2016
DOI: 10.1016/j.ijggc.2016.01.046
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Species distribution of CO 2 absorption/desorption in aqueous and non-aqueous N -ethylmonoethanolamine solutions

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Cited by 45 publications
(38 citation statements)
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“…During the desorption process in aqueous absorbents, the concentration of carbamates increased until the maximum was reached and then decreased; this was consistent with the trend that the signal peak intensities of some carbamates first increased and then decreased. This phenomenon could be explained by R 1 R 2 NH 2 + (R 1 R 2 NH 2 + represents TETAH + or AMPH + ) reacting with bicarbonate to form carbamates and only part of bicarbonate being released as CO 2 with the residual bicarbonate transferred to carbamate that cannot be regenerated . Meanwhile, R 1 R 2 NH 2 + reacted with carbamate to release CO 2 .…”
Section: Resultsmentioning
confidence: 99%
“…During the desorption process in aqueous absorbents, the concentration of carbamates increased until the maximum was reached and then decreased; this was consistent with the trend that the signal peak intensities of some carbamates first increased and then decreased. This phenomenon could be explained by R 1 R 2 NH 2 + (R 1 R 2 NH 2 + represents TETAH + or AMPH + ) reacting with bicarbonate to form carbamates and only part of bicarbonate being released as CO 2 with the residual bicarbonate transferred to carbamate that cannot be regenerated . Meanwhile, R 1 R 2 NH 2 + reacted with carbamate to release CO 2 .…”
Section: Resultsmentioning
confidence: 99%
“…In order to understand their different absorption behaviors by the replacement of water with the organic solvent EGBE, 13 C NMR and FTIR characterizations were performed to verify the product species in nonaqueous and aqueous amine solvents during CO 2 absorption. Peak assignment was performed according to literature data. ,,,,, In our previous work, it was pointed out that misleading carbon signals could be found for the nonaqueous samples using D 2 O as an NMR solvent. DMSO- d 6 was used as a solvent instead of D 2 O for all the nonaqueous samples in order to prevent the carbamate hydrolysis.…”
Section: Resultsmentioning
confidence: 99%
“…Using organic solvents to replace water in the absorbents has proved to have significant advantages as for saving regeneration energy and potentially reducing corrosiveness and degradation. As a result, nonaqueous absorbents by blending secondary amines with organics have led to the advance development. , These reported organic solvents include volatile alcohols (e.g., methanol, ethanol, and butanol), low-volatile alcohols and glycols (e.g., benzyl alcohol and ethylene glycol) or their mixtures, glymes, dimethyl formamide (DMF), and ionic liquids. However, high-volatile alcohols (e.g., methanol and ethanol) as cosolvents can produce huge solvent loss when treating large-scale flue gas volume; thus, it seems to be impractical for potential industrial use.…”
Section: Introductionmentioning
confidence: 99%
“…In recent years, nonaqueous solvent blends formed by amine and a conventional organic solvent have been developed as promising alternatives to the aqueous amine absorbents, because they can provide the advantage of reducing the energy cost during the regeneration steps while retaining high CO 2 capacity [5]. At present, many nonaqueous systems were studied to capture CO 2 , such as the mixture of alcohol and amidines [6], alkanolamine solutions such as monoethanolamine (MEA) and 2-amino-2-methyl-1-propanol (AMP) in ethanol or ethylene glycol (EG) [7][8][9][10][11][12][13][14], and the amine-based deep eutectic solvents [15][16][17].…”
Section: Introductionmentioning
confidence: 99%