US20130272939A1 - System and method for enhanced removal of co2 from a mixed gas stream via use of a catalyst - Google Patents
System and method for enhanced removal of co2 from a mixed gas stream via use of a catalyst Download PDFInfo
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- US20130272939A1 US20130272939A1 US13/793,896 US201313793896A US2013272939A1 US 20130272939 A1 US20130272939 A1 US 20130272939A1 US 201313793896 A US201313793896 A US 201313793896A US 2013272939 A1 US2013272939 A1 US 2013272939A1
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- 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
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/62—Carbon oxides
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- 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
- B01D53/18—Absorbing units; Liquid distributors therefor
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- 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
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/86—Catalytic processes
- B01D53/864—Removing carbon monoxide or hydrocarbons
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- 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
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/96—Regeneration, reactivation or recycling of reactants
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/20—Metals or compounds thereof
- B01D2255/204—Alkaline earth metals
- B01D2255/2047—Magnesium
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/20—Metals or compounds thereof
- B01D2255/207—Transition metals
- B01D2255/20753—Nickel
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2257/00—Components to be removed
- B01D2257/50—Carbon oxides
- B01D2257/504—Carbon dioxide
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- 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
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/77—Liquid phase processes
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- 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
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- 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
Definitions
- the proposed invention relates to a system and method for removing carbon dioxide (CO 2 ) from a process gas stream containing carbon dioxide and sulphur dioxide. More particularly, the proposed invention is directed to a solvent based flue gas processing system for removing CO 2 from a flue gas stream in which a catalyst is provided to increase the efficiency of the solvent in capturing CO2 from the flue gas stream or in regenerating the solvent.
- CO 2 carbon dioxide
- a hot process gas (or flue gas) is generated.
- a flue gas will often contain, among other things, carbon dioxide (CO 2 )
- CO 2 carbon dioxide
- One such system and process has previously been disclosed and is directed to a single-stage Chilled Ammonia based system and method for removal of carbon dioxide (CO2) from a post-combustion flue gas stream.
- Known solvent based CO2 capture systems such as ammonia based systems and processes (CAP) provide a relatively low cost means for capturing/removing CO 2 from a gas stream, such as, for example, a post combustion flue gas stream.
- CAP ammonia based systems and processes
- An example of such a system and process has previously been disclosed in pending patent application PCT/US2005/012794 (International Publication Number: WO 2006/022885/Inventor: Eli Gal)), filed on 12 Apr. 2005 and titled Ultra Cleaning of Combustion Gas Including the Removal of CO 2 .
- PCT/US2005/012794 International Publication Number: WO 2006/022885/Inventor: Eli Gal
- the absorption of CO 2 from a flue gas stream is achieved by contacting a chilled ammonia ionic ammonia solution (or slurry) with a flue gas to stream that contains CO 2 .
- FIG. 1A is a diagram generally depicting a flue gas processing system 15 for use in removing various pollutants from a flue gas stream FG emitted by the combustion chamber of a boiler system 26 used in a steam generator system of, for example, a power generation plant.
- This system includes a CO2 removal is system 70 that is configured to remove CO 2 from the flue gas stream FG before emitting the cleaned flue gas stream to an exhaust stack 90 (or alternatively additional processing). It is also configured to output CO 2 removed from the flue gas stream FG. Details of CO 2 removal system 70 are generally depicted in FIG. 1B .
- CO2 removal System 70 includes a capture system 72 for capturing/removing CO 2 from a flue gas stream FG and a regeneration system 74 for regenerating ionic ammonia solution used to remove CO 2 from the flue gas stream FG. Details of capture system 72 are generally depicted in FIG. 1C .
- a capture system 72 of a CO 2 capture system 70 ( FIG. 1A ) is generally depicted.
- the capture system 72 is a solvent based CO 2 capture system. More particularly, in this example, the solvent used is chilled ammonia.
- a chilled ammonia (CAP) based system/method for CO 2 removal an absorber vessel is provided in which an absorbent ionic ammonia solution (ionic ammonia solution) is contacted with a flue gas stream (FG) containing CO 2 .
- the ionic ammonia solution is typically aqueous and may be composed of, for example, water and ammonium ions, bicarbonate ions, carbonate ions, and/or carbamate ions.
- An example of a known CAP CO 2 removal system is generally depicted in the diagrams of FIG. 1C and FIG. 1D .
- an absorber vessel 170 is configured to receive a flue gas stream (FG) originating from, for example, the combustion chamber of a fossil fuel fired boiler 26 (see FIG. 1A ). It is also configured to receive a lean ionic ammonia solution supply from regeneration system 74 (see FIG. 1B ). The lean ionic ammonia solution is introduced into the vessel 170 via a liquid distribution system 121 while the flue gas stream FG is also received by the absorber vessel 170 via flue gas inlet 76 .
- FG flue gas stream
- regeneration system 74 see FIG. 1B
- the ionic ammonia solution is put into contact with the flue gas stream via a gas-liquid contacting device (hereinafter, mass transfer device, MTD) 111 used for contacting the flue gas stream with solvent and located in the absorber vessel 170 and within the path that the flue gas stream travels from its entrance via inlet 76 to the vessel exit 77 .
- MTD mass transfer device
- the gas-liquid contacting device 111 may be, for example, one or more commonly known structured or random packing materials, or a combination thereof.
- the ionic ammonia solution acts to absorb CO2 from the flue gas stream, thus making the ionic ammonia solution “rich” with CO2 (rich solution).
- the rich ionic ammonia solution continues to flow downward through the mass transfer device and is then collected in the bottom 78 of the absorber vessel 170 .
- the rich ionic ammonia solution is then regenerated via regenerator system 74 (see FIG. 1B ) to release the CO 2 absorbed by the ionic ammonia solution from the flue gas stream.
- the CO 2 released from the ionic ammonia solution may then be output to storage or other predetermined uses/purposes.
- System 74 includes a regenerator vessel 195 .
- Regenerator vessel 195 is configured to receive a rich solution feed from the capture system 72 and to return a lean solution feed to the capture system 72 once CO2 has been separated from the rich solution.
- the rich ionic ammonia solution is heated so that CO2 contained in the solution separates from the chilled ammonia solution. Once separated from the CO 2 , ammonia (ammonia slip) is returned to the capture system for use in capturing further CO 2 from a gas stream.
- Embodiments of the present invention provide for flue gas processing system for use with a fossil fuel fired boiler.
- a flue gas processing system that includes an absorber tower configured to receive a mixed gas stream containing carbon dioxide and to contact it with a solvent; and the absorber tower comprises packing materials that are coated with a catalyst.
- Embodiments of the present invention can also be viewed as providing methods for processing a mixed gas stream wherein the method includes the steps of: receiving a flue gas stream from the combustion chamber of a boiler; contacting the flue gas stream with a solvent and contacting the solvent with a catalyst.
- FIGS. 1A , 1 B and 1 C are diagrams generally depicting a typical flue gas processing system 15 with provisions for CO2 removal.
- FIGS. 2A , 2 B, 2 C and 2 D are diagrams generally illustrating an example of packing materials 315 on which a catalyst has been immobilized on the wall/surfaces of the packing materials.
- FIG. 3 is a diagram generally depicting relevant portions of an amine or ammonia based CO2 capture system 70 in which absorber 110 and regenerator 330 are provided with packing materials 315 and 335 , respectively that have been coated with a catalyst.
- FIG. 4A is a diagram generally depicting relevant portions of an amine or ammonia based CO2 capture system 70 in which a catalyst 425 is added to the solvent supply 195 ( FIG. 4A ) or alternatively it may be added directly into the solvent supply feed.
- the solvent is amine or ammonia.
- FIG. 4B is a diagram generally depicting relevant portions of an amine or ammonia based CO2 capture system 70 in which a catalyst 425 is added directly into the solvent supply feed.
- the proposed invention is directed to increasing CO 2 capture efficiency in a solvent based capture system for use in processing, for example, a flue gas stream.
- the proposed invention is also directed to efficiently regenerating a solvent used to capture CO 2 .
- FIG. 2A-FIG . 2 C are diagrams generally depicting packing materials 315 that have been coated with a catalyst 425 .
- FIGS. 2B and 2C shows that the packing materials 315 may be composed of, for example, a series of corrugated support structures 320 arranged in close proximity to each other so as to form a series of channels 334 through which flue gas entering the absorber vessel 110 flow.
- the catalyst 425 is coated on one or more surfaces of each corrugated support to structures 320 .
- the corrugated troughs 334 form pathways for the flue gas to pass through the packing materials 315 thereby contacting the catalyst layer 425 .
- the catalyst 425 may be either a homogeneous and/or a heterogeneous catalyst.
- Homogeneous type catalyst may include, for example, organo-metallic complex composed of transition metal and inorganic/organic ligands (such as bi-pyradine, aromatics, halogen, etc). Formation of the transition metal complex is one of the most powerful and universal ways of activating inert molecules. Coordination results in a change of reactivity of the ligands and creates favourable steric conditions for ligand interaction. This activation via coordination enables one to carry out numerous catalytic reactions under the influence of transition metal compounds.
- Other examples of catalyst that may be used include, but are not limited to, for example, organo-metallic complex catalysts, such as, for example, halogen-type complex, Ni(bpy) 3 Cl 2 ) [bpy: bipyridine].
- Heterogeneous type catalyst may include, for example, metals or their compounds such as oxides (e.g. MgO), chloride MgCl 2 , etc. (Oxide preferably will not include sulphide and chloride. They are independent of each other) that are dispersed, preferably evenly, on solid materials with a high BET surface area, such as, for example, polymer, metal oxides, SiO 2 , molecular sieves, base- and/or acid-modified clay, etc.
- metals or their compounds such as oxides (e.g. MgO), chloride MgCl 2 , etc.
- Oxide preferably will not include sulphide and chloride. They are independent of each other) that are dispersed, preferably evenly, on solid materials with a high BET surface area, such as, for example, polymer, metal oxides, SiO 2 , molecular sieves, base- and/or acid-modified clay, etc.
- the catalyst 425 is provided to promote the reaction of CO 2 with a solvent such as amine or chilled ammonia, thus resulting in the solvent being able to capture more CO 2 per given period of time (i.e. enhanced amine-based CO2 capture efficiency).
- a solvent such as amine or chilled ammonia
- a catalyst is coated/immobilized on one or more surfaces of the packing materials in the regeneration tower of an amine or ammonia based CO 2 capture system.
- the catalyst may be either a homogeneous and/or a heterogeneous catalyst.
- the catalyst is provided to promote the regeneration of solvent (ex: amine or ammonia) after it has reacted/interacted with CO 2 .
- the catalyst is selected and provided to promote the decomposition of products formed from the interaction/reaction between CO2 and amine, thus resulting in the amine being able to regenerate more efficiently from the rich amine solution per given period of time (i.e. enhanced amine-based CO2 capture efficiency).
- This embodiment is generally depicted in FIG. 3 .
- a catalyst is added to a solvent, such as, for example, amine or ammonia, that is used to capture CO 2 from a flue gas stream.
- the catalyst may also be used to promote the regeneration of solvent after it has reacted with CO2.
- a homogenous catalyst may be used. This embodiment is generally depicted in FIG. 4A and FIG. 4B .
- FIG. 4A illustrates how the catalyst 425 can be fed directly to the solvent supply tank 510 .
- FIG. 4B illustrates how the catalyst 425 can be combined with the solvent supply that is feeding the liquid distribution system 121 .
- the catalyst 425 used in both the absorber tower 110 and the regeneration tower 330 may be the same catalyst or different catalysts. It is not necessary that the same catalyst be used in connection with both capture and regeneration.
- the catalyst 425 may be dispersed/layered/coated onto the solid material 320 with a high BET surface area, such as for example, 100-1000 m 2 /g, square meter per gram solid materials, via, for example, a wet impregnation, followed by being coated/immobilized onto the packing materials 315 located in, for example, the Absorber tower 110 and/or regeneration tower/stripper 330 . This may be accomplished via, for example, known wash-coating techniques, such as those employed in, for example, industrial catalyst preparation processes. These solid materials may be used to make up the packing materials or parts thereof.
- catalysts may be directly coated onto the packing materials 315 (see FIG. 2A-FIG . 2 C) to form a catalyst film (or layer). This may be accomplished via, for example, known coating technologies such as those employed in, for example, industrial semiconductor preparation or self-assembly process or electrochemical coating processes.
- catalysts include, but are not limited to, for example, organo-metallic complex catalysts, such as, for example, halogen-type complex, Ni(bpy) 3 Cl 2 ) [bpy: bipyridine] and transition metal-based inorganic catalysts.
- Any homogeneous and/or heterogeneous catalysts can be used in CO2 capture operations to activate CO 2 adsorbed onto the surface of the catalyst 425 and catalyse carbonation/bi-carbonation and carbomation of amine with CO2 via homogeneous and/or heterogeneous processes. Also these catalysts can be used in solvent (example: amine or ammonia) regeneration to catalyse the decomposition of products formed from the carbonation/bi-carbonation and carbomation of amine with CO2.
- solvent example: amine or ammonia
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Abstract
A solvent based flue gas processing system for removing CO2 from a flue gas stream is described. A catalyst is provided to increase the efficiency of the solvent in capturing CO2 from the flue gas stream or in regenerating the solvent.
Description
- This is a continuation application of pending U.S. application Ser. No. 12/406,289 filed Mar. 18, 3009, which is a non-provisional U.S. provisional application Ser. No. 61/038,467, filed Mar. 21, 2008, each incorporated herein in its entirety by reference; and is related to co-pending non-provisional U.S. patent application having Ser. No. 12/406,360, filed on Mar. 18, 2009, which claimed priority to U.S. provisional patent application having Ser. No. 61/038,494, filed on Mar. 21, 2008.
- The proposed invention relates to a system and method for removing carbon dioxide (CO2) from a process gas stream containing carbon dioxide and sulphur dioxide. More particularly, the proposed invention is directed to a solvent based flue gas processing system for removing CO2 from a flue gas stream in which a catalyst is provided to increase the efficiency of the solvent in capturing CO2 from the flue gas stream or in regenerating the solvent.
- In the combustion of a fuel, such as coal, oil, peat, waste, etc., in a combustion plant, such as those associated with boiler systems for providing steam to a power plant, a hot process gas (or flue gas) is generated. Such a flue gas will often contain, among other things, carbon dioxide (CO2) The negative environmental effects of releasing carbon dioxide to the atmosphere have been widely recognised, and have resulted in the development of processes adapted for removing carbon dioxide from the hot process gas generated in the combustion of the above mentioned fuels. One such system and process has previously been disclosed and is directed to a single-stage Chilled Ammonia based system and method for removal of carbon dioxide (CO2) from a post-combustion flue gas stream.
- Known solvent based CO2 capture systems, such as ammonia based systems and processes (CAP) provide a relatively low cost means for capturing/removing CO2 from a gas stream, such as, for example, a post combustion flue gas stream. An example of such a system and process has previously been disclosed in pending patent application PCT/US2005/012794 (International Publication Number: WO 2006/022885/Inventor: Eli Gal)), filed on 12 Apr. 2005 and titled Ultra Cleaning of Combustion Gas Including the Removal of CO2. In this process the absorption of CO2 from a flue gas stream is achieved by contacting a chilled ammonia ionic ammonia solution (or slurry) with a flue gas to stream that contains CO2.
-
FIG. 1A is a diagram generally depicting a fluegas processing system 15 for use in removing various pollutants from a flue gas stream FG emitted by the combustion chamber of aboiler system 26 used in a steam generator system of, for example, a power generation plant. This system includes a CO2 removal issystem 70 that is configured to remove CO2 from the flue gas stream FG before emitting the cleaned flue gas stream to an exhaust stack 90 (or alternatively additional processing). It is also configured to output CO2 removed from the flue gas stream FG. Details of CO2 removal system 70 are generally depicted inFIG. 1B . - With reference to
FIG. 1B ,CO2 removal System 70 includes acapture system 72 for capturing/removing CO2 from a flue gas stream FG and aregeneration system 74 for regenerating ionic ammonia solution used to remove CO2 from the flue gas stream FG. Details ofcapture system 72 are generally depicted inFIG. 1C . - With reference to
FIG. 1C andFIG. 1D , acapture system 72 of a CO2 capture system 70 (FIG. 1A ) is generally depicted. In this system, thecapture system 72 is a solvent based CO2 capture system. More particularly, in this example, the solvent used is chilled ammonia. In a chilled ammonia (CAP) based system/method for CO2 removal, an absorber vessel is provided in which an absorbent ionic ammonia solution (ionic ammonia solution) is contacted with a flue gas stream (FG) containing CO2. The ionic ammonia solution is typically aqueous and may be composed of, for example, water and ammonium ions, bicarbonate ions, carbonate ions, and/or carbamate ions. An example of a known CAP CO2 removal system is generally depicted in the diagrams ofFIG. 1C andFIG. 1D . - With reference to
FIG. 1C , an absorber vessel 170 is configured to receive a flue gas stream (FG) originating from, for example, the combustion chamber of a fossil fuel fired boiler 26 (seeFIG. 1A ). It is also configured to receive a lean ionic ammonia solution supply from regeneration system 74 (seeFIG. 1B ). The lean ionic ammonia solution is introduced into the vessel 170 via aliquid distribution system 121 while the flue gas stream FG is also received by the absorber vessel 170 via flue gas inlet 76. - The ionic ammonia solution is put into contact with the flue gas stream via a gas-liquid contacting device (hereinafter, mass transfer device, MTD) 111 used for contacting the flue gas stream with solvent and located in the absorber vessel 170 and within the path that the flue gas stream travels from its entrance via inlet 76 to the vessel exit 77. The gas-
liquid contacting device 111 may be, for example, one or more commonly known structured or random packing materials, or a combination thereof. - Once contacted with the flue gas stream, the ionic ammonia solution acts to absorb CO2 from the flue gas stream, thus making the ionic ammonia solution “rich” with CO2 (rich solution). The rich ionic ammonia solution continues to flow downward through the mass transfer device and is then collected in the bottom 78 of the absorber vessel 170. The rich ionic ammonia solution is then regenerated via regenerator system 74 (see
FIG. 1B ) to release the CO2 absorbed by the ionic ammonia solution from the flue gas stream. The CO2 released from the ionic ammonia solution may then be output to storage or other predetermined uses/purposes. Once the CO2 is released from the ionic ammonia solution, the ionic ammonia solution is said to be “lean”. The lean ionic ammonia solution is then again ready to absorb CO2 from a flue gas stream and may be directed back to theliquid distribution system 121 whereby it is again introduced into the absorber vessel 170. Details of regeneratingsystem 74 are shown inFIG. 1E .System 74 includes aregenerator vessel 195.Regenerator vessel 195 is configured to receive a rich solution feed from thecapture system 72 and to return a lean solution feed to thecapture system 72 once CO2 has been separated from the rich solution. - During the regeneration process, the rich ionic ammonia solution is heated so that CO2 contained in the solution separates from the chilled ammonia solution. Once separated from the CO2, ammonia (ammonia slip) is returned to the capture system for use in capturing further CO2 from a gas stream.
- These currently known solvent based CO2 capture technologies typically consume approximately 20-30% of the power generated by the power generation system in order for the CO2 capture process to work effectively. In addition, these technologies often require a large portion of thermal energy generated by boiler/re-boiler functions (reboiler duty) in order to regenerate amine solution for re-use in capturing CO2 from a flue gas stream. In short, while there are known technologies for capturing CO2 from a flue gas stream, they require immense amounts of energy in order to function well. Further, in order to maximize/optimize the amount of time that flue gas is in contact with amine, the physical size of the absorber and/or re-generator tanks in a typical system must be very large. The cost to design and implement these towers of such large scale is very high. Additionally, the physical space that is required on-site to accommodate these vessels is significant. Where on-site space is limited, additional steps must be taken to implement the vessels/system in the limited space, if possible.
- 1. Embodiments of the present invention provide for flue gas processing system for use with a fossil fuel fired boiler. Briefly described, in architecture, one embodiment of the system, among others, can be implemented as a flue gas processing system that includes an absorber tower configured to receive a mixed gas stream containing carbon dioxide and to contact it with a solvent; and the absorber tower comprises packing materials that are coated with a catalyst.
- Embodiments of the present invention can also be viewed as providing methods for processing a mixed gas stream wherein the method includes the steps of: receiving a flue gas stream from the combustion chamber of a boiler; contacting the flue gas stream with a solvent and contacting the solvent with a catalyst.
- Other systems, methods, features, and advantages of the present invention will be or become apparent to one with skill in the art upon examination of the following drawings and detailed description. It is intended that all such additional systems, methods, features, and advantages be included within this description, be within the scope of the present invention, and be protected by the accompanying claims.
- The present invention may be better understood and its numerous objects and advantages will become apparent to those skilled in the art by reference to the accompanying drawings in which:
-
FIGS. 1A , 1B and 1C are diagrams generally depicting a typical fluegas processing system 15 with provisions for CO2 removal. -
FIGS. 2A , 2B, 2C and 2D are diagrams generally illustrating an example of packingmaterials 315 on which a catalyst has been immobilized on the wall/surfaces of the packing materials. -
FIG. 3 is a diagram generally depicting relevant portions of an amine or ammonia basedCO2 capture system 70 in whichabsorber 110 and regenerator 330 are provided with packingmaterials 315 and 335, respectively that have been coated with a catalyst. -
FIG. 4A is a diagram generally depicting relevant portions of an amine or ammonia basedCO2 capture system 70 in which acatalyst 425 is added to the solvent supply 195 (FIG. 4A ) or alternatively it may be added directly into the solvent supply feed. In this example, the solvent is amine or ammonia. -
FIG. 4B is a diagram generally depicting relevant portions of an amine or ammonia basedCO2 capture system 70 in which acatalyst 425 is added directly into the solvent supply feed. - The proposed invention is directed to increasing CO2 capture efficiency in a solvent based capture system for use in processing, for example, a flue gas stream. The proposed invention is also directed to efficiently regenerating a solvent used to capture CO2.
- In one embodiment of the proposed invention a
catalyst 425 that is coated (or immobilized) on one or more surfaces of the packingmaterials 315 located in theabsorber tower 110 of an amine or ammonia based CO2 capture system 70.FIG. 2A-FIG . 2C are diagrams generally depicting packingmaterials 315 that have been coated with acatalyst 425.FIGS. 2B and 2C shows that the packingmaterials 315 may be composed of, for example, a series ofcorrugated support structures 320 arranged in close proximity to each other so as to form a series ofchannels 334 through which flue gas entering theabsorber vessel 110 flow. Thecatalyst 425 is coated on one or more surfaces of each corrugated support tostructures 320. Thecorrugated troughs 334 form pathways for the flue gas to pass through the packingmaterials 315 thereby contacting thecatalyst layer 425. - The
catalyst 425 may be either a homogeneous and/or a heterogeneous catalyst. Homogeneous type catalyst may include, for example, organo-metallic complex composed of transition metal and inorganic/organic ligands (such as bi-pyradine, aromatics, halogen, etc). Formation of the transition metal complex is one of the most powerful and universal ways of activating inert molecules. Coordination results in a change of reactivity of the ligands and creates favourable steric conditions for ligand interaction. This activation via coordination enables one to carry out numerous catalytic reactions under the influence of transition metal compounds. Other examples of catalyst that may be used include, but are not limited to, for example, organo-metallic complex catalysts, such as, for example, halogen-type complex, Ni(bpy)3Cl2) [bpy: bipyridine]. - Heterogeneous type catalyst may include, for example, metals or their compounds such as oxides (e.g. MgO), chloride MgCl2, etc. (Oxide preferably will not include sulphide and chloride. They are independent of each other) that are dispersed, preferably evenly, on solid materials with a high BET surface area, such as, for example, polymer, metal oxides, SiO2, molecular sieves, base- and/or acid-modified clay, etc.
- The
catalyst 425 is provided to promote the reaction of CO2 with a solvent such as amine or chilled ammonia, thus resulting in the solvent being able to capture more CO2 per given period of time (i.e. enhanced amine-based CO2 capture efficiency). - Catalyst on Packing Materials in Regeneration Tower—In one embodiment of the proposed invention, a catalyst is coated/immobilized on one or more surfaces of the packing materials in the regeneration tower of an amine or ammonia based CO2 capture system. The catalyst may be either a homogeneous and/or a heterogeneous catalyst. The catalyst is provided to promote the regeneration of solvent (ex: amine or ammonia) after it has reacted/interacted with CO2. The catalyst is selected and provided to promote the decomposition of products formed from the interaction/reaction between CO2 and amine, thus resulting in the amine being able to regenerate more efficiently from the rich amine solution per given period of time (i.e. enhanced amine-based CO2 capture efficiency). This embodiment is generally depicted in
FIG. 3 . - In a further embodiment, a catalyst is added to a solvent, such as, for example, amine or ammonia, that is used to capture CO2 from a flue gas stream. The catalyst may also be used to promote the regeneration of solvent after it has reacted with CO2. In this embodiment, a homogenous catalyst may be used. This embodiment is generally depicted in
FIG. 4A andFIG. 4B .FIG. 4A illustrates how thecatalyst 425 can be fed directly to the solvent supply tank 510.FIG. 4B illustrates how thecatalyst 425 can be combined with the solvent supply that is feeding theliquid distribution system 121. - In a flue
gas processing system 15 wherein acatalyst 425 is coated/immobilized/layered on packingmaterials 315 in both theabsorber tower 110 and the regeneration tower 330, thecatalyst 425 used in both theabsorber tower 110 and the regeneration tower 330 may be the same catalyst or different catalysts. It is not necessary that the same catalyst be used in connection with both capture and regeneration. - The
catalyst 425 may be dispersed/layered/coated onto thesolid material 320 with a high BET surface area, such as for example, 100-1000 m2/g, square meter per gram solid materials, via, for example, a wet impregnation, followed by being coated/immobilized onto the packingmaterials 315 located in, for example, theAbsorber tower 110 and/or regeneration tower/stripper 330. This may be accomplished via, for example, known wash-coating techniques, such as those employed in, for example, industrial catalyst preparation processes. These solid materials may be used to make up the packing materials or parts thereof. - Alternately, catalysts (organo-metallic complex, transition metal as well as its salt) may be directly coated onto the packing materials 315 (see
FIG. 2A-FIG . 2C) to form a catalyst film (or layer). This may be accomplished via, for example, known coating technologies such as those employed in, for example, industrial semiconductor preparation or self-assembly process or electrochemical coating processes. Some examples of catalysts that may be used include, but are not limited to, for example, organo-metallic complex catalysts, such as, for example, halogen-type complex, Ni(bpy)3Cl2) [bpy: bipyridine] and transition metal-based inorganic catalysts. - Any homogeneous and/or heterogeneous catalysts can be used in CO2 capture operations to activate CO2 adsorbed onto the surface of the
catalyst 425 and catalyse carbonation/bi-carbonation and carbomation of amine with CO2 via homogeneous and/or heterogeneous processes. Also these catalysts can be used in solvent (example: amine or ammonia) regeneration to catalyse the decomposition of products formed from the carbonation/bi-carbonation and carbomation of amine with CO2. - While the invention has been described with reference to a number of preferred embodiments, it will be understood by those skilled in the art that various changes may be made and equivalents may be substituted for elements thereof without departing from the scope of the invention. In addition, many modifications may be made to adapt a particular situation or material to the teachings of the invention without departing from the essential scope thereof. Therefore, it is intended that the invention not be limited to the particular embodiments disclosed as the best mode contemplated for carrying out this invention, but that the invention will include all embodiments falling within the scope of the appended claims. Moreover, the use of the terms first, second, etc. do not denote any order or importance, but rather the terms first, second, etc. are used to distinguish one element from another.
Claims (20)
1. A mixed gas processing system comprising:
a regeneration vessel configured to receive a carbon rich solvent stream and a catalyst, wherein the catalyst promotes the release of carbon dioxide within the carbon rich solvent stream
2. The system of claim 1 , wherein the catalyst is a homogeneous catalyst.
3. The system of claim 1 , wherein the catalyst is a heterogeneous catalyst.
4. The system of claim 1 , wherein said mixed gas system is an amine based mixed gas processing system.
5. The system of claim 1 wherein said mixed gas system is an ammonia based mixed gas processing system.
6. The system of claim 1 , wherein the catalyst promotes decomposition of products formed from the carbonation/bi-carbonation and carbomation of amine with CO2.
7. The system of claim 1 , wherein the catalyst includes organo-metallic complex catalysts.
8. The system of claim 1 , further including a heat source to heat the carbon rich solvent stream in the regeneration vessel.
9. A process for removing carbon dioxide from a mixed gas, the process comprising:
passing a carbon rich solvent stream and a catalyst through a regeneration vessel, wherein the catalyst promotes the release of carbon dioxide within the carbon rich solvent stream.
10. The process of claim 9 , wherein the catalyst is a homogeneous catalyst.
11. The process of claim 9 , wherein the catalyst is a heterogeneous catalyst.
12. The process of claim 9 , wherein said mixed gas system is an amine based mixed gas processing system.
13. The process of claim 9 , wherein said mixed gas system is an ammonia based mixed gas processing system.
14. The process of claim 9 , wherein the catalyst promotes the decomposition of products formed from the carbonation/bi-carbonation and carbomation of amine with CO2.
15. The process of claim 9 , wherein the catalyst includes organo-metallic complex catalysts.
16. The process of claim 9 , further including heating the carbon rich solvent stream in the regeneration vessel.
17. A mixed gas processing system comprising:
regeneration vessel configured to receive a carbon dioxide rich solvent stream; and
packing material disposed in the regeneration vessel, wherein the packing material is coated/immobilized with a catalyst to promote the release of carbon dioxide within the carbon rich solvent stream.
18. The system of claim 17 , wherein the catalyst is a homogeneous catalyst.
19. The system of claim 17 , wherein the catalyst is a heterogeneous catalyst.
20. The system of claim 17 , wherein the catalyst promotes decomposition of products formed from the carbonation/bi-carbonation and carbomation of amine with CO2.
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US13/793,896 US20130272939A1 (en) | 2008-03-21 | 2013-03-11 | System and method for enhanced removal of co2 from a mixed gas stream via use of a catalyst |
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US3846708P | 2008-03-21 | 2008-03-21 | |
US12/406,289 US8414853B2 (en) | 2008-03-21 | 2009-03-18 | System and method for enhanced removal of CO2 from a mixed gas stream via use of a catalyst |
US13/793,896 US20130272939A1 (en) | 2008-03-21 | 2013-03-11 | System and method for enhanced removal of co2 from a mixed gas stream via use of a catalyst |
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US12/406,289 Continuation US8414853B2 (en) | 2008-03-21 | 2009-03-18 | System and method for enhanced removal of CO2 from a mixed gas stream via use of a catalyst |
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- 2009-03-19 BR BRPI0908957-8A patent/BRPI0908957A2/en not_active IP Right Cessation
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US11091408B2 (en) | 2019-06-12 | 2021-08-17 | Shahar Technology Solutions Ltd. | Integration of carbon dioxide absorption and water electrolysis into methanation |
US11407693B2 (en) | 2019-06-12 | 2022-08-09 | 1. Standard Carbon Ltd | Integration of carbon dioxide absorption and water electrolysis into methanation |
US11713285B2 (en) | 2021-11-17 | 2023-08-01 | Shahar Golan Technology Soultions, Ltd. | Methanation and recovery method, system, and apparatus |
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AU2009225583B2 (en) | 2013-01-31 |
IL207982A0 (en) | 2010-12-30 |
ZA201006479B (en) | 2011-12-28 |
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RU2486947C2 (en) | 2013-07-10 |
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CN101977669A (en) | 2011-02-16 |
RU2010143048A (en) | 2012-04-27 |
WO2009117546A1 (en) | 2009-09-24 |
AU2009225583A1 (en) | 2009-09-24 |
CA2718725C (en) | 2013-03-12 |
MX2010010326A (en) | 2010-11-25 |
KR101224439B1 (en) | 2013-01-22 |
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US8414853B2 (en) | 2013-04-09 |
BRPI0908957A2 (en) | 2015-07-28 |
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