TY - JOUR
T1 - Red soil as a regenerable sorbent for high temperature removal of hydrogen sulfide from coal gas
AU - Ko, Tzu Hsing
AU - Chu, Hsin
AU - Lin, Hsiao Ping
AU - Peng, Ching Yu
N1 - Funding Information:
This study was funded in part by the Industrial Technology Research Institute, Taiwan. The authors gratefully acknowledge the constructive comments of anoymous reviews. Also thanks Ms. Meng-Hsiu Shih for her assistance in the basic analysis of soil samples.
PY - 2006/8/25
Y1 - 2006/8/25
N2 - In this study, hydrogen sulfide (H2S) was removed from coal gas by red soil under high temperature in a fixed-bed reactor. Red soil powders were collected from the northern, center and southern of Taiwan. They were characterized by XRPD, porosity analysis and DCB chemical analysis. Results show that the greater sulfur content of LP red soils is attributed to the higher free iron oxides and suitable sulfidation temperature is around 773 K. High temperature has a negative effect for use red soil as a desulfurization sorbent due to thermodynamic limitation in a reduction atmosphere. During 10 cycles of regeneration, after the first cycle the red soil remained stable with a breakthrough time between 31 and 36 min. Hydrogen adversely affects sulfidation reaction, whereas CO exhibits a positive effect due to a water-shift reaction. COS was formed during the sulfidation stage and this was attributed to the reaction of H2S and CO. Results of XRPD indicated that, hematite is the dominant active species in fresh red soil and iron sulfide (FeS) is a product of the reaction between hematite and hydrogen sulfide in red soils. The spinel phase FeAl2O4 was found during regeneration, moreover, the amount of free iron oxides decreased after regeneration indicating the some of the free iron oxide formed a spinel phase, further reducting the overall desulfurization efficiency.
AB - In this study, hydrogen sulfide (H2S) was removed from coal gas by red soil under high temperature in a fixed-bed reactor. Red soil powders were collected from the northern, center and southern of Taiwan. They were characterized by XRPD, porosity analysis and DCB chemical analysis. Results show that the greater sulfur content of LP red soils is attributed to the higher free iron oxides and suitable sulfidation temperature is around 773 K. High temperature has a negative effect for use red soil as a desulfurization sorbent due to thermodynamic limitation in a reduction atmosphere. During 10 cycles of regeneration, after the first cycle the red soil remained stable with a breakthrough time between 31 and 36 min. Hydrogen adversely affects sulfidation reaction, whereas CO exhibits a positive effect due to a water-shift reaction. COS was formed during the sulfidation stage and this was attributed to the reaction of H2S and CO. Results of XRPD indicated that, hematite is the dominant active species in fresh red soil and iron sulfide (FeS) is a product of the reaction between hematite and hydrogen sulfide in red soils. The spinel phase FeAl2O4 was found during regeneration, moreover, the amount of free iron oxides decreased after regeneration indicating the some of the free iron oxide formed a spinel phase, further reducting the overall desulfurization efficiency.
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U2 - 10.1016/j.jhazmat.2006.01.010
DO - 10.1016/j.jhazmat.2006.01.010
M3 - Article
C2 - 16469434
AN - SCOPUS:33746725339
SN - 0304-3894
VL - 136
SP - 776
EP - 783
JO - Journal of Hazardous Materials
JF - Journal of Hazardous Materials
IS - 3
ER -