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Frontiers of Chemical Science and Engineering

ISSN 2095-0179

ISSN 2095-0187(Online)

CN 11-5981/TQ

Postal Subscription Code 80-969

2018 Impact Factor: 2.809

Front Chem Sci Eng    2012, Vol. 6 Issue (1) : 67-83    https://doi.org/10.1007/s11705-011-1162-4
RESEARCH ARTICLE
A thermodynamic study of the removal of HCl and H2S from syngas
Joseph LEE, Bo FENG()
School of Mechanical and Mining Engineering, the University of Queensland, St Lucia Qld4072, Australia
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Abstract

Advanced integrated-gasification combined-cycle (IGCC) and integrated-gasification fuel cell (IFGC) systems require high-temperature sorbents that are capable of removing hydrogen chloride and hydrogen sulfide from coal derived gases to very low levels. HCl and H2S are highly reactive, corrosive, and toxic gases that must be removed to meet stringent environmental regulations, to protect power generation equipment and to control the emissions of contaminants. The thermodynamic behavior of 13 sorbents for the removal of HCl and H2S under various conditions including: initial toxic gas concentration (1–10000 ppm), operating pressure (0.1–11 Mpa), temperature (300 K–1500 K), and the presence of H2O were investigated. The correlation between HCl and H2S was also examined. Thermodynamic calculations were carried out for the reactions of the 13 sorbents using a FactSage 5.2 software package based on free energy minimization. The sorbents, Na2CO3, NaHCO3, K2CO3, and CaO are capable of completely removing chlorine at high temperatures (up to ~1240 K) and at high pressures. Water vapor did not have any significant effects on the dechlorination capability of the sorbents. Nine of the sorbents namely; Cu2O, Na2CO3, NaHCO3, K2CO3, CaO, ZnO, MnO, FeO, and PbO, were determined to have great potential as desulfurization sorbents. Cu2O and ZnO had the best performance in terms of the optimum operating temperature. The addition of water vapor to the reactant gas produces a slightly detrimental effect on most of the sorbents, but FeO exhibited the worst performance with a reduction in the maximum operating temperature of about 428 K. The dechlorination performance of the alkali sorbents was not affected by the presence of H2S in the reactions. However, the desulfurization capability of some sorbents was greatly affected by the presence of HCl. Particularly, the performance of Cu2O was significantly reduced when HCl was present, but the performance of FeO improved remarkably. The thermodynamic results gathered are valuable for the developments of better sorbents.

Keywords syngas cleaning      sorbent      desulfurization      dechlorination     
Corresponding Author(s): FENG Bo,Email:b.feng@uq.edu.au   
Issue Date: 05 March 2012
 Cite this article:   
Joseph LEE,Bo FENG. A thermodynamic study of the removal of HCl and H2S from syngas[J]. Front Chem Sci Eng, 2012, 6(1): 67-83.
 URL:  
https://academic.hep.com.cn/fcse/EN/10.1007/s11705-011-1162-4
https://academic.hep.com.cn/fcse/EN/Y2012/V6/I1/67
Fig.1  Optimum dechlorination conditions for (a) CaO, (b) KCO, (c) NaCO, (d) NaHCO. Initial conditions: temperature 300 K-1500 K, pressure 0.1-11 MPa, initial concentrations 0.5 mol sorbent + 1 mol HCl + 999999 mol N (or 9999 mol N or 99 mol N)
Fig.2  Optimum dechlorination conditions for (a) CaO, (b) KCO, (c) NaCO, (d) NaHCO with the presence of steam. Initial conditions: temperature 300 K–1500 K, pressure 0.1–11 MPa, initial concentrations 0.5 mol sorbent + 1 mol HCl + 1 mol HO + 999998 mol N (or 9998mol N or 98 mol N)
Fig.3  Optimum desulphurisation conditions for (a) CuO, (b) NaCO, (c) NaHCO, (d) KCO, (e) CaO, (f) ZnO, (g) MnO, (h) FeO, (i) PbO. Initial conditions: temperature 300 K–1500 K, pressure 0.1–11 MPa, initial concentrations 1 mol sorbent + 1 mol HS + 999999 mol N (or 9999 mol N or 99 mol N)
Fig.4  Optimum desulphurisation conditions for (a) CuO, (b) NaCO, (c) NaHCO, (d) KCO, (e) CaO, (f) ZnO, (g) MnO, (h) FeO, (i) PbO with the presence of steam. Initial conditions: temperature 300 K–1500 K, pressure 0.1–11 MPa, initial concentrations 1 mol sorbent + 1 mol HS + 1 mol HO + 999998 mol N (or 9998 mol N or 98 mol N)
Fig.5  Optimum dechlorination conditions for (a) CaO, (b) KCO, (c) NaCO, (d) NaHCO when HS is present. Initial conditions: temperature 300–1500K, pressure 0.1–11 MPa, initial concentrations 1.5 mol sorbent + 1 mol HCl + 1 mol HS + 999998 mol N (or 9998 mol N or 98 mol N). Optimum dechlorination conditions for (e) CaO, (f) KCO, (g) NaCO, (h) NaHCO when HS and HO are both present. Initial conditions: temperature 300 K–1500 K, pressure 0.1–11 Mpa, initial concentrations 1.5 mol sorbent+1 mol HCl + 1mol HS + 1 mol HO + 999997 mol N (or 9997 mol N or 97 mol N).
Fig.6  Optimum desulphurisation conditions for (a) CuO, (b) NaCO, (c) NaHCO, (d) KCO, (e) CaO, (f)ZnO, (g) MnO, (h) FeO, (i) PbO when HCl is present. Initial conditions: temperature 300 K–1500 K, pressure 0.1–11 MPa, initial concentrations 1.5 mol sorbent + 1 mol HS + 1 mol HCl + 999998 mol N (or 9998 mol N or 98 mol N)
Fig.7  Optimum desulphurisation conditions for (a) CuO, (b) NaCO, (c) NaHCO, (d) KCO, (e) CaO, (f) ZnO, (g) MnO, (h) FeO, (i) PbO when HCl and HO are both present. Initial conditions: temperature 300 K–1500 K, pressure 0.1–11 MPa, initial concentrations 1.5 mol sorbent + 1 mol HS + 1 mol HCl + 1 mol HO + 999997 mol N (or 9997 mol N or 97 mol N)
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