water Use, Waste and Emissions, Woodhead/Elsevier, Cambridge, UK, 1184 ps. ISBN: 987-0-85709-0. Kopyscinski J., Lam J., Mins C.A., Hill J.M., 2014, K2CO3 catalyzed steam gasification of ash-free coal. Studying the effect of temperature on carbon conversion and gas production rate using a drop-down reactor, Fuel, 128, 210-219. Kwon T.W., Kim, J.R. Kim S.D., Park W.H., 1989, Catalytic steam gasification of lignite char, Fuel, 68, 416–421. Mao Y.D., Li K.Z., Sun Z.Q., Bi J.C., Xin F., Li J.L., 2013, Characteristics of catalytic coal gasification in lab scale autothermal fluidized bed, Journal of Chemical Engineering of Chinese Universities, 27(5), 798-804 (in Chinese) McKee D.W., Spiro C.L., Kosky P.G., Lamby E.J., 1985, Eutectic salt catalysts for graphite and coal char gasification, Fuel, 64, 805–809. Nahas N.C., 1983, Exxon catalytic coal gasification process fundamentals to flowsheets, Fuel, 62 (2), 239–241. Nahas N.C., 1983, Exxon catalytic coal gasification process fundamentals to flowsheets, Fuel,62(2):239-241. NETL, 2017, Great Point Energy, accessed 21,02, 2017. Nzihou A., Stanmore B., Sharrock P., 2013, A review of catalysts for the gasification of biomass char, with some reference to coal, Energy, 58, 305-317. Popa T., Fan M., Argyle M.D., Dyar M.D., Gao Y., Tang J., Speicher E.A., Kammen D.M., 2013, H2 and COx generation from coal gasification catalyzed by a cost-effective iron catalyst, Applied Catalysis A: General, 464–465, 207–217 Sams D.A., Shadman F., 1986, Mechanism of potassium-catalyzed carbon/CO2 reaction. AIChE J 1986; 32:1132–1137. Song B.H, Kim S.D., 1993, Catalytic activity of alkali and iron salt mixtures for steam-char gasification, Fuel, 72, 797-803. Tang J., Wang J., 2016, Catalytic steam gasification of coal char wit alkali carbonates: A study on their synergic effects with calcium hydroxide, Fuel Processing Technology, 142, 34-41. Walker P.L., Matsumoto S., Hanzawa T., 1983, Catalysis of gasification of coal-derived cokes and chars, Fuel, 62, 140–149. Wang Y.W., Wang Z.Q., Huang J.J., Fang Y.T., 2015, Catalytic gasification activity of Na2CO3 and comparison with K2CO3 for a high-Aluminum coal char, Engery Fuels, 29, 6988-6998. Yang J.B., Cai N.S., Zhang Y.W., 2008, Effect of catalyst loadings on the gasification reactivity of a lignite char with steam, Journal of Fuel Chemistry and Technology, 36, 15-22. Yeboah Y.D., Xu Y., Sheth A., Godavarty A., Agrawal P.K., 2003, Catalytic gasification of coal using eutectic salts: identification of eutectics, Carbon, 41, 203–214. Yuan X., Namkung H., Kang T.-J., Kim H.-T., 2015, K2CO3-Catalyzed Steam Gasification of Indonesian Low- Rank Coal for H2-Rich Gas Production in a Fixed Bed Reactor, Energy Technology, 20115, 527-534. Zhou C.G., Stuermer T., Gunarathne R., Yang W.H., Blasiak W., 2014, Effect of calcium oxide on high- temperature steam gasification of municipal; solid waste. Fuel, 122, 36-46. 1170