Lattice structure for sparging evaporator in catalytic inerting system
US-2024408565-A1 · Dec 12, 2024 · US
US9579602B2 · US · B2
| Field | Value |
|---|---|
| Publication number | US-9579602-B2 |
| Application number | US-201514632974-A |
| Country | US |
| Kind code | B2 |
| Filing date | Feb 26, 2015 |
| Priority date | Feb 26, 2015 |
| Publication date | Feb 28, 2017 |
| Grant date | Feb 28, 2017 |
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Embodiments described herein generally relate to apparatus and methods for reducing CO 2 from flue gas. Methods may include performing a chemisorption process in a first reactor comprising using at least a chemisorption solution comprising a sorbent. Methods may also include performing a desorption process treating the chemisorption solution with a powdered desorption catalyst after the chemisorption process has been performed.
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The invention claimed is: 1. A method of reducing CO 2 from flue gas, comprising: performing a chemisorption process in a first reactor comprising using at least a chemisorption solution comprising a sorbent; and performing a desorption process by treating the chemisorption solution with a powdered desorption catalyst after the chemisorption process is performed, wherein the powdered desorption catalyst is of the formula MZ v , wherein M is selected from the group consisting of Ti, Zr, and Hf, wherein Z is selected from the group consisting of —SO 4 , —F, —Cl, —Br, and —I, and wherein v is a numeral from 1 to 4. 2. The method of claim 1 , wherein the desorption process further comprises: introducing a carrier gas into the first reactor, wherein the carrier gas is selected from the group consisting of N 2 , He, H 2 , CO 2 , Argon and mixtures thereof. 3. The method of claim 2 , wherein the flow rate of the carrier gas is about 10,000 m 3 /min to about 20,000 m 3 /min. 4. The method of claim 2 , wherein the carrier gas is N 2 or H 2 . 5. The method of claim 1 , wherein the sorbent comprises an alkanolamine selected from the group consisting of monoethanolamine (MEA), diethanolamine (DEA), diisopropanolamine (DIPA), N-methylethanolamine, triethanolamine (TEA), N-methyldiethanolamine (MDEA), piperazine, N-methylpiperazine (MP), N-hydroxyethylpiperazine (HEP), 2-amino-2-methyl-1-propanol (AMP), 2-(2-aminoethoxy)ethanol, 2-(2-tert-butylaminopropoxy)ethanol, 2-(2-tert-butylaminoethoxy)ethanol (TBEE), 2-(2-tert-amylaminoethoxy)ethanol, 2-(2-isopropylaminopropoxy)ethanol, or 2-(2-(1-methyl-1-ethylpropylamino)ethoxy)ethanol, or mixtures thereof. 6. The method of claim 5 , wherein the alkanolamine is monoethanolamine (MEA). 7. The method of claim 1 , wherein the desorption process is performed at a temperature of about 35° C. to about 75° C. 8. The method of claim 1 , wherein the desorption process is performed with a mechanical stirrer at a stirring rate of about 500 rpm to about 700 rpm. 9. The method of claim 1 , wherein the desorption process is performed in a second reactor. 10. A method of reducing CO 2 from flue gas, comprising: performing a chemisorption process in a first reactor comprising using at least a chemisorption solution comprising a sorbent, wherein the chemisorption process is performed at ambient temperature; and performing a desorption process in a second reactor by treating the chemisorption solution with a powdered desorption catalyst, wherein the powdered desorption catalyst is of the formula MZ v , wherein M is selected from the group consisting of Ti, Zr, and Hf, wherein Z is selected from the group consisting of —SO 4 , —F, —Cl, —Br, and —I, and wherein v is a numeral from 1 to 4, and wherein the desorption process is performed at a temperature from about 35° C. to about 75° C.
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