The present invention relates to an apparatus and method for capturing CO2 from the air. More specifically, the present invention relates to an apparatus and method for capturing carbon dioxide using adsorbents and concentrating same to a high purity.
The continuous increase in the concentration of CO2 in the atmosphere is well known to contribute to the increase in global surface temperatures. This phenomenon is called global warming and causes many negative changes to the planet. To prevent these negative effects, individuals, companies, and governments have invested time and effort into reducing the amount of CO2 entering into the atmosphere, as well as removing CO2 from the atmosphere back to pre-industrialization levels. One way to both mitigate and remove CO2 emissions is through direct air capture (DAC) with utilization of the captured CO2.
DAC involves capturing and concentrating CO2 directly from the air, which reduces the amount of CO2 in the atmosphere. By removing CO2 from the atmosphere, the concentration of green-house gases (GHGs) in the atmosphere decreases. A significant reduction of CO2 from the atmosphere can effectively reverse global warming, if the CO2 is sequestered. The CO2 can be sequestered deep within the earth or can be utilized in a product that will hold the CO2 for a long duration.
Utilizing CO2 from DAC has many benefits. For instance, CO2 from DAC can mitigate the GHG impact of an individual, company, or government. As an example, CO2 is used in many industrial processes. DAC-based mitigation occurs if the industrial user transitions from a traditional fossil fuel-based source of CO2 (e.g., a by-product of the production of ammonia, hydrogen, or ethylene) to a clean CO2 source like that produced by DAC.
Utilizing DAC-produced CO2 is also beneficial because the cost of DAC can be offset by the value of the CO2 produced, making the whole process more economical. As mentioned above, CO2 is traditionally produced by a chemical conversion route. However, this is energetically intensive because CO2 is the most oxidized version of carbon. Further, traditional chemical conversion routes often result in significant impurities.
An alternative method of CO2 production is to increase the concentration of CO2 to the point that it becomes inherently more valuable. As the purity of the CO2 increases, the value of the CO2 increases. Common grades of CO2 range from medical, bone dry, beverage, and food grade CO2 (99.5% and 99.9%) to anaerobic, laser, supercritical fluid, and research grade CO2 (99.95% and 99.9999%). Capturing CO2 from the air and concentrating it to these common grades would provide a green source of high-purity CO2, which would allow individuals, companies, or governments a means to mitigate and remove CO2.
This high-purity green CO2 not only has an increased value but will allow many novel CO2 conversion technology opportunities that were not previously available due to a lack of a green source of high-purity CO2. This is particularly true with high-purity DAC CO2 because the high purity allows many novel electrochemical reactions involving CO2.
Production of high-purity CO2 using DAC has the additional benefit that, because air is everywhere on Earth, CO2 captured directly from the air can also be provided everywhere on Earth. In contrast, traditional sources require infrastructure at a fixed location. This is particularly useful for applications where CO2 production infrastructure does not currently exist, such as in developing countries, remote regions, or disaster-affected areas. Example applications include providing hospitals in such regions with access to reliable, constant CO2, as CO2 is commonly used in medical procedures. Providing high-purity CO2 using DAC has the added benefit that since the CO2 is produced on site, CO2 emissions related to transportation will be mitigated.
A challenge associated using DAC to produce high-purity CO2 is air contains a very dilute stream of CO2. Air comprises 0.04% CO2 (i.e., 400 parts CO2 in one million parts air), but high purity CO2 typically requires above 99.5%. In higher-purity embodiments, concentrations of CO2 produced by DAC are at least 99.9999% (i.e., one part non-CO2 contaminant per million parts CO2). Air consists of approximately 78.084% N2, 20.946% 02, 0.9340% Ar, 0.0407% CO2, 0.000055% H2, 0.001818% Ne, 0.00018% CH4, 0.000114% Kr along with lower concentrations of hydrocarbons and CO.
Thus, there is a need for an economical means of capturing and concentrating the CO2 to a purity of 99.5%, and preferably 99.9999%. No increase in purity to greater than 99.5% pure CO2 from air concentrations has previously been shown using a single adsorption cycle.
Current DAC methods mainly rely on absorption methods. One such method is used by Carbon Engineering, which utilizes a KOH absorption unit with a calcium carbonate cracker, as exemplified in Keith et al., A Process for Capturing CO2 from the Atmosphere, Joule (2018), https://doi.org/10.1016/j.joule.2018.05.006. Another method is that used by Climeworks, which utilizes amines that are impregnated onto fiber supports, as exemplified in U.S. Pat. No. 10,279,306. A third method is that used by Global Thermostat, which uses amines that are impregnated onto ceramic supports, as exemplified in U.S. Pat. No. 9,908,080. All three of these documents are incorporated herein by reference.
However, these absorption methods alone are not designed for the production of high purity CO2. For example, DAC technologies that include carbonate crackers, including Carbon Engineering and Heirloom, use natural gas for the heat of the process. However, such carbonate crackers create significant impurities that would be transferred to the product CO2 stream. Amine-based DAC technologies, including those of Climeworks and Global Thermostat, similarly have major impurity sources that come from the steam used in the process and the oxidative degradation of the amines. These impurities within the product gas stream from absorption-type DAC technologies require additional separation steps, which are costly.
Thus, there is a need for an impurity-free and economical method for capturing carbon dioxide and producing a high-purity carbon dioxide product.
This document discloses an apparatus and method for carbon dioxide capture and concentration from air for the production of high-purity carbon dioxide. The apparatus comprises a chamber having a CO2 adsorbent bed attached to a vacuum source, an input air source, a dryer, and a heater. The apparatus allows for control of the chamber's contents, pressure, and temperature. Adsorbents comprise a zeolite, metal organic framework, covalent organic framework, silica, or alumina. The method provides for: flowing air that has been dried through an adsorbent to capture the CO2; applying a strong vacuum source, or heat and a strong vacuum source to a capture chamber to remove non-CO2 components as an exhaust stream; and heating and applying a vacuum source to the adsorbent to extract high purity CO2.
In a first aspect, this document discloses an apparatus for capturing carbon dioxide, said apparatus comprising: a dryer; a capture chamber, said capture chamber being in fluid communication with said dryer; a CO2 adsorbent bed, said CO2 adsorbent bed being positioned within said capture chamber; a vacuum source, said vacuum source being in fluid communication with said CO2 adsorbent bed; and a heater, said heater being thermally coupled to said CO2 adsorbent bed such that when said heater is in operation, said heater supplies thermal energy to said CO2 adsorbent bed, wherein said dryer removes water from an input air stream to thereby produce a pre-capture stream; wherein said capture chamber receives said pre-capture stream from said dryer; wherein said vacuum source causes a pressure in said capture chamber to be below a pressure of said input air stream; wherein at least one of: said pressure and a temperature of said capture chamber is controlled by at least one of: said vacuum source and said heater; wherein said CO2 adsorbent bed absorbs said carbon dioxide from said pre-capture stream within said capture chamber to thereby produce a purified carbon-dioxide stream, and wherein an exhaust stream is produced from said capture chamber, said exhaust stream having a carbon dioxide concentration lower than that of said input air stream.
The present invention may be implemented such that said CO2 adsorbent bed comprises at least one of: a zeolite adsorbent, a metal-organic framework adsorbent, a covalent-organic framework adsorbent, a silica adsorbent, or an alumina adsorbent.
The present invention may be implemented such that said dryer is coupled to said vacuum source and wherein said vacuum source regenerates said dryer.
The present invention may be implemented such that at least part of said exhaust stream passes through a second dryer.
The present invention may be implemented such that said apparatus is coupled to a beverage device, wherein said beverage device is configured to use said purified carbon-dioxide stream to perform at least one of: carbonating a beverage or dispensing a drink.
In a second aspect, this document discloses a method for capturing carbon dioxide, comprising: flowing an input air stream through a dryer to thereby produce a pre-capture stream, wherein said dryer removes water from said input air stream; flowing said pre-capture stream into a capture chamber in fluid communication with said dryer, wherein a CO2 adsorbent bed is positioned within said capture chamber; using a vacuum source to thereby decrease a pressure of said capture chamber to a blowdown pressure, thereby removing non-CO2 components from said capture chamber as an exhaust stream; and heating said CO2 adsorbent bed and using said vacuum source on said CO2 adsorbent bed to thereby extract said carbon dioxide from said capture chamber to thereby produce a purified carbon-dioxide stream.
The present invention may be implemented such that step (c) further comprises adding heat energy to said CO2 adsorbent bed by way of a heater.
The present invention may be implemented such that said heat energy increases a temperature of said CO2 adsorbent bed to between about a temperature of said input air stream and about 80° C.
The present invention may be implemented as further comprising a step of: (e) passing a dry gas stream through said capture chamber, wherein said dry gas is passed through said CO2 adsorbent bed to thereby cool said CO2 adsorbent bed and to thereby form a heated gas stream, and wherein said heated gas stream is flowed through said dryer to thereby regenerate said dryer.
The present invention may be implemented such that said CO2 adsorbent bed comprises at least one of: a zeolite adsorbent, a metal-organic framework adsorbent, a covalent-organic framework adsorbent, a silica adsorbent, or an alumina adsorbent.
The present invention may be implemented such that said pressure of said capture chamber during step (c) is between 0-0.1 atm.
The present invention may be implemented such that said CO2 adsorbent bed is heated to a temperature of about 80° C. to about 275° C. during step (c).
The present invention may be implemented such that said method is continuously repeated to extract said carbon dioxide from a continual source of air.
The present invention may be implemented such that said vacuum source is used on said dryer to thereby regenerate said dryer.
The present invention may be implemented as comprising a further step: (e) passing at least part of said exhaust stream through a secondary capture chamber having a secondary CO2 adsorbent bed, wherein said secondary CO2 adsorbent bed cools down using said exhaust stream creating a heated exhaust stream.
The present invention may be implemented such that said exhaust stream passes through a separate dryer after being removed from said capture chamber.
The present invention may be implemented as further comprising a step of: (e) executing at least one of: carbonating a beverage or dispensing a drink.
In a third aspect, this document discloses an apparatus for capturing carbon dioxide from air, said apparatus comprising: a first valve controlling a first opening of a major water capture bed enclosure, said first valve being configured to allow an input air stream to introduce said air into said major water capture bed enclosure when said first valve is at least partially open; a major water capture bed positioned within said major water capture bed enclosure; a second valve controlling a boundary between a second opening of said major water capture bed enclosure and a first opening of a capture chamber, wherein said major water capture bed enclosure and said capture chamber are in fluid communication when said second valve is at least partially open; a CO2 adsorbent bed positioned within said capture chamber; a vacuum source in fluid communication with said capture chamber, wherein said vacuum source is used to create a pressure below atmospheric pressure in said capture chamber; a heater, said heater being thermally coupled to said CO2 adsorbent bed such that said heater provides heat to said adsorbent bed when said heater is active; a third valve controlling a boundary between a second opening of said capture chamber and a first opening of a minor water capture bed enclosure, wherein said capture chamber and said minor water capture bed enclosure are in fluid communication when said third valve is at least partially open, and wherein said capture chamber is vacuum tight when said second valve and said third valve are closed; a minor water capture bed positioned within said minor water capture bed enclosure; and a fan in fluid communication with a second opening of said minor water capture bed enclosure; wherein said apparatus performs a temperature vacuum swing adsorption cycle to thereby remove said carbon dioxide from said CO2 adsorbent bed, and wherein CO2-depleted air is removed by said fan.
The present invention may be implemented such that said CO2-depleted air is at least partially recycled into said input air stream.
The present invention may be implemented such that said vacuum source regenerates at least one of said major water capture bed and said minor water capture bed.
These and other features of the invention will become more apparent from the following description in which reference is made to the appended drawings.
The present invention will now be described by reference to the following figures, in which identical reference numerals refer to identical elements and in which:
In a preferred embodiment, the TVSA cycle generally comprises the following steps:
After the pressurization step 8, the cycle can be repeated. By repeating the TVSA cycle, further capture and concentration of CO2 can be achieved from the initial input air.
The dry input air flows over the adsorbent which is located in the CO2 adsorbent bed 10. The CO2 is captured via adsorption onto the adsorbent's surface. The air flowing over the adsorbent would be at near ambient conditions of temperature and pressure of the input air. In a preferred embodiment, the input air has a temperature between about-80° C. and about 50° C.
In a preferred embodiment, the adsorption step 2 can operate at near-atmospheric pressures, which can be between 30 and 120 kPa, and at CO2 concentrations between 10 and 10 000 ppm. Air exiting from the CO2 adsorbent bed 10 would contain significantly less CO2 than the input air up until the CO2 adsorbent bed 10 saturates. This occurs when the adsorbent reaches its adsorption capacity at equilibrium conditions with the input air temperature and partial pressure of CO2 within the air near the exit of the CO2 adsorbent bed 10. The adsorption step 2 proceeds until the adsorbent bed 10 reaches its target adsorption capacity. In a preferred embodiment, target adsorption capacity is measured from a feedback loop measuring the exiting CO2 concentration from the CO2 adsorbent bed 10. In another preferred embodiment, the target adsorption capacity is preconfigured via predictive modelling based upon based the adsorbent's characteristics, and the input air's flow rate and conditions. In a preferred embodiment, the dry CO2 reduced air that exits the CO2 adsorbent bed 10 during the adsorption step 2 could be stored and/or redirected into the pressurization step 8 to repressurize the CO2 adsorbent bed 10 of the same or a separate TVSA cycle. In another preferred embodiment, the dry CO2 reduced air that exits the CO2 adsorbent bed 10 during the adsorption step 2 can be stored or redirected into the CO2 adsorbent bed 10 after the pressurization step 8 and then to the dryer of the same or a separate TVSA cycle.
In a preferred embodiment, the CO2 adsorbent bed 10 is designed to have a low pressure drop across the bed (in the direction of air flow), and in a preferred embodiment the pressure drop across the CO2 adsorbent bed 10 would be below 5000 Pa. In a more preferred embodiment, the pressure drop would be below 500 Pa. In a more preferred embodiment, the pressure drop would be below 200 Pa. These low-pressure drops can be achieved by using monolithic adsorbent structures, structured adsorbent packing, or packed beds filled with large pellets with the packed bed having a low length over diameter ratios. To overcome the pressure drop of the CO2 adsorbent bed 10, forced air flow is required. The air flow may by forced by, e.g., a fan 12, blower, pump, or prevailing wind.
In a preferred embodiment, the ratio of the length of the CO2 adsorbent bed 10 over the diameter of the CO2 adsorbent bed 10 is less than 10 for adsorbent pellets between 0.1 mm and 100 mm in diameter. In a more preferred embodiment, the diameter of the adsorbent pellets is 1 mm to 25 mm, with length over diameter ratios less than 2.
The CO2 adsorbent bed 10 is fully contained within a capture chamber 11, such as a tank or container, and the remaining steps of the method are carried out by altering the pressure, temperature, or air sources within the capture chamber 11. Further, it should be understood that the dimensions of the capture chamber 11 can be selected to best account for the available space and desired output of CO2 from the system.
In further embodiments, the capture chamber 11 is comprised of a series of tanks or containers linked together. In a further alternative embodiment, the capture chamber 11 comprising the CO2 adsorbent bed 10 is configured as a cylindrical or square, column or tube (or series of columns or tubes), which optimizes the interaction between the input air and the CO2 adsorbent material. In a further embodiment, the CO2 adsorbent bed 10 can be isolated via rotation of a rotating/moving conduit gate valve. In another embodiment, the CO2 adsorbent bed 10 can be rotated/moved to be isolated. In a further embodiment of the invention, the CO2 adsorbent bed 10 is designed to minimize the amount of void space when vacuum-tight, to minimize the energy required for vacuum and maximize the purity of the product.
After isolating the CO2 adsorbent bed 10 from the input air, a vacuum source such as a vacuum pump 16 is connected to the CO2 adsorbent bed 10. In a preferred embodiment the vacuum pump 16 can comprise a diffusion pump, rotary, reciprocating, or centrifugal vacuum pump. In a preferred embodiment, the vacuum pump 16 is connected to the CO2 adsorbent bed 10 by a gate, valve, or baffle. The vacuum pump 16 reduces the pressure within the CO2 adsorbent bed 10 to a blowdown pressure that is below ambient pressure. The degree to which the blowdown pressure is reduced during this step affects the purity of the final CO2 product stream. A lower blowdown pressure during the blowdown step 4 results in a higher final purity of the CO2 product stream. In a preferred embodiment, the blowdown pressure 3 is between about 0.00000001 atm and about 0.1 atm pressure.
By reducing the pressure within the CO2 adsorbent bed 10, the weakly adsorbed components of the input air (predominantly composed of N2, O2, and Ar) are removed from the CO2 adsorbent bed 10 while keeping the majority of the CO2 on the adsorbent. This exhaust stream is predominantly composed of N2, O2, and Ar can then be vented out of the process. In a preferred embodiment, the exhaust stream can be stored in a buffer tank for later use.
The heater 14 can apply heat to the CO2 adsorbent bed 10 via any acceptable electrical, chemical, conductive, radiative, or heat exchange process. Similarly, any other suitable device or method for heating the CO2 adsorbent bed 10 may be used. The heater 14 may heat the inner area of the CO2 adsorbent bed 10 via an immersion heater or heat exchanger, or alternatively heat the exterior or other portion of the capture chamber 11, and thereby conduct, convey, or radiate heat to the CO2 adsorbent bed 10 to indirectly heat the CO2 adsorbent material. In a preferred embodiment, the heater 14 utilizes heat from an alternative source, such as utilizing “waste” heat from a separate source to facilitated CO2 capture. In a preferred embodiment, the CO2 adsorbent bed 10 is heated using pressurized CO2 flowing between the heater 14 and CO2 adsorbent bed 10. In a particularly preferred embodiment, this heated CO2 is obtained from previous operation of the TVSA cycle.
In a preferred embodiment, a vacuum source is also used to remove the CO2 from the CO2 adsorbent bed 10. Once the bed is sufficiently heated, a vacuum pump 16 would be turned on to reduce the pressure within the CO2 adsorbent bed 10. In a preferred embodiment, the heating of the CO2 adsorbent bed 10 and the reduction of pressure can occur simultaneously. In a further preferred embodiment, the pressure of the CO2 adsorbent bed 10 is reduced to between 0 to 0.1 atm, to extract as much of the CO2 from the CO2 adsorbent bed 10 as possible. As the evacuation step 6 is occurring, a purified stream of CO2 exits the vacuum pump 16 and can be collected for further use. In a preferred embodiment, a high-purity CO2 product stream can be obtained having a CO2 concentration above 99%, or more preferably above 99.9999%.
In one embodiment, during the adsorption step 2 of the process, the air enters the process and its temperature, humidity, CO2 concentration, and flow rate are measured prior to entering the major water capture bed 32a. The air then has its humidity removed from the major water capture bed 32a which produces a dry air stream. The dry air stream's temperature and humidity is then measured. The dry air then enters the CO2 adsorbent bed 10 where the CO2 is adsorbed onto the structured CO2 adsorbent, thus producing a dry CO2-reduced air stream. The dry CO2-reduced air stream then has its CO2 concentration, temperature and humidity measured. The dry CO2 reduced air stream then flows over the minor water capture bed 32b, allowing the minor water capture bed 32b to be regenerated and release water to produce a somewhat dry CO2 reduced air stream. The somewhat dry CO2 reduced air stream then has its temperature and humidity measured, and then exits out the fan 12. The fan 12 produces a forced convection through the apparatus.
In one embodiment, the use of the temperature sensors 28a, 28b, 28c, 28d, humidity sensors 26a, 26b, 26c, 26d, CO2 concentration sensors 24a, 24c, and flow sensor 22a, allows for the calculation of the predictive performance of the major water capture bed 32a, the CO2 adsorbent bed 10, and the minor water capture bed 32b during the adsorption step, as well as a feed-back loop to maximize the performance of the apparatus.
In one embodiment, during the blowdown step 4 of the method, the gate valve closes. This creates a vacuum tight seal, isolating the CO2 adsorbent bed 10 from the major water capture bed 32a, and the minor water capture bed 32b. This then allows for the vacuum pump 16 to reduce the pressure within the CO2 adsorbent bed 10, removing the non-CO2 components from the bed. The non-CO2 components form an exhaust stream that exit the process. The pressure within the CO2 adsorbent bed 10 is measured using the pressure sensor 30 connected to the capture chamber 11. If heat and vacuum are used to remove the non-CO2 components, a heater, which is not depicted in
In one embodiment, after the pressurization step 8, the waterbed regeneration step begins by opening all the gate valves 20a, 20b. Next, by flowing air from the fan 12 through the minor water capture bed 32b to create a dry air steam, and then flowing the dry air stream through the CO2 adsorbent bed 10 to cool the CO2 adsorbent bed 10, and to create a dry warm air stream. The dry warm air stream would then flow through the major water capture bed 32a, aiding in the regeneration of the major water capture bed 32a. After the major water capture bed 32a has been regenerated, the cycle can be repeated with the adsorption step 2.
In one embodiment, the major water capture bed 32a is significantly larger than the minor water capture bed 32b. The sizing of the major water capture bed 32a is determined based on the amount of water that needs to be removed during the adsorption step 2 of the process and the adsorbent(s) that comprise the major water capture bed 32a. The sizing of the minor water capture bed 32b is determined by the amount of water that needs to be removed during the pressurization step 8 and the waterbed regeneration step and the adsorbent(s) that comprise the minor water capture bed 32b.
In one embodiment, a vacuum is used during the blowdown step 4 on the major water capture bed 32a to aid in regeneration. The vacuum can be created from the same or separate vacuum pump as that of the vacuum pump 16 that is acting on the CO2 adsorbent bed 10.
In one embodiment, heat is applied to the major water capture bed 32a to aid in the regeneration of the bed. In another embodiment, heat is applied to the minor water capture bed 32b to aid in the regeneration of the bed. In another embodiment, a heat pump would connect the major water capture bed 32a to the minor water capture bed 32b, allowing for energy to be transferred from the water capture bed that is desiccating to the water capture bed that is regenerating.
A wide variety of adsorbents, including those previously deemed unsuitable for use in the capture and concentration of CO2, may be suitable for use in accordance with this invention. Preferably, the adsorbent chosen for the CO2 adsorbent bed 10 has at least an adsorption capacity for CO2 greater than 0.1 mmolCO2/g of adsorbent, and more preferably greater than 5.0 mmolCO2/g of adsorbent, at conditions of 20° C. and partial pressures of 0.0004 atm of CO2.
In another preferred embodiment the preferred CO2 adsorbent has a surface area greater than 100 m2/g. In a further preferred embodiment, the CO2 adsorbent has a pore structure that allows CO2 to diffuse through its structure.
In another preferred embodiment the adsorbent has an average heat of adsorption of CO2 that is between about 25 KJ/mol and about 100 KJ/mol.
The heat of adsorption is important with regards to the energy required to desorb the CO2 with larger heats of adsorption requiring more energy for desorption of the CO2. The profile of the heat of adsorption with respects to loading, which can be seen in a Clausius-Clapeyron relationship, is also important. This relationship shows that the initial CO2 that is adsorbed releases more energy than subsequent CO2 adsorbed. Thus, the initial CO2 adsorbed would require more energy to desorb than subsequently adsorbed CO2 molecules. In a particularly preferred embodiment, the heat of adsorption of CO2 on the adsorbent would be as low as possible and constant over a range of loadings.
One beneficial aspect of the invention is that adsorbents that are commonly considered to be water unstable, or otherwise preferentially adsorb water over CO2, can be used to capture and concentrate CO2 due to the water removal prior to the separation of CO2. This allows many adsorbents, such as aluminas, zeolites, covalent organic frameworks (COF), and MOFs, to be used for DAC, contrary to previously accepted practices.
In a preferred embodiment, the CO2 adsorbent bed 10 is made up of zeolites having oxygen tetrahedral frameworks incorporating Si, Al, P, Ge, B, Mg, Zn, Ga, Co, or Be, (including the presence of two or more differing structures, or mixtures of different structures). In an alternatively preferred embodiment, the CO2 adsorbent bed 10 is made up of mixtures of CO2 adsorbent materials having non framework species, or mixtures of framework and non-framework species.
In a further preferred embodiment, the zeolite frameworks include, but are not limited to, Linde Type A, faujasite, or chabazite, which all have large CO2 adsorption capacities at low CO2 partial pressures, but which adsorb water competitively over CO2. Faujasite structured zeolites, and in particular faujasite structured zeolites with a Si/Al ratio of below 2, are particularly preferable adsorbents for this separation.
Preferred zeolites can have a variety of counterbalancing cations in the metals group within them, such as alkali or alkaline earth metals, which change the strength of interaction with CO2 and therefore the heat of adsorption of CO2. In a preferred embodiment, MOF's including, but not limited to, NbOFFIVE-1-Ni, SGU-29, Mg-MOF-74, SIFSIX-3-Cu, SIFSIX-2-Cu, Mg-dobpdc-mmen are also preferred adsorbents for this separation.
In a preferred embodiment, the CO2 adsorbent bed 10 can be composed of one or more types of adsorbents. In a further preferred embodiment, the adsorbents can be arranged according to the flow of input air to first expose the air to an adsorbent with a weaker CO2 interaction, then to an adsorbent with a stronger CO2 interaction. In a further preferred embodiment, the same adsorbent in two configurations can be layered according to the direction of the flow. These two configurations can be a pellet/structure/packing with a higher pellet/structure/packing diffusion resistance, and a lower pellet/structure/packing diffusion resistance. These would be oriented with regard to the flow of air so as to first contact the adsorbent with the higher pellet/structure/packing diffusion resistance, and then contact the adsorbent with the lower pellet/structure/packing diffusion resistance.
In a preferred embodiment, this apparatus and method can be combined with a process that produces a dry (or partially dry) air stream that still has some CO2 within it. This would allow for this method to use less energy by requiring less water to be removed from the air prior to separating the CO2 from the air. This method can be placed after the dryer without affecting the desired properties of the dried air for most applications.
A benefit of the invention is that this method produces safer high purity CO2. With traditional sources of CO2, the production of CO2 is a by-product of the production of ammonia, hydrogen, or ethylene. These sources generate CO2 with a significantly higher concentration of dangerous pollutants (e.g., residual hydrocarbons). This allows high-purity CO2 from air to be inherently safer than that from more traditional sources.
In a further embodiment shown in
In the embodiment of
A further benefit of the present invention is that the method according to one embodiment of the invention takes advantage of the equilibrium adsorption capacities of the adsorbent. Specifically, the method takes advantage of the stronger affinity of CO2 for the surface of the adsorbent compared to the other major components in air during the blowdown step 4. This affinity is illustrated in
This major difference in interaction is due to the stronger van der Waals forces between the CO2 and Na-X, compared to that of N2, O2, and Ar. This relationship holds true for most physisorbent type adsorbents, due to the polarizability and quadrupole moment of CO2 being greater than N2, O2, and Ar, each having a polarizability of 2.65, 1.76, 1.60, and 1.64 Å3, respectively, and a quadrupole moment of 4.3, 1.52, 0.39, and 0 Å2, respectively). With CO2's higher polarizability and quadrupole moment, an adsorbent's surface with more significant interaction with CO2 over N2, O2, and Ar will be able to be purify CO2. The more significant the interaction between CO2 over N2, O2, and Ar, the greater potential to purify higher purities of CO2.
To demonstrate this benefit of this process, the temperature dependant Toth (TD-Toth) model can be used which is shown in
Further, to obtain a high-purity CO2 product, the method includes the ability to remove the N2, O2, and Ar adsorbed onto the adsorbent. To achieve this, two preferred embodiments of this invention can be taken and is shown in
Further, a vacuum and heat can be applied to the CO2 adsorbent bed 10 which was outlined in the blowdown step 4 of FIG. 4Error! Reference source not found. By applying heat, the equilibrium is shifted to warmer temperatures, which is denoted by increasing blowdown temperature in
Additionally, the apparatus can be directly or indirectly coupled to a device that uses the captured and concentrated CO2 produced by the apparatus. For example, such a device may comprise a beverage carbonating device, a drink dispenser, a medical device, or industrial equipment.
It should be understood that the beverage carbonating device can vary. For example, a home countertop water-carbonating device may be used. In another embodiment, a fast food-style soda fountain may be used. Additionally, or alternatively, carbon dioxide can be used to generate pressure to dispense a drink (e.g., using a beer keg).
The embodiment exemplified by
Na-X, a low Si/Al ratio faujasite structured zeolite with Na+ as a cation, was used as the adsorbent in the CO2 adsorbent bed 10 for the TVSA cycle. The adsorption step 2 was kept constant throughout the experiments at 20° C. with 2500 sccm of dry air flowing through the CO2 adsorption bed 10 until the Na-X reached saturation. The evacuation step 6 was kept constant at 200° C. for a duration of 120 min while applying a vacuum to the system. The pressurization step 8 was kept constant by pressurizing the CO2 adsorbent bed 10 rapidly over the course to approximately 10 seconds till the pressure reached 1 atm with dry air.
The blowdown step 4 was varied between the experiments, with four blowdown durations of 7.5 min, 15 min, 30 min, and 60 min tested at a blowdown temperature of 20° C. By varying the blowdown duration, different blowdown vacuum pressures can be tested, with longer durations equating to lower pressures. The exiting flowrate from the blowdown step 4 and the evacuation step 6 are shown for these experiments in
The blowdown step 4 was also varied between the experiments, with four blowdown temperatures of 20° C., 40° C., 60° C., and 80° C. and a blowdown duration of 30 min. The exiting flowrate from the blowdown step 4 and the evacuation step 6 are shown for these experiments in
All references and publication referred to herein are hereby incorporated by reference in their entirety.
The expression “at least one of X and Y”, as used herein, means and should be construed as meaning “X, or Y, or both X and Y”.
The expressions “about” and “approximately”, as used herein when referring to a numerical value, mean and should be construed as meaning a range formed by that value, plus or minus 10%. For example, “about 100° C.” should be construed as “100° C.±10° C.”, that is, “90° C. to 110° C.”.
A person understanding this invention may now conceive of alternative structures and embodiments or variations of the above, all of which are intended to fall within the scope of the invention as defined in the claims that follow.
The present application is a Continuation-in-Part of PCT App. No. PCT/CA2023/050241, entitled “HIGH PURITY CO2 FROM AIR USING ADSORBENTS” and filed Feb. 27, 2023, which claims priority to U.S. Provisional Pat. App. No. 63/314,443, entitled “HIGH PURITY CO2 FROM AIR USING ADSORBENTS” and filed Feb. 27, 2022, the disclosures of which are hereby incorporated by reference in their entirety.
Number | Date | Country | |
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63314443 | Feb 2022 | US |
Number | Date | Country | |
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Parent | PCT/CA2023/050241 | Feb 2023 | WO |
Child | 18815166 | US |