ABSTRACT
CO2 capture (PCCC) process. However, sources of Fe for such degradations are poorly characterized. One aspect of the PCCC process which is poorly researched is the interaction of sulfur dioxide (SO2) gas in the flue gas (FG) with coal fly ash (CFA) and how this can affect amine degradation. Understanding that the SO2 would be dominantly present in the anionic pH speciated forms (bisulfite (HSO3–(aq)) and sulfite (SO32–(aq))) as a result of caustic scrubbing or amine-based desulfurization and that ammonia is commonly present either in original FG or as an amine degradation product, CFA leaching of Fe by ammonium sulfite ((NH4)2SO3) was experimentally examined under different pH (~ 4 to 10) and temperature (50 °C to 90 °C) conditions to simulate various pre-stripper sections within an amine solvent based SO2 and carbon dioxide (CO2) capturing process such as at the Boundary Dam Unit 3 carbon capture and storage (BD3 CCS) facility. The results suggest that SO2 and its pH-speciated aqueous forms can leach Fe, and thereby catalyze oxidative degradation of common amines used in capturing acidic contaminants from post-combustion FG. With the addition of (NH4)2SO3 (0.25 mol ⋅ L–1), the effect of SO32– on the leaching of iron(III) (Fe3+) and iron(II) (Fe2+) was apparent and distinctly different from the effect of pH per se. Thus, irrespective of the amine type, SO2 and its pH speciated forms can generate Fe ions to catalyze the degradation. Still, SO32–-induced Fe leaching occurred more dominantly in acidic solutions that simulate the pre-scrubber and amine-based SO2 capture conditions (pH ≤ 6) and less in alkaline aqueous conditions simulating amine-based CO2 capture (i.e., pH of ~ 8 to 10). The work does not seem to support an effect of SO2 on CFA leaching of Fe under pre-stripper conditions as the principal factor in catalyzing oxidative degradation of amines used in CO2 capture, even though the association with pH depression could still make it significant. At pH = 8, the total leached Fe ions averaged only ≤ 0.2 mg ⋅ L–1 and ≤ 1.0 mg ⋅ L–1 from CFA obtained from flue gas cooler inlet and the caustic polisher in the SO2 loop, respectively. Yet, in an integrated amine solvent SO2 and CO2 capturing process as employed at BD3 CCS, the effect is expected to be more significant with respect to amine degradation within the SO2 capture process.
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