The present invention is generally directed to systems and methods of converting fuel, and is specifically directed to oxidation-reduction reactor systems used in fuel conversion.
There is a constant need for clean and efficient energy generation systems. Most of the commercial processes that generate energy carriers such as steam, hydrogen, synthesis gas (syngas), liquid fuels and/or electricity are based on fossil fuels. Furthermore, the dependence on fossil fuels is expected to continue in the foreseeable future due to the much lower costs compared to renewable sources. Currently, the conversion of carbonaceous fuels such as coal, natural gas, petroleum coke is usually conducted through a combustion or reforming process. However, combustion of carbonaceous fuels, especially coal, is a carbon intensive process that emits large quantities of carbon dioxide to the environment. Sulfur and nitrogen compounds are also generated in this process due to the complex content in coal.
Chemical reactions between metal oxides and carbonaceous fuels, on the other hand, may provide a better way to recover the energy stored in the fuels. Several processes are based on the reaction of metal oxide particles with carbonaceous fuels to produce useful energy carriers. For example, Ishida et al. U.S. Pat. No. 5,447,024 describes processes wherein nickel oxide particles are used to convert natural gas through a chemical looping process into heat, which may be used in a turbine. However, recyclability of pure metal oxides is poor and constitutes an impediment for its use in commercial and industrial processes. Moreover, this technology has limited applicability, because it may only convert natural gas, which is more costly than other fossil fuels. Another well known process is a steam-iron process, wherein coal derived producer gas is reacted with iron oxide particles in a fluidized bed reactor to be later regenerated with steam to produce hydrogen gas. This process however suffers from poor gas conversion rates due to improper contact between reacting solids and gases, and is incapable of producing a hydrogen rich stream.
As demands increase for cleaner and more efficient systems of converting fuel, the need arises for improved systems, and system components therein, which will convert fuel effectively, while reducing pollutants.
The concepts of the present disclosure are generally applicable to systems for producing hydrogen from coal, or other carbonaceous fuels. In accordance with one embodiment of the present disclosure, a system for converting fuel may comprise a first moving bed reactor, a second reactor, and a non-mechanical valve. The first moving bed reactor may comprise at least one tapered section and multiple injection gas ports. The multiple injection gas ports may be configured to deliver a fuel to the first moving bed reactor. The first moving bed reactor may be configured to reduce an oxygen carrying material with a fuel by defining a countercurrent flowpath for the fuel relative to the oxygen carrying material. The second reactor may communicate with the first moving bed reactor and may be operable to receive an oxygen source. The second reactor may be configured to regenerate the reduced oxygen carrying material by oxidation. The non-mechanical valve may comprise a circuitous piping assembly disposed between the first moving bed reactor and the second reactor. At least one gas opening may be configured to receive a gas stream. The gas stream may be operable to reduce gas leakage between the first moving bed reactor and the second reactor.
The following detailed description of specific embodiments of the present disclosure may be best understood when read in conjunction with the following drawings, where like structure is indicated with like reference numerals and in which:
The present invention is generally directed to the components of a system for the conversion of solid carbonaceous fuels into other forms of energy. Other configurations of the present invention may also be applied to convert liquid and gaseous fuels. The conversion of fuels may generally be performed with a binary mixture of particles in a system, wherein the binary mixture may comprise an oxygen carrying material and a solid carbonaceous fuel. In one embodiment, oxygen present in the oxygen carrying material oxidizes the solid fuels, while the oxygen carrying material particles are reduced to a lower oxidation state. Generally, the products of the system may include heat, power, chemicals, liquid fuels and/or H2, which may be generated by re-oxidizing the reduced oxygen carrying material particles using oxidizing agents such as, but not limited to, air and/or steam in a separate reactor. In some embodiments, chemicals and liquid fuels may be produced using H2 and/or CO2 produced by the system, or through partial oxidation of metal oxide particles and coupling of the carbonaceous fuels.
In some embodiments, the systems described herein may involve circulation of primary metal oxide particles in a circulating fluidized bed with a downcomer of either a packed moving bed or a series of interconnected-fluidized beds, in which the solid fuels are injected and dispersed throughout the primary particles for the chemical reaction with primary oxygen carrying material particles. Generally, the metal oxides with coarse particle size may be used in the packed moving bed as the oxygen carrying material to avoid fluidization, whereas the solid fuel particle size is smaller than metal oxides, in order to extend the hydrodynamic limit of moving bed operation. The systems described herein also may utilize the difference of hydrodynamic properties of two types of particles to control their interaction and to separate the byproducts of solid fuels or unconverted solid fuels from the oxygen carrying material particles and gas products. Various application schemes using the oxygen carrying material circulating systems are explained herein. In addition, various reactor designs and details regarding the solid fuel handling and processing strategy in the chemical looping system are explained herein.
Methods for producing hydrogen gas by the use of a chemical looping process in an oxidation and reduction reaction scheme with carbon-based reducing fuels and oxidizing gases are disclosed in Thomas et al. (U.S. Pat. No. 7,767,191), Fan et al. (PCT Application No. WO 2007/082089), and Fan et al. (U.S. Provisional Application No. WO 2010/037011) respectively, and their teachings are incorporated herein in their entirety by reference.
Generally, the present invention is directed to systems and methods for converting fuel by redox reactions of oxygen carrying material particles. In some embodiments, reactor system may utilize a chemical looping process wherein carbonaceous fuels may be converted to heat, power, chemicals, liquid fuels, and/or hydrogen (H2). In the process of converting carbonaceous fuels, oxygen carrying materials within the system such as oxygen carrying particles may undergo reduction/oxidation cycles. The carbonaceous fuels may reduce the oxygen carrying materials in a reduction reactor. The reduced oxygen carrying materials may then be oxidized by steam and/or air in one or more separate reactors. In some embodiments, oxides of iron may be preferred as at least one of the components in the oxygen carrying material in the chemical looping system. In some embodiments, oxides of copper, cobalt and manganese may also be utilized in the system. Oxygen carrying materials are described in Thomas et al. (U.S. Published App. No. 2005/0175533 A1), which is incorporated herein in its entirety by reference.
Now referring to
As would be familiar to one of ordinary skill in the art, the oxygen carrying materials may be fed to the reactor via any suitable solids delivery device/mechanism. These solids delivery devices may include, but are not limited to, pneumatic devices, conveyors, lock hoppers, or the like.
Referring to the reaction in the reduction reactor 100, the reduction reactor 100 generally may receive a fuel, which is utilized to reduce the at least one metal oxide of the oxygen carrying material to produce a reduced metal or a reduced metal oxide. As defined herein, “fuel” may include: a solid carbonaceous composition such as coal, tars, oil shales, oil sands, tar sand, biomass, wax, coke etc; a liquid carbonaceous composition such as gasoline, oil, petroleum, diesel, jet fuel, ethanol etc; and a gaseous composition such as syngas, carbon monoxide, hydrogen, methane, gaseous hydrocarbon gases (C1-C6), hydrocarbon vapors, etc. For example, and not by way of limitation, the following equation illustrates possible reduction reactions:
Fe2O3+2CO→2Fe+2CO2
16Fe2O3+3C5H12→32Fe+15CO2+18H2O
In this example, the metal oxide of the oxygen carrying material, Fe2O3, may be reduced by a fuel, for example, CO, to produce a reduced metal oxide, Fe. Although Fe may be the predominant reduced composition produced in the reduction reaction of the reduction reactor 100, FeO or other reduced metal oxides with a higher oxidation state are also contemplated herein.
The reduction reactor 100 may be configured as a moving bed reactor, a series of fluidized bed reactors, a rotary kiln, a fixed bed reactor, combinations thereof, or others known to one of ordinary skill in the art. Typically, the reduction reactor 100 may operate at a temperature in the range of about 400° C. to about 1200° C. and a pressure in the range of about 1 atm to about 150 atm; temperatures and pressures outside these ranges may be desirable depending on the reaction mechanism and the components of the reaction mechanism.
The CO2/H2O rich gas of the outlet stream 120 may be further separated by a condenser 126 to produce a CO2 rich gas stream 122 and an H2O rich stream 124. The CO2 rich gas stream 122 may be further compressed for sequestration. The reduction reactor 100 may be specially designed for solids and/or gas handling, which is discussed herein. In some embodiments, the reduction reactor 100 may be configured as a packed moving bed reactor. In another embodiment, the reduction reactor may be configured as a series of interconnected fluidized bed reactors, wherein oxygen carrying material may flow counter-currently with respect to a gaseous species.
Still referring to
To regenerate the metal oxide of the oxygen carrying materials, the system 10 may utilize a combustion reactor 300, which is configured to oxidize the reduced metal oxide of the oxygen carrying material. The oxygen carrying material may enter the combustion reactor 300 and may be fluidized with air or another oxidizing gas from an inlet stream 310. The iron in the oxygen carrying material may be re-oxidized by air in the combustion reactor 300 to an average valence state of about 3+. The combustion reactor 300 may release heat during the oxidation of oxygen carrying material particles. Such heat may be extracted for steam and/or power generation or used to compensate the process heat requirements. In some embodiments, the combustion reactor 300 may comprise an air filled line or tube used to oxidize the oxygen carrying material. Alternatively, the combustion reactor 300 may be a heat recovery unit such as a reaction vessel or other reaction tank.
The following equation lists one possible mechanism for the oxidation in the combustion reactor 300:
2Fe3O4+0.5O2→3Fe2O3
Following the oxidation reaction in the combustion reactor 300, the oxidized oxygen carrying materials may be transferred to a gas-solid separation device 500. The gas-solid separation device 500 may separate gas and fine particulates in an outlet stream 510 from the bulk oxygen carrying material solids in an outlet stream 520. The oxygen carrying material may be transported from the combustion reactor 300 to the gas-solid separation device 500 through a solid conveying system 350, such as for example a riser. In one embodiment, the Fe3O4 product may be oxidized to Fe2O3 in the solid conveying system 350.
The bulk oxygen carrying material solids discharged from the gas-solid separation device 500 may be moved through a solid-solid separation device 600, through connection means 710, and to a solid storage vessel 700 where substantially no reaction is carried out. In the solid-solid separation device 500, oxygen carrying materials may be separated from other solids, which flow out of the system through an outlet 610. The oxygen carrying material solids discharged from the solid storage vessel 700 will pass through another non-mechanical gas sealing device 750 and finally return to the reduction reactor 100 to complete a global solids circulation loop.
In some embodiments, the oxygen carrying material particles may undergo numerous regeneration cycles, for example, 10 or more regeneration cycles, and even greater than 100 regeneration cycles, without substantially losing functionality. This system may be used with existing systems involving minimal design change, thus making it economical.
Now referring to
Similar to the system 10 of
The reduced oxygen carrying material exiting the reduction reactor 100 may be transferred through a connection means 160 that may have a non-mechanical gas-sealing device, to an oxidation reactor 200. The reduced oxygen carrying materials may be re-oxidized, with steam from an inlet stream 210. The oxidation reactor 200 may have an outlet stream 220 rich in H2 and steam. Excessive/unconverted steam in the outlet stream 220 may be separated from the H2 in the stream 220 with a condenser 226. An H2 rich gas stream 222 may be generated. The steam inlet stream 210 of the oxidation reactor 200 may come from condensed steam recycled in the system 20 from an outlet stream 124 of the reduction reactor 100. In one embodiment, a portion of the solid carbonaceous fuel in the reduction reactor 100 may be intentionally or unintentionally introduced to the oxidation reactor 200, which may result in a H2, CO, and CO2 containing gas in an outlet stream 220. Such a gas stream 220 may be either used directly as synthetic gas (syngas) or separated into various streams of pure products. In the oxidation reactor 200, the reduced oxygen carrying materials may be partially re-oxidized to an average valence state for iron that is between 0 and 3+. In some embodiments, the reduction reactor 100 is configured to operate in a packed moving bed mode or as a series of interconnected fluidized bed reactors, in which oxygen carrying material may flow counter-currently against the gaseous species.
The oxidation reactor 200, which may comprise the same reactor type or a different reactor type than the reduction reactor 100, may be configured to oxidize the reduced metal or reduced metal oxide to produce a metal oxide intermediate. As used herein, “metal oxide intermediate” refers to a metal oxide having a higher oxidation state than the reduced metal or metal oxide, and a lower oxidation state than the metal oxide of the oxygen carrying material. For example, and not by way of limitation, the following equation illustrates possible oxidation reactions in the oxidation reactor 200:
3Fe+4H2O→Fe3O4+4H2
3Fe+4CO2→Fe3O4+4CO
In this example, which centers on oxygen carrying materials that may be ceramic composites that utilize Fe2O3 as the metal oxide, oxidation in the oxidation reactor 200 using steam may produce a resultant mixture that includes metal oxide intermediates comprising predominantly Fe3O4. Fe2O3 and FeO may also be present. Furthermore, although H2O, specifically steam, is the oxidant in this example, numerous other oxidants are contemplated, for example, CO, O2, air, and other compositions.
The oxidation reactor 200 may be configured as a moving bed reactor, a series of fluidized bed reactors, a rotary kiln, a fixed bed reactor, combinations thereof, or others. Typically, the oxidation reactor 200 may operate at a temperature in the range of about 400° C. to about 1200° C. and a pressure in the range of about 1 atm to about 150 atm; however, temperatures and pressures outside these ranges may be desirable depending on the reaction mechanism and the components of the reaction mechanism.
The oxidation reactor 200 may comprise a moving bed with a countercurrent contacting pattern of gas and solids. Steam may be introduced at the bottom of the reactor and may oxidize the reduced oxygen carrying material particles as the particles move downwardly inside the oxidation reactor 200. In this embodiment, the product formed may be hydrogen, which is subsequently discharged from the top of the oxidation reactor 200. It will be shown in further embodiments that products such as CO and syngas are possible in addition to hydrogen. Though Fe2O3 formation is possible in the oxidation reactor 200, the solid product from the oxidation reactor 200 is expected to be mainly metal oxide intermediate, Fe3O4. The amount of Fe2O3 produced in the oxidation reactor 200 depends on the oxidant used, as well as the amount of oxidant fed to the oxidation reactor 200. The steam present in the hydrogen product of the oxidation reactor 200 may then be condensed in order to provide for a hydrogen rich stream 222. At least part of this hydrogen rich stream may be recycled back to the reduction reactor 100. In addition to utilizing the same reactor type as the reduction reactor 100, the oxidation reactor 200 may similarly operate at a temperature between about 400° C. to about 1200° C. and pressure of about 1 atm to about 150 atm.
The partially re-oxidized oxygen carrying materials exiting the oxidation reactor 200 may flow through a combustion reactor inlet stream 400 and may be transferred to a combustion reactor 300. The reduced oxygen carrying material in the combustion reactor inlet stream 400 may be moved through a non-mechanical gas seal and/or a non-mechanical solids flow rate control device.
The oxygen carrying material may enter the combustion reactor 300 and may be fluidized with air or another oxidizing gas from an inlet stream 310. The iron in the oxygen carrying material may be re-oxidized by air in the combustion reactor 300 to an average valence state of about 3+. The combustion reactor 300 may release heat during the oxidation of oxygen carrying material particles. Such heat may be extracted for steam and/or power generation or used to compensate the process heat requirements.
Followed by the oxidation reactions in the combustion reactor 300, the oxidized oxygen carrying materials may be transferred in the same manner as the previous embodiment in
Referring now to
The reduced oxygen carrying material may then be transferred through a non-mechanical gas-sealing device 160 to an optional oxidation reactor 200. In the oxidation reactor 200, the reduced oxygen carrying materials may be re-oxidized, with steam from an inlet stream 210, into a H2 containing gas stream 220. Steam in the outlet stream 220 may be further condensed in a condenser 126, generating a H2 rich gas stream 122 and a steam rich stream 124. The outlet stream 122 may be used to upgrade the hydrocarbon products generated in the reduction reactor 100. In some embodiments, at least a portion of the carbonaceous fuel may be intentionally or unintentionally introduced to the oxidation reactor 200, which may result in a H2, CO, and CO2 containing gas stream 220. Such a gas stream 220 may either be used directly as syngas or may be separated into various streams of pure products. In some embodiments, the reduction reactor may be configured to operate as a packed moving bed reactor or a series of interconnected fluidized bed reactors, in which oxygen carrying materials may flow counter-currently relative to a gaseous species.
The re-oxidized oxygen carrying material may then be transferred, through a combustion reactor inlet stream 400 optionally comprising a non-mechanical gas seal and/or a non-mechanical solids flow rate control device, to a combustion reactor 300, where it may be fluidized with air. The metal oxides are further oxidized in the combustion reactor 300. The combustion reactor may release heat. Such heat may either be extracted for steam and/or power generation or used to compensate the process heat requirements.
Following oxidation reactions in the combustion reactor 300, the oxidized oxygen carrying materials may be transferred in the same manner as the previous embodiment in
By controlling the amount of steam in the oxidation reactor inlet stream 210, the overall ratio of production rates among hydrocarbons, H2, and power may be adjusted. In the case when H2 is not the desired product, the oxidation reactor may be by-passed and reduction reactor 100 and combustion reactor 300 may be directly connected through the combustion reactor inlet stream, similar to the embodiment of
Now referring to
The reduced oxygen carrying material may then be transferred, through a non-mechanical gas-sealing device 160, to an optional oxidation reactor 200. The reduced oxygen carrying material may be re-oxidized, with steam, producing an H2 containing gas outlet stream 220. Steam in the gas stream 220 may be separated by a condenser 226, generating a H2 rich gas stream 222. H2 may be used to upgrade the pyrolysis oil produced from the reduction reactor 100. For the steam inlet stream 210 of the oxidation reactor 200, usage of condensed steam in outlet stream 124 from the reduction reactor may be optional. In some embodiments, a portion of the carbonaceous fuel may be intentionally or unintentionally introduced to the oxidation reactor 200, which may result in a H2, CO, and CO2 containing gas in the outlet stream 220. Such a gas stream may be either used directly as syngas or separated into various streams of pure products. In the oxidation reactor 200, the iron oxide in the reduce oxygen carrying material is also re-oxidized to an average valence state that is between 0 and 3+. In some embodiments, the oxidation reactor 200 may be operated as a packed moving bed reactor or a series of interconnected fluidized bed reactor where oxygen carrying material flows counter-currently with respect to the gaseous species.
Still referring to
Following the oxidation reaction in the combustion reactor 300, the oxidized oxygen carrying materials may be transferred to a gas-solid separation device 500. The gas-solid separation device 500 may separate gas and fine particulates in an outlet stream 510 from the bulk oxygen carrying material solids in an outlet stream 520. The oxygen carrying material may be transported from the combustion reactor 300 to the gas-solid separation device 500 through solid conveying system 350, such as for example a riser. In one embodiment, the Fe3O4 product may be oxidized to Fe2O3 in the solid conveying system 350.
The bulk oxygen carrying material solids discharged from the gas-solid separation device 500 may be moved through a solid-solid separation device 600, through connection means 710, and to a solid storage vessel 700 where substantially no reaction is carried out. In the solids separation device 500, oxygen carrying materials may be separated from other solids, which flow out of the system through an outlet 610. The oxygen carrying material solids discharged from the solid storage vessel 700 will pass through another non-mechanical gas sealing device 750 and finally return to the reduction reactor 100 to complete a global solids circulation loop.
Alternatively, a portion of the oxygen carrying materials from the gas-solid separation device 500 may by-pass the solid-solid separation device 600 and pyrolyzer reactor 800 and enter directly into the reduction reactor 100 through a stream 550.
Alternatively, a portion of the carbonaceous fuels in the inlet stream 310 may be directly introduced to the combustion reactor 100. By controlling the amount of steam in inlet stream 210 to the oxidation reactor 200 and the fuel injection ratio between the reduction reactor 100 and pyrolysis reactor 800, the overall product ratio among pyrolysis products, H2, and power may be adjusted. In the case when H2 is not the desired product, the oxidation reactor 200 may be by-passed and the reduction reactor 100 and/or the solid conveying system 350 such as a riser may be directly connected through the non-mechanical gas seal and solids flow rate control device, in order to compensate the heat requirement in the reduction reactor 100.
Now referring to
Now referring to
Now referring to
Now referring to
The reactors of the systems described herein may be constructed with various durable materials suitable to withstand temperatures of up at least 1200° C. The reactors may comprise carbon steel with a layer of refractory on the inside to minimize heat loss. This construction also allows the surface temperature of the reactor to be fairly low, thereby improving the creep resistance of the carbon steel. Other alloys suitable for the environments existing in various reactors may also be employed, especially if they are used as internal components configured to aid in solids flow or to enhance heat transfer within a moving bed embodiment. The interconnects for the various reactors can be of lock hopper design or rotary/star valve design to provide for a good seal. However, other interconnects as can be determined easily by a person skilled in the art may also be used.
Various mechanisms can be used for solid transportation in the numerous systems disclosed herein. For example, in some embodiments the solid transportations systems described herein may be transport systems using a pneumatic conveyor driven by air, belt conveyors, bucket elevators, screw conveyors, moving beds and fluidized bed reactors. The resultant depleted air stream may be separated from the particles and its high-grade-heat content recovered for steam production. After regeneration, the oxygen carrying material particle may not be substantially degraded and may maintain full particle functionality and activity.
Heat integration and heat recovery within the system and all system components may be desirable. Heat integration in the system is specifically focused on generating the steam for the steam requirements of the oxidation reactor 200. This steam may be generated using the high grade heat available in the hydrogen, CO2 and depleted air streams exiting the various system reactors 100, 200, and/or, 300, respectively. In the process described herein, there may be a desire to generate pure oxygen. To generate this pure oxygen, at least part of the hydrogen may be utilized.
The residence time in each reactor is dependent upon the size and composition of individual oxygen carrying material particles, as would be familiar to one or ordinary skill in the art. For example, the residence time for a reactor comprising Fe based metal oxides may range from about 0.1 to about 20 hours.
In some embodiments, additional unwanted elements may be present in the system. Trace elements like Hg, As, Se are not expected to react with Fe2O3 at the high temperatures of the process. As a result they are expected to be present in the CO2 stream produced. If CO2 is to be used as a marketable product, these trace elements may be removed from the stream. Various cleanup units, such as mercury removal units are contemplated herein. Similar options will need to be exercised in case the CO2 stream is let out into the atmosphere, depending upon the rules and regulations existing at that time. If it is decided to sequester the CO2 for long term benign storage, e.g. in a deep geological formation, there may not be a need to remove these unwanted elements. Moreover, CO2 may be sequestered via mineral sequestration, which may be more desirable than geological storage, because it may be safer and more manageable.
Furthermore, sulfur may constitute an unwanted element, which must be accounted for in the system. In a solid fuel conversion embodiment, sulfur, which is present in coal, is expected to react with Fe2O3 and form FeS. This will be liberated on reaction with steam in the oxidation reactor 200 as H2S and will contaminate the hydrogen stream. During the condensation of water from this steam, most of this H2S will condense out. The remaining H2S can be removed using conventional techniques like amine scrubbing or high temperature removal using a Zn, Fe or a Cu based sorbent. Another method for removing sulfur would include the introduction of sorbents, for example, CaO, MgO, etc. Additionally, sorbents may be introduced into the reduction reactor 100 in order to remove the sulfur and to prevent its association with Fe. The sorbents may be removed from the system using ash separation device.
Although some embodiments of the present system are directed to producing hydrogen, it may be desirable for further treatment to produce ultra-high purity hydrogen. As would be familiar to one of ordinary skill in the art, some carbon or its derivatives may carry over from the reduction reactor 100 to the oxidation reactor 200 and contaminate the hydrogen stream. Depending upon the purity of the hydrogen required, it may be necessary to use a pressure swing adsorption (PSA) unit for hydrogen to achieve ultra high purities. The off gas from the PSA unit may comprise value as a fuel and may be recycled into the reduction reactor 100 along with coal, in solid fuel conversion embodiments, in order to improve the efficiency of hydrogen production in the system.
It should be understood that the while several of the embodiments of the systems described herein utilized an oxygen carrying material comprising an iron oxide, other oxygen carrying material may be used in the fuel conversion systems described herein.
Reduction Reactor Design
Direct conversion of solid fuels in the chemical looping process may be considered to occur in two stages, i.e. gaseous volatile conversion and non-volatile containing solid fuel conversion. In some embodiments, a packed moving bed configuration is used in the present system for the reduction reactor 100 in the systems of
As the gaseous volatiles are converted in the upper section of the reduction reactor 100, the remains of solid fuel may be converted with aid of oxygen carrying materials and oxidizing gases throughout the reduction reactor 100 or in certain regions of the reduction reactor 100. The oxidizing gases may prompt the conversion of remaining solid fuels and provide consequent reducing gases for reduction of metal oxides to lower their oxidation state. In some embodiments, fresh CO2 or H2O or recycled CO2/H2O stream from the outlet of the reduction reactor 100 may be used as the oxidizing agents, but O2 may also be an acceptable oxidizing gas for the promotion of solid fuel conversion. Reductive gases such as CO and H2 may be formed from the gasification of remains of solid fuel and may lead to the reduction of metal oxides.
In the packed moving bed configuration, the conversion strategy of remains of solid fuel is determined by the gas velocity conceived by the oxidizing gases mentioned above, reactor design, or the configuration of solid fuel injection in the reducer. A feature of the packed moving bed is to provide gas and oxygen carrying material particles in a counter-current contact pattern, and the flow pattern of solid fuel is decided in such way that enough residence time is provided for the conversion. The solid fuels may flow counter-currently or co-currently with respect to the flow of oxygen carrying materials.
Because the solid fuel conversion process evolves gases as they are converted, the gas velocity in the packed moving bed needs to be carefully regulated, in order to maintain the moving bed regime throughout the reduction reactor 100. One or more stage of taper-shape connections, which have a larger cross-sectional area on the upper section, may be utilized to reduce the gas velocity in the upper section where evolved gases flow towards. The number of stages for tapers and angle and height of tapers may be determined based on the solid fuel conversion expectancy and hydrodynamics of oxygen carrying materials and solid fuels. In some embodiments, the oxygen carrying material particle size prefers to be large enough such that they flow counter-currently with gases in the packed moving bed manner in the reduction reactor 100 and the oxidation reactor 200 and solids fluidization/entrainment is generally achievable and practical in the combustion reactor 300 and the solid conveying system 350, respectively. Another potential strategy is to withdraw a portion of the gas from intermediate section of the reactor. This gas may either be directly used as a fuel gas/chemical looping or separated and with the fuel portion recycled.
Referring now to
Referring now to
A series of fluidized beds may alternatively be used for the solid fuel conversion and/or H2 production, in the reduction reactor 100 and the oxidation reactor 200, respectively. In such a configuration, the preferred oxygen carrying material particle size range may be between about 50 and about 2,000 microns. Both oxygen carrying materials and solid fuel remains are fluidized by oxidizing inlet gas and intermediate and products gases from the reactions. In some configurations of multistage fluidized beds, the gases and oxygen carrying materials exchange oxygen counter-currently. Alternatively, the solid fuels and oxygen carrying materials may flow together co-currently and/or flow counter-currently in some embodiments.
In one embodiment, the co-current flow of a series of fluidized bed has inlets and outlets of solid fuels (if any) and oxygen carrying material that are identical, and the oxidizing gases are introduced into a first fluidized bed at the bottom of the series of fluidized beds, which takes solids input from a second fluidized bed above the first fluidized bed and produces a final output of solids. The resultant gases from the first fluidized bed may move into the second fluidized bed. The recycled oxygen carrying materials from the storage vessel are introduced into the upper most fluidized bed. Injection of solid fuels may be made at any of the fluidized beds. The interchanges of gases and solids reputably occur between each fluidized bed. In the co-current flow of series of fluidized bed, the oxygen carrying materials and solid fuels typically have similar properties of hydrodynamics. The oxygen carrying material and solid fuel particle sizes also prefer to be in the range where their simultaneous fluidization is achievable and practical in the reduction reactor 100 and/or the oxidation reactor 200.
In the counter-current flow of series of fluidized beds, where the solid fuels and oxygen carrying materials flow into the opposite direction of each other, the solid fuels may be entrained out from each fluidized bed along with gases, whereas the oxygen carrying materials may be continuously fluidized in each reactor before they are transported to the next ones. For this counter-current fluidized bed operation, the density and size of the oxygen carrying material particle needs to be suitable such that the fluidized regime is maintained in each fluidized reactor and solid fuels are small enough for the quick entrainment by gas for easy separation from the oxygen carrying materials.
Flow Regime
Now referring to
Now referring to
Now referring to
Referring to
Now referring to
Non-Mechanical Valve
The oxygen carrying materials in the chemical looping system may need to be transported from the reduction reactor 100 or oxidation reactor 200 to the combustion reactor 300 at regulated and desired flow rates. Because a conventional mechanical device such as table feeders or ball valves rely on the moving parts, operation cost may be expensive and the devices may be unreliable when they are applied in the chemical looping system where abrasive oxygen carrying materials and solid fuels are handled at elevated temperatures. Therefore, non-mechanical valves may be incorporated into the chemical looping systems disclosed herein at the combustion reactor inlet 400. The non-mechanical valve may transport the solids and be configured such as to prevent gas mixing between the reduction reactor 100 or the oxidation reactor 200 and the combustion reactor 300. As used herein, non-mechanical valve is any valve that does not rely on moving parts, other than for example a gas flow, in its operation. A non-mechanical valve may have a circuitous piping assembly.
Now referring to
The non-mechanical valve may be configured with a specific geometry, which may depend on the specification of the fuel conversion system.
Solid Flow Measurement System
In one embodiment, the fuel conversion systems disclosed herein may comprise a solids flow rate measurement device and may be positioned at the combustion reactor inlet stream 400. The solid flow measurement device may be coupled with a non-mechanical valve. In addition to the solid flow regulatory system, solids flow rate measurements may be installed to ensure the proper operation of the reactor system. It may be important to have knowledge of the oxygen carrying material circulation rate in the system in order to determine the stoichiometric balance between fuel feed and oxygen carrying material. Improper global solid circulation rate may result in solid agglomeration in the reduction reactor 100 and/or the oxidation reactor 200 and/or incomplete fuel conversion.
In one embodiment, the oxygen carrying material circulation is determined by using the characteristics of packed moving bed and low heat capacity of solids in the moving bed. A batch of cold particle may be added into the reactor through a lock-hopper system and the temperature trend of temperature measurement devices on the reactor wall may be monitored. In the given example in
In another embodiment, a solids flow rate measuring system may comprise a transport line with a transport window. The transport line may be located parallel to the main transport lines, such as between the solids separation device 600 and the solids storage vessel 700, and may ensure similar operational condition in the measuring device and the main reaction. The solids flow rate may be obtained from the solids flow rate in the measuring device multiplied by the area ratio between the cross-sections of the measuring line and the main transport line.
Design of Solid Fuel Injection System
No referring to
Now referring to
The reduction reactor may comprise a flow static mixer. As the mixture of two solids passes through the static mixer, mixing between solid fuels and oxygen carrying materials may be achieved. Different shapes of static mixer may be applied to achieve different degree of mixing.
Now referring to
Solids Separation System
In some embodiments, the reactor system is operated with relatively large particles, pellets, or agglomerates of oxygen carrying materials. In this embodiment, attrited/refused fines of oxygen carrying materials, byproduct of solid fuel and/or unconverted carbon may need to be separated since severe accumulations of byproduct of solid fuel, unconverted carbon and/or refused fine may cause oxygen carrying material deactivation and reactor plugage. During the continuous operation of the unit, all or portion of the fines, i.e. byproduct of solid fuel, unconverted carbon and refused oxygen carrying material powder, may need to be purged out from the system before the oxygen carrying materials re-enter the reduction reactor 100.
In some embodiments, entrained particles and gas from the riser 350 may by-pass the gas-solid separator 500. Alternatively, the riser 350 may be directly connected with the solids separator at a slanted angle. Inlet stream 520 may contain particles that need to be separated. For this embodiment, the solids separation system 600 is preferred to have much larger cross-sectional area compared to the solid conveying system 350, such as a riser, in order to avoid the entrainment of particles. As it is mentioned in the previous embodiment, separated particles in the outlet stream 610 and may be eligible to be reprocessed for recycle in the chemical looping system.
Additional aeration gas may be input from the bottom of the solid storage vessel 700, in order to separate fines from the primary oxygen carrying materials that passed the solids separation device 600 and are already settled in the solid storage vessel 700. A small gas outlet is installed at the top of the solid storage vessel 700 to eject the fluidized fines from the surface level of oxygen carrying materials.
Combustion Reactor and Riser Design
Pressure fluctuations occasionally occur in the chemical looping system mainly due to slugging effects of large particle size oxygen carrying materials experienced in the combustion reactor 300. The solid slugging in the combustion reactor 300 causes sudden loss/gain of solids inventory in storage vessel and sudden change in gas and solid flow.
Now referring to
In one embodiment, steam may be produced by recovering heat from the exothermic reaction in the combustion reactor 300 and/or the riser 350. In this embodiment, the heat in the combustion reactor 300 and/or the riser 350 may be transferred to steam generation resulting in a temperature decrease in combustion reactor 300 and/or the riser 350. Since the temperature decrease contracts the gas volume, the gas velocity may be lowered in the upper section of combustion reactor 300 and/or the riser 350. If the gas velocity in the riser is not sufficient to transport the particles back to the storage vessel, additional gas injection ports may be installed on various points of the riser 350.
It is noted that recitations herein of a component of the present disclosure being “configured” in a particular way, to embody a particular property, or function in a particular manner, are structural recitations, as opposed to recitations of intended use. More specifically, the references herein to the manner in which a component is “configured” denotes an existing physical condition of the component and, as such, is to be taken as a definite recitation of the structural characteristics of the component.
For the purposes of describing and defining the present invention it is noted that the term “substantially” is utilized herein to represent the inherent degree of uncertainty that may be attributed to any quantitative comparison, value, measurement, or other representation. The term “substantially” is also utilized herein to represent the degree by which a quantitative representation may vary from a stated reference without resulting in a change in the basic function of the subject matter at issue.
Having described the subject matter of the present disclosure in detail and by reference to specific embodiments thereof, it is noted that the various details disclosed herein should not be taken to imply that these details relate to elements that are essential components of the various embodiments described herein, even in cases where a particular element is illustrated in each of the drawings that accompany the present description. Rather, the claims appended hereto should be taken as the sole representation of the breadth of the present disclosure and the corresponding scope of the various embodiments described herein. Further, it will be apparent that modifications and variations are possible without departing from the scope of the appended claims. More specifically, although some aspects of the present disclosure are identified herein as preferred or particularly advantageous, it is contemplated that the present disclosure is not necessarily limited to these aspects.
This application claims benefit to U.S. Provisional Application Ser. No. 61/485,010, filed May 11, 2011, which is incorporated by reference herein in its entirety.
Filing Document | Filing Date | Country | Kind | 371c Date |
---|---|---|---|---|
PCT/US2012/037544 | 5/11/2012 | WO | 00 | 11/8/2013 |
Publishing Document | Publishing Date | Country | Kind |
---|---|---|---|
WO2012/155054 | 11/15/2012 | WO | A |
Number | Name | Date | Kind |
---|---|---|---|
971206 | Messerschmitt | Sep 1910 | A |
1078686 | Lane | Nov 1913 | A |
1658939 | Parsons | Feb 1928 | A |
2182747 | Marshall, Jr. | Dec 1939 | A |
2198560 | Marshall, Jr. | Apr 1940 | A |
2449635 | Barr | Sep 1948 | A |
2614067 | Reed et al. | Oct 1952 | A |
2635947 | Reed et al. | Apr 1953 | A |
2686819 | Johnson | Aug 1954 | A |
2694622 | Reed et al. | Nov 1954 | A |
2697686 | Leffer | Dec 1954 | A |
2899374 | Gomory | Aug 1959 | A |
3027238 | Watkins | Mar 1962 | A |
3031287 | Benson et al. | Apr 1962 | A |
3338667 | Pundsack | Aug 1967 | A |
3353925 | Baumann et al. | Nov 1967 | A |
3421869 | Benson | Jan 1969 | A |
3442613 | Grotz, Jr. | May 1969 | A |
3442619 | Huebler et al. | May 1969 | A |
3442620 | Huebler et al. | May 1969 | A |
3494858 | Luckenbach | Feb 1970 | A |
3523821 | Bryce et al. | Aug 1970 | A |
3573224 | Strelzoff et al. | Mar 1971 | A |
3619142 | Johnson et al. | Nov 1971 | A |
3726966 | Johnston | Apr 1973 | A |
4017270 | Funk et al. | Apr 1977 | A |
4057402 | Patel et al. | Nov 1977 | A |
4108732 | Nuttall, Jr. | Aug 1978 | A |
4272399 | Davis et al. | Jun 1981 | A |
4325833 | Scott | Apr 1982 | A |
4334959 | Green | Jun 1982 | A |
4343624 | Belke et al. | Aug 1982 | A |
4348487 | Goldstein et al. | Sep 1982 | A |
4404086 | Oltrogge | Sep 1983 | A |
4420332 | Mori et al. | Dec 1983 | A |
4521117 | Ouwerkerk et al. | Jun 1985 | A |
4778585 | Graff | Oct 1988 | A |
4842777 | Lamort | Jun 1989 | A |
4861165 | Fredriksson et al. | Aug 1989 | A |
4869207 | Engstrom et al. | Sep 1989 | A |
4902586 | Wertheim | Feb 1990 | A |
4895821 | Kainer et al. | Jun 1990 | A |
5130106 | Koves et al. | Jul 1992 | A |
5365560 | Tam | Nov 1994 | A |
5447024 | Ishida et al. | Sep 1995 | A |
5509362 | Lyon | Apr 1996 | A |
5518187 | Bruno et al. | May 1996 | A |
5529599 | Calderon | Jun 1996 | A |
5630368 | Wagoner | May 1997 | A |
5730763 | Manulescu et al. | Mar 1998 | A |
5770310 | Noguchi et al. | Jun 1998 | A |
5827496 | Lyon | Oct 1998 | A |
5858210 | Richardson | Jan 1999 | A |
6007699 | Cole | Dec 1999 | A |
6143203 | Zeng et al. | Nov 2000 | A |
6143253 | Radcliffe et al. | Nov 2000 | A |
6180354 | Singh et al. | Jan 2001 | B1 |
6187465 | Galloway | Feb 2001 | B1 |
6361757 | Shikada et al. | Mar 2002 | B1 |
6395944 | Griffiths | May 2002 | B1 |
6412559 | Gunter et al. | Jul 2002 | B1 |
6444712 | Janda | Sep 2002 | B1 |
6494153 | Lyon | Dec 2002 | B1 |
6509000 | Choudhary et al. | Jan 2003 | B1 |
6517631 | Bland | Feb 2003 | B1 |
6631698 | Hyppanen et al. | Oct 2003 | B1 |
6642174 | Gaffney et al. | Nov 2003 | B2 |
6663681 | Kindig et al. | Dec 2003 | B2 |
6667022 | Cole | Dec 2003 | B2 |
6669917 | Lyon | Dec 2003 | B2 |
6682714 | Kindig et al. | Jan 2004 | B2 |
6685754 | Kindig et al. | Feb 2004 | B2 |
6703343 | Park | Mar 2004 | B2 |
6797253 | Lyon | Sep 2004 | B2 |
6834623 | Cheng | Dec 2004 | B2 |
6875411 | Sanfilippo et al. | Apr 2005 | B2 |
6880635 | Vinegar et al. | Apr 2005 | B2 |
6936363 | Kordesch et al. | Aug 2005 | B2 |
7001579 | Metzger et al. | Feb 2006 | B2 |
7244399 | Myohanen et al. | Jul 2007 | B2 |
7404942 | Sanfilippo et al. | Jul 2008 | B2 |
7496450 | Ortiz Aleman et al. | Feb 2009 | B2 |
7749626 | Take | Jul 2010 | B2 |
7767191 | Thomas et al. | Aug 2010 | B2 |
7837975 | Iyer et al. | Nov 2010 | B2 |
7840053 | Liao | Nov 2010 | B2 |
8116430 | Shapiro et al. | Feb 2012 | B1 |
8192706 | Grochowski | Jun 2012 | B2 |
8202349 | Molaison | Jun 2012 | B2 |
8419813 | Hoteit et al. | Apr 2013 | B2 |
8435920 | White et al. | May 2013 | B2 |
8508238 | Mahalingam et al. | Aug 2013 | B2 |
8761943 | Lou et al. | Jun 2014 | B2 |
8771549 | Gauthier et al. | Jul 2014 | B2 |
8814963 | Apanel et al. | Aug 2014 | B2 |
8877147 | Fan et al. | Nov 2014 | B2 |
9376318 | Fan et al. | Jun 2016 | B2 |
9616403 | Fan et al. | Apr 2017 | B2 |
20010055559 | Sanfilippo et al. | Dec 2001 | A1 |
20020011428 | Scheuerman | Jan 2002 | A1 |
20020179887 | Zeng et al. | Dec 2002 | A1 |
20030006026 | Matsumoto et al. | Jan 2003 | A1 |
20030024388 | Scharpf | Feb 2003 | A1 |
20030031291 | Yamamoto et al. | Feb 2003 | A1 |
20030119658 | Allison et al. | Jun 2003 | A1 |
20030130360 | Kindig et al. | Jul 2003 | A1 |
20030180215 | Niu et al. | Sep 2003 | A1 |
20030188668 | Bland | Oct 2003 | A1 |
20040028181 | Charles, Jr. et al. | Feb 2004 | A1 |
20040030214 | Schindler et al. | Feb 2004 | A1 |
20040109800 | Pahlman et al. | Jun 2004 | A1 |
20040126293 | Geerlings et al. | Jul 2004 | A1 |
20040131531 | Geerlings et al. | Jul 2004 | A1 |
20040132833 | Espinoza et al. | Jul 2004 | A1 |
20040138060 | Rapier et al. | Jul 2004 | A1 |
20040152790 | Cornaro et al. | Aug 2004 | A1 |
20040154223 | Powell et al. | Aug 2004 | A1 |
20040197612 | Keefer et al. | Oct 2004 | A1 |
20040213705 | Blencoe et al. | Oct 2004 | A1 |
20040233191 | Mukherjee et al. | Nov 2004 | A1 |
20040244289 | Morozumi et al. | Dec 2004 | A1 |
20040265224 | Papavassiliou et al. | Dec 2004 | A1 |
20050002847 | Maroto-Valer et al. | Jan 2005 | A1 |
20050054880 | Dubois et al. | Mar 2005 | A1 |
20050175533 | Thomas et al. | Aug 2005 | A1 |
20050255037 | Otsuka et al. | Nov 2005 | A1 |
20050265912 | Alvarez, Jr. et al. | Dec 2005 | A1 |
20050274648 | Goldstein et al. | Dec 2005 | A1 |
20060021308 | Merkel | Feb 2006 | A1 |
20060042565 | Hu | Mar 2006 | A1 |
20060094593 | Beech, Jr. et al. | May 2006 | A1 |
20070010588 | Pearson | Jan 2007 | A1 |
20070049489 | Becue et al. | Mar 2007 | A1 |
20070157517 | Tsay et al. | Jul 2007 | A1 |
20070258878 | Sanfilippo et al. | Nov 2007 | A1 |
20080031809 | Norbeck et al. | Feb 2008 | A1 |
20080161624 | Glover et al. | Jul 2008 | A1 |
20080164443 | White et al. | Jul 2008 | A1 |
20080209807 | Tsangaris et al. | Sep 2008 | A1 |
20080314838 | Becker et al. | Dec 2008 | A1 |
20090000194 | Fan et al. | Jan 2009 | A1 |
20090042070 | Brown et al. | Feb 2009 | A1 |
20090160461 | Zangl et al. | Jun 2009 | A1 |
20100071262 | Robinson et al. | Mar 2010 | A1 |
20100184589 | Miyairi et al. | Jul 2010 | A1 |
20100187159 | Naunheimer | Jul 2010 | A1 |
20100258429 | Ugolin | Oct 2010 | A1 |
20100293845 | Zeman et al. | Nov 2010 | A1 |
20100332170 | Gao et al. | Dec 2010 | A1 |
20110005395 | Vimalchand et al. | Jan 2011 | A1 |
20110011720 | Rinker | Jan 2011 | A1 |
20110024687 | White et al. | Feb 2011 | A1 |
20110054049 | Lambert et al. | Mar 2011 | A1 |
20110094226 | McHugh et al. | Apr 2011 | A1 |
20110100274 | Kuske et al. | May 2011 | A1 |
20110146152 | Vimalchand et al. | Jun 2011 | A1 |
20110176968 | Fan et al. | Jul 2011 | A1 |
20110176988 | Okamura et al. | Jul 2011 | A1 |
20110206469 | Furuyama et al. | Aug 2011 | A1 |
20110289845 | Davis et al. | Dec 2011 | A1 |
20110291051 | Hershkowitz et al. | Dec 2011 | A1 |
20110300060 | Guillou et al. | Dec 2011 | A1 |
20110303875 | Hoteit et al. | Dec 2011 | A1 |
20120159841 | Fan et al. | Jun 2012 | A1 |
20120167585 | Wormser | Jul 2012 | A1 |
20120171588 | Fan et al. | Jul 2012 | A1 |
20120214106 | Sit et al. | Aug 2012 | A1 |
20130085365 | Marashdeh et al. | Apr 2013 | A1 |
20130149650 | Gauthier et al. | Jun 2013 | A1 |
20130255272 | Ajhar et al. | Oct 2013 | A1 |
20140034134 | Fan et al. | Feb 2014 | A1 |
20140144082 | Fan et al. | May 2014 | A1 |
20140275297 | Velazquez-Vargas et al. | Sep 2014 | A1 |
20140295361 | Fan et al. | Oct 2014 | A1 |
20150238915 | Fan et al. | Aug 2015 | A1 |
20160002034 | Fan et al. | Jan 2016 | A1 |
20160023190 | Fan et al. | Jan 2016 | A1 |
20160030904 | Fan et al. | Feb 2016 | A1 |
20160268616 | Fan et al. | Sep 2016 | A1 |
20160376512 | Fan et al. | Dec 2016 | A1 |
Number | Date | Country |
---|---|---|
1329761 | Jan 2001 | CN |
1454711 | Oct 2003 | CN |
1501534 | Jun 2004 | CN |
101389734 | Mar 2009 | CN |
101426885 | May 2009 | CN |
102187153 | Sep 2011 | CN |
102612625 | Jul 2012 | CN |
0161970 | Nov 1985 | EP |
1134187 | Sep 2001 | EP |
1138096 | Oct 2001 | EP |
1445018 | Aug 2004 | EP |
1580162 | Sep 2005 | EP |
1845579 | Oct 2007 | EP |
1933087 | Jun 2008 | EP |
2450420 | May 2012 | EP |
2515038 | Oct 2012 | EP |
2601443 | Jun 2013 | EP |
2924035 | May 2009 | FR |
H10249153 | Sep 1998 | JP |
2006-502957 | Jan 2006 | JP |
406055 | Sep 2000 | TW |
426728 | Mar 2001 | TW |
WO 199013773 | Nov 1990 | WO |
1999065097 | Dec 1999 | WO |
200022690 | Apr 2000 | WO |
WO 2000068339 | Nov 2000 | WO |
2001042132 | Jun 2001 | WO |
WO 2003070629 | Aug 2003 | WO |
2007082089 | Jul 2007 | WO |
2007122498 | Nov 2007 | WO |
WO 2007134075 | Nov 2007 | WO |
2008019079 | Feb 2008 | WO |
2008071215 | Jun 2008 | WO |
2008082312 | Jul 2008 | WO |
WO 2008115076 | Sep 2008 | WO |
WO 2009007200 | Jan 2009 | WO |
WO 2009009388 | Jan 2009 | WO |
2009021258 | Feb 2009 | WO |
WO 2009114309 | Sep 2009 | WO |
2010037011 | Apr 2010 | WO |
2010063923 | Jun 2010 | WO |
WO 2010126617 | Nov 2010 | WO |
WO 2011021161 | Feb 2011 | WO |
WO 2011031752 | Mar 2011 | WO |
WO 2011031755 | Mar 2011 | WO |
2011084734 | Jul 2011 | WO |
WO 2012064712 | May 2012 | WO |
WO 2012077978 | Jun 2012 | WO |
WO 2012155054 | Nov 2012 | WO |
WO 2012155059 | Nov 2012 | WO |
WO 2013040645 | Mar 2013 | WO |
WO 2014085243 | Jun 2014 | WO |
2011153568 | Dec 2014 | WO |
2014195904 | Dec 2014 | WO |
2016053941 | Apr 2016 | WO |
Entry |
---|
EP 0161970 A1—English machine translation. |
Fan et al., “Utilization of chemical looping strategy in coal gasification processes”, Particuology, vol. 6, pp. 131-142, 2008. |
Hildebrandt et al., “Producing Transportation Fuels with Less Work”, Science, vol. 323, pp. 1680-1681, Mar. 27, 2009. |
Kaiser et al., “Precombusion and Postcombustion Decarbonization”, IEEE, Power Engineering Review, pp. 15-17, Apr. 2001. |
Li et al., “Clean coal conversion process—progress and challenges”, Energy & Environmental Science, vol. 1, pp. 248-267, Jul. 11, 2008. |
Ockwig et al., “Membranes for Hydrogen Separation”, American Chemical Society, Chem. Rev., vol. 107, pp. 4078-4110, Oct. 10, 2007. |
European Search Report for Application No. 07716591.8 dated Mar. 6, 2012. |
International Search Report and Written Opinion for International Application No. PCT/US2007/000956 dated Dec. 4, 2007. |
International Preliminary Report on Patentability for International Application No. PCT/US2007/000956 dated Jul. 24, 2008. |
International Search Report and Written Opinion for International Application No. PCT/US2009/058579 dated Aug. 3, 2010. |
International Search Report and Written Opinion for International Application No. PCT/US2010/048121 dated Apr. 1, 2011. |
International Preliminary Report on Patentability for International Application No. PCT/US2010/048121 dated Mar. 22, 2012. |
International Search Report and Written Opinion for International Application No. PCT/US2011/059736 dated Mar. 27, 2012. |
International Preliminary Report on Patentability for International Application No. PCT/US2011/059736 dated May 23, 2013. |
International Search Report and Written Opinion for International Application No. PCT/US2012/37544 dated Aug. 10, 2012. |
International Preliminary Report on Patentability for International Application No. PCT/US2012/037544 dated Nov. 12, 2013. |
International Search Report and Written Opinion for International Application No. PCT/US2012/037557 dated Aug. 13, 2012. |
International Preliminary Report on Patentability for International Application No. PCT/US2012/037557 dated Nov. 21, 2013. |
Office Action pertaining to U.S. Appl. No. 12/160,803 dated Jun. 7, 2011. |
Final Rejection pertaining to U.S. Appl. No. 12/160,803 dated Jan. 5, 2012. |
Office Action pertaining to U.S. Appl. No. 12/160,803 dated Jun. 5, 2012. |
Final Rejection pertaining to U.S. Appl. No. 12/160,803 dated Mar. 22, 2013. |
Advisory Action pertaining to U.S. Appl. No. 12/160,803 dated Jul. 11, 2013. |
Examiner's Answer before the Patent Trial and Appeal Board for U.S. Appl. No. 12/160,803 dated Nov. 4, 2013. |
Office Action for Canadian Application No. 2636325 dated Dec. 5, 2012. |
Office Action for Chinese Patent Application No. 200780006757.X dated Apr. 11, 2011. |
Office Action for Chinese Patent Application No. 200780006757.X dated Dec. 8, 2011. |
Office Action for Chinese Patent Application No. 200780006757.X dated Jul. 4, 2012. |
Final Rejection for Chinese Patent Application No. 200780006757.X dated Feb. 1, 2013. |
Office Action for Chinese Patent Application No. 201110226206.2 dated Sep. 5, 2012. |
Office Action for Chinese Patent Application No. 201110226206.2 dated May 14, 2013. |
Office Action for Chinese Patent Application No. 201110226206.2 dated Sep. 18, 2013. |
Office Action pertaining to U.S. Appl. No. 13/121,009 dated Sep. 6, 2012. |
Final Rejection pertaining to U.S. Appl. No. 13/121,009 dated Mar. 14, 2013. |
Advisory Action pertaining to U.S. Appl. No. 13/121,009 dated Jun. 24, 2013. |
Office Action pertaining to U.S. Appl. No. 13/121,009 dated Sep. 13, 2013. |
Final Rejection pertaining to U.S. Appl. No. 13/121,009 dated Jan. 16, 2014. |
Office Action for Taiwanese Patent Application No. 098132745 dated Aug. 7, 2013. |
Office Action for Taiwanese Patent Application No. 098132745 dated Oct. 17, 2012. |
Office Action for Chinese Patent Application No. 200980141285.8 dated Feb. 26, 2013. |
Office Action for Chinese Patent Application No. 200980141285.8 dated Oct. 29, 2013. |
Office Action for Chinese Patent Application No. 201080048173.0 dated Nov. 18, 2013. |
Chinese Patent Office Action for Application No. 201280031083.X dated Feb. 24, 2016 (9 pages, English translation included). |
International Search Report and Written Opinion for Application No. PCT/US14/14877 dated May 14, 2014 (10 pages). |
International Search Report and Written Opinion for Application No. PCT/US14/25520 dated Jul. 11, 2014 (13 pages). |
International Search Report and Written Opinion for Application No. PCT/US14/26071 dated Jul. 10, 2014 (9 pages). |
International Search Report and Written Opinion for Application No. PCT/US2014/027839 dated Jul. 24, 2014 (9 pages). |
International Search Report and Written Opinion for Application No. PCT/US2014/028217 dated Jul. 28, 2014 (8 pages). |
International Search Report and Written Opinion for Application No. PCT/US2015/018123 dated May 8, 2015 (10 pages). |
Chinese Patent Office Action for Application No. 201280031083.X dated Aug. 8, 2014 (12 pages—English translated included). |
Chinese Patent Office Action for Application No. 201280031083.X dated Jun. 15, 2015 (10 pages, English translation included). |
Chinese Patent Office Action for Application No. 201080048130.2 dated Jul. 24, 2014 (6 pages, English translation only). |
Chinese Patent Office Action for Application No. 201080048130.2 dated Mar. 13, 2015 (4 pages, English translation only). |
Chinese Patent Office Action for Application No. 201080048173.0 dated Sep. 2, 2014 (3 pages, English translation only). |
Chinese Patent Office Action for Application No. 201080048173.0 dated Jan. 16, 2015 (14 pages, English translation included). |
United States Patent Office Action for U.S. Appl. No. 13/394,572 dated Apr. 9, 2014 (26 pages). |
United States Patent Office Action for U.S. Appl. No. 13/394,572 dated Aug. 26, 2014 (16 pages). |
United States Patent Office Action for U.S. Appl. No. 13/394,572 dated Dec. 30, 2014 (19 pages). |
United States Patent Office Action for U.S. Appl. No. 13/394,396 dated Dec. 18, 2014 (14 pages). |
United States Patent Office Final Rejection for U.S. Appl. No. 13/394,396 dated Jul. 2, 2015 (15 pages). |
United States Patent Office Action for U.S. Appl. No. 14/091,654 dated Oct. 30, 2014 (14 pages). |
United States Patent Office Action for U.S. Appl. No. 14/091,654 dated Jun. 12, 2015 (16 pages). |
United States Patent Office Notice of Allowance for U.S. Appl. No. 14/504,295 dated Sep. 28, 2015 (10 pages). |
United States Patent Office Notice of Allowance for U.S. Appl. No. 13/394,572 dated Dec. 14, 2015 (10 pages). |
United States Patent Office Action for U.S. Appl. No. 12/160,803 dated Feb. 23, 2016 (27 pages). |
United States Patent Office Action for U.S. Appl. No. 13/394,396 dated Jan. 15, 2016 (13 pages). |
United States Patent Office Action for U.S. Appl. No. 13/394,572 dated Oct. 13, 2015 (21 pages). |
United States Patent Office Notice of Allowance for U.S. Appl. No. 13/394,572 dated Feb. 22, 2016 (8 pages). |
United States Patent Office Action for U.S. Appl. No. 14/091,654 dated Jan. 4, 2016 (17 pages). |
Abad et al., “Chemical-looping combustion in a 300 W continuously operating reactor system using a manganese-based oxygen carrier,” Fuel, 2006, vol. 85, Issue 9, pp. 1174-1185. |
Abad et al., “Reduction Kinetics of Cu-, Ni-, and Fe-Based Oxygen Carriers Using Syngas (CO + H2) for Chemical-Looping Combustion,” Energy Fuels, 2007, 21 (4), pp. 1843-1853. |
Abad et al., “The use of iron oxide as oxygen carrier in a chemical-looping reactor,” Fuel, 2007, vol. 86, Issues 7-8, pp. 1021-1035. |
Adanez et al., “Progress in Chemical-Looping Combustion and Reforming technologies,” Progress in Energy and Combustion Science, 2012, vol. 38, Issue 2, pp. 215-282. |
Azis et al., “On the evaluation of synthetic and natural ilmenite using syngas as fuel in chemical-looping combustion (CLC),” Chemical Engineering Research and Design, 2010, vol. 88, Issue 11, pp. 1505-1514. |
Balasubramanian et al., “Hydrogen from methane in a single-step process,” Chem Engr Science, 1999, 54(15-16), 3543. |
Cao et al., “Investigation of Chemical Looping Combustion by Solid Fuels. 1. Process Analysis,” Energy Fuels, 2006, 20(5), pp. 1836-1844. |
De Diego et al., “Development of Cu-based oxygen carriers for chemical-looping combustion,” Fuel, 2004, vol. 83, Issue 13, pp. 1749-1757. |
Denton et al., “Simultaneous Production of High-Purity Hydrogen and Sequestration-Ready CO2 from Syngas,” 2003. |
Fan et al., “Chemical looping processes for CO2 capture and carbonaceous fuel conversion prospect and opportunity,” Energy Environmental Science, 2012, p. 7254-7280. |
Forero et al., “Syngas combustion in a 500 Wth Chemical-Looping Combustion system using an impregnated Cu-based oxygen carrier,” Fuel Processing Technology, 2009, vol. 90, Issue 12, pp. 1471-1479. |
Gao et al., “Production of syngas via autothermal reforming of methane in a fluidized-bed reactor over the combined CeO2—ZrO2/SiO2 supported Ni catalysts,” International Journal of Hydrogen Energy, 2008, vol. 33, p. 5493-5500. |
Garcia-Labiano et al., “Temperature variations in the oxygen carrier particles during their reduction and oxidation in a chemical-looping combustion system,” Chemical Engineering Science, 2005, vol. 60, No. 3, pp. 851-862. |
Ghanapragasam et al., “Hydrogen production from coal direct chemical looping and syngas chemical looping combustion systems: Assessment of system operation and resource requirements,” International Journal of Hydrogen Energy, 2009, vol. 34, Issue 6, pp. 2606-2615. |
Go et al., “Hydrogen production from two-step steam methane reforming in a fluidized bed reactor,” International Journal of Hydrogen Energy, 2009, vol. 34, p. 1301-1309. |
Hua et al., “Three Dimensional Analysis of Electrical Capacitance Tomography Sensing Fields,” 1999 IOP Publishing Ltd, vol. 10, pp. 717-725. |
Johansson et al., “Combustion of Syngas and Natural Gas in a 300 W Chemical-Looping Combustor,” Chemical Engineering Research and Design Volume, 2006, vol. 84, Issue 9, pp. 819-827. |
Leion et al., “Solid fuels in chemical-looping combustion using oxide scale and unprocessed iron ore as oxygen carriers,” Fuel, 2009, vol. 88, Issue 10, pp. 1945-1954. |
Leion et al., “Solid fuels in chemical-looping combustion,” International Journal of Greenhouse Gas Control, 2008, vol. 2, Issue 2, pp. 180-193. |
Leion et al., “The use of petroleum coke as fuel in chemical-looping combustion,” Fuel, 2007, vol. 86, Issue 12-13, pp. 1947-1958. |
Li et al., “Role of Metal Oxide Support in Redox Reactions of Iron Oxide for Chemical Looping Applications: Experiments and Density Functional Theory Calculations,” Energy Environmental Science, 2011, vol. 4, p. 3661-3667. |
Li et al., “Syngas chemical looping gasification process: Bench-scale studies and reactor simulations,” AICHE Journal, 2010, vol. 56, Issue 8, pp. 2186-2199. |
Li et al., “Syngas Chemical Looping Gasification Process: Oxygen Carrier Particle Selection and Performance,” Energy Fuels, 2009, 23(8), pp. 4182-4189. |
Lyngfelt, “Chemical Looping Combustion of Solid Fuels—Status of Development,” Applied Energy, 2014, vol. 113, p. 1869-1873. |
Lyngfelt, “Oxygen Carriers for Chemical Looping Combustion Operational Experience,” 1st International Conference on Chemical Looping, Mar. 2010. |
Mamman et al., “Simultaneous steam and CO2 reforming of methane to syngas over NiO/MgO/SA-5205 in presence and absence of oxygen,” Applied Catalysis A, 1998, vol. 168, p. 33-46. |
Marashdeh, Q. et al., “A Multimodal Tomography System Based on ECT Sensors,” IEEE Sensors Journal, vol. 7, No. 3, 2007, 426-433. |
Marashdeh, Q., Advances in Electrical Capacitance Tomography, Dissertation, The Ohio State University, 2006. |
Mattisson et al., “Chemical-looping combustion using syngas as fuel,” International Journal of Greenhouse Gas control, 2007, vol. 1, Issue 2, pp. 158-169. |
Mattisson et al., “CO 2 capture from coal combustion using chemical-looping combustion—Reactivity investigation of Fe, Ni and Mn based oxygen carriers using syngas,” Department of Energy and Environment, Division of Energy Technology and Department of Chemical and Biological Engineering, Division of Environmental Inorganic Chemistry, Chalmers University of Technology, 2007. |
Ortiz et al., “Hydrogen Production by Auto-Thermal Chemical-Looping Reforming in a Pressurized Fluidized Bed Reactor Using Ni-based Oxygen Carriers,” International Journal of Hydrogen Energy, 2010, vol. 35, p. 151-160. |
Pröll et al., “Syngas and a separate nitrogen/argon stream via chemical looping reforming—A 140 kW pilot plant study,” Fuel, 2010, vol. 89, Issue 6, pp. 1249-1256. |
Ruchenstein et al., “Carbon dioxide reforming of methane over nickel/alkaline earth metal oxide catalysts,” Applied Catalysis A, 1995, vol. 133, p. 149-161. |
Ryden et al., “Synthesis gas generation by chemical-looping reforming in a continuously operating laboratory reactor,” Fuel, 2006, vol. 85, p. 1631-1641. |
Scott et al., “In situ gasification of a solid fuel and CO2 separation using chemical looping,” AICHE Journal, 2006, vol. 52, Issue 9, pp. 3325-3328. |
Shen et al., “Experiments on chemical looping combustion of coal with a NiO based oxygen carrier,” Combustion and Flame, 2009, vol. 156, Issue 3, pp. 721-728. |
Sridhar et al., “Syngas Chemical Looping Process: Design and Construction of a 25 kWth Subpilot Unit,” Energy Fuels, 2012, 26(4), pp. 2292-2302. |
Tian et al., “Thermodynamic investigation into carbon deposition and sulfur evolution in a Ca-based chemical-looping combustion system,” Chemical Engineering Research & Design, 2011, vol. 89, Issue 9, p. 1524. |
Usachev et al., “Conversion of Hydrocarbons to Synthesis Gas: Problems and Prospects,” Petroleum Chemistry, 2011, vol. 51, p. 96-106. |
Warsito, W. et al., Electrical Capacitance Volume Tomography, 2007, pp. 1-9. |
Yamazaki et al., “Development of highly stable nickel catalyst for methane-steam reaction under low steam to carbon ratio,” Applied Catalyst A, 1996, vol. 136, p. 49-56. |
Zafar et al., “Integrated Hydrogen and Power Production with CO2 Capture Using Chemical-Looping ReformingRedox Reactivity of Particles of CuO, Mn2O3, NiO, and Fe2O3 Using SiO2 as a Support,” Ind. Eng. Chem. Res., 2005, 44(10), pp. 3485-3496. |
Annual Project Report as of Dec. 2001. |
Cho et al., “Comparison of iron-, nickel, copper- and manganese-based oxygen carriers for chemical-looping combustion”, Fuel, vol. 83, pp. 1215-1225, 2004. |
U.S. Department of Energy, NCCTI Energy Technologies Group, Office of Fossil Energy, “CO2 Capture and Storage in Geologic Formations”, pp. 34, Revised Jan. 8, 2002. |
Environmental Protection Agency, “Geological CO2 Sequestration Technology and Cost Analysis”, Technical Support Document, pp. i-vi & pp. 1-61, Jun. 2008. |
Geldart, “Types of Gas Fluidization”, Powder Technology, vol. 7, pp. 285-292, 1973. |
Haque, “Microwave energy for mineral treatment processes—a brief review”, International Journal of Mineral Processing, vol. 57, pp. 1-24, 1999. |
Hawley's Condensed Chemical Dictionary, entry for “ammonium bisulfate”, John Wiley & Sons, Inc. 2002. |
Hossain et al., “Chemical-looping combusion (CLC) for inherent CO2 separations—a review”, Chemical Engineering Science, vol. 63, pp. 4433-4451; 2008. |
Jin et al., “Development of a Novel Chemical-Looping Combustion: Synthesis of a Looping Material with a Double Metal Oxide of Co0—NiO”, Energy & Fuels, vol. 12, pp. 1272-1277, 1998. |
Huijgen et al., “Carbon dioxide sequestration by mineral carbonation”, ECN-C—03-016, www.ecn.nl/docs/library/report/200e/c03016.pdf, Feb. 2003. |
Jadhav et al., “Carbonation of Mg-Bearing Minerals: Kinetic and Mechanistic Studies”, Ohio Coal Research Consortium/Ohio State University Project C3.12, www.ohiocoal.org/projects/year3/c3.12, Jul. 3, 2002. |
Li et at., “Clean coal conversion processes—progress and challenges”, The Royal Society of Chemistry, Energy & Environmental Science, vol. 1, pp. 248-267, Jul. 30, 2008. |
Mattisson et al., “Applications of chemical-looping combustion with capture of CO2”, Second Nordic Minisymposium on Carbon Dioxide Capture and Storate, Goeteborg, pp. 46-51, Oct. 26, 2001. |
Mattisson et al., “Reactivity of Some Metal Oxides Supported on Alumina with Alternating Methane and Oxygen—Application for Chemical-Looping Combustion”, energy & Fuels, vol. 17, pp. 643-651, 2003. |
Mattisson et al., “The use of iron oxide as an oxygen carrier in chemical-looping combustion of methane with inherent separation of CO2”, Fuel, vol. 80, pp. 1953-1962, 2001. |
Mattisson et al., “Use of Ores and Industrial Products As Oxygen Carriers in Chemical-Looping Combustion”, Energy & Fuels, vol. 23, pp. 2307-2315, 2009. |
O'Connor et al., “Carbon Dioxide Sequestration by Direct Mineral Carbonation: Results from Recent Studies and Current Status”, Abstract, USDOE Office of Fossil Energy, 2001. |
Park et al., “CO2 Mineral Sequestration: Chemically Enhanced Aqueous Carbonation of Serpentine”, The Canadian Journal of Chemical Engineering, vol. 81, pp. 885-890, Jun.-Aug. 2003. |
Park et al., “CO2 Mineral Sequestration: physically activated dissolution of serpentine and pH swing process”, Chemical Engineering Science, vol. 59, pp. 5241-5247, 2004. |
Russo et al., “Impact of Process Design of on the Multiplicity Behavior of a Jacketed Exothermic CSTR”, AIChE Journal, vol. 41, No. 1, pp. 135-147, Jan. 1995. |
Shen et al, “Chemical-Looping Combustion of Biomass in a 10 kWth Reactor with Iron Oxide as an Oxygen Carrier”, Energy & Fuels, vol. 23, pp. 2498-2505, 2009. |
Steinfeld et al., “Design Aspects of Solar Thermochemical Engineering—A Case Study: Two-Step Water-Splitting Cycle Using the Fe3O4/FeO Redox System” Solar Energy, vol. 65, No. 1, pp. 43-53, 1999. |
Steinfeld, “Solar hydrogen production via a two-step water-splitting thermochemical cycle based on Zn/ZnO redox reactions”, International Journal of Hydrogen Energy, vol. 27, pp. 611-619, 2002. |
Vernon et al., “Partial Oxidation of Methane to Synthesis Gas”, Catalysis Letters, vol. 6, pp. 181-186, 1990. |
International Search Report and Written Opinion for International Application PCT/US2010/048125 dated Dec. 17, 2010. |
International Preliminary Report on Patentability for International Application PCT/US2010/048125 dated Mar. 22, 2012. |
Office Action for Chinese Patent Application No. 201080048130.2 dated Nov. 13, 2013. |
Herzog, “Carbon Sequestration via Mineral Carbonation: Overview and Assessment”, MIT Laboratory for Energy and the Environment, http://sequestration.mit.edu/pdf/carbonates.pdf, Mar. 14, 2002. |
Ohio Coal Development Office of the Ohio Air Quality Development Authority, “Ohio Coal Research Consortium (OCRC)—IV, Year 3 Proposals Solicitation”, http://www.ohioairquality.org/ocdo/other—pdf/Consortium—IV—Year—3—RFP.pdf. |
Adanez et al., “Selection of oxygen carriers for chemical-looping combustion,” Energy & Fuels, American Chemical Society, 2004, vol. 18, No. 2, pp. 371-377. |
European Patent Office Action for Application No. 12782631.1 dated Nov. 23, 2015 (8 pages). |
United States Patent Office Action for U.S. Appl. No. 15/162,199 dated Jun. 30, 2016 (10 pages). |
United States Patent Office Final Rejection for U.S. Appl. No. 15/162,199 dated Oct. 21, 2016 (9 pages). |
United States Patent Office Notice of Allowance for U.S. Appl. No. 13/394,396 dated Aug. 3, 2016 (8 pages). |
United States Patent Office Action for U.S. Appl. No. 14/116,627 dated Oct. 20, 2016 (6 Pages). |
United States Patent Office Notice of Allowance for U.S. Appl. No. 14/116,627 dated Mar. 10, 2017 (5 pages). |
United States Patent Office Action for U.S. Appl. No. 14/634,319 dated Nov. 7, 2016 (7 pages). |
United States Patent Office Notice of Allowance for U.S. Appl. No. 14/774,730 dated Nov. 16, 2016 (10 pages). |
United States Patent Office Action for U.S. Appl. No. 14/766,086 dated Jan. 13, 2017 (22 pages). |
United States Patent Office Action for U.S. Appl. No. 14/634,319 dated Apr. 11, 2017 (9 pages). |
United States Patent Office Action for U.S. Appl. No. 13/883,795 dated Jun. 20, 2016 (15 pages). |
Australian Patent Examination Report No. 1 for Application No. 2012253328 dated May 6, 2016 (3 pages). |
Bell et al., “H2 Production via Ammonia Decomposition Using Non-Noble Metal Catalysts: A Review,” Top Catal, 2016, 59, 1438-1457. |
Cheng et al., “Carbon Dioxide Adsorption and Activation on Ceria (110),” J. Chem. Phys. 2013, 138, 014702. |
Cheng et al., “Methane Adsorption and Dissociation on Iron Oxide Oxygen Carrier: Role of Oxygen Vacancy,” Phys. Chem. Chem. Phys. 2016, 18, 16423-16435. |
Cheng et al., “Propagation of Olefin Metathesis to Propene on WO3 Catalysts: A Mechanistic and Kinetic Study,” ACS Catal. 2015, 5, 59-72. |
Connell et al., “Process Simulation of Iron-Based Chemical Looping Schemes with CO2 Capture for Hydrogen and Electricity Production from Coal,” Presented at 29th Annual International Pittsburgh Coal Conference, Pittsburgh, PA, Oct. 15-18, 2012, pp. 1274-1281. |
De Klerk, “Gas-to-Liquid Conversion.” Natural Gas Conversion Technologies Workshop of ARPA-E. U.S. Department of Energy, Houston, TX. vol. 13 (2012). |
EIA—Independent Statistics and Analysis. U.S. Department of Energy, U.S. Energy Information Administration “Annual Energy Outlook 2015 with Projections to 2040,” Apr. 2015. |
EIA—Independent Statistics and Analysis. U.S. Department of Energy, U.S. Energy Information Administration, “How Much Petroleum Does the United States Import and from Where?” <https://www.eia.gov/tools/faqs/faq.php?id=727&t=6> webpage available as early as Mar. 22, 2017. |
EIA—Independent Statistics and Analysis. U.S. Department of Energy, U.S. Energy Information Administration, “Natural Gas Vented and Flared.” <https://www.eia.gov/dnav/ng/NG—PROD—SUM—A—EPG0—VGV—MMCF—A.htm> webpage available as early as Feb. 29, 2016. |
EIA—Independent Statistics and Analysis. U.S. Department of Energy, U.S. Energy Information Administration, “Natural Gas Weekly Update.” <https://www.eia.gov/naturalgas/weekly/> webpage available as early as Dec. 4, 2011. |
Fan et al., “Chemical-Looping Technology Platform,” AIChE Journal, 61(1), 2-22 (2015). |
Fan, “Chemical Looping Systems for Fossil Energy Conversions,” Wiley-AIChE: Hoboken, NJ, U.S.A.; 2010. |
Ishida et al., “Evaluation of a Chemical-Looping-Combustion Power-Generation System by Graphic Exergy Analysis,” Energy, 12(2), 147-154 (1987). |
Kathe et al., “Chemical Looping Gasification for Hydrogen Enhanced Syngas Production with in-situ CO2 Capture,” United States Department of Energy, OSTI: 1185194, (2015). |
Li et al., “Ionic Diffusion in the Oxidation of Iron-effect of Support and Its Implications to Chemical Looping Applications,” Energy Environ. Sci. 2011, 4, 876-880. |
Liu et al., “Enhanced Performance of Alkali Metal Doped Fe2O3 and Fe2O3/Al2O3 Composites as Oxygen Carrier Material in Chemical Looping Combustion,” Energy Fuels. 2013, 27, 4977-4983. |
Luo et al., “Shale Gas-to-Syngas Chemical Looping Process for Stable Shale Gas Conversion to High Purity Syngas with H2:CO Ratio of 2:1,” Energy and Environmental Science, 7(12), 4104-4117, (2014). |
Makepeace et. al., “Ammonia decomposition catalysis using non-stoichiometric lithium imide,” Chem. Sci., 2015, 6, 3805. |
Miller et al., “Toward Transformational Carbon Capture,” AIChE Journal, 62, 1-10 (2016). |
NETL, National Energy Technology Laboratory. U.S. Department of Energy, “Quality Guidelines for Energy System Studies—Specification for Selected Feedstocks.” Jan. 2012. |
Qin et al., “Evolution of Nanoscale Morphology in Single and Binary Metal Oxide Microparticles During Reduction and Oxidation Processes,” J. Mater. Chem. A. 2014, 2, 17511-17520. |
Qin et al., “Impact of 1% Lathanum Dopant on Carbonaceous Fuel Redox Reactions with an Iron-Based Oxygen Carrier in Chemical Looping Processes,” ACS Energy Letters, 2017, 2, 70-74. |
Qin et al., “Nanostructure Formation Mechanism and Ion Diffusion in Iron-Titanium Composite Materials with Chemical Looping Redox Reactions,” J. Mater. Chem. A. 2015, 3, 11302-11312. |
Quin et al., “Improved Cyclic redox reactivity of lanthanum modified iron-based oxygen carriers in carbon monoxide xhemical looping combustion,” Journal of Materials Chemistry A, 2017, 8 pages. |
Yin et. al., “A mini-review on ammonia decomposition catalysts for on-site generation of hydrogen for fuel cell applications,” Applied Catalysis A: General, 2004, 277, 1-9. |
International Search Report and Written Opinion for Application No. PCT/US2017/027241 dated Jul. 10, 2017 (11 pages). |
International Search Report and Written Opinion for Application No. PCT/US2017/034503 dated Aug. 15, 2017 (14 pages). |
United States Patent Office Action for U.S. Appl. No. 13/883,795 dated Jun. 23, 2017 (11 pages). |
United States Patent Office Notice of Allowance for U.S. Appl. No. 14/116,627 dated Jun. 14, 2017 (5 pages). |
United States Patent Office Action for U.S. Appl. No. 14/775,044 dated May 30, 2017 (15 pages). |
Velazquez-Vargas et al., “Atmospheric Iron-based Coal Direct Chemical Looping (CDCL) Process for Power Generation”, presented in Power-Gen International 2012, Orlando, FL, Dec. 11-13, 2012, BR-1892, 1-5. |
United States Patent Office Action for U.S. Appl. No. 14/766,086 dated Sep. 7, 2017 (19 pages). |
United States Patent Office Action for U.S. Appl. No. 14/774,727 dated Sep. 14, 2017 (10 pages). |
United States Patent Office Action for U.S. Appl. No. 14/766,086 dated Jan. 2, 2018 (21 pages). |
United States Patent Office Action for U.S. Appl. No. 15/191,249 dated Dec. 28, 2017 (14 pages). |
Number | Date | Country | |
---|---|---|---|
20140072917 A1 | Mar 2014 | US |
Number | Date | Country | |
---|---|---|---|
61485010 | May 2011 | US |