https://doi.org/10.1016/j.ccst.2021.100015
“Figure 3 showed the effects of SO2 concentrations (as shown in Table 2, run 2#–4#) on the CO2 capture capacity and cumulative SO2 adsorption capacity of NaBr modified “Dolomite” in the calcium looping process. It can be seen that with the increase of SO2 concentration in the reaction, the cyclic CO2 capture capacity of the CaO-based sorbent decreased more rapidly. When exposed to 0.1 %, 0.2 %, and 0.3 % SO2, the cyclic CO2 capture capacity of dolomite decreased rapidly from 0.31 g/g, 0.27 g/g, and 0.26 g/g during the 1st reaction to 0.14 g/g, 0.08 g/g and 0.06 g/g during the 10th reaction; at the same time, after 10 reactions in these atmospheres, the cumulative SO2 capture capacity of dolomite was 0.162 g/g, 0.225 g/g and 0.280 g/g respectively.”
“Exposed in the atmosphere of 0.1%, 0.2%, and 0.3% SO2, the “NaBr/Dolomite” showed a slightly weaker CO2 capture capacity in the first cycle than the “Dolomite”; however, “NaBr/dolomite” showed significantly better cyclic stability over the cycles, i.e., after 10 cycles, the modified adsorbent showed an increase of 1.63 times, 2.81 times and 3.32 times on CO2 capture capacity than that of “Dolomite”. In addition, the cumulative SO2 capture capacity of “NaBr/Dolomite” over the 10 cyclic reactions is 0.176 g/g, 0.27 g/g, and 0.335 g/g respectively. With the increase of SO2 concentration, its cumulative SO2 capture capacity has been significantly improved. Hence, NaBr modification improved the SO2 capture capacity of dolomite, but the sulfation of the absorbent did not reduce its cyclic CO2 capture capacity.”

“Figure 3. (a). Effect of SO2 concentration on CO2 capture characteristics in the “NaBr/Dolomite” over the calcium looping process; (b). Effect of NaBr modification on the cumulative SO2 capture capacity of “Dolomite”.”