The present disclosure is generally directed to a chilled ammonia process (CAP) for carbon dioxide (CO2) removal from flue gas and is more specifically directed to a CAP CO2 removal system having a membrane separator system for recovering ammonia from an ionic solution.
Energy used in the world can be derived from the combustion of carbon and hydrogen-containing fuels such as coal, oil, peat, waste and natural gas. In addition to carbon and hydrogen, these fuels contain oxygen, moisture and contaminants. The combustion of such fuels results in the production of a flue gas stream containing the contaminants in the form of ash, carbon dioxide (CO2), sulfur compounds (often in the form of sulfur oxides, referred to as “SOx”), nitrogen compounds (often in the form of nitrogen oxides, referred to as “NOx”), chlorine, mercury, and other trace elements. Awareness regarding the damaging effects of the contaminants released during combustion triggers the enforcement of ever more stringent limits on emissions from power plants, refineries and other industrial processes. There is an increased pressure on operators of such plants to achieve near zero emission of contaminants. However, removal of contaminants from the flue gas stream requires a significant amount of energy.
According to aspects disclosed herein, there is provided a carbon dioxide removal system that includes an absorber that receives flue gas, for example, from a combustion system. The absorber contains an ionic solution in an interior area of the absorber. The ionic solution can remove carbon dioxide from the flue gas. The carbon dioxide removal system includes a regenerator that is in fluid communication with the absorber. The regenerator can separate carbon dioxide from the ionic solution and can supply regenerated ionic solution to the absorber. The carbon dioxide removal system includes a carbon dioxide water wash system in fluid communication with the regenerator. The carbon dioxide water wash system receives a mixture of carbon dioxide and ammonia from the regenerator and separates the ammonia from the carbon dioxide. The carbon dioxide removal system includes an ammonia water wash system that is in fluid communication with the absorber and the carbon dioxide water wash system. The ammonia water wash system can remove ammonia from the flue gas supplied thereto. The carbon dioxide removal system also includes a membrane separator in communication with the ammonia water wash system, the regenerator and/or the carbon dioxide water wash system.
When the membrane separator is in communication with the ammonia water wash system, the membrane separator separates water and/or molecular ammonia from ionic species in the ionic solution. The ionic solution can include ionic species such as, but not limited to NH4+, NH2COO—, HCO3—, and CO32−.
In one embodiment, the membrane separator is an electrodialysis membrane system, a nano filtration system and/or a reverse osmosis system.
When the membrane separator is in communication with the carbon dioxide water wash system, the membrane separator supplies water to the carbon dioxide water wash system. The membrane separator can also supply the ionic species to the regenerator for further treatment.
In one embodiment, the carbon dioxide removal system includes an air stripper in communication with the membrane separator. The membrane separator can supply a mixture of water and molecular ammonia to the air stripper. The air stripper can also be in communication with the carbon dioxide water wash system and supply water thereto.
According to another aspect defined herein, a method for removing carbon dioxide from flue gas includes providing an absorber having an ionic solution contained therein. A regenerator is in fluid communication with the absorber and a carbon dioxide water wash system is in communication with the regenerator. An ammonia water wash system is in communication with the absorber and the carbon dioxide water wash system. A membrane separator in communication with the ammonia water wash system, the regenerator and/or the carbon dioxide water wash system, is also provided.
A flue gas containing carbon dioxide is received by the absorber and an ionic solution is supplied to the absorber. At least a portion of the carbon dioxide is removed from the flue gas and a carbon dioxide lean flue gas is generated by exposing the flue gas to the ionic solution. A portion of the ionic solution used to treat the flue gas is conveyed to the regenerator. The ionic solution is processed in the regenerator to separate a mixture of the carbon dioxide and ammonia from the ionic solution. The mixture of the carbon dioxide and the ammonia is conveyed to the carbon dioxide water wash system for removal of the carbon dioxide from the mixture. In particular, water is supplied to the carbon dioxide water wash system for separation of the carbon dioxide, during which a mixture of water and ammonia is created. The mixture of the water and the ammonia is conveyed to the ammonia water wash system. The carbon dioxide lean flue gas is also conveyed to the ammonia water wash system where the ammonia is recovered. As a result of the recovery of the ammonia, a mixture of ionic species and water is created in the ammonia water wash system. The mixture of the ionic species and the water are conveyed to the membrane separator for further processing. The membrane separator separates water and/or molecular ammonia from the ionic species in the ionic solution. The water can be conveyed to the carbon dioxide water wash system for use in separating the carbon dioxide from the mixture of carbon dioxide and ammonia.
Use of the membrane separator reduces the amount of energy required to operate the carbon dioxide removal system compared to prior art systems which use a steam consuming stripper column to separate the water and/or molecular ammonia from the ionic species in the ionic solution. For example, for coal fired power plants about a 20% reduction in energy requirements can be accomplished by using the membrane separator in lieu of the steam consuming stripper column. For natural gas fired power plants, about a 15% reduction in energy requirements can be accomplished by using the membrane separator in lieu of the steam consuming stripper column. For combined cycle power plants about a 40-50% reduction in energy requirements can be accomplished by using the membrane separator in lieu of the steam consuming stripper column.
With reference now to the figures where all like parts are numbered alike;
As illustrated in
The carbon dioxide removal system 10 includes a CO2 absorber 20, such as, but not limited to, a chilled ammonia CO2 capture system. The CO2 absorber 20 has a flue gas inlet 22 in communication with a flue gas exhaust of a combustion plant (not shown). The CO2 absorber 20 includes a first outlet 24 for discharging CO2 lean flue gas therefrom for further processing, as described below. The CO2 absorber 20 further includes an inlet 26 for receiving an ionic solution for use in capturing the CO2 from the flue gas. The ionic solution may be composed of, for example, water, ammonia (NH3) and ammonium ions, such as ammonium cations NH4+. The ammonia in the absorber 20 has a molarity of about 8 to 10 M. The CO2 absorber 20 also includes an outlet 28 for discharging a CO2 rich ionic solution therefrom. Although the ammonia in the absorber 20 is described as having a molarity of about 8 to 10 M, the present disclosure is not limited in this regard as the ammonia in the absorber 20 may have any molarity.
As illustrated in
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As illustrated in
Referring to
An anode 64 is positioned on one side of the electrodialysis membrane system 12 and a cathode 65 is positioned on an opposing side thereof. The anode 64 and cathode 65 are coupled to a suitable electricity supply (not shown) for establishing an electrical potential between the anode and the cathode. The interior area 62 is segmented into five cavities 62A-E. A first cation exchange membrane 66 separates the cavity 62A and the cavity 62B. A first anion exchange membrane 67 separates the cavity 62B and the cavity 62C. A second cation exchange membrane 68 separates the cavity 62C and the cavity 62D. A second anion exchange membrane 69 separates the cavity 62D and the cavity 62E. The second outlet 19A is in fluid communication with the cavity 62B and the third outlet 19B is in fluid communication with the cavity 62D. The first inlet 17 and the first outlet 14 are in fluid communication with the cavity 62C. While the electrodialysis membrane system 12 is shown and described as having two anion exchange membranes 67 and 69 and two cation exchange membranes 66 and 68, the present disclosure is not limited in this regard as any number of anion and cation exchange membranes may be employed.
The carbon dioxide (CO2) removal system illustrated in
Still referring to
Referring to
While the feed solution is described as including about 0.52 molar % CO2; 1.3 molar % NH3; 80.6 molar % H2O; 9.4 molar % NH4+; 4.4 molar % NH2COO−; 3.7 molar % HCO3−; and 0.6 molar % CO32−, the present disclosure is not limited in this regard as other concentrations, compounds and ionic species may be employed without departing from the broader aspects disclosed herein. Although the membrane separator 92 is described as being operable to generate a permeate flow of about 90% of an amount of fluid entering the membrane separator and a retentate flow of about 10% of the amount of fluid entering the separator and producing a retentate including NH2COO−; HCO3−; and CO32− and a permeate including NH3; H2O; and NH4+, the present disclosure is not limited in this regard as other membranes which produce other percentages of retenate and permeate and/or other compositions of permeate and/or retentate may be employed without departing from the broader aspects disclosed herein.
The presence of molecular and ionic ammonia in solutions used in ammonia based CO2 removal systems is dependent on the pH and the temperature of the solution. For example, if the pH of the solution exiting the CO2 water wash system 40 via line 47 is low, for example, having a pH of about 6 to 9 or 4 to 9, then molecular ammonia will be present at an amount of about 0 to 10% of the total ammonia content. However, if the pH of the solution is high, for example, having a pH of about 9 to 12, then molecular ammonia will be present at an amount of about 10 to 100% of the total ammonia content. The CO2 removal system 10 of
In addition, the carbon dioxide (CO2) removal systems 10 and 110 employ one or more heat exchangers (not shown) for heat recovery purposes. For example, one or more heat exchangers (not shown) may be employed between the CO2 absorber 20, 120 and the NH3 regenerator 30, 130 for heat recovery between fluids exchanged between and flowing to and from the CO2 absorber 20, 120 and the NH3 regenerator 30, 130. Such heat exchangers reduce steam duty to the NH3 regenerator 30, 130. One or more heat exchangers (not shown) may also be employed to remove heat generated in the CO2 absorber 20, 120 as a result of an exothermic reaction of CO2 absorption in the CO2 absorber 20, 120. In addition, heat exchangers (not shown) may be employed to remove heat from the CO2 water wash system 40, 140 and/or the NH3 water wash system 50, 150.
During operation of the CO2 removal system 10 illustrated in
As a result of the reaction between the flue gas and the ionic solution, a feed solution, rich in CO2 is collected at a lower portion 82 of the absorber 20. The feed solution includes about 0.57 molar % CO2; 1.3 molar % NH3; 80.6 molar % H2O; 9.4 molar % NH4+; 4.4 molar % NH2COO−; 3.7 molar % HCO3−; and 0.6 molar % CO32−. The feed solution is conveyed to the regenerator 30 via the first pump 33 and the lines 34. Heat is supplied to the regenerator via the hot leg 38 of the heat exchanger 35. The heat enables the CO2 to be separated from the feed solution. As a result, a regenerated supply of ionic solution including H2O, NH3 and NH4+ is generated in the regenerator and subsequently recirculated to the absorber 20. In addition, a mixture of CO2 and NH3 is created in the regenerator 30 and discharged from the outlet 39 of the regenerator. The mixture of CO2 and NH3 is admitted to the CO2 water wash system 40 via the first inlet 41. While the feed solution is described as including about 0.57 molar % CO2; 1.3 molar % NH3; 80.6 molar % H2O; 9.4 molar % NH4+; 4.4 molar % NH2COO−; 3.7 molar % HCO3−; and 0.6 molar % CO32−, the present disclosure is not limited in this regard as feed solutions having other chemical compositions can be employed. Although the a regenerated supply of ionic solution is described as including H2O, NH3 and NH4+ the present disclosure is not limited in this regard as ionic solutions having other compositions may also be employed without departing from the broader aspects disclosed herein.
Water is supplied to the CO2 water wash system 40 by the electrodialysis membrane system 12 via the first outlet 14, the line 16 and the second inlet 42. The water is sprayed into an interior area defined by the CO2 water wash system 40 through a liquid distribution system 83. Water is also sprayed into the interior area of the water wash system 40 through another liquid distribution system 84 via the third pump 44, the line 45 and the third inlet 46. The water spray absorbs the NH3 in the mixture of CO2 and NH3, thereby separating the CO2 from the mixture. The separated CO2 is discharged from the water wash system 40 via line 49 for storage or further processing. In addition, the third pump 44 supplies a portion of an ionic solution collected in a lower portion 85 of the CO2 water wash system 40 to a liquid distribution system 88 located in an interior area defined by the NH3 water wash system 50, via the line 47 and the inlet 51. A portion the ionic solution collected at a lower portion 87 of the NH3 water wash system is conveyed to the electrodialysis membrane system 12 via the fourth pump 53, the line 18 and the first inlet 17. The fourth pump 53 recirculates a portion of the ionic solution collected in a lower portion 85 to another liquid distribution system 89 located in the interior area defined by the NH3 water wash system 50.
The ionic solution collected in a lower portion 85 of the NH3 water wash system 50 and conveyed to the first inlet 17 and the cavity 62C of the electrodialysis membrane system 12 includes 96.6 molar % H2O; and ionic species, such as, 2.2 molar % NH4+; 0.3 molar % NH2COO−; 0.6 molar % HCO3−; and 0.3 molar % CO32−. The cation exchange membrane 68 separates the NH4+ from the ionic solution and accumulates the NH4+ in the cavity 62D. The NH4+ is discharged from the electrodialysis membrane system 12 via the third outlet 19B. The anion exchange membrane 67 separates the NH2COO−, the HCO3−, and the CO32− from the ionic solution and accumulates the NH2COO−, the HCO3−, and the CO32− in the cavity 62B. The NH2COO−, the HCO3−, and the CO32− are discharged from the electrodialysis membrane system 12 via the second outlet 19A. The NH4+ from the third outlet 19B mixes with the NH2COO−, the HCO3−, and the CO32− from the second outlet 19A in the common line 19. The mixture of the ionic species NH4+, NH2COO−, the HCO3−, and the CO32− is conveyed to the regenerator 30 via the fifth pump 60, the line 61 and the lines 34. A portion of the mixture of the ionic species NH4+, NH2COO−, the HCO3−, and the CO32− is conveyed as a makeup to the NH3 water wash system 50 via the branch line 91. As a result of the operation of the electrodialysis membrane system 12 and separation of the (NH4+) and the (NH2COO−, the HCO3−, and the CO32−) from the ionic solution, water is generated in the cavity 62C for use as a supply to the CO2 water wash system 40.
While the NH3 water wash system 50 is described as conveying 96.6 molar % H2O; and ionic species, such as, 2.2 molar % NH4+; 0.3 molar % NH2COO−; 0.6 molar % HCO3−; and 0.3 molar % CO32− to the cavity 62C of the electrodialysis membrane system 12, the present disclosure is not limited in this regard as other solutions and ionic species may also be generated in the NH3 water wash system and/or processed in the electrodialysis membrane system 12.
The CO2 removal system 110 of
Use of the electrodialysis membrane separator reduces the amount of energy required to operate the carbon dioxide removal system compared to prior art systems which use a steam consuming stripper column to separate the water and/or molecular ammonia from the ionic species in the ionic solution. For example, for coal fired power plants about a 20% reduction in energy requirements can be accomplished by using the electrodialysis membrane separator in lieu of the steam consuming stripper column For natural gas fired power plants, about a 15% reduction in energy requirements can be accomplished by using the electrodialysis membrane separator in lieu of the steam consuming stripper column For combined cycle power plants about a 40-50% reduction in energy requirements can be accomplished by using the electrodialysis membrane separator in lieu of the steam consuming stripper column. Thus the method for removing carbon dioxide from flue gas using the electrodialysis membrane separator is at least fifteen percent more efficient than carbon dioxide removal systems using steam consuming stripper columns, for natural gas fired power plants and at least twenty percent more efficient for coal fired power plants.
While the present disclosure has been described with reference to various exemplary 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 embodiment 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.
This patent application claims priority benefit under 35 U.S.C. §119(e) of copending, U.S. Provisional Patent Application Ser. No. 61/583,298, filed Jan. 5, 2012, the disclosure of which is incorporated by reference herein in its entirety.
Number | Date | Country | |
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61583298 | Jan 2012 | US |