CN115138178A - Polyamine-based organic amine and ionic liquid composite CO 2 Absorbent, preparation method and application thereof - Google Patents

Polyamine-based organic amine and ionic liquid composite CO 2 Absorbent, preparation method and application thereof Download PDF

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Publication number
CN115138178A
CN115138178A CN202210802490.1A CN202210802490A CN115138178A CN 115138178 A CN115138178 A CN 115138178A CN 202210802490 A CN202210802490 A CN 202210802490A CN 115138178 A CN115138178 A CN 115138178A
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China
Prior art keywords
absorbent
ionic liquid
organic amine
gas
polyamine
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CN202210802490.1A
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Chinese (zh)
Inventor
吴再坤
佘刘星
马家玉
穆新伟
孔剑
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Wuhan Institute of Technology
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Wuhan Institute of Technology
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Priority to CN202210802490.1A priority Critical patent/CN115138178A/en
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/14Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
    • B01D53/1493Selection of liquid materials for use as absorbents
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/14Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
    • B01D53/1456Removing acid components
    • B01D53/1475Removing carbon dioxide
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2252/00Absorbents, i.e. solvents and liquid materials for gas absorption
    • B01D2252/20Organic absorbents
    • B01D2252/204Amines
    • B01D2252/20415Tri- or polyamines
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2252/00Absorbents, i.e. solvents and liquid materials for gas absorption
    • B01D2252/20Organic absorbents
    • B01D2252/205Other organic compounds not covered by B01D2252/00 - B01D2252/20494
    • B01D2252/2053Other nitrogen compounds
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2252/00Absorbents, i.e. solvents and liquid materials for gas absorption
    • B01D2252/50Combinations of absorbents
    • B01D2252/504Mixtures of two or more absorbents
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/50Carbon oxides
    • B01D2257/504Carbon dioxide

Abstract

The invention relates to a polyamine organic amine and ionic liquid composite CO 2 An absorbent, a preparation method and application thereof. The CO is 2 The absorbent is prepared by mixing active components such as polyamino organic amine, ionic liquid and the like and a solvent, and when the absorbent is used, the absorbent and CO-containing components are mixed 2 The mixed gas is fully contacted to complete absorption, and the liquid obtained by absorption is heated or stripped to complete desorption, so that the gas can be regenerated and reused. The invention provides composite CO 2 The absorbent has the advantages of high absorption rate, large circulation capacity, low regeneration energy consumption, low circulation loss and the like, and can maintain high CO even after repeated regeneration 2 The absorption rate and the absorption capacity, and has better application prospect.

Description

Polyamine-based organic amine and ionic liquid composite CO 2 Absorbent, preparation method and application thereof
Technical Field
The invention relates to gas separation and CO 2 The technical field of trapping, in particular to a poly-amino organic amine and ionic liquid composite CO 2 An absorbent, a preparation method and application thereof.
Background
Climate change due to "carbon emissions" has become a worldwide problem. 2016, 4/22/100 countries and regions, including China, have jointly signed Paris' agreement in New York. Under this vision, carbon capture utilization and sequestration technology (CCS) is becoming one of the important ways to achieve carbon neutralization goals in various countries.
In the process of absorbing and trapping carbon dioxide by using a solvent, the alcohol amine method in the chemical absorption method is the most widely applied and most studied technology at present. The method has the advantages of large absorption capacity, good absorption effect, low cost, recyclable absorbent, and capability of recovering high-purity CO 2 And the like, however, how to reduce the energy consumption cost of the desorption process and how to regenerate the solvent is still very critical. Therefore, whether the alcohol amine method carbon dioxide trapping technology with low cost can be realized has very important significance for industrial development and environmental protection in China.
CO common to industry at present 2 The absorbent is mostly aqueous alcohol amine absorbent, however, the specific heat of water is high, so that a large amount of energy is used for raising the temperature of water in the desorption process, and the high regeneration temperature of the alcohol amine absorbent also causes high energy consumption. In addition, the alcohol amine absorbent is easy to volatilize and absorbs CO 2 And in the solvent regeneration process, a large amount of alcohol amine is volatilized and escapes, so that a large amount of material loss is caused. If the water content in the absorption liquid can be effectively reduced and an absorbent with lower regeneration temperature and difficult volatilization is adopted, the reduction of CO is facilitated 2 Energy, material and cost in the trapping process. Therefore, a method which has low regeneration energy consumption, low loss and CO resistance is sought 2 Absorbents having a prominent trapping effect have been the focus of research.
Disclosure of Invention
One purpose of the invention is to provide a polyamine organic amine and ionic liquid composite CO 2 An absorbent comprising at least 3 components: polyamine organic amine, ionic liquid and solvent.
Further, the polyamino organic amine is selected from at least one of diethylenetriamine and triethylene tetramine.
Further, the ionic liquid is selected from at least one of 1-ethyl-3-methylimidazolidine (or glutamic acid, alanine, histidine, lysine, arginine) salt ionic liquid, 1-butyl-3-methylimidazolidine (or glutamic acid, alanine, histidine, lysine, arginine) salt ionic liquid, 1-hexyl-3-methylimidazolidine (or glutamic acid, alanine, histidine, lysine, arginine) salt ionic liquid, 1-octyl-3-methylimidazolidine (or glutamic acid, alanine, histidine, lysine, arginine) salt ionic liquid, sodium glycinate, potassium glycinate and potassium sulfamate.
Further, the solvent is selected from at least one of water and aliphatic alcohol, wherein the aliphatic alcohol comprises ethanol, isopropanol, butanol, pentanol, octanol, glycol and the like.
Further, the total mass concentration of the polyamino organic amine and the ionic liquid in the absorbent is 0.2-6.0mol/L, and the mass ratio of the polyamino organic amine to the ionic liquid is x: (1-x), x is more than or equal to 1 and less than or equal to 9.
The second purpose of the invention is to provide the above poly-amino organic amine and ionic liquid composite CO 2 The preparation method of the absorbent comprises the following specific steps: preparing raw materials according to a formula, mixing the polyamine organic amine with the ionic liquid, adding a part of solvent to completely dissolve the polyamine organic amine, and finally adding the rest solvent to stir uniformly.
The third purpose of the invention is to provide a method for separating CO by using the polyamino organic amine and the ionic liquid composite absorbent 2 The method comprises the following steps: will contain CO 2 The gas to be treated is fully contacted with the compound absorbent for absorption to obtain the treated gas and rich liquid, and the rich liquid is regenerated and then repeatedly absorbed.
Furthermore, the absorption temperature is not more than 55 ℃, and the absorption pressure is 1-2bar.
Further, the gas to be treated is specifically pure carbon dioxide gas, fossil fuel power plant flue gas, automobile exhaust, chemical synthesis gas, steel plant exhaust, lime kiln gas and all containing CO 2 The gas of (2).
Further, CO in the gas to be treated 2 The volume fraction of (A) is 1% to 100%.
Further, the pregnant solution is desorbed and regenerated by heating or stripping, the desorption temperature is 70-130 ℃, and the desorption pressure is 0.8-1.2bar.
Compared with the alcohol amine absorbent mainly used in the existing industry, the compound absorbent provided by the invention contains the ionic liquid with low volatility and low regeneration temperature, so that the material loss is low; the energy consumption in the desorption process is lower than that of the existing alcohol amine absorbent, so that CO is generated 2 The trapping cost is low. Even after repeated multiple times of cyclic absorption-desorption, the catalyst still has better CO 2 And (4) absorption effect. In addition, the prior industrially commonly used alcohol amine absorbent is mainly monoethanolamine, diethanolamine or triethanolamine, the organic amines only contain one amino group, and the invention adopts the organic amine containing a plurality of amino groups, thereby having higher absorption capacity compared with the prior alcohol amine absorbent.
Detailed Description
In order to make those skilled in the art fully understand the technical solutions and advantages of the present invention, the following embodiments are further described.
Example 1
8.50g of diethylenetriamine and 1.94g of sodium glycinate were added to a 100mL beaker, and 50mL of a mixture of butanol and water (V) Alcohol(s) /V Water (W) = 1), stirring to completely dissolve the components, transferring the obtained mixture into a 100mL volumetric flask, performing volume fixing by using a butanol aqueous solution of 1.
CO was carried out by using an apparatus shown in CN113842748A or CN113842749A 2 In the adsorption experiment, the water bath temperature is stabilized at 40 ℃, N with the flow of 121mL/min is introduced into the absorption device under normal pressure 2 And 20mL/min CO 2 . CO in portable infrared gas analyzer 2 After the content is stable, 40mL of the prepared absorbent is injected into a double-kettle stirrer through an injector for adsorption. Calculating to know CO 2 The absorption rate is 8.60 mmol/s.m 2 And the level of the conventional absorbent is reached.
And (3) blowing nitrogen at normal pressure, desorbing and regenerating the absorbed rich solution for 1h at 90 ℃ by using a device shown in CN113842748A or CN113842749A, wherein the desorption rate is 85% by calculation.
The regenerated solution is absorbed again under the same conditions, and the absorption-desorption is repeated 4 timesThen, the calculated absorption rate still reaches 8.55 mmol/s.m 2
Example 2
7.31g of triethylene tetramine and 21.27g of 1-butyl-3-methylimidazolium glutamate ionic liquid are added into a 100mL beaker, and then ethylene glycol aqueous solution (V) is added Alcohol(s) /V Water (W) And 4), stirring to completely dissolve, transferring the obtained mixture into a 100mL volumetric flask, and carrying out constant volume by using the aqueous solution and shaking up to obtain a compound absorbent product.
CO was carried out by using an apparatus shown in CN113842748A or CN113842749A 2 In the adsorption experiment, the water bath temperature is stabilized at 30 ℃, N with the flow rate of 150mL/min is introduced into an absorption device under normal pressure 2 And 25mL/min CO 2 . CO in portable infrared gas analyzer 2 After the content is stable, 40mL of the prepared absorbent is injected into a double-kettle stirrer through an injector for adsorption. Calculating to know CO 2 The absorption rate is 9.13 mmol/s.m 2 And has higher absorption rate.
And (3) blowing nitrogen at normal pressure, desorbing and regenerating the absorbed rich solution at 93 ℃ for 40 minutes by using a device shown in CN113842748A or CN113842749A, wherein the desorption rate is 87% by calculation.
After the absorption rich solution is subjected to absorption-desorption circulation for 5 times, the absorption rate still reaches 9.05 mmol/s.m 2 The description will be given of the ability to be recycled.
Example 3
Adding 7.40g of triethylene tetramine, 5.90g of diethylenetriamine and 9.27g of 1-ethyl-3-methylimidazolium glycinate ionic liquid into a 50mL beaker, and adding an ethanol water solution (V) Alcohol(s) /V Water (W) And (4) = 7) constant volume shaking up to obtain a compound absorbent product.
CO was carried out by using an apparatus shown in CN113842748A or CN113842749A 2 In the adsorption experiment, the water bath temperature is stabilized at 30 ℃, N with the flow rate of 140mL/min is introduced into an absorption device under normal pressure 2 And 25mL/min CO 2 . CO in portable infrared gas analyzer 2 After the content is stable, 40mL of the prepared absorbent is injected into a double-kettle stirrer through an injectorAnd (4) carrying out adsorption. Calculating to know CO 2 The absorption rate is 12.09 mmol/s.m 2 This indicates that the absorbent has a higher absorption rate.
And (3) blowing nitrogen at normal pressure, desorbing and regenerating the absorbed rich solution at 100 ℃ for 50 minutes by using a device shown in CN113842748A or CN113842749A, wherein the desorption rate is 85.5 percent by calculation.
After the absorption pregnant solution is subjected to absorption-desorption circulation for 5 times, the absorption rate still reaches 11.98 mmol/s.m 2 This indicates that the absorbent does have the ability to be recycled.
Example 4
11.80g of diethylenetriamine, 10.10g of 1-ethyl-3-methylimidazol alanine salt and 15.61g of 1-hexyl-3-methylimidazol lysine salt ionic liquid are added into a 100mL beaker, and then ethylene glycol aqueous solution (V) Alcohol(s) /V Water (W) And (6) fixing the volume and shaking up to obtain a compound absorbent product.
CO was carried out by using an apparatus shown in CN113842748A or CN113842749A 2 In the adsorption experiment, the water bath temperature is stabilized at 50 ℃, N with the flow rate of 90mL/min is introduced into the absorption device under normal pressure 2 And 16mL/min CO 2 . CO in portable infrared gas analyzer 2 After the content is stable, 40mL of the prepared absorbent is injected into a double-kettle stirrer through an injector for adsorption. Calculating to know CO 2 The absorption rate was 9.21 mmol/s.m 2 This indicates that the absorbent has a higher absorption rate.
And (3) purging with nitrogen at normal pressure, desorbing and regenerating the absorbed rich solution at 105 ℃ for half an hour by using a device shown in CN113842748A or CN113842749A, wherein the desorption rate is 90.2% by calculation.
After the absorption rich solution is subjected to absorption-desorption circulation for 4 times, the absorption rate still reaches 9.18 mmol/s.m 2 This indicates that the absorbent has the ability to be recycled.

Claims (8)

1. Polyamine-based organic amine and ionic liquid composite CO 2 An absorbent characterized by: the absorbent comprises at least 3 components: polyamine-based organic amine and ionic liquidThe organic amine with polyamine group is selected from at least one of diethylenetriamine and triethylene tetramine; the ionic liquid is at least one selected from 1-ethyl-3-methylimidazole amino acid salt ionic liquid, 1-butyl-3-methylimidazole amino acid salt ionic liquid, 1-hexyl-3-methylimidazole amino acid salt ionic liquid, 1-octyl-3-methylimidazole amino acid salt ionic liquid, sodium glycinate, potassium glycinate and potassium sulfamate, and the amino acid is specifically one selected from glycine, glutamic acid, alanine, histidine, lysine and arginine; the solvent is at least one of water and fatty alcohol; the aliphatic alcohol comprises ethanol, isopropanol, butanol, pentanol, octanol and glycol.
2. The absorbent of claim 1, wherein: the total mass concentration of the polyamine-based organic amine and the ionic liquid is 0.2-6.0mol/L, and the mass ratio of the polyamine-based organic amine to the ionic liquid is x: (1-x), x is more than or equal to 1 and less than or equal to 9.
3. The polyamino organic amine, ionic liquid composite CO according to any one of claims 1 to 2 2 A process for the preparation of an absorbent, characterized in that the process comprises the steps of: preparing raw materials according to a formula, mixing the polyamine organic amine with the ionic liquid, adding a part of solvent to completely dissolve the polyamine organic amine, and finally adding the rest solvent and stirring uniformly.
4. CO separation by absorption with the absorbent according to any of claims 1-2 2 The method of (2), characterized in that the method comprises the steps of: will contain CO 2 The gas to be treated is fully contacted with the compound absorbent for absorption to obtain the treated gas and rich liquid, and the rich liquid is regenerated and then repeatedly absorbed.
5. The method of claim 4, wherein: the absorption temperature is not more than 55 deg.C, and the absorption pressure is 1-2bar.
6. The method of claim 4The method is characterized in that: the gas to be treated is CO-containing gas such as pure carbon dioxide gas, flue gas of fossil fuel power plant, automobile tail gas, chemical synthesis gas, tail gas of steel plant, lime kiln gas, etc 2 Of (2) is used.
7. The method of claim 4, wherein: CO in the gas to be treated 2 The volume fraction of (A) is 1% to 100%.
8. The method of claim 4, wherein: the pregnant solution is desorbed and regenerated by heating or stripping, the desorption temperature is 70-130 deg.C, and the desorption pressure is 0.8-1.2bar.
CN202210802490.1A 2022-07-07 2022-07-07 Polyamine-based organic amine and ionic liquid composite CO 2 Absorbent, preparation method and application thereof Pending CN115138178A (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN116272259A (en) * 2023-03-28 2023-06-23 四川精事达科技有限公司 Desulfurization and decarbonization solvent suitable for low-pressure gas and application thereof

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102179132A (en) * 2011-03-24 2011-09-14 浙江大学 Absorbent for catching or separating dioxide carbon
CN104548903A (en) * 2013-10-09 2015-04-29 中国石油化工股份有限公司 Organic amine solvent for capturing carbon dioxide
CN105854524A (en) * 2016-05-27 2016-08-17 四川益能康生环保科技有限公司 Absorbent for gathering carbon dioxide in exhaust gas
CN107970743A (en) * 2016-10-20 2018-05-01 中国石化工程建设有限公司 A kind of method for separating carbon dioxide

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102179132A (en) * 2011-03-24 2011-09-14 浙江大学 Absorbent for catching or separating dioxide carbon
CN104548903A (en) * 2013-10-09 2015-04-29 中国石油化工股份有限公司 Organic amine solvent for capturing carbon dioxide
CN105854524A (en) * 2016-05-27 2016-08-17 四川益能康生环保科技有限公司 Absorbent for gathering carbon dioxide in exhaust gas
CN107970743A (en) * 2016-10-20 2018-05-01 中国石化工程建设有限公司 A kind of method for separating carbon dioxide

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN116272259A (en) * 2023-03-28 2023-06-23 四川精事达科技有限公司 Desulfurization and decarbonization solvent suitable for low-pressure gas and application thereof
CN116272259B (en) * 2023-03-28 2024-02-13 四川精事达科技有限公司 Desulfurization and decarbonization solvent suitable for low-pressure gas and application thereof

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