WO2009105255A2 - Separation of carbon dioxide from nitrogen utilizing zeolitic imidazolate framework materials - Google Patents
Separation of carbon dioxide from nitrogen utilizing zeolitic imidazolate framework materials Download PDFInfo
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- WO2009105255A2 WO2009105255A2 PCT/US2009/001100 US2009001100W WO2009105255A2 WO 2009105255 A2 WO2009105255 A2 WO 2009105255A2 US 2009001100 W US2009001100 W US 2009001100W WO 2009105255 A2 WO2009105255 A2 WO 2009105255A2
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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
- B01D53/02—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 adsorption, e.g. preparative gas chromatography
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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
- B01D53/22—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 diffusion
- B01D53/228—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 diffusion characterised by specific membranes
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D67/00—Processes specially adapted for manufacturing semi-permeable membranes for separation processes or apparatus
- B01D67/0039—Inorganic membrane manufacture
- B01D67/0051—Inorganic membrane manufacture by controlled crystallisation, e,.g. hydrothermal growth
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D69/00—Semi-permeable membranes for separation processes or apparatus characterised by their form, structure or properties; Manufacturing processes specially adapted therefor
- B01D69/14—Dynamic membranes
- B01D69/141—Heterogeneous membranes, e.g. containing dispersed material; Mixed matrix membranes
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D71/00—Semi-permeable membranes for separation processes or apparatus characterised by the material; Manufacturing processes specially adapted therefor
- B01D71/02—Inorganic material
- B01D71/028—Molecular sieves
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/22—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
- B01J20/223—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material containing metals, e.g. organo-metallic compounds, coordination complexes
- B01J20/226—Coordination polymers, e.g. metal-organic frameworks [MOF], zeolitic imidazolate frameworks [ZIF]
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2253/00—Adsorbents used in seperation treatment of gases and vapours
- B01D2253/20—Organic adsorbents
- B01D2253/204—Metal organic frameworks (MOF's)
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2256/00—Main component in the product gas stream after treatment
- B01D2256/10—Nitrogen
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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
- B01D2325/00—Details relating to properties of membranes
- B01D2325/12—Adsorbents being present on the surface of the membranes or in the pores
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2325/00—Details relating to properties of membranes
- B01D2325/20—Specific permeability or cut-off range
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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 present invention relates to the selective separation of carbon dioxide (“CO 2 ”) from nitrogen (“N 2 ”) in streams containing both carbon dioxide and nitrogen utilizing a zeolitic imidazolate framework (“ZIF") material.
- CO 2 carbon dioxide
- N 2 nitrogen
- ZIF zeolitic imidazolate framework
- the stream to be separated is fed to the present process in a substantially gaseous phase.
- the current invention is utilized in a process to separate carbon dioxide from combustion gas (e.g., flue gas) streams preferably for sequestration of at least a portion of the carbon dioxide produced in combustion processes.
- Gas separation is an important process utilized in various industries, particularly in the production of fuels, chemicals, petrochemicals and specialty products.
- a gas separation can be accomplished by a variety of methods that, assisted by heat, solids, or other means, generally exploits the differences in physical and/or chemical properties of the components to be separated.
- gas separation can be achieved by partial liquefaction or by utilizing a solid adsorbent material that preferentially retains or adsorbs a more readily adsorbed component relative to a less readily adsorbed component of the gas mixture, or by several other gas separation techniques known in the industry.
- One such commercially practiced gas separation process is pressure swing adsorption ("PSA").
- PSA processes when operated under certain conditions, allow a selective component or components in a gas mixture to be preferentially adsorbed within the pore structure of porous adsorbent materials relative to a second component or components in the gas mixture.
- adsorbed of each component in the material i.e., the adsorption capacity
- selectivity of the adsorption for a specific component over another component may often be improved by operating the process under specific pressure and temperature conditions since both pressure and temperature influence the adsorption loading of the components to a different extent.
- the efficiency of the PSA process may be further improved by the implementation of processing steps, such as the use of purge stream(s) that have optimally chosen composition, pressures and temperatures.
- relatively few adsorbent materials have separation selectivities, adsorption capacities and other beneficial properties (such as chemical and physical inertness and durability) so as to be able to function as commercially viable and cost-efficient adsorbents in a PSA process.
- Some adsorbent materials are able to adsorb a greater amount of one component than another component under certain conditions. Certain components may not be selectively adsorbed or may not be adsorbed to an acceptable level that would lead to an economically viable process.
- PSA processes can be used to effectively separate certain component gases from a mixture. For example, if a gas mixture such as air is passed at some pressure and temperature through a vessel containing an adsorbent material that selectively adsorbs more oxygen than nitrogen, at least a portion of the oxygen contained in the feedstream will stay in the adsorbent and the gas coming out of the vessel will be enriched in nitrogen.
- the bed When the bed reaches a selected fraction of its total capacity to adsorb oxygen, it can be regenerated by various pressure swing techniques, thereby releasing the adsorbed oxygen (and any other associated gas components), which can then be captured and isolated as a separate product stream.
- the adsorbent material which has now been "desorbed” of the oxygen can then be reused and the various steps of the PSA process cycle are repeated so as to allow a continuous operation.
- TSA temperature swing adsorption
- a stream containing components to be separated flows through an adsorbent material wherein one or more of the components are selectively adsorbed over another component or components.
- An effluent stream, reduced in concentration of the selectively adsorbed component(s) is obtained during this adsorption "stage" or "step" of the TSA process.
- TSA processes can be used to separate components in a mixture when used with an adsorbent that selectively adsorbs one or more of the stream components in the feed mixture relative to one or more different stream components comprising the feed mixture.
- PSA and TSA processes do not need to be mutually exclusive.
- a combined PSA/TSA process may be utilized, for example, by increasing the temperature of the adsorbent materials during the lower pressure purge step of a conventional PSA process to improve the desorption of the selectively adsorbed component(s) in the process.
- the bed temperature can then be reduced (or allowed to be reduced) during the adsorption portion of the PSA cycle to improve the adsorption characteristics and/or adsorption capacity of the material.
- the adsorbent can be regenerated with a purge that is flowed through the adsorbent bed in a manner that displaces adsorbed molecules from the adsorbent.
- Processes that are conducted with this type of adsorbent regeneration technique are often called partial pressure purge displacement processes ("PPSA").
- PPSA partial pressure purge displacement processes
- Processes such as PSA, TSA, purge displacement, and combination thereof are referred to as swing adsorption processes.
- swing adsorption processes can be conducted with rapid cycles (i.e., cycles of short duration) in which case they are referred to as rapid cycle thermal swing adsorption (RCTSA), rapid cycle pressure swing adsorption (RCPSA), and rapid cycle partial pressure swing or displacement purge adsorption (RCPPSA) technologies.
- rapid cycle thermal swing adsorption RCTSA
- rapid cycle pressure swing adsorption RCPSA
- rapid cycle partial pressure swing or displacement purge adsorption RCPPSA
- membrane separation processes can be used for the separation of gas components in a mixture.
- one or more components of the mixed stream contact one side of a membrane material and a portion of the mixed stream permeates through the membrane and is retrieved from the other side of the membrane material as a "permeate" stream.
- the permeate stream has a higher concentration (in mole%, weight %, or volume % as defined by the process) of a select component than the mixed stream that initially contacts the membrane.
- a "retentate" stream is also obtained from the first side of the membrane which has a lower concentration (in mole%, weight %, or volume % as defined by the process) of a select component than the mixed stream that initially contacts the membrane.
- a separation of components is made resulting in a higher value for the two separated streams (i.e., the retentate and the permeate streams) than the original mixed stream that is fed to the membrane separations process.
- the physical conditions on the permeate side of the membrane for example pressure, temperature, and purge conditions are chosen so that there is a gradient of chemical potential across the membrane that is favorable to drive the select component from the feed side to the permeate side of the membrane.
- United States Patent Publication No. US2007/0202038A1 discloses a family of materials which shall be referred to herein as zeolitic imidazolate frameworks (or "ZIF"s) materials.
- ZIF zeolitic imidazolate frameworks
- This publication describes in detail the synthesis and structural and pore volume characterization of various ZIF materials. It includes the low temperature physisorption characterization (N 2 and H 2 at 77K and Ar at 87K) of selected ZIF structures but it does not disclose adsorption properties of these materials at pressure and temperature conditions that would be relevant to separation processes of gases and hydrocarbons of interest in industrial applications.
- the present invention is a separation process utilizing ZIF-containing materials to effectively separate carbon dioxide, CO 2 , from nitrogen, N 2 , in process feedstreams comprised of both components.
- a process for separating CO 2 from a process feedstream comprising: a) contacting an adsorbent bed comprised of a zeolitic imidazolate framework material with a process feedstream comprising CO 2 and N 2 at a first pressure and first temperature; b) adsorbing at least a portion of the CO 2 in the adsorbent bed; c) producing a CO 2 -lean product stream, wherein the CO 2 -lean product stream has a lower concentration of CO 2 by vol% than the process feedstream; and d) producing a CO 2 -HCh product stream at a second pressure and second temperature, wherein the CO 2 -rich product stream has a higher concentration of CO 2 by vol% than the process feedstream; wherein the zeolitic imidazolate framework material has a framework structure wherein each vertex of the framework structure is comprised of a single metal ion and each pair of connected adjacent vertices of the framework
- a process for separating CO 2 from a process feedstream comprising: a) contacting a first side of a membrane comprised of a zeolitic imidazolate framework material with a process feedstream comprising CO 2 and N 2 at a first pressure and first temperature; b) retrieving a first permeate stream from a second side of the membrane at a second pressure and second temperature, wherein the first permeate stream consists of components that selectively permeate through the membrane and the first permeate stream has a higher concentration of CO 2 by vol% than the process feedstream; and c) retrieving a first retentate stream; wherein the zeolitic imidazolate framework material has a framework structure wherein each vertex of the framework structure is comprised of a single metal ion and each pair of connected adjacent vertices of the framework structure is linked by nitrogen atoms of an imidazolate anion or its derivative, and wherein the zeolitic imid
- the process feedstream is comprised of a combustion gas, an FCC regenerator off-gas, or a synthetically produced gas.
- the zeolitic imidazolate framework material is selected from ZIF-9, ZIF-I, ZIF-7, ZIF-I l, and ZIF-8.
- FIGURE 1 is the experimental powder X-ray diffraction ("PXRD") patterns of the as-synthesized and acetonitrile-exchanged ZIF-7 samples of Example 1 herein.
- the calculated PXRD pattern (shown as the vertical stick patterns in the figure) for ZIF-7 based on the single crystal structure of ZIF-7 reported in the "Park Reference” as referenced herein is also shown in the figure.
- FIGURE 2 shows the thermogravimetric analyses ("TGA”s) for the as-synthesized and acetonitrile-exchanged ZIF-7 samples of Example 1 herein.
- FIGURE 3 is the experimental powder X-ray diffraction ("PXRD") patterns of the as-synthesized and acetonitrile-exchanged ZIF-9 samples of Example 2 herein.
- the calculated PXRD pattern (shown as the vertical stick patterns in the figure) for ZIF-9 based on the single crystal structure of ZIF-9 reported in the "Park Reference” as referenced herein is also shown in the figure.
- FIGURE 4 shows the thermogravimetric analyses ("TGA”s) for the as-synthesized and acetonitrile-exchanged ZIF-9 samples of Example 2 herein.
- FIGURE 5 is the experimental powder X-ray diffraction ("PXRD") patterns of the as-synthesized, the acetonitrile-exchanged and the toluene- exchanged ZIF-I samples of Example 3 herein.
- the calculated PXRD pattern (shown as the vertical stick patterns in the figure) for ZIF-I based on the single crystal structure of ZIF-I reported in the "Park Reference” as referenced herein is also shown in the figure.
- FIGURE 6 shows the thermogravimetric analyses ("TGA”s) for the as-synthesized, the acetonitrile-exchanged and the toluene-exchanged ZIF- 1 samples of Example 3 herein.
- FIGURE 7 is the experimental powder X-ray diffraction ("PXRD") patterns of the purified and methanol-exchanged ZIF-11 samples of Example 4 herein.
- the calculated PXRD pattern (shown as the vertical stick patterns in the figure) for ZIF-11 based on the single crystal structure of ZIF-11 reported in the "Park Reference” as referenced herein is also shown in the figure.
- FIGURE 8 shows the thermogravimetric analyses ("TGA”s) for the purified and methanol-exchanged ZIF-11 samples of Example 4 herein.
- FIGURE 9 is the experimental powder X-ray diffraction ("PXRD") patterns of the purified and methanol-exchanged ZIF-8 samples of Example 5 herein.
- the calculated PXRD pattern (shown as the vertical stick patterns in the figure) for ZIF-8 based on the single crystal structure of ZIF-8 reported in the "Park Reference” as referenced herein is also shown in the figure.
- FIGURE 10 shows the thermogravimetric analyses ("TGA”s) for the purified and methanol-exchanged ZIF-8 samples of Example 5 herein.
- FIGURE 11 is a Scanning Electron Microscopy ("SEM”) image of a ZIF-7 sample of Example 6.
- FIGURE 12 shows the CO 2 adsorption isotherm at 301 K for a ZTP-I sample of Example 6.
- FIGURE 13 shows the CO 2 adsorption isotherm and the N 2 adsorption isotherm at 301 K for a ZIF-7 sample of Example 6.
- FIGURE 14 is a bar graph comparing the adsorption loadings of a ZIF-7 sample of Example 5 for CO 2 and N 2 at 301 K and 106.6 kPa.
- FIGURE 15 shows the CO 2 adsorption isotherms at 301 K, 308 K, and 323 K for a ZIF-7 sample of Example 6.
- FIGURE 16 is a Scanning Electron Microscopy ("SEM”) image of a ZIF-9 sample of Example 7.
- FIGURE 17 shows the CO 2 adsorption isotherm at 301 K for a ZIF-9 sample of Example 7.
- FIGURE 18 shows the CO 2 adsorption isotherm and the N 2 adsorption isotherm at 301 K for a ZIF-9 sample of Example 7.
- FIGURE 19 is a bar graph comparing the adsorption loadings of a ZIF-9 sample of Example 7 for CO 2 and N 2 at 301 K and 106.6 kPa.
- FIGURE 20 is a Scanning Electron Microscopy ("SEM”) image of a ZIF-I (acetonitrile-exchanged) sample of Example 8.
- FIGURE 21 is a Scanning Electron Microscopy ("SEM") image of a ZIF-I (toluene-exchanged) sample of Example 8.
- FIGURE 22 shows the CO 2 adsorption isotherm and the N 2 adsorption isotherm at 301 K for a ZIF-I (acetonitrile-exchanged) sample of Example 8.
- FIGURE 23 is a bar graph comparing the adsorption loadings of a ZIF-I (acetonitrile-exchanged) sample of Example 8 for CO 2 and N 2 at 301 K and 106.6 kPa.
- FIGURE 24 is a Scanning Electron Microscopy ("SEM”) image of a ZIF-11 sample of Example 9.
- FIGURE 25 shows the CO 2 adsorption isotherm and the N 2 adsorption isotherm at 301 K for a ZIF-11 sample of Example 9.
- FIGURE 26 is a bar graph comparing the adsorption loadings of a ZIF-11 sample of Example 9 for CO 2 and N 2 at 301 K and 106.6 kPa.
- FIGURE 27 is a Scanning Electron Microscopy ("SEM”) image of a ZIF-8 sample of Example 10.
- FIGURE 28 shows the CO 2 adsorption isotherm and the N 2 adsorption isotherm at 301 K for a ZIF-8 sample of Example 10.
- FIGURE 29 is a bar graph comparing the adsorption loadings of a ZIF-8 sample of Example 10 for CO 2 and N 2 at 301 K and 106.6 kPa.
- the present invention is directed to processes for the separation of carbon dioxide (“CO 2 ”) from nitrogen (“N 2 ”) in streams containing both carbon dioxide and nitrogen utilizing adsorbents comprised of zeolitic imidazolate framework (“ZIF") materials.
- ZIF zeolitic imidazolate framework
- the zeolitic imidazolate frameworks are utilized in a swing adsorption process.
- swing adsorption process as used herein shall be taken to include Pressure Swing Adsorption (“PSA”) processes, Temperature Swing Adsorption (“TSA”) processes, Pressure Purge Displacement Processes (“PPSA”), Rapid Cycle Pressure Swing Adsorption (“RCPSA”) processes, Rapid Cycle Temperature Swing Adsorption (“RCTSA”) processes, Rapid Cycle Pressure Purge Displacement Processes (“RCPPSA”) as well as combinations of these swing adsorption processes.
- PSA Pressure Swing Adsorption
- TSA Pressure Purge Displacement Processes
- RCPSA Rapid Cycle Pressure Swing Adsorption
- RCTSA Rapid Cycle Temperature Swing Adsorption
- RCPPSA Rapid Cycle Pressure Purge Displacement Processes
- the stream to be separated is fed to the process in a substantially gaseous state.
- a zeolitic imidazolate framework (“ZIF") adsorbent material is incorporated into a membrane material for the selective separation of carbon dioxide (“CO 2 ”) from nitrogen (“N 2 ”) in streams containing both carbon dioxide and nitrogen.
- the ZIF materials will preferably be utilized in a matrixed membrane material to facilitate the separation of CO 2 from N 2 .
- the feedstream to be separated will contact the membrane wherein the CO 2 and the N 2 in the feedstream will be substantially in a gaseous phase.
- Zeolitic imidazolate framework (or "ZIF") materials are defined herein as crystalline microporous structures having framework topologies commonly found in zeolites and/or in other crystalline materials wherein each vertex of the framework structure is comprised of a single metal ion and each pair of connected adjacent vertices of the framework structure is linked by nitrogen atoms of an imidazolate anion or its derivative.
- micropore or “microporous” as utilized herein are defined as a pore diameter or a material containing pore diameters of less than or equal to 2.0 nm (20 A), respectively. Descriptions and the synthesis of some of the ZIF materials that can be utilized in the present invention are disclosed in United States Patent Publication No. US 2007/0202038Al to Yaghi et al., which is hereby incorporated by reference.
- ZIF materials can selectively separate CO 2 from N 2 in streams containing both of these components. Furthermore, this may be accomplished at conditions of pressure, temperature and compositions that are relevant to industrial processes.
- the adsorption loading (e.g., in mmole/g) for the first component must be greater than the adsorption loading (e.g., in mmole/g) for the second component.
- process schemes can be designed to operate at low ratios of adsorption loading (in mmole/g) for the first component vs.
- the adsorption loading (in mmole/g) for the second component it is preferred that this "adsorptive loading ratio for CO 2 over N 2 " for the ZIF material utilized be at least 5. Since the required equipment size, cost and operating expenses tend to be significantly lowered at higher adsorptive loading ratios, the separations processes become much more attractive utilizing materials and conditions that lead to higher adsorptive loading ratios.
- the ZIF material utilized in the present invention has an adsorptive loading ratio for CO 2 over N 2 of at least about 10, even more preferably at least about 25, and most preferably, at least about 50.
- the ratio described above is a property for a specific adsorbate- adsorbent pair, at given conditions of pressure and temperature.
- This ratio is referred to herein as the "adsorptive loading ratio” or more particularly as the “adsorptive loading ratio for CO 2 over N 2 ".
- This ratio is defined herein as a unitless quantity that is equal to the adsorption loading (in mmole/g) for the first component divided by the adsorption loading (in mmole/g) for the second component for a specific adsorbent material at a specific pressure and temperature.
- the term "first component” is synonymous with the - -
- component carbon dioxide, CO 2 , and the term "second component” is synonymous with the component nitrogen, N 2 .
- the adsorption loading for each component on a particular ZIF material be measured under the operating component partial pressure and temperature conditions for the system, it is often more advantageous to measure the adsorption loading for a particular ZIF for each component material at more "standard" conditions of pressure and temperature.
- the adsorptive loading ratio for two components can be measured at either operating partial pressure for the specific components and operating temperature conditions for the feedstream contacting the ZIF-containing adsorbent, or at single component testing conditions chosen herein to be 301 K (28 0 C) and 106.6 kPa (800 torr). Unless stated otherwise, these latter conditions were used in the testing of the samples in the examples herein, which can be readily duplicated in a laboratory test facility.
- ZIF materials that exhibit significantly large adsorptive loading ratios may be used in the swing adsorption processes of the present invention to effectively and economically separate CO 2 from N 2 in streams containing both components.
- Each of these swing adsorption processes are comprised of a number of "steps” that include a variety of adsorption and desorption steps that in combination lead to a complete swing adsorption "cycle” that is periodically repeated. Since multiple adsorbent beds are typically used, their appropriate time synchronization leads to the continuous production of products.
- a complete swing adsorption cycle on a particular adsorbent bed therefore, comprises all of the adsorption and desorption steps that are taken, beginning with the very first contacting of the feed gas mixture with the adsorbate-free or substantially adsorbate-free adsorbent and continuing through the last desorption stage that regenerates the adsorbent into its adsorbate-free or substantially adsorbate-free state and further including any additional repressurizing and/or purging steps that may occur thereafter to bring the "cycle” back to the first contacting of the feed gas mixture with the adsorbate-free or substantially adsorbate-free adsorbent which has begun the "cycle". At this point, the next swing adsorption "cycle" is started and the cycle is subsequently repeated.
- process feedstream or "inlet stream” as used herein in swing adsorption embodiments of the present invention is the mixed component stream comprising at least two components to be separated which is contacted with the adsorbent material during the adsorption cycle.
- the process feedstream contacts the adsorbent material under certain process temperature and pressure conditions and as the process feedstream flows through the adsorbent material at least a portion of the "first component" (or “strongly adsorbed component") of the process feedstream is preferentially adsorbed by the adsorbent material with respect to a "second component” (or “weakly adsorbed component”).
- an "effluent stream” (or "CO 2 -lean product stream” herein) is drawn from the swing adsorption process wherein the total number of moles of the first component into the swing adsorption process is higher than the total number of moles of the first component out of the swing adsorption process during this adsorption step.
- the molar concentration of the first component in the inlet stream be greater than the molar concentration of the first component in the effluent stream.
- the swing adsorption process is also comprised of at least one desorption step wherein at least a portion of the first component that has been preferentially adsorbed by the adsorbent material is recovered in what is termed herein as a "desorbed stream” (or "CO 2 -rich product stream” herein). During this step, the process conditions in the swing adsorption process are changed to - -
- the molar concentration of the first component in the desorbed stream is greater than the molar concentration of the first component in the process feedstream. In another preferred embodiment, the molar concentration of the first component in the desorbed stream is greater than the molar concentration of the first component in the effluent stream.
- steps i.e., adsorption and desorption
- additional steps may be utilized in the swing adsorption processes. These steps include, but are not limited to, concurrent purge steps, counter-current purge steps, and/or multiple partial pressurization or depressurization steps. These additional steps may be utilized to improve first and/or second component recovery, improve first or second component purity, and/or obtain multiple product streams in addition to the effluent stream and desorbed stream described above.
- One embodiment of the swing adsorption process of the present invention utilizes a Pressure Swing Adsorption ("PSA") process wherein the adsorbent material is comprised of a ZIF material and the "first component" as described above is CO 2 and the "second component” as described above is N 2 .
- PSA Pressure Swing Adsorption
- the partial pressure of the first component in the adsorption step is higher than the partial pressure of the first component in the desorption step which allows at least a portion of the adsorbed first component to be recovered in the desorption step and the adsorbent material to be regenerated by depletion of the adsorbed components for reuse in a subsequent adsorption step.
- This desorption can be further assisted by utilizing a purge gas to lower the partial pressure of the first component during the desorption step, a purge step, a partial pressurization step, or a partial depressurization step as described above.
- TSA Temperature Swing Adsorption
- the adsorbent material is comprised of a ZIF material and the "first component" as described above is CO 2 and the "second component” as described above is N 2 .
- the TSA processes operate similar to the PSA processes above wherein the partial pressure of the first component in the adsorption step is higher than the partial pressure of the first component in the desorption step which allows at least a portion of the adsorbed first component to be recovered in the desorption step and the adsorbent material to be regenerated by depletion of the adsorbed components for reuse in a subsequent adsorption step.
- This desorption can be further assisted by utilizing a purge gas to lower the partial pressure of the first component and/or provide heating of the adsorbent material during the desorption step, a purge step, a partial pressurization step, or a partial depressurization step as described above.
- steps of the PSA and TSA processes can be combined in a PSA/TSA process of the present invention.
- both pressure and temperature changes or "swings" are made between the adsorption steps and desorption steps of the process, resulting in a desired separation of at least a portion of the first component from the second component of the mixed component process feedstream fed to the inlet of the PSA/TSA process.
- the ZIF materials may be incorporated into the adsorption swing process in many structural forms and/or in combination with additional components.
- the ZIF materials may be incorporated as crystallites of preferred size and shape of substantially uniform dimensions or with dimensions suitably distributed according to a preferred distribution.
- the crystallites may be used directly as produced in the synthesis steps or be more preferably formulated into larger aggregates or incorporated into a structured or matrix material to provide form, stability, and/or in combination with other complementary co-adsorbent materials that can fulfill a variety of other beneficial functions to the overall process.
- Non-limiting examples include incorporating the ZIF material with a binder material to form a matrix comprising a binder material selected from a crystalline polymer, a non-crystalline polymer, an epoxy, a thermoplastic, a clay, a silica-containing material, an alumina-containing material, and a titania- containing material.
- the binder material may also exhibit either a microporous or a mesoporous structure. Additionally, it may be advantageous to add suitably chosen additives into this binder material. These additives can be used to improve the adsorption/desorption and transport properties of the selected components within the ZIF materials.
- Non-limiting examples of these additional additives include zeolites and microporous crystalline materials such as pure silicates, silicoaluminophosphates ("SAPO"s), aluminophosphates ("AlPO 11 S).
- SAPO silicoaluminophosphates
- AlPO 11 S aluminophosphates
- the additional additive is a zeolite.
- Other additives such as metals or other high heat adsorbing capacity and high heat conductivity materials may also be incorporated into the matrix to assist in the capture and transfer of at least a portion of the heat that is generated during the exothermic adsorption step(s) of the swing adsorption process, thereby shortening the duration of the cycling process, increasing throughput, and further improving the overall efficiency of the ZIF material for adsorbing the select component or components.
- the adsorbent material can be formulated into optimal geometric shapes or be applied onto supporting substrates which further improve the durability of the adsorbent and the rate at which the selected adsorbing components are brought into contact with the adsorption sites of the ZIF material.
- Non-limiting examples include beads, extrudates, formed pellets, structured beds, monoliths and hollow fibers, as well as coatings applied to plates or monolithic structures fibers or hollow fibers.
- inlet stream composition as well as product stream compositions, process conditions and equipment design for the process of the present invention certain structures and/or matrix compositions can provide improved separation efficiencies and/or selectivities for the overall process.
- the ZIF material is utilized in a swing adsorption process wherein the cycle time is less than about 1 minute, and more preferably, the ZIF material is utilized in a swing adsorption process wherein the cycle time is less than about 30 seconds. In an even more preferred embodiment of the present invention, these short cycle times are incorporated into a rapid cycle pressure swing adsorption ("RCPSA") process embodiment of the present invention.
- RPSA rapid cycle pressure swing adsorption
- the ZIF material can be incorporated into a membrane process for the selective separation of carbon dioxide, CO 2 , from nitrogen, N 2 , in streams comprising a mixture of these components.
- a ZIF material is incorporated within or coated onto an inorganic substrate or a polymer material and utilized in a membrane separation process, thereby producing a "ZIF-containing membrane".
- the ZIF material of the membrane has a net permeation affinity for CO 2 over N 2 .
- the permeation rate can be typically described in terms of two multiplicative factors, one related to the diffusion rate and another related to the adsorption loadings of the components of the mixture on the ZIF material.
- a ZIF material incorporated into the membrane which has a higher adsorptive loading ratio for CO 2 over N 2 , improves the concentration gradient for CO 2 either at the membrane surface (if coated onto the membrane surface) and/or in the membrane (if incorporated into the membrane matrix). This improved concentration gradient enhances the selective permeation of CO 2 relative to N 2 through the membrane, resulting in an improved recovery of CO 2 in the membrane permeate stream.
- a process feedstream comprising CO 2 and N 2 contacts a first side of a ZIF-containing membrane and at least a portion of the process feedstream permeates through the membrane and is retrieved from a second side of the membrane material as a permeate stream.
- the permeate stream is obtained from the second side of the membrane and the permeate stream thus obtained has a higher vol% of CO 2 than the process feedstream.
- process feedstream or "inlet stream” as used herein in membrane process embodiments of the present invention is the mixed component stream comprising at least two components to be separated which is contacted with the first side of the ZIF-containing membrane. It should be noted that in some embodiments, a "sweep stream" may be utilized on the permeate - -
- permeate stream as used herein and its composition properties are measured based solely upon the composition of the stream that permeates through the ZIF-containing membrane. For purposes of this invention, if any additional stream, such as a sweep stream, is added on the permeate side of the membrane process, the composition of this sweep stream must be excluded from the compositional analysis of the permeate stream.
- At least one retentate stream is also obtained from the first side of the membrane which has a lower vol% of CO 2 than the process feedstream that initially contacts the membrane.
- a separation of components is made resulting in a higher value for the two separated streams (i.e., the retentate and the permeate streams) than the original mixed stream that is fed to the membrane separations process.
- the ZIF material utilized in the membrane process of the present invention has an adsorptive loading ratio for CO 2 over N 2 of at least about 5, more preferably at least about 10, even more preferably at least about 25, and most preferably at least about 50.
- the membranes utilized in embodiments of the present invention can be asymmetric and can be comprised of several layers of different materials. To improve the mass transfer characteristics of these asymmetric membrane structures one or more of these layers can be a porous material.
- a thin selective layer imparts most of the molecular selectivity in the asymmetric membrane structure and in a preferred embodiment this selective layer contains the ZIF material.
- On the feed side molecules are selectively adsorbed in the selective layer and on the permeate side the molecules are desorbed.
- the selective ZIF- containing layer can optionally include other materials.
- One of the materials that can be present in the ZIF-containing layer is a polymer. When the ZIF containing layer contains more than 10 vol% of another material the selective layer is called a mixed matrix.
- a reparation coating or reparation layer can be incorporated in the membrane structure.
- the ZIF-containing membrane will typically be part of a membrane module that includes a pressure housing.
- Non-limiting examples of ZIF- containing membrane structures that can be incorporated into the membrane module are hollow-fiber membrane structures, flat sheet membrane structures, and monolithic membrane structures.
- the membrane module will typically contain seals to isolate the retentate and permeate zones of the module and to prevent flow bypass or cross-contamination of the retentate stream(s) to the permeate stream(s). The seals may also serve as a device for holding the membrane in place within the membrane module.
- CO 2 and N 2 are typically the majority components in these combustion gas (or flue gas) streams that are released to the environment at slightly above atmospheric pressure and the composition of the combustion gas produced can vary significantly with the carbonaceous source that is utilized by these fossil fuel burning technologies.
- a typical combustion gas stream produced in a coal-fired power plant contains about 14 vol% CO 2 , 5 vol% O 2 and 81 vol% N 2 , with lesser amounts of contaminants that include SOx ( ⁇ 3000 ppm), NOx ( ⁇ 1000 ppm) and particulates ( ⁇ 10 g/m 3 ).
- a combustion gas stream produced in a natural gas turbine process contains about 4 vol% CO 2 , 15 vol% O 2 and 81 vol% N 2 , with other trace amounts of contaminants such as SOx ( ⁇ 1 ppm), NOx ( ⁇ 500 ppm) and particulates (O.01 g/m 3 ).
- all component concentrations expressed herein are on a water-free basis.
- porous solid adsorbents such us the ZIFs materials of the present invention
- the materials of the present invention exhibit unique adsorption properties for selectively adsorbing CO 2 from a combustion gas stream at relatively low pressures and moderate temperatures.
- Figure 13 shows the adsorption isotherms for ZIF-7 for carbon dioxide, CO 2 , and for nitrogen, N 2 .
- ZIF- 7 (as well as ZIF-9 in Figure 18) has a very large adsorptive loading ratio for CO 2 over N 2 .
- the overall adsorption loading of these components at standard test conditions of 301 K and 106.6 kPa for ZIF-7 is shown in the bar graph of Figure 14. As can be seen in Figure 14, under these standard test conditions, - -
- ZIF-7 has an adsorption loading for CO 2 of about 2.29 mmole/g while the ZIF-7 has an adsorption loading for N 2 of only about 0.02 mmole/g. Therefore, the adsorptive loading ratio for CO 2 over CH 4 for ZIF-7 at these conditions is greater than about 100. Such high adsorptive loading ratios render these ZIF materials as very effective adsorbents materials in the processes of the present invention.
- ZIF-7 (as well as ZIF-9) exhibits a unique isotherm shape not typically found in microporous crystalline materials such as zeolites.
- this unique isotherm shape for CO 2 in ZIF-7 and ZIF-9 has important implications and distinctively enables embodiments of the present invention.
- Figure 13 shows that the isotherm for CO 2 at 301 K-displays a hysteretic behavior characterized by unique adsorption (solid diamonds) and desorption (open diamonds) branches. The transition from low to high loading in the adsorption branch at about 60 kPa signals a more favorable accommodation of the CO 2 within the ZIF-7 structure than in the Henry's law- like region below about 60 kPa.
- the transition from high to low loading in the desorption branch at about 50 kPa signals the less favorable accommodation of the CO 2 within the ZIF-7 structure.
- This behavior is the result of unique energetic interactions between the adsorbed CO 2 and the ZIF-7 structure that, as described herein, advantageously enables embodiments of the pressure swing adsorption processes of the present invention.
- this particular isotherm shape it is possible to develop an effective pressure swing adsorption cycle that requires a narrow pressure swing that is only of the order of the pressure gap that exists between the rising adsorption branch and the decreasing desorption branch (i.e., a pressure swing of approximately 20 to 30 kPa in this example).
- working capacity of an adsorbate material is defined herein as the difference between the adsorbate loading in the adsorption step and the adsorbate loading in the desorption step of the "strongly adsorbed component" (which herein is CO 2 ). Larger values of the working capacity are desirable.
- Figure 13 shows that when N 2 is contacted with the ZIF-7 material at pressures as high as 106.6 kPa and 301 K, the adsorption loading remains low, in a Henry's law kind of regime, ultimately giving rise to a high adsorptive loading ratio for CO 2 over N 2 at those conditions. While it is expected that higher N 2 partial pressures could eventually cause the transition to a higher loading state to take place in a material like ZIF-7 at the - -
- the ZIF material is utilized in a swing adsorption process wherein the applied pressure swing is less than about 300 kPa.
- the ZIF material is utilized in a swing adsorption process wherein the applied pressure swing is less than about 200 kPa, and even more preferably, the ZIF material is utilized in a swing adsorption process wherein the applied pressure swing is less than about 100 kPa.
- these narrow applied pressure swings are incorporated into a pressure swing adsorption ("PSA”) process embodiment of the present invention.
- PSA pressure swing adsorption
- the term "applied pressure swing” as utilized herein is defined as the difference in the maximum and minimum CO 2 partial pressures that are experienced in the adsorbent bed during a swing adsorption cycle.
- the temperature can be increased to displace or prevent the low to high adsorption loading transition for an adsorbate in a given pressure range (as shown above), the temperature can be alternatively decreased to cause such a low to high adsorption loading transition to take place for an adsorbate in a given pressure range or to displace such transition from a higher pressure to a lower pressure.
- Such interplay of pressure and temperature can be used to design advantageous swing adsorption schemes of the present invention over a wide range of components pressures in the gaseous feedstreams.
- the temperature of the process feedstream is reduced prior to contacting the ZIF-containing adsorbent material.
- This embodiment is particularly beneficial when it is desired to separate CO 2 from CH 4 in low pressure process feedstreams, especially when the temperatures of the process feedstream may be significant enough to appreciably shift the adsorption and desorption branches to higher CO 2 pressures than those experienced at lower temperatures.
- ZIF-7 for example, can achieve a significant separation of CO 2 from N 2 at near ambient temperatures of about 28 0 C (301 K) under low CO 2 partial pressures conditions of less than about 80 kPa.
- Figures 17 and 18 show that the transition from low to high adsorption loading occurs at a slightly higher CO 2 pressure in ZIF-9 (i.e., about 90 kPa) than in ZIF-7 (i.e., about 60 kPa) at the same temperature of 301 K.
- This difference between ZIF-9 and ZIF-7 simply reflects some small differences in energetics between the corresponding adsorbate-adsorbent pairs but the overall adsorption characteristics are substantially the same.
- these results further illustrate the advantages and breadth of applications of the ZIFs materials of the present invention for separating gaseous mixtures containing CO 2 and N 2 through swing adsorption processes.
- Combustion gas streams include any reaction effluent stream produced by the combustion of fossil fuels for the production of heat and/or energy.
- Such combustion gas streams are typical in the industry and include industrial processes such as, but not limited to, coal or gas fired power plants, as well as coal or gas fired heating. Following extraction of the heat and/or energy from the combustion process, these combustion gases are often released to the atmosphere.
- Combustion gas stream compositions can vary significantly depending upon the composition of the fuel source, the combustion process utilized, as well as the process conditions utilized in the process.
- the major components of the combustion gas streams produced by conventional industrial processes will generally range from about 3 to about 25 vol% CO 2 , from about 65 to about 85 vol% N 2 , and from about 5 to about 20 vol% O 2 .
- the total amount of CO 2 emitted to the atmosphere by the combustion of fossil fuels represents about 60% of the global CO 2 emissions today ("Advanced Technologies for the Capture of Carbon Dioxide from Flue Gases", S. Chakravarti, A. Gupta, B. Hunek, First National Conference on Carbon Sequestration, Washington DC, May 15-17, 2001).
- These combustion gas streams also normally contain varying amounts OfH 2 O and additional trace contaminants such as, but not limited to, SOx, NOx, and particulates.
- Gas streams can be treated for the removal of CO 2 in certain conventional processes, such as amine-based treating technologies. Additionally, CO 2 can be sequestered in underground formations, but this usually requires the gas streams containing the CO 2 to be compressed to very high pressures of about 500 to about 3,500 psig (3,447 to 24,132 kPa) to be injected into high pressure underground formations. However, both of these processes for the separation and sequestration of the CO 2 have problems efficiently operating with the composition of most combustion gas streams. One of the main problems restricting commercially viable CO 2 separation and/or sequestration processes is the high nitrogen content present in most combustion gas streams.
- the final combustion products to be treated are usually at relatively low temperatures and pressures.
- the final working pressures of the majority of these combustion gas streams are in the range of about 0.1 to about 50 psig (0.7 to 345 kPa) since these products are typically released to the atmosphere or are or transferred to an enclosed low pressure flare gas or treatment system.
- the temperature conditions of the temperature-activated pressure swing adsorption process can be suitably chosen optimize the effectiveness of the PSA cycle.
- the temperature can be suitably reduced to ensure that the cycle operates selectively and under a high working capacity and thus ensure the operation of an effective swing adsorption process.
- the temperatures at which these streams are produced may be significantly high enough to shift the adsorption/desorption branches to CO 2 partial pressures above those required for optimum separations at low pressures. Therefore, in an embodiment of the present invention, the temperature of the combustion gas stream, or a process stream comprised of a combustion gas stream, is reduced prior to contacting the ZIF-containing adsorbent material. In this manner, the compression required to raise the combustion gas to optimum separation conditions for the present invention can be minimized, and in certain embodiments, the need for compression equipment to raise the pressure of the feedstream to the processes of the present invention may be completely eliminated.
- the PSA and TSA processes of the present invention can be operated at inlet stream pressures less than about 50 psig (345 kPa), or even less than about 25 psig (172 kPa) due to the significant low pressure adsorption loading characteristics for CO 2 of ZIF materials.
- the PSA and TSA processes of the present invention may be operated at very low inlet stream pressures of less than about 10 psig (69 kPa), or even less than about 5 psig (34 kPa).
- the PSA and TSA processes of the present invention may be incorporated into existing combustion gas process and/or utilized with conventional combustion gas equipment without the need for additional compression. This can potentially save significant system costs, thus making embodiments of the present invention highly cost effective and able to retrofit into existing combustion gas systems without the need for additional combustion gas compression systems.
- One embodiment of the present invention is to provide a process feedstream comprising a combustion gas stream to a swing adsorption process wherein the adsorbent material in the swing adsorption process is comprised of a - -
- a process feedstream comprising a combustion gas stream is provided to a swing adsorption process wherein the adsorbent material in the swing adsorption process is comprised of a ZIF material that has adsorptive loading ratio for CO 2 over N 2 of at least about 10.
- the ZIF material utilized in this process has an adsorptive loading ratio for CO 2 over N 2 of at least about 25, and in a most preferable embodiment of the present invention, the ZIF material utilized in this process has an adsorptive loading ratio for CO 2 over N 2 of at least 50.
- the process feedstream is comprised of a combustion gas stream which contacts an adsorbent material comprised of a ZIF material with an adsorptive loading ratio for CO 2 over N 2 of at least about 5.
- a CO 2 -lean product stream is obtained from the effluent stream from the adsorption step of the swing adsorption process.
- a CO 2 -rich product stream is obtained from the desorbed stream from the desorption step of the swing adsorption process.
- the CO 2 content of a combustion gas stream can typically range from about 3 to about 25 vol% CO 2 .
- a CO 2 -lean product stream is obtained as the effluent stream from the separations process wherein the CO 2 content is less than 10 vol%, and even more preferably, a CO 2 -lean product stream is obtained with a CO 2 content of less than about 5 vol%. It is desired that when separating the CO 2 present in the combustion gas that the processes of the present invention recover a large portion of the CO 2 in the CO 2 -rich product stream thereby allowing the CO 2 -lean product stream (now rich in N 2 and very low in CO 2 ) to pass through as an effluent stream and be exhausted to the atmosphere or to further treatment with a significant reduction in the CO 2 greenhouse gas component.
- the CO 2 -rich product stream When coupled with the need to sequester the CO 2 obtained from the combustion gas stream, it is highly desirable that the CO 2 -rich product stream be high in CO 2 content. This is to minimize both the energy required to pressurize the gas to the high pressures required for sequestration as well as minimize the storage capacity required to contain the CO 2 . Therefore, in preferred embodiments of the present invention, the CO 2 -rich product stream has a CO 2 content of at least about 50 vol%, more preferably at least about 60 vol%, and most preferably, at least about 70 vol%.
- the terms "sequestration” or "CO 2 sequestration” as utilized herein are defined as the confinement of a waste stream containing at least 50 vol% of CO 2 in an underground structure, or repository, or in the deep ocean at pressures of at least 500 psig (3,447 kPa).
- at least a portion of the CO 2 -rich product stream obtained from the separation of CO 2 from N 2 by the present invention is further sequestered at a pressure of at least 500 psig (3,447 kPa), and even more preferably, at least 1000 psig (6,895 kPa).
- the N 2 content of the CO 2 -rich product stream is less than about 20 vol%.
- a CO 2 -HCh product stream is obtained wherein the N 2 content of the CO 2 -rich product stream is less than 10 vol%, or even more preferably less than about 5 vol%.
- the N 2 content by vol% of the CO 2 -lean product stream is less than 25% of the N 2 content by vol% of the combustion gas stream.
- the N 2 content by vol% of the CO 2 -lean product stream is less than 20%, and more preferably less than 15%, of the N 2 content by vol% of the combustion gas stream.
- the CO 2 -rich product stream produced by the present invention also has improved composition for amine treating of the CO 2 gases.
- the increased CO 2 content and lower N 2 content of the CO 2 -rich product stream significantly improves the ability of the amine to adsorb CO 2 due to the higher available CO 2 partial pressure under comparable amine treating conditions.
- the total volume of the overall combustion gas stream to be treated is significantly reduced by the separation of most of the nitrogen which can be in the order of about 65 to about 85 vol% N 2 in a typical combustion gas stream. Therefore, the total volume that would be required to be treated in an amine unit can easily be reduced by a factor of about 3 to about 5, resulting in significant capital, chemical and energy savings.
- at least a portion of the CO 2 -rich product stream produced from the removal of CO 2 from a combustion gas stream is further processed in an amine treating unit.
- a swing adsorption process utilizing a ZIF-containing adsorbent material is utilized to separate CO 2 from N 2 present in the regenerator off-gas of a fluid catalytic cracking ("FCC") unit.
- FCCs are well known in the industry and the regenerator off-gas can contain a significant amount Of CO 2 and N 2 . Similar to the combustion gas processes described prior, most of the regenerator off-gas is emitted to the atmosphere after some treatment for contaminants. However, the conventional treatments typically do not target the removal of CO 2 from the regenerator off- gas and therefore have little effect on the overall CO 2 emissions.
- the FCC regenerators in refineries and chemical plans produce sizable amounts of off-gas streams which can contribute significantly to CO 2 emissions and its associated greenhouse effect.
- These FCC regenerator off-gas streams can also be difficult to treat due to other contaminant compounds and catalyst fines generated from the FCC process.
- the FCC regenerator off- gas streams can have similar properties to combustion gas streams described prior, particularly in regard to their total pressures as well as their CO 2 and N 2 content. These FCC regenerator off-gas streams can therefore be treated by the processes of the present invention to remove at least a portion of the CO 2 from the N 2 , thereby producing a CO 2 -rich product stream and a CO 2 -lean product stream in a similar manner and component concentrations as described above for combustion gas streams.
- At least a portion of a FCC regenerator off-gas stream is subjected to a swing adsorption process of the present invention thereby producing a CO 2 -lean product stream wherein the CO 2 -lean product stream, or a portion thereof, with a reduced CO 2 content is emitted to the atmosphere and the CO 2 -rich product stream, or a portion thereof, is either sequestered or further processed in an amine treating unit.
- Another desirable commercial process embodiment of the separation processes of the present invention is for use in the separation of synthetically produced gas streams that are obtained through a variety of reactive processes that utilize a carbonaceous source and an oxidant and/or heat.
- These synthetically produced gas streams find use, for example, as synthesis gas for the production of other chemical products and intermediates (e.g., methanol) as well as in the synthesis of higher molecular weight hydrocarbons (e.g., kerosene fuels, aviation grade fuels, diesel grade fuels or lube blending products obtained, for example, via Fischer-Tropsch synthesis) which themselves find use as final products or as intermediates for further functionalization or for the synthesis of other products.
- chemical products and intermediates e.g., methanol
- hydrocarbons e.g., kerosene fuels, aviation grade fuels, diesel grade fuels or lube blending products obtained, for example, via Fischer-Tropsch synthesis
- these synthetically produced gas streams may also target the generation of enriched hydrogen streams for use as fuels (e.g., fuel cells) or for use in the chemical processing of hydrocarbons (e.g., hydrodesulfurization and hydrodenitrogenation).
- fuels e.g., fuel cells
- hydrocarbons e.g., hydrodesulfurization and hydrodenitrogenation
- carbonaceous sources can be used, ranging from gaseous (e.g., natural gas) to liquid (e.g., naphthas, heavy oils and residue, bitumens, or shale oils) to solids (e.g., coal).
- gaseous e.g., natural gas
- liquid e.g., naphthas, heavy oils and residue, bitumens, or shale oils
- solids e.g., coal
- oxygen source pure oxygen, air, or steam (plus heat) are typically used.
- the carbonaceous source In some instances, only heat is applied to the carbonaceous source to produce a "gasification" gas mixture that contains lesser amounts of full combustion products, which may be used as fuel or chemicals.
- the specific composition of the synthetically produced gas is strongly dependent on the nature of the carbonaceous source, the oxidant and the use of heat (if any).
- the produced gas typically contains varying amounts OfH 2 , CO, CO 2 , H 2 O, CH 4 and N 2 as majority components and lesser amounts of sulfur and nitrogen containing species (e.g., H 2 S and NH 3 ) as well as other contaminants (e.g., COS).
- the synthetically produced gas streams contain significant amounts on N 2 , which does not incorporate into any major reaction products, with the exception of the smaller amounts OfNH 3 formed.
- various levels of purification and preconditioning are required.
- a particularly important step in the production of a synthetically produced gas is the removal of CO 2 from the product stream.
- the CO 2 in the synthetically produced gas is generally not beneficial as it does not incorporate into any subsequent reaction products and it does not add heating value.
- the CO 2 present in the synthetically produced gas can exist in sufficiently high concentrations that can contribute to the corrosion of processing equipment, as well as contribute to the production of greenhouse gas emissions.
- One embodiment of the present invention is to provide a process feedstream comprising a synthetically produced gas to a swing adsorption process wherein the adsorbent material in the swing adsorption process is comprised of a ZIF material that has an adsorptive loading ratio for CO 2 over N 2 of at least about 5 to remove at least a portion of the CO 2 from the process feedstream.
- a process feedstream comprising a synthetically produced gas is provided to a swing adsorption process wherein the adsorbent material in the swing adsorption process is comprised of a ZIF material that has an adsorptive loading ratio for CO 2 over N 2 of at least about 10 to remove at least a portion of the CO 2 from the process feedstream.
- the ZIF material utilized in this process has an adsorptive loading ratio for CO 2 over N 2 of at least about 25, and most preferably an adsorptive loading ratio for CO 2 over N 2 of at least 50.
- the process will pass through the adsorbent material and be recovered in the effluent stream from the process.
- the N 2 in the obtained effluent stream can then be separated from the H 2 by conventional methods resulting in a higher purity H 2 stream.
- the H 2 stream thus obtained can be directly utilized as a final product or mixed with a carbon monoxide stream for use in further synthesis steps for the catalytic production, for example, of methanol or other liquid hydrocarbon products.
- the effluent stream (or "CO 2 -lean product stream") produced in the process above for the removal of CO 2 from a synthetically produced gas contains less than about 5 vol% CO 2 , and even more preferably less than about 3 vol% CO 2 .
- the CO 2 selectively permeates through the ZIF-containing membrane process producing at least one CO 2 -rich permeate stream wherein the CO 2 -rich permeate stream has a higher vol% of CO 2 than the process feedstream that contacts the ZIF-containing membrane. Additionally, at least one CO 2 -lean retentate stream is also produced by the process wherein a CO 2 -lean retentate stream has a lower vol% of CO 2 than the process feedstream.
- the stream compositions, separations selectivities and properties of the final products produced by the ZIF-containing membrane process embodiments of the present invention are similar to those identified in the swing adsorption process embodiments described above.
- Another important process in the industry concerning greenhouse gases, such as CO 2 is the sequestration of at least a portion of the CO 2 removed from a process stream.
- the terms "sequestration” or “CO 2 sequestration” as utilized herein are defined as the confinement of a waste stream containing at least 50 vol% of CO 2 in an underground structure, or repository, or in the deep ocean at pressures of at least 500 psig (3,447 kPa).
- the separation processes of the present invention may be designed to minimize the amount of CO 2 that remains in the CO 2 -lean product stream produced.
- the CO 2 -rich product stream produced by any of the separation process embodiments of the present invention can be further sequestered.
- At least a portion of the CO 2 -rich stream produced by the separation process of the current invention is sequestered.
- the CO 2 -rich stream that is produced has a CO 2 content of at least 75 vol% wherein at least a portion of the CO 2 -rich stream is sequestered.
- the CO 2 -rich stream has a CO 2 content of at least 85 vol% wherein at least a portion of the CO 2 -rich stream is sequestered.
- the CO 2 -lean product stream obtained has a CO 2 content of less than about 5 vol%, and more preferably less than about 2 vol%. The utilization of this process embodiment is particularly beneficial wherein the CO 2 -lean stream is released to the atmosphere as an exhaust stream.
- ZIFs Zeolitic Imidazolate Frameworks
- the X-ray diffraction pattern can be altered upon solvent- exchange or desolvation.
- the ZIF materials used in the gas adsorption screening studies were prepared according to published procedures with slight modifications in reaction scale and/or sample activation; see reference Park, K. S.; Ni, Z.; Cote, A. P.; Choi, J. Y.; Huang, R.; Uribe-Romo, F. J.; Chae, H. K.; O'Keeffe, M.; Yaghi, O. M. Proc. Natl. Acad. ScL U.S.A. 2006, 103, 10186- 10191, which is incorporated herein by reference and herein referred to as the "Park Reference".
- a ZIF-7 material was synthesized.
- SOD is a three-letter framework type code as defined by the International Zeolite Association (“IZA") in the "Atlas of Zeolite Framework Types" (Ch. Baerlocher, L.B. McCusker, D.H. Olson, Sixth Revised Edition, Elsevier Amsterdam, 2007).
- the as-synthesized solid was heated under vacuum at 473 K for 24 hours, transferred to a 120 ml vial, immersed in acetonitrile (c.a. 100 ml) and soaked at 348 K for 48 hours.
- acetonitrile- exchanged ZIF-7 was loaded in a glass tube and evacuated on a vacuum line apparatus at room-temperature for 16 hours to remove the solvent molecules residing in its pores.
- 2.1O g of activated ZIF-7 was obtained, corresponding to 55% yield (based on Benzimidazole).
- Figure 1 shows a comparison of the experimental powder X-ray diffraction ("PXRD") patterns of the as-synthesized and the acetonitrile- exchanged ZIF-7 samples and the calculated PXRD pattern (shown as the stick pattern) based on the single crystal structure of ZIF-7 reported in the "Park Reference” as referenced herein.
- the PXRD patterns as shown in Figure 1 are plotted as the diffraction intensity (in arbitrary units) against the diffraction angle two theta (in degrees).
- FIG. 2 shows the thermogravimetric analyses ("TGA") for the as- synthesized and the acetonitrile-exchanged ZIF-7 samples in nitrogen atmosphere.
- TGA thermogravimetric analyses
- Figure 11 is a Scanning Electron Microscopy ("SEM”) image of a sample of ZIF-7 produced.
- a ZIF-9 material was synthesized.
- SOD is a three-letter framework type code as defined by the International Zeolite Association (“IZA") in the "Atlas of Zeolite Framework Types" (Ch. Baerlocher, L.B. McCusker, D.H. Olson, Sixth Revised Edition, Elsevier Amsterdam, 2007).
- the as-synthesized solid was heated under vacuum at 473 K for 24 hours, transferred to a 20 ml vial, immersed in acetonitrile (c.a. 15 ml) and soaked at 348 K for 48 hours.
- the acetonitrile- exchanged ZIF-9 was loaded in a glass tube and evacuated on a vacuum line apparatus at room-temperature for 16 hours to remove the solvent molecules residing in its pores. 0.07 g of activated ZIF-9 was obtained, corresponding to 15% yield (based on Benzimidazole).
- the acetonitrile-exchanged ZIF-9 was loaded directly in the sample holder of the gravimetric gas adsorption unit and activated in-situ by using the conditions described in Example 7.
- Figure 3 shows a comparison of the experimental powder X-ray diffraction ("PXRD") patterns of the as-synthesized and the acetonitrile- exchanged ZIF-9 samples and the calculated PXRD pattern (shown as the stick pattern) based on the single crystal structure of ZIF-9 reported in the "Park Reference” as referenced herein.
- the PXRD patterns as shown in Figure 3 are plotted as the diffraction intensity (in arbitrary units) against the diffraction angle two theta (in degrees).
- FIG 4 shows the thermogravimetric analyses ("TGA") for the as- synthesized and the acetonitrile-exchanged ZIF-9 samples in nitrogen atmosphere.
- TGA thermogravimetric analyses
- Figure 16 is a Scanning Electron Microscopy ("SEM”) image of a sample of ZIF-9 produced.
- Example 3 a ZIF-I material was synthesized.
- BCT is a three-letter framework type code as defined by the International Zeolite Association (“IZA") in the "Atlas of Zeolite Framework Types" (Ch. Baerlocher, L.B. McCusker, D.H. Olson, Sixth Revised Edition, Elsevier Amsterdam, 2007).
- the as-synthesized solid was immersed in acetonitrile (c.a. 15 ml) for a total of 72 hours. The solvent volume was replaced every 24 hours.
- the acetonitrile-exchanged ZIF-I was loaded in a glass tube and evacuated on a vacuum line apparatus at room temperature for 16 hours to remove the solvent molecules residing in its pores. 0.13 g of activated ZIF-I was obtained, corresponding to 14% yield (based on zinc nitrate tetrahydrate).
- the as-synthesized ZIF- 1 was activated by exchanging with toluene followed by heating under vacuum at 443 K for 2 hours.
- Figure 5 shows a comparison of the experimental powder X-ray diffraction ("PXRD") patterns of the as-synthesized, the acetonitrile-exchanged and the toluene-exchanged ZIF-I samples and the calculated PXRD pattern (shown as the stick pattern) based on the single crystal structure of ZIF-I reported in the "Park Reference” as referenced herein.
- the PXRD patterns as shown in Figure 5 are plotted as the diffraction intensity (in arbitrary units) against the diffraction angle two theta (in degrees).
- Figure 6 shows the thermogravimetric analyses ("TGA") for the as- synthesized, the acetonitrile-exchanged and the toluene-exchanged ZIF-I samples in nitrogen atmosphere. The activation conditions described above were chosen based on TGA data.
- Figure 20 is a Scanning Electron Microscopy (“SEM”) image of a sample of ZIF-I (acetonitrile-exchanged) produced.
- Figure 21 is a Scanning Electron Microscopy (“SEM”) image of a sample of ZIF-I (toluene-exchanged) produced.
- a ZIF-11 material was synthesized.
- RHO is a three-letter framework type code as defined by the International Zeolite Association (“IZA") in the "Atlas of Zeolite Framework Types" (Ch. Baerlocher, L.B. McCusker, D.H. Olson, Sixth Revised Edition, Elsevier Amsterdam, 2007).
- the solid crystallized on the side wall and the bottom part of the vial was collected and washed with DMF (N,N-Dimethylformamide) repeatedly to remove any residual mother liquor and an amorphous by-product.
- the product was then transferred to a 20 ml vial and the DMF solvent was decanted.
- chloroform c.a. 15 ml
- the vial was capped and the mixture was immersed in an ultrasonic bath for 30 minutes to mechanically detach an unidentified dense-phase from the surfaces of ZIF-11 crystals.
- Two layers of solids appeared after the vial sat on a level surface undisturbed for 30 minutes.
- the solid layer floating on the surface of chloroform was carefully collected using a pipette and transferred to another 20 ml vial.
- the solid was washed with and stored in DMF and labeled "purified ZIF-H".
- the purified solid was immersed in methanol (c.a. 15 ml) for a total of 72 hours. The solvent volume was replaced every 24 hours.
- the methanol-exchanged ZIF-11 was loaded in a glass tube and evacuated on a vacuum line apparatus. After the removal of external methanol solvent at room temperature, the solid was heated under vacuum at 423 K for 16 hours to remove the solvent molecules residing in the pores of the ZIF-11. A 0.09 g sample of activated ZIF-11 was thus obtained, corresponding to 27% yield (based on zinc nitrate hexahydrate).
- Figure 7 shows a comparison of the experimental powder X-ray diffraction ("PXRD") patterns of the purified and the methanol-exchanged ZIF- 11 samples and the calculated PXRD pattern (shown as the stick pattern) based on the single crystal structure of ZIF-11 reported in the "Park Reference” as referenced herein.
- the PXRD patterns as shown in Figure 7 are plotted as the diffraction intensity (in arbitrary units) against the diffraction angle two-theta (in degrees).
- Figure 24 is a Scanning Electron Microscopy ("SEM”) image of a sample of ZIF-I l produced.
- a ZIF-8 material was synthesized.
- SOD is a three-letter framework type code as defined by the International Zeolite Association (“IZA") in the "Atlas of Zeolite Framework Types" (Ch. Baerlocher, L.B. McCusker, D.H. Olson, Sixth Revised Edition, Elsevier Amsterdam, 2007
- the product was then transferred to a 120 ml vial and the DMF solvent was decanted.
- chloroform c.a. 100 ml
- the vial was capped and the mixture was immersed in an ultrasonic bath for 30 minutes to mechanically detach zinc oxide particles from the surfaces of ZIF-8 crystals.
- Two layers of solids appeared after the vial sat on a level surface undisturbed for 30 minutes.
- the solid layer floating on the surface of chloroform was carefully collected using a pipette and transferred to another 120 ml vial. The solid was washed with and stored in DMF and labeled "purified ZIF-8".
- the purified solid was immersed in methanol (c.a. 100 ml) for a total of 72 hours. The solvent volume was replaced every 24 hours.
- This methanol-exchanged ZIF-8 was loaded in a glass tube and evacuated on a vacuum line apparatus. After the removal of external methanol solvent at room-temperature, the solid was heated under vacuum at 523 K for 16 hours to remove the solvent molecules residing in the pores of ZIF-8. 1.70 g of activated ZIF-8 was obtained, corresponding to 41% yield (based on 2- Methylimidazole).
- the methanol-exchanged ZIF-8 was loaded directly in the sample holder of the gravimetric gas adsorption unit and activated in-situ by using the conditions described in Example 10.
- Figure 9 shows a comparison of the experimental powder X-ray diffraction ("PXRD") patterns of the purified and the methanol-exchanged ZIF-8 samples and the calculated PXRD pattern (stick pattern) based on the single crystal structure of ZIF-8 reported in the "Park Reference” as referenced herein. The high purity of the sample is evidenced by the coincidence of experimental and calculated PXRD patterns.
- the PXRD patterns as shown in Figure 9 are plotted as the diffraction intensity (in arbitrary units) against the diffraction angle two theta (in degrees).
- FIG 10 shows the thermogravimetric analyses ("TGA") for the purified and the methanol-exchanged ZIF-8 samples in nitrogen atmosphere.
- TGA thermogravimetric analyses
- Figure 27 is a Scanning Electron Microscopy ("SEM”) image of a sample of ZIF-8 produced.
- a Cahn ® microbalance apparatus (TG 121, 0.1 ⁇ g) was used to gravimetrically characterize the adsorption/desorption properties of gases and hydrocarbons (i.e., adsorbates) in various zeolitic imidazolate frameworks (i.e., adsorbents).
- adsorbate-adsorbent pairs were carried out on various adsorbate-adsorbent pairs to determine the adsorption isotherms for the various ZIF materials synthesized in Examples 1 through 5 above.
- the equilibrium adsorbate loading was measured at various adsorbate pressures up to 106.6 kPa.
- the adsorbate feed was brought into the feed manifold from lecture bottles or from house supply lines containing high purity gases and hydrocarbons.
- the feed manifold was in contact with the adsorbent located in the sample holder of the microbalance.
- the adsorbate pressure within the feed manifold was controlled between vacuum and 106.6 kPa by a MKS® Type 146 Measurement and Control System, which was connected to the computer via RS232 communications.
- the feed manifold was equipped with three MKS® 120A pressure transducers (0-0.0133 kPa, 0-1.33 kPa and 0-133 kPa) that provided the adsorbate pressure information to the controller.
- the controller actuated two electronic valves to adjust the adsorbate pressure within the feed manifold.
- One valve (MKS 0248A, Type OOIOORK) was connected to the adsorbate feed supply and the other valve (MKS 0248A, Type 10000RV) was connected to the vacuum line.
- a Pfeiffer® TSU 261 turbomolecular pump was used to achieve the vacuum conditions.
- adsorbent typically, prior to the adsorption isotherm measurements, about 15- 90 mg of adsorbent was loaded in the microbalance at 301 K. In order to avoid the contacting of the adsorbent with ambient air, the adsorbent was fully immersed in an excess of a specified solvent (i.e., an amount well in excess of that required to fill its internal pore volume). The solvent was removed through the use of dynamic vacuum. In some cases, where the solvent was held more strongly within the interior of the adsorbate, heating was also used.
- a specified solvent i.e., an amount well in excess of that required to fill its internal pore volume
- the following steps were applied: (a) out-gassing at 301 K for a prescribed duration, (b) heating to a prescribed temperature and kept there for a prescribed duration, (c) cooling to 301 K. Because the microbalance was tare just prior to loading the sample, the dry weight was directly obtained from the microbalance upon completion of the clean-up procedure. The type of solvent, the heating temperature as well as the duration of the steps was dependent on the particular ZIF material under study. For a given ZIF sample, the same clean-up steps were repeated each time a new successive experiment was conducted. Prior to removing the sample from the microbalance, the first and/or second adsorption experiments were repeated. These repeat experiments revealed excellent reproducibility, confirming the adequacy of the experimental adsorption isotherm procedures as well as the stability of the samples throughout the adsorption experiments. X-ray measurements of the removed samples further confirmed their integrity.
- the upper abscissa displays the relative CO 2 pressure, where the normalizing pressure Po corresponds to the CO 2 saturation pressure at 301 K. From thermodynamic equilibrium vapor pressure data, a value of 6583.8 kPa was estimated for P 0 .
- the filled and open symbols identify the corresponding adsorption and desorption branches, respectively (the adsorption branch is shown with filled diamond legend and the desorption branch is shown with open diamond legend).
- an adsorption isotherm for nitrogen, N 2 was also generated and is shown together in Figure 13 with the adsorption/desorption isotherm from Figure 12 above.
- nitrogen did not exhibit the separate adsorption and desorption branches as was exhibited for carbon dioxide and therefore, the adsorption and desorption curves for nitrogen in this regime overlap for ZIF-7.
- the adsorption loading of carbon dioxide, CO 2 was significantly larger than the adsorption loading for nitrogen, N 2 , on the ZIF-7 material. In fact, only 0.02 mmole/g of adsorbed nitrogen was detected at 301 K and 106.6 kPa.
- Figure 14 is a bar graph comparing the corresponding adsorption loadings of the ZIF-7 material for carbon dioxide, CO 2 , and nitrogen, N 2 , at test conditions of 301 K and 106.6 kPa obtained from the tests above.
- the adsorption loading of the ZIF-7 material for CO 2 at 106.6 kPa @ 301 K was approximately 2.29 mmole/g while the adsorption loading for N 2 was approximately 0.02 mmole/g.
- the adsorptive loading ratio for CO 2 over N 2 is approximately 114.5, illustrating the very high selectivity of the ZIF-7 material for CO 2 over N 2 , making ZIF-7 a suitable material for use in the present invention.
- the upper abscissa displays the relative CO 2 pressure, where the normalizing pressure P 0 corresponds to the CO 2 saturation pressure at 301 K. From thermodynamic equilibrium vapor pressure data, a value of 6583.8 kPa was estimated for P 0 .
- the filled and open symbols identify the corresponding adsorption and desorption branches, respectively (the adsorption branch is shown with filled diamond legend and the desorption branch is shown with open diamond legend).
- an adsorption isotherm for nitrogen, N 2 was also generated and is shown together in Figure 18 with the adsorption/desorption isotherm from Figure 17 above.
- nitrogen did not exhibit the separate adsorption and desorption branches, and in fact, nitrogen did not load measurably on the ZIF-9 during the test.
- the adsorption loading of carbon dioxide, CO 2 was significantly larger than the adsorption loading for nitrogen, N 2 , on the ZIF-9 material.
- Figure 19 is a bar graph comparing the corresponding adsorption loadings of the ZIF-9 material for carbon dioxide, CO 2 , and nitrogen, N 2 , at test conditions of 301 K and 106.6 kPa obtained from the tests above.
- the adsorption loading of the ZIF-9 material for CO 2 at 106.6 kPa @ 301 K was approximately 2.33 mmole/g while the adsorption loading for N 2 was not measurable.
- the adsorptive loading ratio for CO 2 over N 2 is immeasurable (approaching infinity), illustrating the extremely high selectivity of the ZIF-9 material for CO 2 over N 2 , making ZIF-9 a suitable material for use in the present invention.
- Figure 22 shows the adsorption isotherms of the acetonitrile- exchanged ZIF-I for carbon dioxide, CO 2 , and nitrogen, N 2 , at 301 K.
- the ordinate displays the equilibrium adsorption loading in typical units of mmole/g;
- the abscissa displays the absolute pressure of the adsorbate in kPa.
- the adsorption loading of carbon dioxide, CO 2 was higher than the adsorption loading for nitrogen, N 2 , on the acetonitrile-exchanged ZIF-I material.
- Figure 23 is a bar graph comparing the corresponding adsorption loadings of the acetonitrile-exchanged ZIF- 1 material for carbon dioxide, CO 2 , and nitrogen, N 2 , at test conditions of 301 K and 106.6 kPa obtained from the tests above.
- the adsorption loading of the acetonitrile-exchanged ZIF-I material for CO 2 at 106.6 kPa @ 301 K was approximately 1.05 mmole/g while the adsorption loading for N 2 was approximately 0.004 mmole/g.
- the adsorptive loading ratio for CO 2 over N 2 is approximately 262.5, illustrating the very high selectivity of the ZIF- 1 material for CO 2 over N 2 , making ZIF- 1 a suitable material for use in the present invention.
- the toluene-exchanged ZIF-I material exhibits similar adsorption loading characteristics as the acetonitrile-exchanged ZIF-I material.
- the abscissa displays the absolute pressure of the adsorbate in kPa.
- the adsorption loading of carbon dioxide, CO 2 was significantly higher than the adsorption loading for nitrogen, N 2 , on the ZIF- 11 material.
- Figure 26 is a bar graph comparing the corresponding adsorption loadings of the ZIF-11 material for carbon dioxide, CO 2 , and nitrogen, N 2 , at test conditions of 301 K and 106.6 kPa obtained from the tests above. As can be seen from this bar graph, the adsorption loading of the ZIF-11 material for CO 2 at 106.6 kPa @ 301 K was approximately 0.87 mmole/g while the adsorption - -
- the adsorptive loading ratio for CO 2 over N 2 is approximately 7.9, illustrating the high selectivity of the ZIF-11 material for CO 2 over N 2 , making ZIF-11 a suitable material for use in the present invention.
- the abscissa displays the absolute pressure of the adsorbate in kPa.
- the adsorption loading of carbon dioxide, CO 2 was significantly higher than the adsorption loading for nitrogen, N 2 , on the ZIF-8 material.
- Figure 29 is a bar graph comparing the corresponding adsorption loadings of the ZIF-8 material for carbon dioxide, CO 2 , and nitrogen, N 2 , at test conditions of 301 K and 106.6 kPa obtained from the tests above. As can be seen from this bar graph, the adsorption loading of the ZIF-8 material for CO 2 at - O -
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Abstract
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| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| AU2009215790A AU2009215790B2 (en) | 2008-02-21 | 2009-02-20 | Separation of carbon dioxide from nitrogen utilizing zeolitic imidazolate framework materials |
| AT09713512T ATE532573T1 (en) | 2008-02-21 | 2009-02-20 | SEPARATION OF CARBON DIOXIDE FROM NITROGEN USING MATERIALS WITH A ZEOLITE IMIDAZOLATE BACKGROUND |
| ES09713512T ES2376615T3 (en) | 2008-02-21 | 2009-02-20 | SEPARATION OF NITROGEN CARBON DIOXIDE USING MATERIALS WITH ZEOLIC IMIDAZOLATE STRUCTURE. |
| CA2716323A CA2716323C (en) | 2008-02-21 | 2009-02-20 | Separation of carbon dioxide from nitrogen utilizing zeolitic imidazolate framework materials |
| EP09713512A EP2249947B1 (en) | 2008-02-21 | 2009-02-20 | Separation of carbon dioxide from nitrogen utilizing zeolitic imidazolate framework materials |
| CN200980113353.XA CN102015065B (en) | 2008-02-21 | 2009-02-20 | Separation of carbon dioxide from nitrogen utilizing zeolitic imidazolate framework materials |
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| US12/321,751 US8142745B2 (en) | 2008-02-21 | 2009-01-23 | Separation of carbon dioxide from nitrogen utilizing zeolitic imidazolate framework materials |
| US12/321,751 | 2009-01-23 |
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| GB202206101D0 (en) | 2022-04-27 | 2022-06-08 | Mof Tech Limited | Method and apparatus for carbon dioxide separation |
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Family Cites Families (39)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US3885927A (en) | 1974-02-05 | 1975-05-27 | Union Carbide Corp | Process for removing carbon dioxide from gas streams |
| DD143712A3 (en) | 1978-08-18 | 1980-09-10 | Manfred Schingnitz | PROCESS FOR PROVISION OF PROCESS STEAM IN INTEGRATED BROWN COATING PLANTS |
| US4775396A (en) | 1987-11-05 | 1988-10-04 | Union Carbide Corporation | Selective adsorption of CO2 on zeolites |
| US4857078A (en) | 1987-12-31 | 1989-08-15 | Membrane Technology & Research, Inc. | Process for separating higher hydrocarbons from natural or produced gas streams |
| US4869883A (en) | 1988-06-24 | 1989-09-26 | Air Products And Chemicals, Inc. | Inert gas purifier for bulk nitrogen without the use of hydrogen or other reducing gases |
| US5507856A (en) | 1989-11-14 | 1996-04-16 | Air Products And Chemicals, Inc. | Hydrogen recovery by adsorbent membranes |
| CA2041874C (en) | 1990-01-09 | 1999-04-06 | Richard T. Maurer | Separation of ethane from methane by pressure swing adsorption |
| JPH0859770A (en) | 1994-08-15 | 1996-03-05 | Dainippon Ink & Chem Inc | Polyurethane polyurea crosslinked fine particle dispersion and method for producing the same |
| US5726118A (en) * | 1995-08-08 | 1998-03-10 | Norit Americas, Inc. | Activated carbon for separation of fluids by adsorption and method for its preparation |
| US5642630A (en) | 1996-01-16 | 1997-07-01 | Abdelmalek; Fawzy T. | Process for solids waste landfill gas treatment and separation of methane and carbon dioxide |
| CN1178129A (en) * | 1996-09-30 | 1998-04-08 | 波克股份有限公司 | Process and apparatus for gas purification |
| US5753011A (en) | 1997-01-17 | 1998-05-19 | Air Products And Chemicals, Inc. | Operation of staged adsorbent membranes |
| US6011192A (en) | 1998-05-22 | 2000-01-04 | Membrane Technology And Research, Inc. | Membrane-based conditioning for adsorption system feed gases |
| EP1213049B8 (en) | 1999-03-23 | 2007-02-14 | National Institute of Advanced Industrial Science and Technology | Gas separation membrane and process for producing a polymer |
| DE60129626T2 (en) | 2000-04-20 | 2008-05-21 | Tosoh Corp., Shinnanyo | Process for purifying a gas mixture containing hydrogen |
| US6544316B2 (en) | 2000-05-19 | 2003-04-08 | Membrane Technology And Research, Inc. | Hydrogen gas separation using organic-vapor-resistant membranes |
| ATE334992T1 (en) | 2001-04-30 | 2006-08-15 | Univ Michigan | ISORETICULAR ORGANOMETALLIC BASIC STRUCTURES, METHOD FOR THEIR FORMATION AND SYSTEMATIC DEVELOPMENT OF THEIR PORE SIZE AND FUNCTIONALITY, WITH APPLICATION FOR GAS STORAGE |
| US20030078311A1 (en) | 2001-10-19 | 2003-04-24 | Ulrich Muller | Process for the alkoxylation of organic compounds in the presence of novel framework materials |
| FR2832141B1 (en) * | 2001-11-14 | 2004-10-01 | Ceca Sa | SYNTHESIS GAS PURIFICATION PROCESS |
| US7078235B2 (en) * | 2001-12-06 | 2006-07-18 | Electric Power Research Institute | Sulfur trioxide conditioning system control algorithm |
| US6929679B2 (en) | 2002-02-01 | 2005-08-16 | Basf Aktiengesellschaft | Method of storing, uptaking, releasing of gases by novel framework materials |
| US6624318B1 (en) | 2002-05-30 | 2003-09-23 | Basf Aktiengesellschaft | Process for the epoxidation of an organic compound with oxygen or an oxygen-delivering compounds using catalysts containing metal-organic frame-work materials |
| US6893564B2 (en) | 2002-05-30 | 2005-05-17 | Basf Aktiengesellschaft | Shaped bodies containing metal-organic frameworks |
| US6617467B1 (en) | 2002-10-25 | 2003-09-09 | Basf Aktiengesellschaft | Process for producing polyalkylene carbonates |
| EP1633760B1 (en) | 2003-05-09 | 2010-05-05 | The Regents of The University of Michigan | MOFs with a high surface area and methods for producing them |
| US7056482B2 (en) * | 2003-06-12 | 2006-06-06 | Cansolv Technologies Inc. | Method for recovery of CO2 from gas streams |
| US7309380B2 (en) | 2003-06-30 | 2007-12-18 | Basf Aktiengesellschaft | Gas storage system |
| US20050004404A1 (en) | 2003-07-03 | 2005-01-06 | Basf Akiengesellschaft | Process for the alkoxylation of monools in the presence of metallo-organic framework materials |
| CN1914219A (en) | 2003-12-05 | 2007-02-14 | 密歇根大学董事会 | Metal-organic polyhedra |
| US7411081B2 (en) | 2004-01-13 | 2008-08-12 | Basf Aktiengesellschaft | Process for preparing and organometallic framework material |
| CA2573685A1 (en) | 2004-08-03 | 2006-02-16 | The Regents Of The University Of Colorado, A Body Corporate | Membranes for highly selective separations |
| KR101227824B1 (en) | 2004-10-22 | 2013-01-30 | 더 리젠츠 오브 더 유니버시티 오브 미시간 | Covalently linked organic frameworks and polyhedra |
| US7524444B2 (en) | 2004-11-09 | 2009-04-28 | Basf Aktiengesellschaft | Shaped bodies containing metal-organic frameworks |
| DE102004061238A1 (en) | 2004-12-20 | 2006-06-22 | Basf Ag | Method for the enrichment of methane in methane containing gas mixtures comprises contacting the gas mixture with at least a sorbent containing a porous metal-organic structure material |
| US7343747B2 (en) | 2005-02-23 | 2008-03-18 | Basf Aktiengesellschaft | Metal-organic framework materials for gaseous hydrocarbon storage |
| CN101151091B (en) | 2005-04-07 | 2010-06-23 | 密歇根大学董事会 | High adsorption of gases in microporous metal-organic frameworks with open metal sites |
| US7799120B2 (en) | 2005-09-26 | 2010-09-21 | The Regents Of The University Of Michigan | Metal-organic frameworks with exceptionally high capacity for storage of carbon dioxide at room-temperature |
| PL1988996T3 (en) | 2006-02-28 | 2018-01-31 | Univ Michigan Regents | Preparation of functionalized zeolitic frameworks |
| US7687432B2 (en) | 2007-02-02 | 2010-03-30 | Miami University | Mesh-adjustable molecular sieve |
-
2009
- 2009-01-23 US US12/321,751 patent/US8142745B2/en not_active Expired - Fee Related
- 2009-02-20 EP EP09713512A patent/EP2249947B1/en not_active Not-in-force
- 2009-02-20 WO PCT/US2009/001100 patent/WO2009105255A2/en not_active Ceased
- 2009-02-20 CA CA2716323A patent/CA2716323C/en not_active Expired - Fee Related
- 2009-02-20 ES ES09713512T patent/ES2376615T3/en active Active
- 2009-02-20 AU AU2009215790A patent/AU2009215790B2/en not_active Ceased
- 2009-02-20 CN CN200980113353.XA patent/CN102015065B/en not_active Expired - Fee Related
- 2009-02-20 AT AT09713512T patent/ATE532573T1/en active
Non-Patent Citations (1)
| Title |
|---|
| CH. BAERLOCHER, L.B. MCCUSKER, D.H. OLSON: "Atlas of Zeolite Framework Types", 2007, ELSEVIER |
Cited By (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| EP1988996A4 (en) * | 2006-02-28 | 2011-01-05 | Univ Michigan | PREPARATION OF FUNCTIONALIZED ZEOLITIC STRUCTURES |
| US8314245B2 (en) | 2006-02-28 | 2012-11-20 | The Regents Of The University Of Michigan | Preparation of functionalized zeolitic frameworks |
| US8809546B2 (en) | 2006-02-28 | 2014-08-19 | The Regents Of The University Of California | Preparation of functionalized zeolitic frameworks |
| EP2167511A4 (en) * | 2007-07-17 | 2010-12-22 | Univ California | PREPARATION OF FUNCTIONALIZED ZEOLITHIC STRUCTURES |
| CN102218298A (en) * | 2011-04-28 | 2011-10-19 | 华南理工大学 | Preparation method of modified ZIF-8 zeolitic imidazolate framework material |
| CN104390815A (en) * | 2013-10-23 | 2015-03-04 | 中国科学院地球环境研究所 | Automatic gas collection device and method thereof |
| CN107516741A (en) * | 2017-06-28 | 2017-12-26 | 浙江工业大学 | A Synthetic Method of Co-supported N-doped Three-dimensional Porous Carbon Materials with Excellent Electrocatalytic Oxygen Reduction Performance |
Also Published As
| Publication number | Publication date |
|---|---|
| US8142745B2 (en) | 2012-03-27 |
| EP2249947A2 (en) | 2010-11-17 |
| US20090214407A1 (en) | 2009-08-27 |
| AU2009215790B2 (en) | 2013-05-23 |
| ES2376615T3 (en) | 2012-03-15 |
| AU2009215790A1 (en) | 2009-08-27 |
| CN102015065B (en) | 2014-09-10 |
| CA2716323C (en) | 2015-03-31 |
| ATE532573T1 (en) | 2011-11-15 |
| CN102015065A (en) | 2011-04-13 |
| WO2009105255A3 (en) | 2010-04-22 |
| EP2249947B1 (en) | 2011-11-09 |
| CA2716323A1 (en) | 2009-08-27 |
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