Energy Sources, Part A, 34:90–98, 2012
Copyright © Taylor & Francis Group, LLC
ISSN: 1556-7036 print/1556-7230 online
DOI: 10.1080/15567030903567675
Removal of Sulfur Dioxide by a Slurry of
Jordanian Oil Shale Ash
A. M. AL-HARAHSHEH,
1
R. A. SHAWABKEH,
2
M. S. AL-HARAHSHEH,
3
and M. M. BATIHA
3
1
Department of Chemical Engineering, Mutah University, Karak, Jordan
2
Department of Chemical Engineering, King Fahd University of Petroleum and
Minerals, Saudi Arabia
3
College of Mining and Environmental Engineering, Al-Hussein Bin Talal
University, Ma’an, Jordan
Abstract This work presents a study on the capacity of oil shale ash to remove
sulphur dioxide from air streams before escaping into the atmosphere. Slurries of
different concentrations of this ash showed an uptake capacity of 4 10
4
mol
SO
2
/g ash obtained after 250 sec. This value increases with the increase of solution
pH, temperature, and ash concentration, and decreases the ash particle size. The
process of uptake seems to be coupled with both adsorption of SO
2
3
on the surface
of metal oxides and reaction with alkali and alkali earth metal hydroxides.
Keywords absorption, air pollution, oil shale ash, SO
2
removal, toxic gases
Introduction
Air pollution is considered as one of the undesired changes in the environment associated
with the development of chemical and related industries. The main source of air pollution
is the emission of toxic gases, such as SO
2
,H
2
S, NO
X
, CO, and CO
2
, which come
from thermal conversion processing of liquid and solid fuels in power plants, refineries,
petrochemical industries, and automobiles emission.
Sulfur dioxide is usually produced from desulphurization processes of petroleum
fractions, coal, and oil shale, as well as metallurgical smelting operation, and sulfuric
acid manufacture. Sulfur content in petroleum ranges from less than 0.5 to 2 wt% (Erika
et al., 1988). This value is as high as 7–9 wt% in the oil extracted from Jordanian oil
shale by thermal cracking (Al-Harahsheh et al., 2005). This amount of sulfur is converted
into H
2
S or SO
2
.
There are several environmental drawbacks of toxic SO
2
emission. Acidification of
the soil surface, poisoning of vegetation and living organisms, and corrosion are the
negative actions of SO
2
contained in the atmosphere (Querol et al., 1999; Kachur et al.,
2003).
A number of effluent gas desulphurization techniques are available. These can be
broadly classified into four categories: absorption of SO
2
in liquids, absorption by moist
particles, gas phase conversion of SO
2
, and sorption by solids (Chattopadhyaya et al.,
Address correspondence to Dr. Adnan Al-Harahsheh, Engineering Department, Mutah Uni-
versity, P.O. Box 7, Karak 61710, Jordan. E-mail: adnan@mutah.edu.jo
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