Experiments were conducted in an externally heated drop-tube furnace t
o assess the effectiveness of the chemical calcium magnesium acetate [
CMA, CaMg2(CH3COO)6] as a combustion catalyst and a coal pretreatment
agent for reducing SO2 emissions. Bituminous coal particles of two dis
tinct sizes, pulverized (75-90 mum) or micronized and beneficiated (me
an diameter approximately 3.5 mum) were burned. To measure the coal pa
rticle temperatures and burn times, combustion traces were recorded fo
r single pulverized coal particles and clusters of micronized coal par
ticles using a three-colour near-infrared optical pyrometer. The volat
ile and the char phase combustion temperatures of untreated pulverized
-grind particles, in air at a gas temperature of 1450 K, were determin
ed to be 2200 and 1800 K, respectively. Particles treated with CMA und
er the same conditions burned hotter, with the temperature of volatile
and char phase being 2400 and 2000 K, respectively. SO2 and NO(x) con
centrations were measured at the exit of the furnace for both the pulv
erized and the micronized coals. For furnace gas temperatures between
1250 and 1450 K, in a background gas containing 10-50 ppm SO2 and equi
valence ratios, phi, between 0.4 to 0.7, untreated micronized and pulv
erized bituminous coal particles produced SO2 emissions in the range 1
00-200 ppm and NO(x) emissions in the range 200-450 ppm. In contrast,
combustion of pulverized particles treated with CMA, burning under the
same conditions, not only did not produce any SO2 but also eliminated
the background SO2 concentration. The combustion of micronized coal t
reated with CMA produced less SO2 than untreated micronized coal, but
complete reduction of SO2 was not achieved. Experiments with CMA-treat
ed micronized coal in atmospheres containing 40% oxygen suggested that
the primary mechanism for sulfur removal in this virtually ash-free c
oal was the sulfation of resulting CaO/MgO fly ash/aerosols. Experimen
ts in which the effluent of the combustion of pulverized coal was quen
ched immediately after the heated furnace zone suggest that a fraction
of the fuel sulfur (up to 50% of the released SO2) may have been enca
psulated by ash during the combustion of treated pulverized coals, wit
h the remaining released SO2 being removed by sulfation of Ca/Mg-conta
ining ash or submicron CaO/MgO aerosols in the cool-down region of the
furnace.