The International Journal of Coal Science & Technology is a peer-reviewed open access journal. It focuses on key topics of coal scientific research and mining development, serving as a forum for scientists to present research findings and discuss challenging issues.
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A forum for new research findings, case studies and discussion of important challenges in coal science and mining development
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Published with the China Coal Society
Research Article
Open Access
Published: 12 September 2014
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International Journal of Coal Science & Technology Volume 1, 81-87, (2014)
1.
School of Chemical and Environmental Engineering, China University of Mining and Technology, Beijing, China
The authors proposed an integrated gasification fuel cell zero-emission system. The coal char gasification is discussed using high temperature and concentration of CO2 produced by solid oxide fuel cells and oxy-fuel combustion. The gasification is simulated by Aspen plus based on Gibbs free energy minimization method. Gasification model of pulverized coal char is computed and analyzed. Effects of gas flow rate, pressure, preheating temperature, heat losses on syngas composition, reaction temperature, lower heating value and carbon conversion are studied. Results and parameters are determined as following. The optimum O2 flow rate is 20 kg/h. The reaction temperature decreases from 1645 to 1329 °C when the CO2 flow rate increases from 0 to 5 kg/h, the CO2 flow rate should be operated reasonably; lower heating value reduces and reaction temperature increases as the pressure increases; compared to the CO2 preheating, O2 preheating has greater influence on reaction temperature and lower heating value.
In recent years, global demand for fossil energy has been growing rapidly with the economic and social development of the world. Long-term use of fossil energy has led to serious environmental problems. Especially the green house effect is getting worse because of CO2 emission, which has attracted worldwide concerns (Gleick et al. 2010; Mao 2010; Wei et al. 2011). Chinese government has proposed that by the year 2020, CO2 emission of unit GDP could be reduced by 40 % to 45 % compared with the emission in 2005. As a result, CO2 emission reduction and development of low carbon science and technology have become the most urgent scientific issues to solve for the world (Xie H 2010; Xie et al. 2012).
Coal production in China was 3.66 billion tons in 2012, increased by 4 % than in 2011. Coal utilization is the main source of CO2 emission. The percentage of CO2 emission produced by coal utilization is as high as 70 % (Huang 2012; Sun and Gao 2013). Clean and effective utilization of coal is the key to achieve sustainable development of energy for the world, especially for China. Coal gasification is the core technology in fuel cells, coal chemical synthesis, IGCC, and coal gasification-based poly-generation. It is the most efficient way to achieve clean and effective utilization of coal.
CO2 can be used as gasification agent to gasify coal char. Then high purity CO can be used for chemical synthesis and Solid Oxide Fuel Cells (SOFCs), which can realize clean and effective utilization of coal (Peng and Han 2009).
Coal gasification in CO2 rich gas atmosphere is recognized as one of the most promising technology for controlling CO2 emission in pulverized coal-fired power plants. This technology has been reviewed (Antonio and Mara 2004). Large amount of syngas, mainly CO, can be produced by this technology. Syngas production from coal gasification under O2/CO2 atmosphere has been simulated using CFD software Fluent. A 3D geometry simulation model for gasification was established. The results show that the gas temperature decreases and the gross heating value of syngas increases with the increasing of CO2 concentration; besides, effect of particle size on coal gasification is significant (Alam et al. 2012). Gasification of aquatic biomass under O2/CO2 atmosphere has been carried out. Effects of O2, CO2 concentrations, feeding rate and [H2O]/[C] ratio on O2/CO2 gasification behavior have been reported (Toshiaki et al. 2009; Toshiaki et al. 2013).
The syngas produced by coal gasification can be used for SOFCs. Then high temperature and concentration of CO2 is produced after electrochemical reaction. The CO2 could be used for gasification of char. For this closed cycle system, vast heat of exhaust could be used efficiently and energy needed in the gasification could be reduced. Also the system can realize CO2 emission reduction and even zero emission. The specific principle is shown in Fig. 1. O2 can be separated from air by oxygen transportation Membrane (OTM), which is prepared by perovskite powders and operated at high temperature from 800 to 1000 °C. Then high temperature O2 is produced.
The process flowsheet simulation program Aspen plus is used in this paper. The simulation is based on entrained-flow gasifier. The physical property databases and unit module in Aspen plus have also been used in the simulation model. Coal char gasification model under O2/CO2 has been established, which can provide theory bases for the determination of process conditions.
As shown in Fig. 2, the simulation model consists of three unit modules, five material streams and two heat streams. They are the unit module of RYIELD, RGIBBS, SSPLIT; material streams of NATCOKE (coal char), CO2, O2, SYNGAS and ash; heat streams of QLOSE (heat loss of the gasifier) and QDECOMP (Heat of char cracking). The reaction blocks used are the RYIELD, RGIBBS and SSPLIT. Nonconventional material of coal char can crack to single element molecule in the RYIELD reactor and the cracking heat can be led into the RGIBBS reactor.
The computation in the RGIBBS reactor is based on Gibbs free energy minimization method. SSPLIT module is used to simulate the separation of syngas and ash. The model is established under the assumptions that the gasifier runs stably, no operating parameters change, the gasification agent and coal char particle can mix completely instantly, the elements hydrogen, oxygen, nitrogen and sulfur convert to gas phase totally except element carbon. There is no pressure drop in the gasifier, ash in the coal char is inert material that does not take part in gasification reaction, temperature distribution in coal particle is uniform, all the gas-state reactions are fast and attain equilibrium (Wang et al. 2004; Zhou et al. 2010).
Coal char used in this paper is from Xuzhou, China (Lin and Zhao 2012). The proximate analysis, ultimate analysis and sulfur analysis are shown in Table 1. O2 and CO2 are chosen as gasification agents.
Proximate analysis (%) | Ultimate analysis (%) (d) | Sulfur analysis/ % (d) | Heating value (MJ/kg) | |||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
Mad | Ad | Vd | FCd | Cd | Hd | Od | Nd | Sd | Sp | Ss | So | |
0.81 | 16.28 | 9.12 | 74.6 | 77.96 | 1.66 | 2.69 | 0.92 | 0.48 | 0.2 | 0.12 | 0.16 | 26.81 |
The handling capacity of coal char is 21.59 kg/h (The mass flow rates are set according to simulation requirement). Gasification pressure is 3 MPa when it keeps steady. Mass ratio of O2, CO2 to coal char is the key factor to the quality of syngas.
Other parameters keep steadily. The coal char and CO2 mass flow rate are 21.59 and 2.16 kg/h respectively. The relationships among syngas composition, reaction temperature, lower heating value of syngas and O2 content are shown in Fig. 3. The reaction temperature increases rapidly with the rising of O2 content because of the increased combustion reaction. At the start of gasification there is not enough O2, so imperfect combustion of char occupies a predominant position. As a result, molar ratio of CO increases gradually at first. Then the molar fraction of CO decreases because the complete combustion reaction increases as a result of more O2 being injected into the gasifier. Combustion reactions of H2 and CO increase with the rising of O2 content, which leads to higher H2O and CO2 content.
As shown in Fig. 3 the concentration of CO increases with the increasing of O2 flow rate, and then decreases. Although the concentration of H2 decreases gradually, it is much lower than CO’s. As a result, the concentration of CO is the leading factor, which promotes lower heating value and the lower heating value of syngas increasing to the maximum value and then decreasing with increasing of O2 mass flow rate.
As illustrated in Fig. 4 the reaction temperature decreases gradually with the increasing of CO2 flow rate when the coal char and O2 mass flow rates are 21.59 and 17.57 kg/h respectively. It decreases from 1645 °C to 1329 °C when CO2 flow rate increases from 0 to 5 kg/h. Reaction temperature decreasing is caused by several factors listed below. First, diffusion rate of O2 in the CO2 atmosphere is slower with the increasing of CO2 flow rate, which leads to slower combustion reaction. Second, the larger heat capacity of CO2, increasing of CO2 flow rate and keeping O2 flow rate steady, leads to lower reaction temperature. Third, the Boudouard reaction rate is enhanced with the increasing of CO2 flow rate and more heat is consumed, which leads to lower reaction temperature.
Reaction temperature decreasing is not favorable to Boudouard reaction. However, the increasing of CO2 concentration promotes Boudouard reaction and its effect on Boudouard reaction is more dominant than the temperature. As a result, the molar ratio of CO increases with the rising of CO2 flow rate. Reaction of coal char with H2O is endothermic. Temperature decreasing is not favorable to the reaction. Temperature decreasing is good for water gas shift reaction and the production of CO2 and H2, but the concentrations of CO2 and H2 are very low. Therefore, the reaction of coal char with H2O is more dominant in the production of H2. As shown in Fig. 4, the concentration of H2 decreases with the increasing of CO2.
The reverse water gas shift reaction increases as a result of increasing of CO2 and partly H2 converts to H2O. As a result, the lower heating value of syngas decreases slightly with the increasing of CO2 mass flow rate as shown in the Fig. 4.
The relationship of the pressure with gasification is shown in Fig. 5 when the coal char, O2 and CO2 mass flow rate are 21.59, 17.57 and 2.16 kg/h respectively. The reverse Boudouard reaction rate increases with the rising of pressure, which leads to slightly decreasing of CO molar ratio and increasing of heat and CO2 content. The reaction temperature is high enough and the effect of pressure is not remarkable, but pressurizing can increase syngas production per unit time and production capacity. CO2 content increasing is favorable to the reverse water gas shift reaction and the molar ratio of H2 decreases. As a result, the lower heating value decreases slightly.
Effect of preheating temperature on the gasification with coal char, O2 and CO2 mass flow rates are 21.59, 17.57 and 2.16 kg/h is shown in Fig. 6. The preheating of O2 and CO2 can increase the reaction temperature and the lower heating value, but the effect of CO2 preheating on reaction temperature and lower heating value is weaker than the O2 preheating. The reaction temperature and the heating value increase by only 25 °C and 0.0063 MJ/M3 respectively, when the preheating temperature of CO2 increases from 300 to 1000 °C. However, the heat capacity of CO2 is so high that it is unnecessary for high preheating temperature.
To obtain the effect of temperature on gasification, heat loss of gasifier is introduced in the gasification. The gasifier heat loss is the ratio of heat loss of the gasifier with heating value of coal. As coal char, O2 and CO2 mass flow rates are 21.59, 17.57 and 2.16 kg/h separately, the relationships between syngas composition, temperature, lower heating value and gasifier heat loss are illustrated in Fig. 7. Reaction temperature decreases as the heat loss increases from 0 % to 2 %, which leads to slower Boudouard reaction rate and lower molar fraction of CO. The H2 content decreases because of the decreasing temperature and the reaction rate of char with H2O.
Effects of O2 and CO2 mass flow rates, pressure, preheating temperature and heat loss on the carbon conversion were simulated. The results are shown in Table 2.
O2 mass flow rates (kg/h) | 10 | 15 | 17.5 | 20 | |||
Carbon conversion | 0.4343 | 0.7272 | 0.8537 | 0.9657 | |||
CO2 mass flow rates (kg/h) | 0 | 0.5 | 1.5 | 2.16 | 3 | 4 | 5 |
Carbon conversion | 0.8208 | 0.8286 | 0.8439 | 0.8538 | 0.8657 | 0.8791 | 0.8911 |
Pressure (bar) | 1 | 2 | 3 | 4 | 5 | 30 | |
Carbon conversion | 0.8581 | 0.8579 | 0.8578 | 0.8576 | 0.8574 | 0.8537 | |
O2 preheating (°C) | 100 | 200 | 400 | 600 | 700 | 800 | 900 |
Carbon conversion | 0.8532 | 0.8538 | 0.8547 | 0.8555 | 0.8558 | 0.856 | 0.8563 |
CO2 preheating (°C) | 300 | 600 | 700 | 800 | 900 | 1000 | |
Carbon conversion | 0.8537 | 0.8539 | 0.854 | 0.8541 | 0.8541 | 0.8542 | |
Heat loss of gasifier (%) | 2.5 | 2 | 1.5 | 0.5 | 0 | ||
Carbon conversion | 0.8537 | 0.8545 | 0.8551 | 0.8561 | 0.8564 |
Carbon conversion increases with increasing of O2 and CO2 mass flow rates. Carbon combustion reactions are enhanced with the increasing of O2 mass flow rates so carbon conversion increases greatly. We can get that the optimum O2 mass flow rate is 20 kg/h for syngas heating value in Fig. 3. Increasing of CO2 mass flow rates is good for Boudouard reaction and carbon conversion. Pressure, preheating and gasifier heat loss have also some effects on carbon conversion, but they are not apparent.
The coal char gasification using O2/CO2 based on IGFC was proposed. The thermodynamic analysis of the gasification under O2/CO2 atmosphere was studied using Aspen plus simulation method. The results are concluded as following.
The molar ratio of CO increased gradually when the O2 flow rate is lower than 20 kg/h. Then the molar fraction of CO decreases. H2 molar ratio decreases gradually with the increasing of O2 mass flow rate. The optimum lower heating value is obtained when the O2 flow rate is 20 kg/h.
The Mass flow rates of CO2 has a significant effect on reaction temperature. The reaction temperature decreases from 1645 to 1329 °C when CO2 flow rates increases from 0 to 5 kg/h because of the slower diffusion of O2 in CO2 atmosphere, larger heat capacity of CO2 and promoting of Boudouard reaction. The syngas lower heating value decreases gradually with the increasing of CO2 mass flow rates.
The heating value is lower with the raising of pressure, but pressurize is favorable to reaction temperature. The molar ratios of CO and H2 decreased slightly even under high pressure because of the high reaction temperature.
Preheating of O2 and CO2 can both enhance reaction temperature and syngas heating value, but effect of CO2 preheating is weaker than O2 preheating.
The carbon conversion increases with the increasing of O2, CO2 flow rates and O2, CO2 preheating temperature. Pressure is not favorable to the carbon conversion because it could inhibit the Boudouard reaction. The gasifier heat loss can reduce reaction temperature and then the carbon conversion decreases.
[1] | Alam MS, Wijayanta AT, Nakaso K, Fukai J (2012) Numerical investigation of syngas production from coal gasification under various CO2/O2 mixtures. Can J Comput Math Nat Sci Eng Med 3(4):88–97 |
[2] | Antonio C, Mara DJ (2004) Mild combustion. Prog Energy Combust Sci 30(4):329–366 |
[3] | Gleick PH, Adams RM, Amasino RM et al (2010) Climate change and the integrity of science. Science 328:689–690 |
[4] | Huang J (2012) Coal list and study on emission reduction policy. Doctor’s Thesis, University of Fudan |
[5] | Lin LS, Zhao CS (2012) Study of the simulation of natural coke-H2O gasification reaction by using the software Aspen plus. J Eng Therm Energy Power 27(3):355–360 |
[6] | Mao ZQ (2010) Discussing about CO2 emission and H2 energy. Mod Phys 22(5):41–45 |
[7] | Peng SP, Han MF (2009) Development of coal/carbon based solid oxide fuel cell. Chin J Nat 31(4):187–192 |
[8] | Sun CS, Gao F (2013) Review of development of China’s coal industry in 2012 and prediction of its development trend in 2013. China Coal 39(3):10–16 |
[9] | Toshiaki H, Hiroto S, Kinya S, Yusuke E (2009) Syngas production by woody biomass gasification with a CO2/O2 mixture. J Jpn Inst Energy 88:862–868 |
[10] | Toshiaki H, Shou H, Yusuke E (2013) Syngas production by CO2/O2 gasification of a aquatic biomass. Fuel Process Technol 116:9–15 |
[11] | Wang Y, Dai ZH, Yu GS, Yu ZH (2004) Simulation of entrained-flow bed coal gasifier by the method of Gibbs free energy minimization. Coal Convers 27(4):27–33 |
[12] | Wei W, Sun YH, Wen X, Sun NN (2011) Opportunities and challenges of carbon dioxide utilization as a resource. Chem Ind Eng Prog 30(1):216–224 |
[13] | Xie HP (2010) CO2 storage and climate change. Science and Technology Review 28(18) |
[14] | Xie HP, Xie LZ, Wang YF, Zhu JY, Liang B, Ju Y (2012) CCU: a more feasible and economic strategy than CCS for reducing CO2 emissions. J Sichuan Univ 44(4):1–5 |
[15] | Zhou JH, Chen XL, Guo Q, Wang YZ (2010) Process simulation of biomass and coal entrained flow co-gasification based on Aspen plus. Acta Energiae Solaris Sinica 31(9):1112–1116 |
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