CN107158895B - Carbon dioxide absorbent - Google Patents
Carbon dioxide absorbent Download PDFInfo
- Publication number
- CN107158895B CN107158895B CN201710572449.9A CN201710572449A CN107158895B CN 107158895 B CN107158895 B CN 107158895B CN 201710572449 A CN201710572449 A CN 201710572449A CN 107158895 B CN107158895 B CN 107158895B
- Authority
- CN
- China
- Prior art keywords
- absorbent
- carbon dioxide
- parts
- carbon
- absorption
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Active
Links
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation 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
- B01D53/14—Separation 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
- B01D53/1493—Selection of liquid materials for use as absorbents
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation 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
- B01D53/14—Separation 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
- B01D53/1456—Removing acid components
- B01D53/1475—Removing carbon dioxide
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2252/00—Absorbents, i.e. solvents and liquid materials for gas absorption
- B01D2252/50—Combinations of absorbents
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02C—CAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
- Y02C20/00—Capture or disposal of greenhouse gases
- Y02C20/40—Capture or disposal of greenhouse gases of CO2
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Analytical Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Gas Separation By Absorption (AREA)
- Treating Waste Gases (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
Abstract
The invention provides a carbon dioxide absorbent, which consists of an alcohol amine main absorbent, piperazine serving as an absorption auxiliary agent, an organic auxiliary agent, activated carbon, a carbon nano tube and deionized water, wherein the organic auxiliary agent is a mixture of dimethyl sulfoxide (DMSO) and Dimethylformamide (DMF); the dosage ratio is as follows: 30-50 parts of main alcohol amine absorbent and piperazine, 10-15 parts of organic auxiliary agent, 50-70 parts of deionized water and 3-8 parts of activated carbon and carbon nano tube. The carbon dioxide absorbent has good absorption rate, absorption capacity and regeneration rate, particularly good stability, and is suitable for various scene applications.
Description
Technical Field
For absorbing dioxygenCarbon conversion of CO2And related methods.
Background
Carbon dioxide emissions from industrial sources to the atmosphere are the main cause of the greenhouse effect. In the prior art, particular attention has been paid to the absorption removal of carbon dioxide from flue gas streams. For example, aqueous solutions of hindered amines of aqueous monoethanolamine MEA or methyldiethanolamine MDEA and 2-amino-2-methyl-1-propanol AMP are used as solvents for absorption/scrubbing type regeneration processes for carbon dioxide absorption from coal-fired power plants and gas turbines.
CN1127156A of Kansai electric power Co Ltd and Mitsubishi heavy industry Co Ltd discloses a method for removing carbon dioxide in a gas by using a catalyst containing a compound represented by the general formula R1NHC(CH3)2CH2OH,R1An aqueous solution of an amine compound represented by C1-4 alkyl or an aqueous solution containing an amine compound represented by the general formula R2CHR3NHCH2CH2OH,R2Is H or C1-4 alkyl, R3An aqueous solution of a compound represented by H or methyl and a piperazine compound selected from piperazine, 2-methylpiperazine, 2, 3-dimethylpiperazine and 2, 5-dimethylpiperazine, or an aqueous solution of a mixed amine solution having a concentration of each of secondary and tertiary amines in the range of 10 to 45% by weight, or an aqueous solution of a piperazine derivative, for example, by contacting with combustion exhaust gas at atmospheric pressure to remove CO in the combustion exhaust gas2. Treatment of atmospheric combustion exhaust gas to increase CO levels over previously used amine absorption solutions2The absorption capacity of (1).
CN1608712A of China eastern science and technology university discloses an improved N-methyldiethanolamine decarburization solution, which consists of an N-methyldiethanolamine aqueous solution and an activating agent, wherein the weight ratio of the activating agent to the N-methyldiethanolamine is 0.05-0.20, and the improved N-methyldiethanolamine decarburization solution is characterized in that the activating agent consists of morpholine and piperazine or diethanolamine. The decarbonization solution can be used for removing carbon dioxide in mixed gas such as synthesis gas, city gas or natural gas and the like, and can also be used for removing sulfides. The decarbonizing liquid has the advantages of large absorption capacity, high purification degree, low regeneration energy consumption and the like.
Chengdu Huaxi chemical research place CN1887407A disclosesRemoving CO from mixed gas2The solvent of (2) is to add a diazacyclo compound and an organic amine with steric hindrance effect as an activating agent into an N-Methyldiethanolamine (MDEA) solution to remove carbon dioxide from a mixed gas. Diazacyclo compounds include piperazine, imidazole, 2-methylimidazole, 2, 5-dimethylimidazole, 4-methylimidazole, and the like, and sterically hindered amines include: tert-butylamine ethyl alcohol (TBE), tert-butylamine ethoxyethyl alcohol (TBEE), 1,2- (di-tert-butylamine ethoxy) ethane (BIS-TB), 2-Piperidineethanol (PE), 1, 8-p-menthane diamine (MPA), 2-amino-2-methyl-1-propanol (AMP), and the like. The solution formula is adopted to purify CO in gas2The content can be reduced to a very low level, which is obviously reduced compared with the conventional MDEA decarburization method.
Shell in CN101970081A discloses a method for removing CO from a gas2The method of (2), the method comprising the steps of: (a) obtaining CO enrichment by contacting the gas with an absorption liquid in an absorber2And purifying the gas to remove CO from the gas2(ii) a (b) Heating rich in CO2The absorbing liquid of (4); (c) make the heated CO rich2Is contacted with a stripping gas in a regenerator at an elevated temperature to obtain a regenerated absorption liquid and a rich CO2The hot gas stream of (a); wherein at least part is enriched in CO2Through the absorption liquid rich in CO2The hot air flow is heated by external heat exchange. The method enables simple and more energy-efficient removal of CO using an absorption liquid2Because of the use for warming CO-rich2By partial heat demand of the absorption liquid from the rich CO2Is provided by the hot gas flow of (a). By making the CO rich2At least partially condensing the steam in the hot gas stream to transfer the heat demand. The process results in an increase in the overall energy efficiency of 5-25%, preferably 10-25%.
CN103596662A of asahi chemical company discloses a carbon dioxide absorbent and a method for separating and recovering carbon dioxide using the same, which comprises an amine compound, a weak acid compound and water, wherein the amine compound has a pKb of 4.0 to 7.0 in an aqueous solution at 30 ℃, the weak acid compound is boric acid or a boric acid ester having a pKa of 7.0 to 10.0 in an aqueous solution at 30 ℃, and the amount of the weak acid compound is in the range of 0.01 to 1.50 equivalents relative to the amino group of the amine compound; the amine compound includes an amine compound represented by the following general formula (I):
wherein R1 and R2 each represent a hydrogen atom or an alkyl group having 1 to 4 carbon atoms.
The enfriedel systems company, CN103648612A, discloses a sorbent for the reduction of carbon dioxide from indoor air comprising a solid support; and an amine-based compound carried by the carrier, wherein the amine-based compound is configured to capture at least some of the CO in the room air of the enclosed space2And releasing at least a portion of the captured CO by flowing outdoor air through the sorbent2. The carrier is selected from: gels, molecular sieves, nanotube-containing materials, porous materials, sponges and sponge-like materials, electromagnetically charged objects, porous organic polymers, ion exchange resins, polymeric absorbent resins, acrylate polymers, polystyrene divinyl benzene, polymethyl methacrylate (PMMA), polystyrene, Styrene Divinyl Benzene (SDB), fly ash, activated carbon, carbon nanotubes, alumina nanoparticles, synthetic zeolites, porous alumina, porous minerals, porous silica, silica nanoparticles, fumed silica, activated carbon, aluminum phyllosilicates, bentonite, ball clay, fuller's earth, montmorillonite, attapulgite, hectorite, palygorskite, saponite, sepiolite metal, organic frameworks, and one or more combinations thereof. The amine-based compound is selected from: monoethanolamine (MEA), ethanolamine, methylamine, Polyethyleneimine (PEI), Diethanolamine (DEA), dimethylamine, diethylamine, Diisopropanolamine (DIPA), Tetraethylenepentamine (TEPA), Methyldiethanolamine (MDEA), methylethanolamine, and one or more combinations thereof. Can be used for reducing CO from gas2Comprising a solid support formed from a plurality of particles, wherein the particles are formed substantially in the range of 0.1-10 mmDiameter. The support may be impregnated with an amine-based compound comprising at least 25% secondary amines and is operable for capturing CO2For the purpose of self-contained 100-2000ppm CO2CO reduction of concentrated gases2。
The general electric company, CN103764258A, discloses a composition for absorbing carbon dioxide and related method and system, wherein the carbon dioxide absorbent comprises a) a liquid non-aqueous silicon-based material consisting of a polymer with CO2Reversibly reacting and/or having a reaction towards CO2High affinity functionalization of one or more groups; and b) at least one amino alcohol compound. The aminoalcohol compound is selected from the group consisting of diethanolamine, triethanolamine, tripropanolamine, dimethylethanolamine, methyldiethanolamine, diethylethanolamine, di- (3-hydroxypropyl) amine, N-tris (3-hydroxybutyl) amine, N-tris- (4-hydroxybutyl) amine, N-tris- (2-hydroxypropyl) amine, N-diisopropylethanolamine, N-diethylpropanolamine, N-diethyl- (2, 3-dihydroxypropyl) amine, N-ethyldiethanolamine, N-propyldiethanolamine, and combinations thereof. The functionalized silicon-based material is selected from the group consisting of linear, branched, star-shaped or cyclic aminopropyl-, aminobutyl-or aminoisobutyl-substituted siloxanes.
The traditional Chinese medicine is CN104548903A, which discloses an organic amine solvent for capturing carbon dioxide, and is characterized in that the organic amine solvent comprises 10-40% of a main absorption component, 5-20% of an absorption-assisting component, 0.05-1.0% of a corrosion inhibitor, 0.05-1.0% of an antioxidant and 30-84% of a mixed solvent by mass. The main absorption component is one or more of glycinate, polyether amine, morpholine and derivatives thereof, and polyethylene glycol dimethyl ether. The absorption-aiding component is one or more of diethylaminoethanol, 2-amino-2-methyl-1-propanol, N-methyldiethanolamine and hydroxyethyl ethylenediamine. The corrosion inhibitor is one or more of sodium metavanadate, sodium chromate and hexamethylenetetramine. The antioxidant is one or more of sodium sulfite, potassium sodium tartrate and antimony sodium tartrate. The mixed solvent is one or more of deionized water, methyl pyrrolidone and propylene carbonate. The initial degradation time reaches 226min at the longest, which shows that the formula of the decarburization solution has the best oxidation degradation resistance which is far higher than that of the comparative example, and the initial degradation time is prolonged by 4 to 7 times.
China petrochemical is CN105561756A, which discloses a compound solvent for capturing carbon dioxide and application thereof, wherein the solvent comprises a solvent containing amino ether oxy, alcohol amine and water. Wherein, the content of the solvent containing amino ether oxyl is 5 to 85 weight percent, the content of alcohol amine is 1.5 to 70 weight percent, and the content of water is 5 to 80 weight percent. The structural formula of the solvent containing amino and ether oxygen groups is NH2-R1-(O-CHR3-CH2) And x-R2, wherein R1 and R2 are independently selected from alkyl, alkyl substituted by hydroxyl, alkyl substituted by amino, or alkyl substituted by both amino and hydroxyl, R3 is alkyl or hydrogen, and x is 1-6. The carbon dioxide collecting device can be used for collecting carbon dioxide discharged by various low-concentration carbon dioxide discharge sources such as coal-fired boiler discharge gas of a power plant, cement and lime kiln gas, blast furnace gas, catalyst regeneration discharge gas of a refinery FCC device and the like at the temperature of 10-80 ℃. The method has the advantages of large absorption capacity, high absorption rate, high regeneration rate, high stability and the like, and has good prospect in the field of large-scale carbon dioxide capture. The alcohol amine is one or more of monoethanolamine, diethanolamine, triethanolamine, N-methyldiethanolamine, and 2-amino-2-methyl-1-propanol.
At present, the mixed alcohol amine absorbent has characteristics in the aspects of carbon dioxide absorption capacity, absorption rate, analysis performance and regeneration energy consumption, but needs to further improve the comprehensive performance and stability of the absorbent in the aspects of carbon dioxide absorption capacity, absorption rate, analysis performance and regeneration energy consumption.
Disclosure of Invention
The technical problem to be solved by the invention is to provide an absorbent for carbon dioxide, which has better absorption rate, absorption capacity and regeneration rate, and particularly has better stability.
The technical scheme adopted by the invention is as follows: a carbon dioxide absorbent is characterized by comprising an alcohol amine main absorbent, piperazine serving as an absorption aid, an organic aid, activated carbon, carbon nanotubes and deionized water, wherein the organic aid is a mixture of dimethyl sulfoxide (DMSO) and Dimethylformamide (DMF); the dosage ratio is as follows:
30-50 parts of alcamines main absorbent and piperazine
10-15 parts of organic auxiliary agent
50-70 parts of deionized water
3-8 parts of activated carbon and carbon nanotubes.
Preferably, the molar ratio of DMSO to DMF is between 3:1 and 1:3, preferably 3: 2.
Preferably, the mass ratio of the activated carbon to the carbon nanotubes is 10-20:1, preferably 15: 1.
Preferably, the main alcohol amine absorbent is one or more of N-methyldiethanolamine, hydroxyethyl ethylenediamine and triethylene diamine.
Preferably, the mass ratio of the main alcohol amine absorbent to the piperazine is 10: 2-8.
Preferably, the organic adjuvant is used in an amount of 12 parts by weight.
Preferably, the absorbent has an absorption capacity of 0.85 or more and an absorption capacity of 0.80 or more after standing for 6 months.
Preferably, the degree of regeneration of the absorbent is 90% or more.
Preferably, the absorbent has an absorption temperature of 20 to 60 ℃ and an operating pressure of 0 to 0.2 MPa.
Preferably, the regeneration temperature of the absorbent is 80-110 ℃ and the operating pressure is 0-0.5 MPa.
Tests prove that the carbon dioxide absorbent can achieve better absorption rate, absorption capacity (more than 0.85) and regeneration degree, particularly has better stability, and the absorption capacity after being placed at room temperature for 6 months is kept above 0.80.
Wherein the absorption rate, absorption capacity and degree of regeneration are measured according to the method disclosed in CN 105080326A.
Detailed Description
Example 1:
a carbon dioxide absorbent is characterized by comprising an alcohol amine main absorbent, piperazine serving as an absorption aid, an organic aid, activated carbon, carbon nanotubes and deionized water, wherein the organic aid is a mixture of dimethyl sulfoxide (DMSO) and Dimethylformamide (DMF); the dosage ratio is as follows:
40 parts of main alcohol amine absorbent and 40 parts of piperazine, wherein the MDEA accounts for 30 parts by weight, and the piperazine accounts for 10 parts by weight; 10 parts of organic auxiliary agent, wherein the mol ratio of DMSO to DMF is 3: 1;
50 parts by weight of deionized water;
3 parts of activated carbon and carbon nano tubes by weight, wherein the mass ratio of the activated carbon to the carbon nano tubes is 10: 1.
All examples and comparative examples measure the average absorption rate, absorption capacity and regeneration degree of the carbon dioxide absorbent, and the absorption capacity after being left for 6 months, and the results are recorded in table 1. Wherein the absorption temperature is 20 ℃ and the regeneration temperature is 80 ℃.
Example 2:
otherwise as in example 1, the molar ratio of DMSO to DMF was 1: 3.
Example 3:
otherwise as in example 1, the molar ratio of DMSO to DMF was 3: 2.
Example 4:
otherwise, as in example 1, the mass ratio of the activated carbon to the carbon nanotubes was 20: 1.
Example 5:
otherwise, as in example 1, the mass ratio of activated carbon to carbon nanotubes was 15: 1.
Example 6:
in the same manner as in example 1, the alkanolamines as the main absorbent were N-methyldiethanolamine, hydroxyethylethylenediamine and triethylenediamine each in 10 parts by weight.
Example 7:
the rest of the organic auxiliary was 12 parts by weight as in example 1.
Example 8:
otherwise as in example 1, the primary alkanolamine absorbent is hydroxyethylethylenediamine.
Example 9:
otherwise, as in example 1, the primary alkanolamine absorbent is triethylenediamine.
Comparative example 1:
the procedure is as in example 1 except that no organic auxiliary is used.
Comparative example 2-a:
the organic adjuvant was only DMSO, and the procedure was otherwise the same as in example 1.
Comparative example 2-b:
the organic auxiliary agent is DMF only, and the rest is the same as example 1.
Comparative example 2-c:
the organic auxiliary was 20 parts by weight, and the rest was the same as in example 1.
Comparative examples 2-d:
the organic auxiliary was 5 parts by weight, and the rest was the same as in example 1.
Comparative example 3:
the same procedure as in example 1 was repeated, except that activated carbon and carbon nanotubes were not used.
Comparative example 4:
the same procedure as in example 1 was repeated, except that no organic auxiliary was used, and no activated carbon or nanotubes were used.
Comparative example 5-a:
the same procedure as in example 1 was repeated except that 3 parts by weight of activated carbon was used alone.
Comparative example 5-b:
the same procedure as in example 1 was repeated except that 3 parts by weight of carbon nanotubes were used.
Comparative example 5-c:
the amount of activated carbon and carbon nanotubes used was 10 parts by weight, and the rest was the same as in example 1.
Comparative examples 5-d:
the amount of activated carbon and carbon nanotubes used was 2 parts by weight, and the rest was the same as in example 1.
TABLE 1
As can be seen, the organic auxiliary had a greater effect on the stability in example 1 compared to comparative example 1. In example 1 compared to the four groups of comparative example 2, the choice of organic adjuvant has an impact on both capacity and stability.
Example 1 compared to comparative example 3, activated carbon and carbon nanotubes all have an impact on the rate of absorption, capacity and stability. Example 1 in comparison to comparative example 4, the use of an organic solvent with activated carbon and carbon nanotubes may act synergistically. Meanwhile, the stability and the capacity are improved.
In example 1, compared with the four groups of comparative example 5, stability and capacity are affected by using activated carbon or carbon nanotubes alone or by excessively large or small mixing ratio of the activated carbon or the carbon nanotubes.
Further, in comparison of example 1 with examples 2-3, the molar ratio of DMSO to DMF is optimally 3: 2. the mass ratio of activated carbon to carbon nanotubes is optimally 15:1 for example 1 versus examples 4-5.
Compared with the examples 6 and 8-9, the main absorbent of the alcamines is N-methyldiethanolamine, hydroxyethylethylenediamine and triethylenediamine, each 10 weight parts, which has better effect than that of using any one of the three alone.
As can be seen from a comparison of example 1 with example 7, the organic auxiliary is used in an optimum amount of 12 parts by weight.
Claims (6)
1. A carbon dioxide absorbent is characterized by comprising an alcohol amine main absorbent, piperazine serving as an absorption aid, an organic aid, activated carbon, carbon nanotubes and deionized water, wherein the organic aid is a mixture of dimethyl sulfoxide (DMSO) and Dimethylformamide (DMF); the dosage ratio is as follows:
30-50 parts of an alcamines main absorbent and piperazine, wherein the mass ratio of the alcamines main absorbent to the piperazine is 10: 2-8; 10-15 parts of organic auxiliary agent
50-70 parts of deionized water
3-8 parts of activated carbon and carbon nanotubes;
wherein the mol ratio of DMSO to DMF is 3: 2;
the mass ratio of the activated carbon to the carbon nano tubes is 15: 1;
the absorbent has an absorption capacity of 0.85 or more, and an absorption capacity of 0.80 or more after standing for 6 months.
2. The carbon dioxide absorbent according to claim 1, wherein the main alcohol amine absorbent is one or more of N-methyldiethanolamine, hydroxyethylethylenediamine and triethylenediamine.
3. The carbon dioxide absorbent according to claim 1, wherein the organic auxiliary is used in an amount of 12 parts by weight.
4. The carbon dioxide absorbent according to claim 1, wherein the absorbent is regenerated to a degree of 90% or more.
5. The carbon dioxide absorbent according to claim 1, wherein the absorbent has an absorption temperature of 20 to 60 ℃ and an operating pressure of 0 to 0.2 MPa.
6. The carbon dioxide absorbent according to claim 1, wherein the absorbent has a regeneration temperature of 80 to 110 ℃ and an operating pressure of 0 to 0.5 MPa.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710572449.9A CN107158895B (en) | 2017-07-13 | 2017-07-13 | Carbon dioxide absorbent |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710572449.9A CN107158895B (en) | 2017-07-13 | 2017-07-13 | Carbon dioxide absorbent |
Publications (2)
Publication Number | Publication Date |
---|---|
CN107158895A CN107158895A (en) | 2017-09-15 |
CN107158895B true CN107158895B (en) | 2020-07-28 |
Family
ID=59820643
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201710572449.9A Active CN107158895B (en) | 2017-07-13 | 2017-07-13 | Carbon dioxide absorbent |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN107158895B (en) |
Families Citing this family (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108084980A (en) * | 2017-12-01 | 2018-05-29 | 中海油天津化工研究设计院有限公司 | A kind of efficiently molten sulphur agent and preparation method thereof |
CN109603425A (en) * | 2018-12-13 | 2019-04-12 | 大连理工大学 | Recycle the composite decarbonizing solution of the addition carbon nanotube of carbon dioxide in gas mixture |
CN109758871A (en) * | 2018-12-28 | 2019-05-17 | 胜利油田森诺胜利工程有限公司 | A kind of novel few water absorption CO2The preparation method of ternary built organic amine medicament |
CN111715031B (en) * | 2020-06-24 | 2022-08-05 | 江西师范大学 | Carbon dioxide absorption medium and optimization process thereof |
CN114192122A (en) * | 2020-09-02 | 2022-03-18 | 中国船舶重工集团公司第七一八研究所 | Renewable nano-porous adsorption material for removing carbon dioxide and preparation method thereof |
CN114534452A (en) * | 2022-03-15 | 2022-05-27 | 武汉理工大学 | Method for separating and trapping carbon dioxide in flue gas |
CN117959916B (en) * | 2024-03-28 | 2024-06-07 | 深碳科技(深圳)有限公司 | Liquid-liquid two-phase absorbent and preparation method and application thereof |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102989295A (en) * | 2012-11-23 | 2013-03-27 | 中国华能集团清洁能源技术研究院有限公司 | Absorbent which gathers carbon dioxide in flue gas or synthesis gas |
CN103648612A (en) * | 2011-05-17 | 2014-03-19 | 恩弗里德系统公司 | Sorbents for carbon dioxide reduction from indoor air |
CN106876722A (en) * | 2015-12-13 | 2017-06-20 | 中国科学院大连化学物理研究所 | A kind of Carbon dioxide electrochemical reduction gas-diffusion electrode and its preparation and application |
Family Cites Families (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103418356B (en) * | 2012-05-17 | 2016-03-09 | 神华集团有限责任公司 | Gas adsorption material and preparation method thereof |
CN105561734A (en) * | 2014-10-14 | 2016-05-11 | 中国石油化工股份有限公司 | Thermosensitive amine group carbon dioxide absorbent |
CN104524928A (en) * | 2014-12-30 | 2015-04-22 | 上海锅炉厂有限公司 | Absorbent for collecting carbon dioxide |
KR101746561B1 (en) * | 2015-06-24 | 2017-06-13 | 광주과학기술원 | Carbon dioxide absorbents and method for regenerating of carbon dioxide absorbents |
-
2017
- 2017-07-13 CN CN201710572449.9A patent/CN107158895B/en active Active
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103648612A (en) * | 2011-05-17 | 2014-03-19 | 恩弗里德系统公司 | Sorbents for carbon dioxide reduction from indoor air |
CN102989295A (en) * | 2012-11-23 | 2013-03-27 | 中国华能集团清洁能源技术研究院有限公司 | Absorbent which gathers carbon dioxide in flue gas or synthesis gas |
CN106876722A (en) * | 2015-12-13 | 2017-06-20 | 中国科学院大连化学物理研究所 | A kind of Carbon dioxide electrochemical reduction gas-diffusion electrode and its preparation and application |
Also Published As
Publication number | Publication date |
---|---|
CN107158895A (en) | 2017-09-15 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN107158895B (en) | Carbon dioxide absorbent | |
CN101993378B (en) | Amido-containing ionic liquid used for absorbing acidic gases and preparation method and application thereof | |
CN104168979B (en) | CO is absorbed from admixture of gas 2method | |
DK2300127T3 (en) | ABSORPENT AND PROCEDURE FOR THE REMOVAL OF ACID GASES FROM LIQUID FLOWS, PARTICULARLY FROM Flue gases | |
CN107715845B (en) | Flue gas desulfurization and denitrification adsorbent and preparation and use methods thereof | |
JP2017164696A (en) | Carbonic acid gas absorbent material, carbonic acid gas recovery system and carbonic acid gas recovery method | |
WO2011121633A1 (en) | Acidic gas absorbent, acidic gas removal device, and acidic gas removal method | |
JP2013516304A (en) | Removal of CO2 from gas by aqueous amine solution with sterically hindered amine | |
CN100411709C (en) | A method for purifying flue gas by use of powdered activated coke | |
JP6615813B2 (en) | Carbon dioxide absorbent and carbon dioxide separation and recovery system | |
CN106943845A (en) | For absorbing CO from admixture of gas2Method and absorbing medium | |
JP2012143744A (en) | Acid gas absorbent, acid gas removal method, and acid gas removal device | |
WO2012162944A1 (en) | Composite decarburized solution for capturing carbon dioxide in mixed gas | |
CA2893611A1 (en) | Method of absorbing co2 from a gas mixture | |
KR20100047068A (en) | Absorbents for separation of acidic gas | |
WO2013118819A1 (en) | Aqueous solution which efficiently absorbs and recovers carbon dioxide in exhaust gas, and method for recovering carbon dioxide using same | |
CA2673711A1 (en) | Carbon dioxide and hydrogen sulfide absorbents and process for their use | |
KR20120067046A (en) | An absorbent for capturing carbon dioxide comprising amino acid having multi amine groups and metal hydroxide | |
JP2015027647A (en) | Acid gas absorbent, acid gas removal method and acid gas removal device | |
KR101210929B1 (en) | Carbon dioxide absorbent and method of removal of carbon dioxide from landfill gas by the simultaneous generation of barium carbonate using the same | |
KR101094327B1 (en) | Absorbents for separation of acidic gas | |
JP2019098284A (en) | Formic acid recovery agent, formic acid removal method, formic acid removal device, carbon dioxide separation recovery method and carbon dioxide separation recovery device | |
JP2012091130A (en) | Co2 recovery device, co2 recovery method, and co2 capturing material | |
WO2011121635A1 (en) | Acidic gas absorbent, acidic gas removal device, and acidic gas removal method | |
CN104415653A (en) | Capture solvent used for capturing low-concentration carbon dioxide |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
GR01 | Patent grant | ||
GR01 | Patent grant | ||
TR01 | Transfer of patent right |
Effective date of registration: 20210726 Address after: 730000 Room 301, No. 145, Wanli West Village, Anning District, Lanzhou City, Gansu Province Patentee after: Liu Shengming Address before: 730000 401, No. 136 Dazhong lane, Chengguan District, Lanzhou City, Gansu Province Patentee before: Si Yang Wu |
|
TR01 | Transfer of patent right |