Aqueous amine solvents are used to capture CO2 from
various flue gas sources. In this work, the chemical stability of
a blend of 3-amino-1-propanol (3A1P) and 1-(2-hydroxyethyl)pyrrolidine
[1-(2HE)PRLD] was studied. The chemical stability tests were conducted
both in batch and cycled systems using various oxygen and NOx concentrations,
additives (iron), and temperatures. In the thermal degradation experiments
with CO2 present, the blend was more stable than the primary
amines [(3A1P or monoethanolamine (MEA)] but less stable than the
tertiary amine 1-(2HE)PRLD alone. Similar stability was observed between
MEA, 3A1P, and the blend in the batch experiments at medium oxygen
concentration (21% O2) and no iron present. 1-(2HE)PRLD
was more stable. However, the presence of high oxygen concentration
(96% O2) and iron reduced the stability of 1-(2HE)PRLD
significantly. Furthermore, in the case of the blend, the chemical
stability increased with increasing promoter concentration in batch
experiments. During the cyclic experiment, the amine loss for the
blend was similar to what was previously observed for MEA (30 wt %)
under the same conditions. A thorough mapping of degradation compounds
in the solvent and condensate samples resulted in the identification
and quantification of 30 degradation compounds. The major components
in batch and cycled experiments varied somewhat, as expected. In the
cyclic experiments, the major components were ammonia, 3-(methylamino)-1-propanol
(methyl-AP), N,N′-bis(3-hydroxypropyl)-urea
(AP-urea), pyrrolidine, formic acid (formate), and N-(3-hydroxypropyl)-glycine (HPGly). Finally, in this paper, formation
pathways for the eight degradation compounds (1,3-oxazinan-2-one,
AP-urea, 3-[(3-aminopropyl)amino]-1-propanol, tetrahydro-1-(3-hydroxypropyl)-2(1H)-pyrimidinone, methyl-AP, N-(3-hydroxypropyl)-formamide, N-(3-hydroxypropyl)-β-alanine, and HPGly) are suggested.