In many chemical processes an alkaline solution comprising, e.g., hydroxide ions and/or carbonate ions and/or bicarbonate ions is utilized to achieve a chemical reaction, e.g., to neutralize an acid, or buffer the pH of a solution, or precipitate an insoluble hydroxide and/or carbonate and/or bicarbonate from a solution. An alkaline solutions can be produced by an electrochemical system that converts an aqueous salt solution to the alkaline solution and an acid as described in the above-referenced US Provisional patent applications, herein incorporated by reference in their entirety. However, as the process is very energy intensive, a large amount of electrical energy is consumed; also, large amounts of salt and water are consumed. Consequently, lowering the energy and material consumed are very desirable.
This invention provides for a low-voltage, low-energy electrochemical system and method of producing an alkaline solution, comprising reducing water at the cathode to hydroxide ions and hydrogen gas, and allowing the hydroxide ions to migrate into the cathode electrolyte to produce the alkaline solution. By the system and method, at the anode, hydrogen gas is oxidized to protons without producing a gas at the anode, and the protons are allowed to migrate into the anode electrolyte or an adjacent electrolyte to produce an acid. In some embodiments, the alkaline solution further comprises bicarbonate ions and/or carbonate ions produced by adding carbon dioxide to the cathode electrolyte. In some embodiments, the alkaline solution is produced by applying less than 3V across the anode and cathode. In some embodiments, hydrogen gas produced at the cathode is recovered and directed to the anode where it is reduced to protons.
In some embodiments, an electrocatalyst is provided on the electrodes to catalyze the oxidation of hydrogen at the anode and catalyze the reduction of water to hydroxide ions and hydrogen gas at the cathode.
In some embodiments, a plurality of anodes and cathodes are arranged in series, or in parallel or in a cascading configuration to minimize the energy expended in producing the alkaline solution.
In one embodiment, the system comprises an electrochemical unit comprising an anode compartment comprising a hydrogen-oxidizing anode, a cathode compartment comprising a cathode, and a hydrogen-delivery system configured to deliver hydrogen gas to the anode, wherein the unit is operable connected to a carbon sequestration system configured to sequester carbon dioxide with the cathode electrolyte.
In another embodiment, the system comprises a hydrogen-oxidizing anode in communication with a cathode electrolyte; and a carbon sequestration system configured to sequester carbon dioxide with the cathode electrolyte.
In some embodiments of the system, the hydrogen gas oxidized at the anode is obtained from hydrogen gas generated at a cathode. In some embodiments, the cathode electrolyte comprises added carbon dioxide; in some embodiments, the carbon dioxide is contained in an industrial waste gas. In some embodiments, the cathode electrolyte comprises hydroxide ions and/or carbonate ions and/or bicarbonate ions.
In some embodiments, the system is configured to produce bicarbonate ions and/or carbonate ions and/or hydroxide ions in the cathode electrolyte; produce hydrogen gas at the cathode; and produce protons at the anode by applying less than 3V across the anode and cathode, without producing a gas at the anode.
In some embodiments, the anode and/or cathode comprise an electrocatalyst selected from platinum, a single-crystal nickel, Raney nickel, platinized nickel, a metal carbide (W2C, Pt—W2C), a platinum group metal alloy (Pt-M, where M=Fe, Mn, Cr, Co, Au), a transition metal, a nickel alloy, sintered nickel, a platinum group metals (Pt, Pd, Ru, Rh), gold, silver, a precious or non-precious chalcogenides, a discrete macrocyclic complexe of transition metals and biological complexes. In some embodiments, the electrocatalyst is configured on the anode to catalyze the oxidation of hydrogen gas to protons; and on the cathode to catalyze production of hydrogen gas and hydroxide ions.
In some embodiments, the system includes a carbon sequestration system configured to sequester carbon dioxide with the cathode electrolyte; in some embodiments, the carbon dioxide is contained in an industrial waste gas; in some embodiments, the carbon dioxide is sequestered as carbonates and/or bicarbonates comprising divalent cations, e.g., calcium ions and/or magnesium ions.
In some embodiments, the system is configured to produce an acid in the anode electrolyte; in some embodiments, the system includes an acid dissolution system configured to produce divalent cations with the acid; in some embodiments, the divalent cations comprise calcium ions and/or magnesium ions. In some embodiments, the divalent cations are produced by dissolving a mineral with the acid, and are provided to the carbon sequestration system.
In some embodiments, the system comprises a plurality of pairs of anodes and cathodes configured in series to receive a series current through each anode-cathode pair; in some embodiments, the system comprises a plurality of pairs of anodes and cathodes configured in parallel to receive a parallel voltage across each pair anode-cathode pair.
In some embodiments, the system comprises a plurality of pairs of anode electrolytes and cathode electrolytes wherein the cathode electrolyte of a first pair is connected to the cathode electrolyte of a second pair; and wherein the anode electrolyte of a first pair is connected to the anode electrolyte of a second pair. In some embodiments, the pH of the cathode electrolyte of the second pair is equal to or greater than the pH of the cathode electrolyte in the first pair; and the pH of the anode electrolyte of the second pair is equal to or less than the pH of the anode electrolyte of the first pair.
In some embodiments, the system comprises a plurality of pairs of anode electrolytes and cathode electrolytes wherein the cathode electrolyte and anode electrolyte of a second pair comprise cathode electrolyte from a first pair; and the cathode electrolyte and anode electrolyte of a third pair comprise anode electrolyte from the first pair. In some embodiments, the pH of the cathode electrolyte of the second pair is equal to or greater than pH of the cathode electrolyte of the first pair; and the pH of the anode electrolyte of the third pair is equal to or less that pH of the anode electrolyte of the first pair. In some embodiments, the cathode electrolyte of the second pair comprises diluted cathode electrolyte of the first pair; and the anode electrolyte of the third pair comprises diluted anode electrolyte of the first pair.
In another embodiment, the invention provides for a low-voltage, low energy method of producing an alkaline solution, comprising oxidizing hydrogen gas to protons at an anode without producing a gas at the anode; and producing bicarbonate ions in a cathode electrolyte in communication with the anode.
In another embodiment, the method comprises configuring an electrochemical unit comprising: an anode compartment comprising a hydrogen-oxidizing anode, a cathode compartment comprising a cathode, and a hydrogen-delivery system configured to deliver hydrogen gas to the anode, wherein the unit is operable connected to carbon sequestration system; and sequestering carbon dioxide with the cathode electrolyte.
In some embodiments of the method, the voltage applied across the anode and a cathode is less than 3V, and hydrogen gas oxidized at the anode is provided from hydrogen produced at the cathode.
In some embodiments, the method comprises adding carbon dioxide to the cathode electrolyte and producing hydroxide ions and/or carbonate ions and/or bicarbonate ions in the cathode electrolyte; in some embodiments, the carbon dioxide is contained in an industrial waste gas.
In some embodiments of the method, the anode and/or cathode comprises an electrocatalyst selected from platinum, a single-crystal nickel, Raney nickel, platinized nickel, a metal carbide (W2C, Pt—W2C), a platinum group metal alloy (Pt-M, where M=Fe, Mn, Cr, Co, Au), a transition metal, a nickel alloy, sintered nickel, a platinum group metals (Pt, Pd, Ru, Rh), gold, silver, a precious or non-precious chalcogenides, a discrete macrocyclic complexe of transition metals and biological complexes. In some embodiments, the electrocatalyst is configured to catalyze oxidation of hydrogen gas to protons at the anode, and catalyze production of hydrogen gas and hydroxide ions at the cathode.
In some embodiments, the method comprises configuring a carbon sequestration system to sequester carbon dioxide with the cathode electrolyte, wherein the carbon dioxide is contained in an industrial waste gas; in some embodiments, the carbon dioxide is sequestered as carbonates and/or bicarbonates; in some embodiment, the carbonates and/or bicarbonates comprise divalent cations; in some embodiments, the divalent cations comprise calcium ions and/or magnesium ions.
In some embodiments, the method comprises producing an acid in the anode electrolyte; and configuring an acid dissolution system to produce divalent cations with the acid. In some embodiments, the divalent cations comprise calcium ions and/or magnesium ions; and in some embodiments, the method comprises producing divalent cations by dissolving a mineral with the acid. In some embodiments, the method comprises configuring the acid dissolution system to provide divalent cations to the carbon sequestration system.
In some embodiments, the method comprises configuring a plurality of pairs of anodes and cathodes in series to receive a series current through each pair of anode and cathode. In some embodiments, the method comprises configuring a plurality of pairs of anodes and cathodes in parallel to receive a parallel voltage across each anode-cathode pair.
In some embodiments, the method comprises configuring a plurality of pairs of the anode electrolytes and cathode electrolytes whereby the cathode electrolyte of a first pair is connected to the cathode electrolyte of a second pair; and the anode electrolyte of a first pair is connected to the anode electrolyte of a second pair. In some embodiments, the method comprises adjusting the pH of the cathode electrolyte of the second pair to a value equal to or greater than the pH of the cathode electrolyte in the first pair; and adjusting the pH of the anode electrolyte of the second pair to a value equal to or less than the pH of the anode electrolyte of the first pair.
In some embodiments, the method comprises configuring a plurality of pairs of anode electrolytes and cathode electrolytes whereby the cathode electrolyte and anode electrolyte of a second pair comprise cathode electrolyte from a first pair; and the cathode electrolyte and anode electrolyte of a third pair comprise anode electrolyte from the first pair. In some embodiments, the method comprises adjusting the pH of the cathode electrolyte of the second pair to a value equal to or greater than pH of the cathode electrolyte of the first pair; and adjusting the pH of the anode electrolyte of the third pair to a value equal to or less that pH of the anode electrolyte of the first pair.
In various embodiments, the products comprise sodium hydroxide and/or sodium bicarbonate and/or sodium carbonate, hydrochloric acid and an ion-depleted brine from which certain cation and anions have been removed. In some embodiments, the products are utilized to sequester carbon dioxide and other constituents of industrial waste gases, e.g., sulfur gases, nitrogen oxide gases and other combustion gases, by contacting the waste gas with a solution comprising divalent cations and the hydroxide and/or bicarbonate and/or carbonate ions to precipitate divalent cation carbonates and/or bicarbonates as described in commonly assigned U.S. patent application Ser. No. 12/344,019 filed on Dec. 24, 2008, herein incorporated by reference in its entirety. The precipitates, comprising, e.g., calcium and/or magnesium carbonates and/or bicarbonates in various embodiments are utilized as building materials, e.g., as cements and aggregates, as described in commonly assigned U.S. patent application Ser. No. 12/126,776 filed on May 23, 2008, herein incorporated by reference in its entirety.
In another application, the ion-depleted brine from which certain cation and anions have been removed, e.g., sodium and chloride ions, is used as feed water in a desalination system where the ion-depleted is further processed as described in commonly assigned U.S. patent application Ser. No. 12/163,205 filed on Jun. 27, 2008, herein incorporated by reference in its entirety.
In another embodiment, the acid produced in the system and/or the alkaline solution produced in the cathode electrolyte are utilized to dissolve minerals and waste materials comprising divalent cations, e.g., Ca++ and Mg++ to produce divalent cation solutions for use in producing divalent metal ion carbonate precipitates using the cathode electrolyte herein. In various embodiments, the precipitates are used as building materials, e.g., cement and aggregates as described in commonly assigned U.S. patent application Ser. No. 12/126,776, herein incorporated by reference in its entirety.
Advantageously, with the present system and method, since a relatively low voltage is utilized across the anode and cathode to produce the alkaline solution, and since hydrogen gas generated at the cathode is oxidized to protons at the anode without producing a gas at the anode, a relatively low energy is utilized to produce the alkaline solution. Also, by the system and method, since carbon dioxide from industrial waste gases is utilized to produce the alkaline solution, the system and method is utilized to sequester large amounts of carbon dioxide and thus reduce carbon dioxide emissions into the atmosphere. Similarly, the acid produced is utilized in various ways including dissolving materials, e.g., minerals and biomass to produce cation for use in the system.
The following are brief descriptions of drawings that illustrate embodiments of the invention:
This invention provides for a low-voltage/low-energy system and method of producing an alkaline solution in an electrochemical system by oxidizing hydrogen at the anode to protons, and reducing water at the cathode to hydroxide ions and hydrogen at the cathode. In some embodiments, carbon dioxide is added to the cathode electrolyte to produce carbonate ions and/or bicarbonate ions in the cathode electrolyte; a gas is not produced at the anode. In some embodiments, an alkaline solution comprising, e.g., sodium hydroxide and/or sodium carbonate and/or sodium bicarbonate is produced in the cathode electrolyte by applying a voltage across the anode and cathode. In some embodiments, the volts is less than 3V.
In some embodiments, subterranean brine is utilized as a source of salt/cations/anions used in producing the alkaline solution. In some embodiments, electrocatalysts are provided on the electrodes to catalyze the oxidation of hydrogen at the anode and catalyze the production hydroxide ions and hydrogen gas at the cathode. In some embodiments, a plurality of anodes and cathodes are arranged in series, parallel and cascading configurations to minimize the energy expended in producing the alkaline solution. In some embodiments, a salt solution comprising, e.g., sodium chloride, is used to produce the alkaline solution.
In some embodiments, an acid, e.g., hydrochloric acid, is produced in the anode electrolyte from hydrogen ions, produced at the anode and migrated from the anode into the anode, and cations in the cations in the electrolyte, e.g., chloride ions.
In some embodiments, the acid is utilized to dissolve a material, e.g., a mineral, e.g., serpentine or olivine, to provide divalent cation solution, e.g., calcium and magnesium ions, which may in some embodiments be used with the alkaline solution to precipitate carbonates and/or bicarbonates derived from carbon dioxide in a waste gas stream, e.g., carbon dioxide in the exhaust gases of a fossil fuelled power generating plant or a cement producing plant. In some embodiments, sodium chloride solution is used as the anode electrolyte.
In some embodiments, on applying a voltage across the anode and cathode, cations, e.g., sodium ions in the anode electrolyte, migrate from the salt solution through a cation exchange membrane into the cathode electrolyte to produce an alkaline solution comprising, e.g., sodium hydroxide and/or sodium carbonate and/or sodium bicarbonate in the cathode electrolyte; concurrently, anions in the salt solution, e.g., chloride ions, migrate into the anode electrolyte to produce an acid, e.g., hydrochloric acid, with in the protons that form at the anode.
In some embodiments, hydrogen gas and hydroxide ions are produced at the cathode, and in some embodiments, some or all of the hydrogen gas produced at the cathode is directed to the anode where it is oxidized to produce hydrogen ions.
As can be appreciated by one ordinarily skilled in the art, since the embodiments herein can be configured with an alternative or equivalent salt, e.g., a potassium sulfate solution, to produce an equivalent alkaline solution, e.g., potassium hydroxide and/or potassium carbonate and/or potassium bicarbonate in the cathode electrolyte, and an alternative acid, e.g., sulfuric acid in the anode electrolyte, by applying the voltage herein across the anode and cathode, the invention is not limited to the exemplarary embodiments described herein, but is useable with an equivalent salt, e.g., potassium sulfate, to produce an alkaline solution in the cathode electrolyte, e.g., potassium carbonate and/or potassium bicarbonate and an acid, e.g., sulfuric acid in the anode electrolyte. Accordingly, to the extent that such equivalents are based on or are suggested by the embodiment herein, these equivalents are within the scope of the appended claims.
In the following detailed description, embodiments of the system and method are described with reference to the one or more illustrated Figures. However, it should be understood that this description is illustrative and is not restrictive since the invention is adaptable for use with other cell configurations including a one-cell, a two-cell, three-cell and other multi-cell configurations, not described in detail herein but are reasonably contemplated.
Similarly, it should be understood that although the invention is described with particularity with use of a brine comprising sodium ions and chloride ions, this description also is also illustrative and is not restrictive since the invention is adaptable for use with equivalent aqueous salt, e.g., sulfates and nitrates and like, e.g., potassium sulfate, as can be appreciated by those ordinarily skilled in the art.
With reference to
The carbon dioxide added to the cathode electrolyte may be obtained from various industrial sources that releases carbon dioxide including carbon dioxide from combustion gases of fossil fuelled power plants, e.g., conventional coal, oil and gas power plants, or IGCC (Integrated Gasification Combined Cycle) power plants that generate power by burning sygas; cement manufacturing plants that convert limestone to lime; ore processing plants; fermentation plants; and the like. In some embodiments, the carbon dioxide may comprise other gases, e.g., nitrogen, oxides of nitrogen (nitrous oxide, nitric oxide), sulfur and sulfur gases (sulfur dioxide, hydrogen sulfide), and vaporized materials.
In some embodiments, the system includes a gas treatment system that removes constituents in the carbon dioxide gas stream before the carbon dioxide is utilized in the cathode electrolyte. In some embodiments, a portion of, or the entire amount of, cathode electrolyte comprising bicarbonate ions and/or carbonate ions/and or hydroxide ions is withdrawn from the system and is contacted with carbon dioxide gas in an exogenous carbon dioxide gas/liquid contactor to increase the absorbed carbon dioxide content in the solution. In some embodiments, the solution enriched with carbon dioxide is returned to the cathode compartment; in other embodiments, the solution enriched with carbon dioxide is reacted with a solution comprising divalent cations to produce divalent cation hydroxides, carbonates and/or bicarbonates.
In some embodiments, the pH of the cathode electrolyte is adjusted upwards by hydroxide ions that migrate from the cathode, and/or downwards by dissolving carbon dioxide gas in the cathode electrolyte to produce carbonic acid and/or carbonate ions and/or bicarbonate ions that react with and remove hydroxide ions. Thus, it can be appreciated that the pH of the cathode electrolyte is determined, at least in part, by the balance of these processes.
Referring to
As is illustrated in
In some embodiments, the system is configurable to migrate anions, e.g., chloride ions, from the salt solution 118 to the anode electrolyte 104 through the anion exchange membrane 120; migrate cations, e.g., sodium ions from the salt solution 118 to the cathode electrolyte 108, 108A, 108B through the first cation exchange membrane 116; migrate protons from the anode 102 to the anode electrolyte 104; and migrate hydroxide ions from the cathode 106 to the cathode electrolyte 108, 108A, 108B. Thus, in some embodiments, the system can be configured to produce sodium hydroxide and/or sodium bicarbonate and/or sodium carbonate in the cathode electrolyte 108, 108A, 108B; and produce an acid e.g., hydrochloric acid 124 in the anode electrolyte.
In some embodiments as illustrated in
Thus, in some embodiments, on applying the present voltage across the anode and cathode, the system can be configured to produce hydroxide ions and hydrogen gas at the cathode 106; migrate hydroxide ions from the cathode into the cathode electrolyte 108, 108B, 108A; migrate cations from the salt solution 118 to the cathode electrolyte through the first cation exchange membrane 116; migrate chloride ions from the salt solution 118 to the anode electrolyte 104 through the anion exchange membrane 120; and migrate protons from the anode 102 to the anode electrolyte 104. Hence, depending on the salt solution 118 used, the system can be configured to produce an alkaline solution, e.g., sodium hydroxide in the cathode electrolyte.
In some embodiments, the system is operatively connected to a carbon dioxide gas/liquid contactor 128 configured to remove cathode electrolyte from the system and dissolve carbon dioxide in the cathode electrolyte in the gas/liquid contactor before the cathode electrolyte is returned to the system.
In other embodiments, the cathode electrolyte is operatively connected to a system (not shown) that is configured to precipitate divalent cation carbonates and/or divalent cation bicarbonates and/or divalent cation hydroxides from a solution comprising carbon dioxide gas and divalent cations.
In some embodiments, the catalyst may comprise platinum, ruthenium, iridium, rhodium, manganese, silver or alloys thereof. Suitable gas diffusion anodes are available commercially, e.g., from E-TEK (USA) and other suppliers.
In some embodiments of the anode as is illustrated in
As is illustrated in
With reference to
Referring to
Simultaneously at the cathode 106, the voltage across the anode and cathode will produce hydroxide ions and hydrogen gas at the cathode. In some embodiments, the hydrogen produced at the cathode is recovered and directed to the anode 102 where it is oxidized to protons. In the system, hydroxide ions produced at the cathode 106 will enter into the cathode electrolyte 108, 108A, 108B from where they will attempt to migrate to the anode 102 via the salt solution 118 between the cathode and anode. However, since the cathode electrolyte 108, 108A, 108B is separated from the salt solution electrolyte by the first cation exchange membrane 116 which will block the passage of anions, the first cation exchange membrane will block the migration of hydroxide ions from the cathode electrolyte to the salt solution; consequently, the hydroxide ions will accumulate in the cathode electrolyte 108, 108A, 108B.
In the system as illustrated in
With reference to
With reference to
With reference to
In an alternative as illustrated in
Referring to
With reference to
CO2+H2O<==>H2CO3<==>H++HCO3−<==>H++CO32−
In the system, as cathode electrolyte in the first cathode electrolyte portion 108A may mix with second cathode electrolyte portion 108B, the carbonic acid, bicarbonate and carbonate ions formed in the first cathode electrolyte portion 108A by absorption of carbon dioxide in the cathode electrolyte may migrate and equilibrate with cathode electrolyte in the second cathode electrolyte portion 108B. Thus, in some embodiments, first cathode electrolyte portion 108A may comprise dissolved and un-dissolved carbon dioxide gas, and/or carbonic acid, and/or bicarbonate ions and/or carbonate ions; while second cathode electrolyte portion 108B may comprise dissolved carbon dioxide, and/or carbonic acid, and/or bicarbonate ions and/or carbonate ions.
With reference to
2H2O+2e−═H2+2OH−
As cathode electrolyte in first cathode electrolyte portion 108A can intermix with cathode electrolyte in second cathode electrolyte portion 108B, hydroxide ions formed in the second cathode electrolyte portion may migrate and equilibrate with carbonate and bicarbonate ions in the first cathode electrolyte portion 108A. Thus, in some embodiments, the cathode electrolyte in the system may comprise hydroxide ions and dissolved and/or un-dissolved carbon dioxide gas, and/or carbonic acid, and/or bicarbonate ions and/or carbonate ions. In the system, as the solubility of carbon dioxide and the concentration of bicarbonate and carbonate ions in the cathode electrolyte are dependent on the pH of the electrolyte, the overall reaction in the cathode electrolyte 104 is either:
2H2O+2CO2+2e−═H2+2HCO3−; or Scenario 1:
H2O+CO2+2e−═H2+CO32− Scenario 2:
or a combination of both, depending on the pH of the cathode electrolyte. This is illustrated in as a arbonate speciation diagram in
For either scenario, the overall cell potential of the system can be determined through the Gibbs energy change of the reaction by the formula:
Ecell=−ΔG/nF
Or, at standard temperature and pressure conditions:
Eocell=−ΔGo/nF
where, Ecell is the cell voltage, ΔG is the Gibbs energy of reaction, n is the number of electrons transferred, and F is the Faraday constant (96485 J/Vmol). The Ecell of each of these reactions is pH dependent based on the Nernst equation as illustrated in
Also, for either scenario, the overall cell potential can be determined through the combination of Nernst equations for each half cell reaction:
E=Eo−RT ln(Q)/nF
where, Eo is the standard reduction potential, R is the universal gas constant, (8.314 J/mol K) T is the absolute temperature, n is the number of electrons involved in the half cell reaction, F is Faraday's constant (96485 J/V mol), and Q is the reaction quotient such that:
Etotal=Ecathode+Eanode.
When hydrogen is oxidized to protons at the anode as follows:
H2=2H++2e−,
Eo is 0.00 V, n is 2, and Q is the square of the activity of H+ so that:
Eanode+0.059 pHa,
where pHa is the pH of the anode electrolyte.
When water is reduced to hydroxide ions and hydrogen gas at the cathode as follows:
2H2O+2e−═H2+2OH−,
Eo is −0.83 V, n is 2, and Q is the square of the activity of OH− so that:
Ecathode=−0.059 pHc,
where pHc is the pH of the cathode electrolyte.
For either Scenario, the E for the cathode and anode reactions varies with the pH of the anode and cathode electrolytes. Thus, for Scenario 1 if the anode reaction, which is occurring in an acidic environment, is at a pH of 0, then the E of the reaction is 0V for the half cell reaction. For the cathode reaction, if the generation of bicarbonate ions occur at a pH of 7, then the theoretical E is 7×(−0.059 V)=−0.413V for the half cell reaction where a negative E means energy is needed to be input into the half cell or full cell for the reaction to proceed. Thus, if the anode pH is 0 and the cathode pH is 7 then the overall cell potential would be −0.413V, where:
Etotal=−0.059(pHa−pHc)=−0.059ΔpH.
For Scenario 2 in which carbonate ions are produced, if the anode pH is 0 and the cathode pH is 10, this would represent an E of 0.59 V.
Thus, in some embodiments, directing CO2 gas into the cathode electrolyte may lower the pH of the cathode electrolyte by producing bicarbonate ions and/or carbonate ions in the cathode electrolyte, which consequently may lower the voltage across the anode and cathode in producing hydroxide, carbonate and/or bicarbonate in the cathode electrolyte.
Thus, if the cathode electrolyte is allowed to increase to a pH of 14 or greater, the difference between the anode half-cell potential (represented as the thin dashed horizontal line, Scenario 1, above) and the cathode half cell potential (represented as the thick solid sloping line in Scenario 1, above) will increase to 0.83V. With increased duration of cell operation without CO2 addition or other intervention, e.g., diluting with water, the required cell potential will continue to increase. The cell potential may also increase due to ohmic resistance loses across the membranes in the electrolyte and the cell's overvoltage potential.
Herein, an overvoltage potential refers to the voltage difference between a thermodynamically determined half-cell reduction potential, and the experimentally observed potential at which the redox reaction occurs. The term is related to a cell voltage efficiency as the overvoltage potential requires more energy than is thermodynamically required to drive a reaction. In each case, the extra energy is lost as heat. Overvoltage potential is specific to each cell design and will vary between cells and operational conditions even for the same reaction.
In embodiments wherein it is desired to produce bicarbonate and/or carbonate ions in the cathode electrolyte, the system as illustrated in
In some embodiments, hydroxide ions and/or carbonate ions and/or bicarbonate ions produced in the cathode electrolyte, and hydrochloric acid produced in the anode electrolyte are removed from the system, while sodium chloride in the salt solution electrolyte is replenished to maintain continuous operation of the system. In some embodiments, the system can be configured to operate in various production modes including batch mode, semi-batch mode, continuous flow mode, with or without the option to withdraw portions of the hydroxide solution produced in the cathode electrolyte, or withdraw all or a portions of the acid produced in the anode electrolyte, or direct the hydrogen gas produced at the cathode to the anode where it may be oxidized.
In some embodiments, hydroxide ions and/or bicarbonate ions and/or carbonate ion solutions are produced in the cathode electrolyte when the voltage applied across the anode and cathode is less than 3V, 2.9V or less, 2.8V or less, 2.7V or less, 2.6V or less, 2.5V or less, 2.4V or less, 2.3V or less, 2.2V or less, 2.1V or less, 2.0V or less, 1.9V or less, 1.8V or less, 1.7V or less, 1.6V, or less 1.5V or less, 1.4V or less, 1.3V or less, 1.2V or less, 1.1V or less, 1.0V or less, 0.9V or less or less, 0.8V or less, 0.7V or less, 0.6V or less, 0.5V or less, 0.4V or less, 0.3V or less, 0.2V or less, or 0.1 V or less.
In another embodiment, the voltage across the anode and cathode can be adjusted such that gas will form at the anode, e.g., oxygen or chlorine, while hydroxide ions, carbonate ions and bicarbonate ions are produced in the cathode electrolyte and hydrogen gas is generated at the cathode. However, in this embodiment, hydrogen gas is not supplied to the anode. As can be appreciated by one ordinarily skilled in the art, in this embodiment, the voltage across the anode and cathode will be generally higher compared to the embodiment when a gas does not form at the anode.
With reference to
The ohmic resistance of the membranes will affect the voltage drop across the anode and cathode, e.g., as the ohmic resistance of the membranes increase, the voltage drop across the anode and cathode will increase, and vice versa. Membranes currently available can be used and they include membranes with relatively low ohmic resistance and relatively high ionic mobility; similarly, membranes currently available with relatively high hydration characteristics that increase with temperatures, and thus decreasing the ohmic resistance can be used. Consequently, as can be appreciated, by selecting currently available membranes with lower ohmic resistance, the voltage drop across the anode and cathode at a specified temperature can be lowered.
Scattered through currently available membrane are ionic channels consisting of acid groups. These ionic channels may extend from the internal surface of the matrix to the external surface and the acid groups may readily bind water in a reversible reaction as water-of-hydration. This binding of water as water-of-hydration follows first order reaction kinetics, such that the rate of reaction is proportional to temperature. Consequently, currently available membranes can be selected to provide a relatively low ohmic and ionic resistance while providing for improved strength and resistance in the system for a range of operating temperatures. Suitable membranes are commercially available from Asahi Kasei of Tokyo, Japan; or from Membrane International of Glen Rock, N.J., and USA.
In some embodiments, the cathode electrolyte 108, 108A, 108B is operatively connected to a waste gas treatment system (not illustrated) where the alkaline solution produced in the cathode electrolyte is utilized, e.g., to sequester carbon dioxide contained in the waste gas by contacting the waste gas and the cathode electrolyte with a solution of divalent cations to precipitate hydroxides and/or carbonates and/or bicarbonates as described in commonly assigned U.S. patent application Ser. No. 12/344,019 filed on Dec. 24, 2008, herein incorporated by reference in its entirety. The precipitates, comprising, e.g., calcium and magnesium hydroxides, carbonates and bicarbonates in some embodiments may be utilized as building materials, e.g., as cements and aggregates, as described in commonly assigned U.S. patent application Ser. No. 12/126,776 filed on May 23, 2008, supra, herein incorporated by reference in its entirety. In some embodiments, some or all of the carbonates and/or bicarbonates are allowed to remain in an aqueous medium, e.g., a slurry or a suspension, and are disposed of in an aqueous medium, e.g., in the ocean depths or a subterranean site.
In some embodiments, the cathode and anode are also operatively connected to an off-peak electrical power-supply system 114 that supplies off-peak voltage to the electrodes. Since the cost of off-peak power is lower than the cost of power supplied during peak power-supply times, the system can utilize off-peak power to produce an alkaline solution in the cathode electrolyte at a relatively lower cost.
In another embodiment, the system produces an acid, e.g., hydrochloric acid 124 in the anode electrolyte 104. In some embodiments, the anode compartment is operably connected to a system for dissolving minerals and/or waste materials comprising divalent cations to produce a solution of divalent cations, e.g., Ca++ and Mg++. In some embodiments, the divalent cation solution is utilized to precipitate hydroxides, carbonates and/or bicarbonates by contacting the divalent cation solution with the present alkaline solution and a source of carbon dioxide gas as described in U.S. patent application Ser. No. 12/344,019 filed on Dec. 24, 2008, supra, herein incorporated by reference in its entirety. In some embodiments, the precipitates are used as building materials e.g., cement and aggregates as described in commonly assigned U.S. patent application Ser. No. 12/126,776, supra, herein incorporated by reference in its entirety.
With reference to
H2=2H++2e− (anode, oxidation reaction)
2H2O+2e−═H2+2OH− (cathode, reduction reaction)
Since protons are formed at the anode from hydrogen gas provided to the anode; and since a gas such as oxygen does not form at the anode; and since water in the cathode electrolyte forms hydroxide ions and hydrogen gas at the cathode, the system will produce hydroxide ions in the cathode electrolyte and protons in the anode electrolyte when a voltage is applied across the anode and cathode. Further, as can be appreciated, in the present system since a gas does not form at the anode, the system will produce hydroxide ions in the cathode electrolyte and hydrogen gas at the cathode and hydrogen ions at the anode when less than 2V is applied across the anode and cathode, in contrast to the higher voltage that is required when a gas is generated at the anode, e.g., chlorine or oxygen. For example, in some embodiments, hydroxide ions are produced when less than 2.0V, 1.5V, 1.4V, 1.3V, 1.2V, 1.1V, 1.0V, 0.9V, 0.8V, 0.7V, 0.6V, 0.5V, 0.4V, 0.3V, 0.2V, 0.1 V or less is applied across the anode and cathode.
In the system, on applying a voltage across the anode 102 and cathode 106, the positively charged protons formed at the anode will attempt to migrate to the cathode through the anode electrolyte 104, while the negatively charged hydroxide ions formed at the cathode will attempt to migrate to the anode through the cathode electrolyte 108, 108A, 108B. As is illustrated in
In some embodiments, depending on the ionic species desired in cathode electrolyte 108, 108A, 108B and/or the anode electrolyte 104 and/or the salt solution 118, alternative reactants can be utilized. Thus, for example, if a potassium salt such as potassium hydroxide or potassium carbonate is desired in the cathode electrolyte 1108, 108A, 108B, then a potassium salt such as potassium chloride can be utilized in the salt solution 118. Similarly, if sulfuric acid is desired in the anode electrolyte, then a sulfate such as sodium sulfate can be utilized in the salt solution 118. As described in some embodiments herein, carbon dioxide gas is absorbed in the cathode electrolyte; however, it will be appreciated that other gases, including volatile vapors, can be absorbed in the electrolyte, e.g., sulfur dioxide, or organic vapors to produce a desired result. The gas can be added to the electrolyte in various ways, e.g., by bubbling it directly into the electrolyte, or dissolving the gas in a separate compartment connected to the cathode compartment and then directed to the cathode electrolyte as described herein.
With reference to
In some embodiments, hydroxide ions are formed at the cathode 106 and in the cathode electrolyte 108, 108A, 108B by applying a voltage of less than 2V across the anode and cathode without forming a gas at the anode, while providing hydrogen gas at the anode for oxidation at the anode. In some embodiments, method 300 does not form a gas at the anode when the voltage applied across the anode and cathode is less than 3V or less, 2.9V or less, 2.8V or less, 2.7V or less, 2.6V or less, 2.5V or less, 2.4V or less, 2.3V or less, 2.2V or less, 2.1V or less, 2.0V or less, 1.9V or less, 1.8V or less, 1.7V or less, 1.6V or less, 1.5V or less, 1.4V or less, 1.3V or less, 1.2V or less, 1.1V or less, 1.0V or less, 0.9V or less, 0.8V or less, 0.7V or less, 0.6V or less, 0.5V or less, 0.4V or less, 0.3V or less, 0.2V or less, or 0.1 V or less, while hydrogen gas is provided to the anode where it is oxidized to protons. As will be appreciated by one ordinarily skilled in the art, by not forming a gas at the anode and by providing hydrogen gas to the anode for oxidation at the anode, and by otherwise controlling the resistance in the system for example by decreasing the electrolyte path lengths and by selecting ionic membranes with low resistance and any other method know in the art, hydroxide ions can be produced in the cathode electrolyte with the present lower voltages.
In some embodiments, hydroxide ions, bicarbonate ions and carbonate ions are produced in the cathode electrolyte where the voltage applied across the anode and cathode is less than 3.0V, 2.9V, 2.8V, 2.7V, 2.6V, 2.5V, 2.4V, 2.3V, 2.2V, 2.1V, 2.0V, 1.9V, 1.8V, 1.7V, 1.6V, 1.5V, 1.4V, 1.3V, 1.2V, 1.1V, 1.0V, 0.9V, 0.8V, 0.7V, 0.6V, 0.5V, 0.4V, 0.3V, 0.2V, 0.1V or less without forming a gas at the anode. In some embodiments, the method is adapted to withdraw and replenish at least a portion of the cathode electrolyte and the acid in the anode electrolyte back into the system in either a batch, semi-batch or continuous mode of operation.
With reference to
In systems as illustrated in
In certain embodiments as illustrated in
In certain embodiments, the first cation exchange membrane 116 is selected to allow passage of cations therethrough while restricting passage of anions therethrough. Thus, as is illustrated in
As is illustrated in
Concurrently, in the anode electrolyte 104, an acid, e.g., hydrochloric acid is produced from hydrogen ions migrating from the anode 102 and anions, e.g., chloride ions, present from the anode electrolyte.
As is illustrated in
Thus, in the embodiment of
Also, in the embodiment as illustrated in
In some embodiments, cation exchange membranes 116 and 122 are conventional and are available from, for example, Asahi Kasei of Tokyo, Japan; or from Membrane International of Glen Rock, N.J., or DuPont, in the USA. However, it will be appreciated that in some embodiments, depending on the need to restrict or allow migration of a specific cation or an anion species between the electrolytes, a cation exchange membrane that is more restrictive and thus allows migration of one species of cations while restricting the migration of another species of cations may be used as, e.g., a cation exchange membrane that allows migration of sodium ions into the cathode electrolyte from the anode electrolyte while restricting migration of hydrogen ions from the anode electrolyte into the cathode electrolyte, may be used. Such restrictive cation exchange membranes are commercially available and can be selected by one ordinarily skilled in the art.
As is illustrated in
With reference to
Although carbon dioxide is present in ordinary ambient air, partly due to the very low concentration, ambient carbon dioxide may not provide sufficient carbon dioxide to achieve the results obtained with the present system and method that utilize carbon dioxide taken from an industrial waste gas steam, e.g., from the stack gases of a fossil fuelled power generating plant or a cement production plant. Also, in some embodiments of the system and method, since the cathode electrolyte is contained in closed system wherein the pressure of the added carbon dioxide gas within the system is greater than the ambient atmospheric pressure, ambient air and hence ambient carbon dioxide is typically prevented from infiltrating into the cathode electrolyte.
In some embodiments, and with reference to
Similarly, in some embodiments of the system, the pH of the anode electrolyte is adjusted and is maintained between less than 0 and up to 7 and/or between less than 0 and up to 4, by regulating the concentration of hydrogen ions that migrate into the anode electrolyte from oxidation of hydrogen gas at the anode, and/or the withdrawal and replenishment of anode electrolyte in the system. In this regard and as can be appreciated by one ordinarily skilled in the art and with reference to
With reference to
With reference to
In the some embodiments, the mineral dissolution system is operatively connected to nano-filtration system that is configured to separate sodium ions and chloride ions from the mineral solution comprising, e.g., calcium ions, magnesium ions, silica, hydrochloric acid and/or sodium hydroxide. In some embodiments, the nano-filtration system 910 is configured with a reverse osmosis system that is capable of concentrating sodium ions and chloride ions into a salt solution that is used as the anode electrolyte 104.
With reference to
In some embodiments of the method, the anode 102 is in contact with a second cation exchange membrane 122 that separates the anode from the anode electrolyte; the alkaline solution 108 comprises hydroxide ions and/or bicarbonate ions and/or carbonate ions; the carbon dioxide 107 is contained in wastes gases of an industrial plant, e.g., an electrical power generating plant, a cement production plant, a fermentation process or an ore processing facility.
In some embodiments, ambient air is excluded the cathode electrolyte 108; a pH of between and 7 and 14 or greater is maintained in the cathode electrolyte; a pH of between 7 and 9 is maintained in the cathode electrolyte; a pH of between 8 and 11 is maintained in the cathode electrolyte; a pH of from less than 0 and up to 7 is maintained in the anode electrolyte; a pH of from less than 0 and up to 4 is maintained in the anode electrolyte; hydrogen gas is oxidized at the anode 102 to produce hydrogen ions and hydrogen ions are migrated from the anode through the second cation exchange membrane 122 into the anode electrolyte; hydroxide ions and hydrogen gas are produced at the cathode 106; hydroxide ions are migrated from the cathode 106 into the cathode electrolyte 108; hydrogen gas is directed from the cathode 106 to the anode 102; cations ions are migrated from the anode electrolyte 104 through the first cation exchange membrane 122 into the cathode electrolyte 108 wherein the cations comprise sodium ions.
In some embodiments, the method comprises producing sodium hydroxide and/or sodium carbonate ions and/or sodium bicarbonate ions in the cathode electrolyte 108; producing an acid and a depleted salt solution in the anode electrolyte 104 comprising sodium ions and chloride ions; utilizing the anode electrolyte to dissolve minerals and produce a mineral solution comprising calcium ions and/or magnesium ions, wherein the minerals comprises mafic minerals; filtering the mineral solution to produce a filtrate comprising sodium ions and chloride ions; concentrating the filtrate to produce the salt solution, wherein the concentrator comprises a reverse osmosis system; utilizing the salt solution as the anode electrolyte 104; precipitating a carbonate and/or bicarbonate with the cathode electrolyte; wherein the carbonate and/or bicarbonate comprises calcium and/or magnesium carbonate and/or bicarbonate. In some embodiments, the method includes disposing of the acid in an underground storage site where the acid can be stored in an un-reactive salt or rock formation without environmental acidification.
With reference to
With reference to
In some embodiments, the alkaline solution is produced in the cathode electrolyte and comprises hydroxide ions (from the cathode) and/or bicarbonate ions and/or carbonate ions from added carbon dioxide. In some embodiments, the hydrogen generated at the cathode is recovered and oxidized at the anode. In various embodiments, the redox reaction at the anode and cathode are catalyzed by electrocatalysts.
With reference to
In some embodiments of the system, hydrogen gas to the anode is provided from hydrogen gas generated at a cathode in contact with the cathode electrolyte; the cathode electrolyte comprises added carbon dioxide; the cathode electrolyte comprises hydroxide ions and/or bicarbonate ions and/or carbonate ions; the bicarbonate ions and/or carbonate ions and/or hydroxide ions, hydrogen gas at the cathode, and the protons at the anode are produced by a voltage applied across the anode and cathode, without producing a gas at the anode; and the voltage is less than 3V.
In some embodiment of the system, and with reference to
As noted above, in various embodiments, the present anode comprises electrocatalyst material that catalyzes the oxidation of hydrogen gas at the anode without allowing for formation of a gas, e.g., chlorine or oxygen from the electrolyte in contact with the anode. In various embodiments, suitable electrocatalyst material include: platinum, single-crystal nickel, Raney nickel, platinized nickel, metal carbides (including W2C, Pt—W2C), platinum group metal alloys (including Pt-M, where M=Fe, Mn, Cr, Co, Au and other elements), transition metals, nickel alloys and sintered nickel, platinum group metals (including Pt, Pd, Ru, Rh and mono, bi and ternary combinations), gold, and silver, precious and non-precious chalcogenides, discrete macrocyclic complexes of transition metals and biological complexes. Optionally, these materials can also be used as electrocatalysts at the cathode.
In various embodiments, rather that forming the anode entirely of the electrocatalysts material, a relatively small amount of the electrocatalyst material is used. Thus as is illustrated in illustrated in
With reference to
As is illustrated in
In some embodiments, the system comprises a carbon sequestration system (not shown) configured to sequester carbon dioxide with the cathode electrolyte; in some embodiments, the carbon dioxide is contained in an industrial waste gas; in some embodiments, the carbon dioxide is sequestered as carbonates and/or bicarbonates comprising divalent cations e.g., calcium ions and/or magnesium ions.
In some embodiments, the system comprises an acid 124 in the anode electrolyte 104; in some embodiments, the system comprises an acid dissolution system configured to produce divalent cations e.g., calcium ions and magnesium ions with the acid; in some system the divalent cations are produced by dissolving a mineral with the acid, and the divalent cations are provided to the carbon sequestration system.
With reference
In some embodiments of the system 1500 as illustrated in
In some embodiments of the system as illustrated in
With reference to the system 1700 as illustrated in
With reference to
In some embodiments, the method comprises applying a voltage across the anode and a cathode in contact with the cathode electrolyte, e.g. a voltage of less than 3V, and producing hydrogen gas at the cathode. In some embodiments, the method comprises configuring a hydrogen delivery system to provide the hydrogen gas to the anode from hydrogen gas produced at the cathode, and adding carbon dioxide to the cathode electrolyte. In some embodiments, the method comprises comprising producing hydroxide ions and/or carbonate ions and/or bicarbonate ions in the cathode electrolyte.
In some embodiments of the method, the anode and/or cathode comprises an electrocatalyst selected from platinum, a single-crystal nickel, Raney nickel, platinized nickel, a metal carbide (W2C, Pt—W2C), a platinum group metal alloy (Pt-M, where M=Fe, Mn, Cr, Co, Au), a transition metal, a nickel alloy, sintered nickel, a platinum group metals (Pt, Pd, Ru, Rh), gold, silver, a precious or non-precious chalcogenides, a discrete macrocyclic complex of transition metals and biological complexes. In some embodiments, the electrocatalyst is configured to catalyze the oxidation of hydrogen gas to protons at the anode, and catalyze production of hydrogen gas and hydroxide ions at the cathode.
In some embodiments, the method comprises sequestering carbon dioxide with the cathode electrolyte, wherein the carbon dioxide is contained in an industrial waste gas, and wherein the carbon dioxide is sequestered as carbonates and/or bicarbonates, e.g., as carbonates and/or bicarbonates comprising divalent cations such as calcium ions and/or magnesium ions.
In some embodiments, the method comprises producing an acid in the anode electrolyte, and configuring an acid dissolution system to produce divalent cations with the acid, e.g., produce calcium ions and/or magnesium ions by dissolving a mineral with the acid. In some embodiments, the acid dissolution system is configured to provide divalent cations to the carbon sequestration system.
In some embodiments of the method, and with reference to the system 1300 of
In some embodiments is illustrated in the system of
In some embodiments of the method, and with reference to the system 1500 of
In some embodiments of the method and with reference to the
In another embodiment, and with reference to
In an exemplary embodiment, a system configured substantially as illustrated in
As is illustrated in Table 1, a range of current densities was achieved across the electrode in the system. As can be appreciated, the current density that can be achieved with other configurations of the system may vary, depending on several factors including the cumulative electrical resistance losses in the cell, environmental test conditions, the over-potential associated with the anodic and cathodic reactions, and other factors.
The current densities achieved in the present configuration and as set forth in Table 1 are correlated with the production of hydroxide ions at the cathode, and thus correlates with the production of sodium hydroxide and/or sodium carbonate and/or sodium bicarbonate in the cathode electrolyte, as follows. With reference to Table 1, at 75° C., 0.8 V and a pH of 10, each cm2 of electrode passed 13.3 mA of current, where current is a measure of charge passed (Coulomb) per time (second). Based on Faraday's Laws, the amount of product, e.g., hydroxide ions, produced at an electrode is proportional to the total electrical charge passed through the electrode as follows:
n=(I*t)/(F*z)
where n is moles of product, I is a current, t is time, F is Faraday's constant, and z is the electrons transferred per product ionic species (or reagent ionic species). Thus, based on the present example, 1.38×10−4 moles of hydroxide ions are produced per second per cm2 of electrode, which is correlated with the production of sodium hydroxide in the cathode electrolyte. In the system the production rate of NaOH dictates the production rate of NaHCO3 and Na2CO3 through Le Chatelier's principle following the net chemical equilibria equations of
H2CO3+OH−═H2O+HCO3−
and HCO3−+OH−═H2O+CO32−,
where an increase in concentration of one species in equilibria will change the concentration of all species so that the equilibrium product maintains the equilibrium constant. Thus, in the system, the equilibrium concentrations of H2CO3, HCO3−, and CO32− vs. pH in the electrolyte will follow the carbonate speciation diagram as discussed above.
In the system as illustrated in
In another embodiment, the system and method are integrated with a carbonate and/or bicarbonate precipitation system (not illustrated) wherein a solution of divalent cations, when added to the present cathode electrolyte, causes formation of precipitates of divalent carbonate and/or bicarbonate compounds, e.g., calcium carbonate or magnesium carbonate and/or their bicarbonates. In some embodiments, the precipitated divalent carbonate and/or bicarbonate compounds may be utilized as building materials, e.g., cements and aggregates as described for example in commonly assigned U.S. patent application Ser. No. 12/126,776 filed on May 23, 2008, herein incorporated by reference in its entirety.
In an alternative embodiment, the system and method are integrated with a mineral and/or material dissolution and recovery system (not illustrated) wherein the acidic anode electrolyte solution 104 or the basic cathode electrolyte 108 is utilized to dissolve calcium and/or magnesium-rich minerals e.g., serpentine or olivine, or waste materials, e.g., fly ash, red mud and the like, to form divalent cation solutions that may be utilized, e.g., to precipitate carbonates and/or bicarbonates as described herein. In some embodiments, the precipitated divalent carbonate and/or bicarbonate compounds may be utilized as building materials, e.g., cements and aggregates as described for example in commonly assigned U.S. patent application Ser. No. 12/126,776 filed on May 23, 2008, herein incorporated by reference in its entirety.
In an alternative embodiment, the system and method are integrated with an industrial waste gas treatment system (not illustrated) for sequestering carbon dioxide and other constituents of industrial waste gases, e.g., sulfur gases, nitrogen oxide gases, metal and particulates, wherein by contacting the flue gas with a solution comprising divalent cations and the present cathode electrolyte comprising hydroxide, bicarbonate and/or carbonate ions, divalent cation carbonates and/or bicarbonates are precipitated as described in commonly assigned U.S. patent application Ser. No. 12/344,019 filed on Dec. 24, 2008, herein incorporated by reference in its entirety. The precipitates, comprising, e.g., calcium and/or magnesium carbonates and bicarbonates in some embodiments may be utilized as building materials, e.g., as cements and aggregates, as described in commonly assigned U.S. patent application Ser. No. 12/126,776 filed on May 23, 2008, herein incorporated by reference in its entirety.
In another embodiment, the system and method are integrated with an aqueous desalination system (not illustrated) wherein the partially desalinated water of the third electrolyte of the present system is used as feed-water for the desalination system, as described in commonly assigned U.S. patent application Ser. No. 12/163,205 filed on Jun. 27, 2008, herein incorporated by reference in its entirety.
In an alternative embodiment, the system and method are integrated with a carbonate and/or bicarbonate solution disposal system (not illustrated) wherein, rather than producing precipitates by contacting a solution of divalent cations with the first electrolyte solution to form precipitates, the system produces a solution, slurry or suspension comprising carbonates and/or bicarbonates. In some embodiments, the solution, slurry or suspension is disposed of in a location where it is held stable for an extended periods of time, e.g., the solution/slurry/suspension is disposed in an ocean at a depth where the temperature and pressure are sufficient to keep the slurry stable indefinitely, as described in U.S. patent application Ser. No. 12/344,019 filed on Dec. 24, 2008, herein incorporated by reference in its entirety; or in a subterranean site.
This application is a divisional of U.S. patent application Ser. No. 12/991,898, filed Dec. 15, 2010, which is a National stage application under 35 U.S.C. 371 of PCT/US2010/023783 which claims priority to U.S. Provisional Application No. 61/151,472 filed Feb. 10, 2009 and titled “Low Voltage Electrochemical Hydroxide with Circulating Hydrogen Gas”; U.S. Provisional Application No. 61/151,484 filed Feb. 10, 2009 and titled “Electrocatalyst Electrodes for Low-voltage Electrochemical Hydroxide System”; and U.S. Provisional Application No. 61/151,481 filed Feb. 10, 2009 and titled “Low-voltage Electrochemical Hydroxide Cell Stacking System”, all herein fully incorporated by reference in their entirety.
Number | Name | Date | Kind |
---|---|---|---|
1169766 | Brassert | Feb 1916 | A |
1172930 | Brassert et al. | Feb 1916 | A |
1176747 | Ferguson | Mar 1916 | A |
1493579 | Walter | May 1924 | A |
1543942 | Mathesius | Jun 1925 | A |
1655171 | Wagner | Jan 1928 | A |
1678345 | Mattison | Jul 1928 | A |
1759361 | Miller | May 1930 | A |
1785365 | Seil | Dec 1930 | A |
1823269 | Grilli | Sep 1931 | A |
1865833 | Chesny | Jul 1932 | A |
1897725 | Gaus et al. | Feb 1933 | A |
1924503 | Lambert | Aug 1933 | A |
1986736 | Mauthe et al. | Jan 1935 | A |
2006295 | Chewning et al. | Jun 1935 | A |
2054315 | Ebner et al. | Sep 1936 | A |
2082101 | Dougherty | Jun 1937 | A |
2204771 | Rice et al. | Jun 1940 | A |
2227465 | Roche, Jr. et al. | Jan 1941 | A |
2241674 | Mohr, Jr. et al. | May 1941 | A |
2242294 | Fox et al. | May 1941 | A |
2273795 | Heise et al. | Feb 1942 | A |
2304391 | Zimmerman | Dec 1942 | A |
2329940 | Ponzer | Sep 1943 | A |
2383674 | Osborne | Aug 1945 | A |
2458039 | Wait | Jan 1949 | A |
2474381 | Sladick | Jun 1949 | A |
2606839 | Evans | Aug 1952 | A |
2650084 | White | Aug 1953 | A |
2776132 | Pyzel | Jan 1957 | A |
2810450 | Hartmann | Oct 1957 | A |
2934419 | Cook | Apr 1960 | A |
2967807 | Osborne et al. | Jan 1961 | A |
3046152 | Tsuneyoshi | Jul 1962 | A |
3067007 | Hatch et al. | Aug 1962 | A |
3120426 | Crawford, Jr. | Feb 1964 | A |
3165460 | Zang et al. | Jan 1965 | A |
3179579 | Gustave et al. | Apr 1965 | A |
3196092 | Beer | Jul 1965 | A |
3202522 | Chi-Sun Yang et al. | Aug 1965 | A |
3222267 | Tirrell et al. | Dec 1965 | A |
3262865 | Waters, Jr. | Jul 1966 | A |
3264125 | Bourlin et al. | Aug 1966 | A |
3321269 | Yasui et al. | May 1967 | A |
3322574 | Justi et al. | May 1967 | A |
3340003 | Judd | Sep 1967 | A |
3350292 | Weinberger et al. | Oct 1967 | A |
3374164 | Balej et al. | Mar 1968 | A |
3420775 | Cadwallader | Jan 1969 | A |
3463814 | Blanco et al. | Aug 1969 | A |
3466169 | Nowak et al. | Sep 1969 | A |
3471999 | Schon | Oct 1969 | A |
3511595 | Fuchs | May 1970 | A |
3511712 | Giner | May 1970 | A |
3525675 | Gaudin | Aug 1970 | A |
3538036 | Frazier et al. | Nov 1970 | A |
3558769 | Globus | Jan 1971 | A |
3574530 | Suriani et al. | Apr 1971 | A |
3627479 | Yee | Dec 1971 | A |
3627480 | Birchall | Dec 1971 | A |
3630762 | Olton et al. | Dec 1971 | A |
3663379 | Kendall | May 1972 | A |
3686372 | Hiatt et al. | Aug 1972 | A |
3721621 | Hough | Mar 1973 | A |
3725267 | Gelblum | Apr 1973 | A |
3733788 | Crowley | May 1973 | A |
3816592 | Rinaldi et al. | Jun 1974 | A |
3834129 | Darlinger et al. | Sep 1974 | A |
3847632 | Blengsli | Nov 1974 | A |
3861928 | Slater et al. | Jan 1975 | A |
3864236 | Lindstrom | Feb 1975 | A |
3869255 | De Witt et al. | Mar 1975 | A |
3904496 | Harke et al. | Sep 1975 | A |
3907526 | Saleem et al. | Sep 1975 | A |
3912801 | Stephens | Oct 1975 | A |
3917795 | Pelczarski et al. | Nov 1975 | A |
3925534 | Singleton et al. | Dec 1975 | A |
3953568 | Seko et al. | Apr 1976 | A |
3959419 | Kitterman | May 1976 | A |
3963592 | Lindstrom | Jun 1976 | A |
3970528 | Zirngiebl et al. | Jul 1976 | A |
3975503 | Hauschild et al. | Aug 1976 | A |
3984523 | Schafer et al. | Oct 1976 | A |
3997303 | Newton | Dec 1976 | A |
4000991 | Melin, Jr. et al. | Jan 1977 | A |
4002721 | Guffy et al. | Jan 1977 | A |
4026716 | Urschel, III et al. | May 1977 | A |
4036749 | Anderson | Jul 1977 | A |
4040852 | Jones | Aug 1977 | A |
4045524 | Bornert | Aug 1977 | A |
4069063 | Ball | Jan 1978 | A |
4080270 | O'Leary et al. | Mar 1978 | A |
4106296 | Leonard, Jr. et al. | Aug 1978 | A |
4107022 | Strempel et al. | Aug 1978 | A |
4117060 | Murray | Sep 1978 | A |
4128462 | Ghiringhelli et al. | Dec 1978 | A |
4140510 | Scholze et al. | Feb 1979 | A |
4147599 | O'Leary et al. | Apr 1979 | A |
4157250 | Regehr et al. | Jun 1979 | A |
4164537 | Drostholm et al. | Aug 1979 | A |
4181580 | Kitayama et al. | Jan 1980 | A |
4188291 | Anderson | Feb 1980 | A |
4217186 | McRae | Aug 1980 | A |
4219396 | Gancy et al. | Aug 1980 | A |
4242185 | McRae | Dec 1980 | A |
4246075 | Hilbertz | Jan 1981 | A |
4253922 | Welch | Mar 1981 | A |
4263021 | Downs et al. | Apr 1981 | A |
4264367 | Schutz | Apr 1981 | A |
4303549 | Boylan | Dec 1981 | A |
4307066 | Davidson | Dec 1981 | A |
4308298 | Chen | Dec 1981 | A |
4312646 | Fattinger et al. | Jan 1982 | A |
4315872 | Senjo et al. | Feb 1982 | A |
4335788 | Murphey et al. | Jun 1982 | A |
4337230 | Ellestad et al. | Jun 1982 | A |
4340572 | Ben-Shmuel et al. | Jul 1982 | A |
4361475 | Moeglich | Nov 1982 | A |
4363667 | Birchall | Dec 1982 | A |
4370307 | Judd | Jan 1983 | A |
4376101 | Sartori et al. | Mar 1983 | A |
4377554 | Johnson | Mar 1983 | A |
4410606 | Loutfy et al. | Oct 1983 | A |
4432175 | Smith | Feb 1984 | A |
4440611 | Dhar et al. | Apr 1984 | A |
4450009 | Childs et al. | May 1984 | A |
4477573 | Taufen | Oct 1984 | A |
4508545 | DeLoach | Apr 1985 | A |
4561945 | Coker et al. | Dec 1985 | A |
4588443 | Bache | May 1986 | A |
4620969 | Wilkinson | Nov 1986 | A |
4634533 | Somerville et al. | Jan 1987 | A |
4670234 | Holter et al. | Jun 1987 | A |
4716027 | Morrison | Dec 1987 | A |
4738695 | Carr et al. | Apr 1988 | A |
4804449 | Sweeney | Feb 1989 | A |
4818367 | Winkler | Apr 1989 | A |
4838941 | Hill | Jun 1989 | A |
4852344 | Warner | Aug 1989 | A |
4876097 | Autant et al. | Oct 1989 | A |
4880447 | Bloch | Nov 1989 | A |
4889633 | Pfenninger | Dec 1989 | A |
4899544 | Boyd | Feb 1990 | A |
4915877 | Shepherd | Apr 1990 | A |
4915914 | Morrison | Apr 1990 | A |
4931264 | Rochelle et al. | Jun 1990 | A |
5037286 | Roberts | Aug 1991 | A |
5100633 | Morrison | Mar 1992 | A |
5127765 | Millgard | Jul 1992 | A |
5141620 | Molter | Aug 1992 | A |
5230734 | Kumasaka et al. | Jul 1993 | A |
5244304 | Weill et al. | Sep 1993 | A |
5246551 | Pletcher et al. | Sep 1993 | A |
5275651 | Minayoshi et al. | Jan 1994 | A |
5275794 | Luna | Jan 1994 | A |
5282935 | Cawlfield et al. | Feb 1994 | A |
5318758 | Fujii et al. | Jun 1994 | A |
5332564 | Chapnerkar et al. | Jul 1994 | A |
5348712 | Marquis et al. | Sep 1994 | A |
5362688 | Porta et al. | Nov 1994 | A |
5364611 | Iijima et al. | Nov 1994 | A |
5366513 | Goldmann et al. | Nov 1994 | A |
5376343 | Fouche | Dec 1994 | A |
5378279 | Conroy | Jan 1995 | A |
5388456 | Kettel | Feb 1995 | A |
5427608 | Auer et al. | Jun 1995 | A |
5439509 | Spink et al. | Aug 1995 | A |
5455013 | Shibata et al. | Oct 1995 | A |
5470671 | Fletcher et al. | Nov 1995 | A |
5520898 | Pinnavaia et al. | May 1996 | A |
5527387 | Andersen et al. | Jun 1996 | A |
5531821 | Wu | Jul 1996 | A |
5531865 | Cole | Jul 1996 | A |
5536310 | Brook et al. | Jul 1996 | A |
5547027 | Chan et al. | Aug 1996 | A |
5569558 | Takeuchi et al. | Oct 1996 | A |
5584923 | Wu | Dec 1996 | A |
5584926 | Borgholm et al. | Dec 1996 | A |
5587083 | Twardowski | Dec 1996 | A |
5595641 | Traini et al. | Jan 1997 | A |
5614078 | Lubin et al. | Mar 1997 | A |
5618392 | Furuya | Apr 1997 | A |
5624493 | Wagh et al. | Apr 1997 | A |
5643415 | Wise et al. | Jul 1997 | A |
5676749 | Takagi | Oct 1997 | A |
5683587 | Ferrara et al. | Nov 1997 | A |
5690729 | Jones, Jr. | Nov 1997 | A |
5702585 | Hillrichs et al. | Dec 1997 | A |
5749930 | Wolf et al. | May 1998 | A |
5766338 | Weber | Jun 1998 | A |
5766339 | Babu et al. | Jun 1998 | A |
5776328 | Traini et al. | Jul 1998 | A |
5785868 | Li et al. | Jul 1998 | A |
5792440 | Huege | Aug 1998 | A |
5792441 | Paleologou et al. | Aug 1998 | A |
5803894 | Kao et al. | Sep 1998 | A |
5833736 | Durham et al. | Nov 1998 | A |
5846669 | Smotkin et al. | Dec 1998 | A |
5849075 | Hopkins et al. | Dec 1998 | A |
5853686 | Doxsee | Dec 1998 | A |
5855666 | Kao et al. | Jan 1999 | A |
5855759 | Keating et al. | Jan 1999 | A |
5879948 | Van Pelt et al. | Mar 1999 | A |
5885478 | Montgomery et al. | Mar 1999 | A |
5897704 | Baglin | Apr 1999 | A |
5904829 | Foller et al. | May 1999 | A |
5925255 | Mukhopadhyay | Jul 1999 | A |
5958353 | Eyal | Sep 1999 | A |
5965201 | Jones, Jr. | Oct 1999 | A |
5994838 | Klinedinst et al. | Nov 1999 | A |
6024848 | Dufner et al. | Feb 2000 | A |
6059974 | Scheurman, III | May 2000 | A |
6071336 | Fairchild et al. | Jun 2000 | A |
6080297 | Ayers | Jun 2000 | A |
6080320 | von Phul | Jun 2000 | A |
6090197 | Vivian et al. | Jul 2000 | A |
6129832 | Fuhr et al. | Oct 2000 | A |
6139605 | Carnell et al. | Oct 2000 | A |
6174507 | Wallace et al. | Jan 2001 | B1 |
6180012 | Rongved | Jan 2001 | B1 |
6180074 | Fourcot et al. | Jan 2001 | B1 |
6186426 | Killer | Feb 2001 | B1 |
6190301 | Murray et al. | Feb 2001 | B1 |
6190428 | Rolison et al. | Feb 2001 | B1 |
6200381 | Rechichi | Mar 2001 | B1 |
6200543 | Allebach et al. | Mar 2001 | B1 |
6217728 | Lehmann et al. | Apr 2001 | B1 |
6221225 | Mani | Apr 2001 | B1 |
6228145 | Falk-Pedersen et al. | May 2001 | B1 |
6235186 | Tanaka et al. | May 2001 | B1 |
6248166 | Solsvik | Jun 2001 | B1 |
6251255 | Copping et al. | Jun 2001 | B1 |
6251356 | Mathur | Jun 2001 | B1 |
6264736 | Knopf et al. | Jul 2001 | B1 |
6264740 | McNulty, Jr. | Jul 2001 | B1 |
6280505 | Torkildsen et al. | Aug 2001 | B1 |
6284208 | Thomassen | Sep 2001 | B1 |
6293731 | Studer | Sep 2001 | B1 |
6309570 | Fellabaum | Oct 2001 | B1 |
6331207 | Gebhardt | Dec 2001 | B1 |
6352576 | Spencer et al. | Mar 2002 | B1 |
6375825 | Mauldin et al. | Apr 2002 | B1 |
6387174 | Knopf et al. | May 2002 | B2 |
6387212 | Christian | May 2002 | B1 |
6402824 | Freeman et al. | Jun 2002 | B1 |
6402831 | Sawara et al. | Jun 2002 | B1 |
6416574 | Steelhammer et al. | Jul 2002 | B1 |
6428767 | Burch et al. | Aug 2002 | B1 |
6444107 | Hartel et al. | Sep 2002 | B2 |
6447437 | Lee et al. | Sep 2002 | B1 |
6468074 | Wu | Oct 2002 | B1 |
6475460 | Max | Nov 2002 | B1 |
6495013 | Mazur et al. | Dec 2002 | B2 |
6500319 | LaConti et al. | Dec 2002 | B2 |
6517631 | Bland | Feb 2003 | B1 |
6518217 | Xing et al. | Feb 2003 | B2 |
6537456 | Mukhopadhyay | Mar 2003 | B2 |
6589405 | Weres et al. | Jul 2003 | B2 |
6602630 | Gopal | Aug 2003 | B1 |
6613141 | Key, Jr. | Sep 2003 | B2 |
6620856 | Mortimer et al. | Sep 2003 | B1 |
6623555 | Haverinen et al. | Sep 2003 | B1 |
6638413 | Weinberg et al. | Oct 2003 | B1 |
6648949 | Der et al. | Nov 2003 | B1 |
6676744 | Merkley et al. | Jan 2004 | B2 |
6712946 | Genders et al. | Mar 2004 | B2 |
6755905 | Oates et al. | Jun 2004 | B2 |
6776972 | Vohra et al. | Aug 2004 | B2 |
6786963 | Matherly et al. | Sep 2004 | B2 |
6841512 | Fetcenko et al. | Jan 2005 | B1 |
6881256 | Orange et al. | Apr 2005 | B2 |
6890419 | Reichman et al. | May 2005 | B2 |
6890497 | Rau et al. | May 2005 | B2 |
6908507 | Lalande et al. | Jun 2005 | B2 |
6936573 | Wertz et al. | Aug 2005 | B2 |
6938425 | Simpson et al. | Sep 2005 | B2 |
7037434 | Myers et al. | May 2006 | B2 |
7040400 | de Rouffignac et al. | May 2006 | B2 |
7132090 | Dziedzic et al. | Nov 2006 | B2 |
7135604 | Ding et al. | Nov 2006 | B2 |
7147692 | Fornai et al. | Dec 2006 | B2 |
7182851 | Gomez | Feb 2007 | B2 |
7198722 | Hussain | Apr 2007 | B2 |
7255842 | Yeh et al. | Aug 2007 | B1 |
7261912 | Zeigler | Aug 2007 | B2 |
7264704 | Nevosi et al. | Sep 2007 | B2 |
7273540 | Sonoda et al. | Sep 2007 | B2 |
7282189 | Zauderer | Oct 2007 | B2 |
7285166 | Luke et al. | Oct 2007 | B2 |
7314847 | Siriwardane | Jan 2008 | B1 |
7347896 | Harrison | Mar 2008 | B2 |
7390444 | Ramme et al. | Jun 2008 | B2 |
7427449 | Delaney et al. | Sep 2008 | B2 |
7440871 | McConnell et al. | Oct 2008 | B2 |
7452449 | Weinberg et al. | Nov 2008 | B2 |
7455854 | Gower et al. | Nov 2008 | B2 |
7459134 | Cadours et al. | Dec 2008 | B2 |
7541011 | Hu | Jun 2009 | B2 |
7595001 | Arakel et al. | Sep 2009 | B2 |
7597747 | Nagel | Oct 2009 | B1 |
7628847 | Pope et al. | Dec 2009 | B2 |
7674443 | Davis | Mar 2010 | B1 |
7699909 | Lackner et al. | Apr 2010 | B2 |
7704369 | Olah et al. | Apr 2010 | B2 |
7704370 | Coustry et al. | Apr 2010 | B2 |
7727374 | Jones | Jun 2010 | B2 |
7735274 | Constantz et al. | Jun 2010 | B2 |
7736430 | Barron et al. | Jun 2010 | B2 |
7744761 | Constantz et al. | Jun 2010 | B2 |
7749476 | Constantz et al. | Jul 2010 | B2 |
7753618 | Constantz et al. | Jul 2010 | B2 |
7754169 | Constantz et al. | Jul 2010 | B2 |
7771684 | Constantz et al. | Aug 2010 | B2 |
7790012 | Kirk et al. | Sep 2010 | B2 |
7815880 | Constantz et al. | Oct 2010 | B2 |
7829053 | Constantz et al. | Nov 2010 | B2 |
7842264 | Cooper et al. | Nov 2010 | B2 |
7875163 | Gilliam et al. | Jan 2011 | B2 |
7875674 | Kirkpatrick et al. | Jan 2011 | B2 |
7887694 | Constantz et al. | Feb 2011 | B2 |
7906028 | Constantz et al. | Mar 2011 | B2 |
7914685 | Constantz et al. | Mar 2011 | B2 |
7919064 | Kawatra et al. | Apr 2011 | B2 |
7922809 | Constantz et al. | Apr 2011 | B1 |
7931809 | Constantz et al. | Apr 2011 | B2 |
7939336 | Constantz et al. | May 2011 | B2 |
7966250 | Constantz et al. | Jun 2011 | B2 |
7993500 | Gilliam et al. | Aug 2011 | B2 |
7993511 | Gilliam et al. | Aug 2011 | B2 |
8006446 | Constantz et al. | Aug 2011 | B2 |
8062418 | Constantz et al. | Nov 2011 | B2 |
8105558 | Comrie | Jan 2012 | B2 |
8114214 | Constantz et al. | Feb 2012 | B2 |
8137455 | Constantz et al. | Mar 2012 | B1 |
8431100 | Constantz et al. | Apr 2013 | B2 |
8470275 | Constantz et al. | Jun 2013 | B2 |
8603424 | Constantz et al. | Dec 2013 | B2 |
8834688 | Gilliam | Sep 2014 | B2 |
8869477 | Ha et al. | Oct 2014 | B2 |
8883104 | Seeker et al. | Nov 2014 | B2 |
8894830 | Gilliam et al. | Nov 2014 | B2 |
9061940 | Chen et al. | Jun 2015 | B2 |
20010022952 | Rau et al. | Sep 2001 | A1 |
20010023655 | Knopf et al. | Sep 2001 | A1 |
20010054253 | Takahashi et al. | Dec 2001 | A1 |
20020009410 | Mathur | Jan 2002 | A1 |
20020127474 | Fleischer et al. | Sep 2002 | A1 |
20020151017 | Stemmer et al. | Oct 2002 | A1 |
20020155103 | Crippen et al. | Oct 2002 | A1 |
20030017088 | Downs et al. | Jan 2003 | A1 |
20030027023 | Dutil et al. | Feb 2003 | A1 |
20030039729 | Murphy | Feb 2003 | A1 |
20030123930 | Jacobs et al. | Jul 2003 | A1 |
20030126899 | Wolken | Jul 2003 | A1 |
20030146163 | Sasowsky et al. | Aug 2003 | A1 |
20030170159 | Honjo et al. | Sep 2003 | A1 |
20030188668 | Bland | Oct 2003 | A1 |
20030213937 | Yaniv | Nov 2003 | A1 |
20030229572 | Raines et al. | Dec 2003 | A1 |
20040007476 | Tennakoon et al. | Jan 2004 | A1 |
20040014845 | Takamura et al. | Jan 2004 | A1 |
20040028963 | Kormann et al. | Feb 2004 | A1 |
20040040671 | Duesel, Jr. et al. | Mar 2004 | A1 |
20040040715 | Wellington et al. | Mar 2004 | A1 |
20040052865 | Gower et al. | Mar 2004 | A1 |
20040094279 | Myatt | May 2004 | A1 |
20040109927 | Ang et al. | Jun 2004 | A1 |
20040111968 | Day et al. | Jun 2004 | A1 |
20040126293 | Geerlings et al. | Jul 2004 | A1 |
20040139891 | Merkley et al. | Jul 2004 | A1 |
20040151957 | Brooks et al. | Aug 2004 | A1 |
20040213705 | Blencoe et al. | Oct 2004 | A1 |
20040219090 | Dziedzic et al. | Nov 2004 | A1 |
20040224214 | Vamos et al. | Nov 2004 | A1 |
20040228788 | Nagai et al. | Nov 2004 | A1 |
20040231568 | Morioka et al. | Nov 2004 | A1 |
20040234443 | Chen et al. | Nov 2004 | A1 |
20040259231 | Bhattacharya | Dec 2004 | A1 |
20040267077 | Ding et al. | Dec 2004 | A1 |
20050002847 | Maroto-Valer et al. | Jan 2005 | A1 |
20050011770 | Katsuyoshi et al. | Jan 2005 | A1 |
20050031515 | Charette | Feb 2005 | A1 |
20050031522 | Delaney et al. | Feb 2005 | A1 |
20050036932 | Takahashi et al. | Feb 2005 | A1 |
20050087496 | Borseth | Apr 2005 | A1 |
20050098499 | Hussain | May 2005 | A1 |
20050103234 | McNutty | May 2005 | A1 |
20050106110 | Liu | May 2005 | A1 |
20050112044 | Kuma et al. | May 2005 | A1 |
20050118081 | Harris et al. | Jun 2005 | A1 |
20050129606 | Mitsuhashi et al. | Jun 2005 | A1 |
20050136310 | Luo et al. | Jun 2005 | A1 |
20050154669 | Streetman | Jul 2005 | A1 |
20050180910 | Park et al. | Aug 2005 | A1 |
20050232855 | Stevens et al. | Oct 2005 | A1 |
20050232856 | Stevens et al. | Oct 2005 | A1 |
20050238563 | Eighmy et al. | Oct 2005 | A1 |
20050252215 | Beaumont | Nov 2005 | A1 |
20050255174 | Shelley et al. | Nov 2005 | A1 |
20060039853 | Fan et al. | Feb 2006 | A1 |
20060048517 | Fradette et al. | Mar 2006 | A1 |
20060051274 | Wright et al. | Mar 2006 | A1 |
20060057036 | Ayala Hermosillo | Mar 2006 | A1 |
20060060532 | Davis | Mar 2006 | A1 |
20060093540 | Fan et al. | May 2006 | A1 |
20060105082 | Zeigler | May 2006 | A1 |
20060165583 | Makino et al. | Jul 2006 | A1 |
20060169177 | Jardine et al. | Aug 2006 | A1 |
20060169593 | Xu et al. | Aug 2006 | A1 |
20060173169 | Cheryan | Aug 2006 | A1 |
20060184445 | Sandor et al. | Aug 2006 | A1 |
20060185516 | Moriyama et al. | Aug 2006 | A1 |
20060185560 | Ramme et al. | Aug 2006 | A1 |
20060185985 | Jones | Aug 2006 | A1 |
20060186562 | Wright et al. | Aug 2006 | A1 |
20060189837 | Forrester | Aug 2006 | A1 |
20060194086 | Hsu | Aug 2006 | A1 |
20060195002 | Grandjean et al. | Aug 2006 | A1 |
20060196836 | Arakel et al. | Sep 2006 | A1 |
20060245993 | Magumbe et al. | Nov 2006 | A1 |
20060249380 | Gestermann et al. | Nov 2006 | A1 |
20060286011 | Anttila et al. | Dec 2006 | A1 |
20060288912 | Sun et al. | Dec 2006 | A1 |
20070045125 | Hartvigsen et al. | Mar 2007 | A1 |
20070056487 | Anthony et al. | Mar 2007 | A1 |
20070084344 | Moriya et al. | Apr 2007 | A1 |
20070092427 | Anthony et al. | Apr 2007 | A1 |
20070099038 | Galloway | May 2007 | A1 |
20070113500 | Zhao | May 2007 | A1 |
20070148509 | Colbow et al. | Jun 2007 | A1 |
20070163443 | Moriyama et al. | Jul 2007 | A1 |
20070184394 | Comrie | Aug 2007 | A1 |
20070186820 | O'Hearn | Aug 2007 | A1 |
20070187247 | Lackner et al. | Aug 2007 | A1 |
20070202032 | Geerlings et al. | Aug 2007 | A1 |
20070212584 | Chuang | Sep 2007 | A1 |
20070217981 | Van Essendelft | Sep 2007 | A1 |
20070233616 | Richards et al. | Oct 2007 | A1 |
20070240570 | Jadhav et al. | Oct 2007 | A1 |
20070251393 | Pope et al. | Nov 2007 | A1 |
20070261947 | Geerlings et al. | Nov 2007 | A1 |
20070266632 | Tsangaris et al. | Nov 2007 | A1 |
20080031801 | Lackner et al. | Feb 2008 | A1 |
20080035036 | Bassani et al. | Feb 2008 | A1 |
20080053104 | Haase et al. | Mar 2008 | A1 |
20080059206 | Jenkins | Mar 2008 | A1 |
20080099122 | Andersen et al. | May 2008 | A1 |
20080104858 | Carin et al. | May 2008 | A1 |
20080112868 | Blencoe et al. | May 2008 | A1 |
20080134891 | Jarvenpaa | Jun 2008 | A1 |
20080138265 | Lackner et al. | Jun 2008 | A1 |
20080171158 | Maddan | Jul 2008 | A1 |
20080178739 | Lewnard et al. | Jul 2008 | A1 |
20080213146 | Zauderer | Sep 2008 | A1 |
20080223727 | Oloman et al. | Sep 2008 | A1 |
20080233029 | Fan et al. | Sep 2008 | A1 |
20080236143 | Lo | Oct 2008 | A1 |
20080241337 | Durand et al. | Oct 2008 | A1 |
20080245012 | Boisvert et al. | Oct 2008 | A1 |
20080245274 | Ramme | Oct 2008 | A1 |
20080245660 | Little et al. | Oct 2008 | A1 |
20080245672 | Little et al. | Oct 2008 | A1 |
20080248350 | Little et al. | Oct 2008 | A1 |
20080270272 | Branscomb | Oct 2008 | A1 |
20080275149 | Ladely et al. | Nov 2008 | A1 |
20080276553 | Ingjaldsdottir et al. | Nov 2008 | A1 |
20080276803 | Molaison et al. | Nov 2008 | A1 |
20080277319 | Wyrsta | Nov 2008 | A1 |
20080289495 | Eisenberger et al. | Nov 2008 | A1 |
20090001020 | Constantz et al. | Jan 2009 | A1 |
20090010827 | Geerlings et al. | Jan 2009 | A1 |
20090020044 | Constantz et al. | Jan 2009 | A1 |
20090043687 | van Soestbergen et al. | Feb 2009 | A1 |
20090078162 | Clausi et al. | Mar 2009 | A1 |
20090081092 | Yang et al. | Mar 2009 | A1 |
20090081093 | Comrie | Mar 2009 | A1 |
20090081096 | Pellegrin | Mar 2009 | A1 |
20090081112 | Virtanen | Mar 2009 | A1 |
20090087890 | Pyle et al. | Apr 2009 | A1 |
20090090277 | Joshi et al. | Apr 2009 | A1 |
20090101008 | Lackner et al. | Apr 2009 | A1 |
20090107038 | Wan | Apr 2009 | A1 |
20090117019 | Comrie | May 2009 | A1 |
20090120288 | Lackner | May 2009 | A1 |
20090120644 | Roddy et al. | May 2009 | A1 |
20090143211 | Riman et al. | Jun 2009 | A1 |
20090148238 | Smith | Jun 2009 | A1 |
20090169452 | Constantz et al. | Jul 2009 | A1 |
20090186244 | Mayer | Jul 2009 | A1 |
20090202410 | Kawatra et al. | Aug 2009 | A1 |
20090214408 | Blake et al. | Aug 2009 | A1 |
20090232861 | Wright et al. | Sep 2009 | A1 |
20090263301 | Reddy et al. | Oct 2009 | A1 |
20090294366 | Wright et al. | Dec 2009 | A1 |
20090301352 | Constantz et al. | Dec 2009 | A1 |
20090308760 | Wei et al. | Dec 2009 | A1 |
20090317488 | Mehta et al. | Dec 2009 | A1 |
20100000444 | Constantz et al. | Jan 2010 | A1 |
20100024686 | Constantz et al. | Feb 2010 | A1 |
20100037653 | Enis et al. | Feb 2010 | A1 |
20100051859 | House et al. | Mar 2010 | A1 |
20100063902 | Constantz et al. | Mar 2010 | A1 |
20100068109 | Comrie | Mar 2010 | A1 |
20100077691 | Constantz et al. | Apr 2010 | A1 |
20100077922 | Constantz et al. | Apr 2010 | A1 |
20100083880 | Constantz et al. | Apr 2010 | A1 |
20100084280 | Gilliam et al. | Apr 2010 | A1 |
20100089142 | Sukhija et al. | Apr 2010 | A1 |
20100111810 | Constantz et al. | May 2010 | A1 |
20100116683 | Gilliam et al. | May 2010 | A1 |
20100132556 | Constantz et al. | Jun 2010 | A1 |
20100132591 | Constantz et al. | Jun 2010 | A1 |
20100135865 | Constantz et al. | Jun 2010 | A1 |
20100135882 | Constantz et al. | Jun 2010 | A1 |
20100140103 | Gilliam et al. | Jun 2010 | A1 |
20100144521 | Constantz et al. | Jun 2010 | A1 |
20100150802 | Gilliam et al. | Jun 2010 | A1 |
20100154679 | Constantz et al. | Jun 2010 | A1 |
20100155258 | Kirk et al. | Jun 2010 | A1 |
20100158786 | Constantz et al. | Jun 2010 | A1 |
20100196104 | Constantz et al. | Aug 2010 | A1 |
20100200419 | Gilliam et al. | Aug 2010 | A1 |
20100219373 | Seeker et al. | Sep 2010 | A1 |
20100224503 | Kirk et al. | Sep 2010 | A1 |
20100229725 | Farsad et al. | Sep 2010 | A1 |
20100230293 | Gilliam et al. | Sep 2010 | A1 |
20100230830 | Farsad et al. | Sep 2010 | A1 |
20100236242 | Farsad et al. | Sep 2010 | A1 |
20100239467 | Constantz et al. | Sep 2010 | A1 |
20100239487 | Constantz et al. | Sep 2010 | A1 |
20100247410 | Constantz et al. | Sep 2010 | A1 |
20100258035 | Constantz et al. | Oct 2010 | A1 |
20100258506 | Berkowitz et al. | Oct 2010 | A1 |
20100276299 | Kelly et al. | Nov 2010 | A1 |
20100290967 | Detournay et al. | Nov 2010 | A1 |
20100313793 | Constantz et al. | Dec 2010 | A1 |
20100313794 | Constantz et al. | Dec 2010 | A1 |
20100319586 | Blount et al. | Dec 2010 | A1 |
20100326328 | Constantz et al. | Dec 2010 | A1 |
20110024361 | Schwartzel et al. | Feb 2011 | A1 |
20110030586 | Constantz et al. | Feb 2011 | A1 |
20110030957 | Constantz et al. | Feb 2011 | A1 |
20110033239 | Constantz et al. | Feb 2011 | A1 |
20110035154 | Kendall et al. | Feb 2011 | A1 |
20110036728 | Farsad et al. | Feb 2011 | A1 |
20110042230 | Gilliam et al. | Feb 2011 | A1 |
20110054084 | Constantz et al. | Mar 2011 | A1 |
20110059000 | Constantz et al. | Mar 2011 | A1 |
20110067600 | Constantz et al. | Mar 2011 | A1 |
20110067603 | Constantz et al. | Mar 2011 | A1 |
20110067605 | Constantz et al. | Mar 2011 | A1 |
20110071309 | Constantz et al. | Mar 2011 | A1 |
20110079515 | Gilliam et al. | Apr 2011 | A1 |
20110083968 | Gilliam et al. | Apr 2011 | A1 |
20110091366 | Kendall et al. | Apr 2011 | A1 |
20110091955 | Constantz et al. | Apr 2011 | A1 |
20110132234 | Constantz et al. | Jun 2011 | A1 |
20110147227 | Gilliam et al. | Jun 2011 | A1 |
20110203489 | Constantz et al. | Aug 2011 | A1 |
20110226989 | Seeker et al. | Sep 2011 | A9 |
20110240916 | Constantz et al. | Oct 2011 | A1 |
20110247336 | Farsad et al. | Oct 2011 | A9 |
20110277474 | Constantz et al. | Nov 2011 | A1 |
20110277670 | Self et al. | Nov 2011 | A1 |
20110290156 | Constantz et al. | Dec 2011 | A1 |
20110303551 | Gilliam et al. | Dec 2011 | A1 |
20110308964 | Gilliam et al. | Dec 2011 | A1 |
20120082839 | Ha et al. | Apr 2012 | A1 |
20120111236 | Constantz et al. | May 2012 | A1 |
20120213688 | Constantz et al. | Aug 2012 | A1 |
20120312697 | Gilliam et al. | Dec 2012 | A1 |
20130036945 | Constantz et al. | Feb 2013 | A1 |
20130243674 | Constantz et al. | Sep 2013 | A1 |
20140041553 | Constantz et al. | Feb 2014 | A1 |
20150000558 | Ha et al. | Jan 2015 | A1 |
20150037231 | Seeker et al. | Feb 2015 | A1 |
20150083607 | Gilliam et al. | Mar 2015 | A1 |
Number | Date | Country |
---|---|---|
2001213118 | Dec 2001 | AU |
2007100157 | Apr 2007 | AU |
2007201171 | Oct 2007 | AU |
2007101174 | Jan 2008 | AU |
2008256636 | Dec 2008 | AU |
2008101140 | Jan 2009 | AU |
1303822 | Jun 1988 | CA |
1335974 | Jun 1995 | CA |
2308224 | Apr 1999 | CA |
2255287 | Jun 2000 | CA |
2353830 | Jun 2000 | CA |
2440325 | Jan 2003 | CA |
2646462 | Sep 2007 | CA |
2617325 | Nov 2007 | CA |
2682952 | Oct 2008 | CA |
2659447 | Dec 2008 | CA |
1059173 | Mar 1992 | CN |
1185989 | Jul 1998 | CN |
1369576 | Sep 2002 | CN |
1220793 | Sep 2005 | CN |
101219330 | Jul 2008 | CN |
101240426 | Aug 2008 | CN |
101250711 | Aug 2008 | CN |
101289200 | Oct 2008 | CN |
101990523 | Mar 2011 | CN |
102335553 | Feb 2012 | CN |
2653649 | Jun 1978 | DE |
3146326 | Jun 1983 | DE |
3638317 | Jun 1987 | DE |
19512163 | Oct 1995 | DE |
19523324 | Mar 1996 | DE |
19631794 | Aug 1997 | DE |
0522382 | Jan 1993 | EP |
0558275 | Sep 1993 | EP |
0487102 | Aug 1995 | EP |
0591350 | Nov 1996 | EP |
0628339 | Sep 1999 | EP |
0844905 | Mar 2000 | EP |
1379469 | Mar 2006 | EP |
1650162 | Apr 2006 | EP |
1716911 | Nov 2006 | EP |
1554031 | Dec 2006 | EP |
1571105 | Dec 2006 | EP |
2253600 | Nov 2010 | EP |
911386 | Nov 1962 | GB |
1392907 | May 1975 | GB |
2032441 | May 1980 | GB |
2050325 | Jan 1981 | GB |
2208163 | Mar 1989 | GB |
2210035 | Jun 1989 | GB |
2371810 | Aug 2002 | GB |
51102357 | Sep 1976 | JP |
59100280 | Jun 1984 | JP |
63-312988 | Dec 1988 | JP |
03-020491 | Jan 1991 | JP |
03-170363 | Jul 1991 | JP |
04-190829 | Nov 1992 | JP |
04-317721 | Nov 1992 | JP |
7061842 | Mar 1995 | JP |
7265688 | Oct 1995 | JP |
H 08246178 | Sep 1996 | JP |
10287461 | Oct 1998 | JP |
10305212 | Nov 1998 | JP |
2000226402 | Aug 2000 | JP |
03184892 | Jul 2001 | JP |
2002-273163 | Sep 2002 | JP |
2003041388 | Feb 2003 | JP |
2004-174370 | Jun 2004 | JP |
2004-174371 | Jun 2004 | JP |
2005-052762 | Mar 2005 | JP |
2006-075717 | Mar 2006 | JP |
2006-076825 | Mar 2006 | JP |
2006-076825 | Mar 2006 | JP |
2006-137620 | Jun 2006 | JP |
2009279530 | Dec 2009 | LY |
7607470 | Jan 1978 | NL |
1819854 | Jun 1993 | SU |
WO 9316216 | Aug 1993 | WO |
WO 9418119 | Aug 1994 | WO |
WO 9634997 | Nov 1996 | WO |
WO 9908778 | Feb 1999 | WO |
WO 9913967 | Mar 1999 | WO |
WO 2006009600 | Jan 2000 | WO |
WO 0010691 | Mar 2000 | WO |
WO 0107365 | Feb 2001 | WO |
WO 0196243 | Dec 2001 | WO |
WO 0200551 | Jan 2002 | WO |
WO 02085788 | Oct 2002 | WO |
WO 03008071 | Jan 2003 | WO |
WO 03054508 | Jul 2003 | WO |
WO 03068685 | Aug 2003 | WO |
WO 2004041731 | May 2004 | WO |
WO 2004094043 | Nov 2004 | WO |
WO 2004098740 | Nov 2004 | WO |
WO 2005028379 | Mar 2005 | WO |
WO 2005078836 | Aug 2005 | WO |
WO 2005086843 | Sep 2005 | WO |
WO 2005108297 | Nov 2005 | WO |
WO 2006008242 | Jan 2006 | WO |
WO 2006032797 | Mar 2006 | WO |
WO 2006034339 | Mar 2006 | WO |
WO 2006036396 | Apr 2006 | WO |
WO 2006094968 | Sep 2006 | WO |
WO 2006099599 | Sep 2006 | WO |
WO 2006113997 | Nov 2006 | WO |
WO 2006134080 | Dec 2006 | WO |
WO 2007003013 | Jan 2007 | WO |
WO 2007016271 | Feb 2007 | WO |
WO 2007022595 | Mar 2007 | WO |
WO 2007060149 | May 2007 | WO |
WO 2007069902 | Jun 2007 | WO |
WO 2007071633 | Jun 2007 | WO |
WO 2007082505 | Jul 2007 | WO |
WO 2007094691 | Aug 2007 | WO |
WO 2007096671 | Aug 2007 | WO |
WO 2007106372 | Sep 2007 | WO |
WO 2007106883 | Sep 2007 | WO |
WO 2007123917 | Nov 2007 | WO |
WO 2007139392 | Dec 2007 | WO |
WO 2007140544 | Dec 2007 | WO |
WO 2007142945 | Dec 2007 | WO |
WO 2008018928 | Feb 2008 | WO |
WO 2008026201 | Mar 2008 | WO |
WO 2008031834 | Mar 2008 | WO |
WO 2008061305 | May 2008 | WO |
WO 2008068322 | Jun 2008 | WO |
WO 2008089523 | Jul 2008 | WO |
WO 2008095057 | Aug 2008 | WO |
WO 2008101293 | Aug 2008 | WO |
WO 2008108657 | Sep 2008 | WO |
WO 2008115662 | Sep 2008 | WO |
WO 2008124538 | Oct 2008 | WO |
WO 2008140821 | Nov 2008 | WO |
WO 2008142017 | Nov 2008 | WO |
WO 2008142025 | Nov 2008 | WO |
WO 2008148055 | Dec 2008 | WO |
WO 2008151060 | Dec 2008 | WO |
WO 2009006295 | Jan 2009 | WO |
WO 2009024826 | Feb 2009 | WO |
WO 2009032331 | Mar 2009 | WO |
WO 2009036087 | Mar 2009 | WO |
WO 2009039655 | Apr 2009 | WO |
WO 2009049085 | Apr 2009 | WO |
WO 2009052313 | Apr 2009 | WO |
WO 2009065031 | May 2009 | WO |
WO 2009070273 | Jun 2009 | WO |
WO 2009086460 | Jul 2009 | WO |
WO 2009102816 | Aug 2009 | WO |
WO 2009102817 | Aug 2009 | WO |
WO 2009146436 | Dec 2009 | WO |
WO 2009155378 | Dec 2009 | WO |
WO 2010006242 | Jan 2010 | WO |
WO 2010008896 | Jan 2010 | WO |
WO 2010009273 | Jan 2010 | WO |
WO 2010030826 | Mar 2010 | WO |
WO 2010039903 | Apr 2010 | WO |
WO 2010039909 | Apr 2010 | WO |
WO 2010048457 | Apr 2010 | WO |
WO 2010051458 | May 2010 | WO |
WO 2010068924 | Jun 2010 | WO |
WO 2010074686 | Jul 2010 | WO |
WO 2010074687 | Jul 2010 | WO |
WO 2010087823 | Aug 2010 | WO |
WO 2010091029 | Aug 2010 | WO |
WO 2010093713 | Aug 2010 | WO |
WO 2010093716 | Aug 2010 | WO |
WO 2010101953 | Sep 2010 | WO |
WO 2010104989 | Sep 2010 | WO |
WO 2010132863 | Nov 2010 | WO |
WO 2010136744 | Dec 2010 | WO |
WO 2011008223 | Jan 2011 | WO |
WO 2011017609 | Feb 2011 | WO |
WO 2011038076 | Mar 2011 | WO |
WO 2011049996 | Apr 2011 | WO |
WO 2011066293 | Jun 2011 | WO |
WO 2011075680 | Jun 2011 | WO |
WO 2011081681 | Jul 2011 | WO |
WO 2011097468 | Aug 2011 | WO |
WO 2011102868 | Aug 2011 | WO |
Entry |
---|
U.S. Appl. No. 60/921,598, filed Apr. 3, 2007, Little et al. |
U.S. Appl. No. 14/488,835, filed Sep. 7, 2014, Ha et al. |
Aker, “Aker Clean Carbon, Carbon Capture Solutions Provider” Aker Clean Carbon Presentation for UN'S IPCC; Jan. 24 (2008); 8pp. |
Alexander, G. et al., “Evaluation of reaction variables in the dissolution of serpentine for mineral carbonation”; Elsevier; ScienceDirect Fuel 86 Jun. 2007 273-281. |
Allen, L.M. Boron and Sulfur Isotopic Fractionation in the Coal Combustion System. A Thesis Submitted to the Faculty of the Department of Hydrology and Water Resources. The University of Arizona. Dec. 1992. |
Amelingmeier. “Aragonit”, Roempp, Fachgebiet: Chemie Unterthema: Mineralogie, Geochimie May 2005, Retrieved from the internet: URL: http://www.roempp.com/prod/ [retrieved on Jun. 19, 2012]—with machine English translation. |
Amelingmeier. “Vaterit”, Roempp, Fachgebiet: Chemie Unterthema: Mineralogie, Geochimie Nov., 2010, Retrieved from the internet: URL: http://www.roempp.com/prod/ [retrieved on Jun. 19, 2012]—with machine English translation. |
Avery, G.B. et al. Carbon isotopic characterization of dissolved organic carbon in rainwater: Terrestrial and marine influences. Science Direct. Dec. 2006; 40(39): 7539-7545. Retrieved from the internet on May 20, 2010. |
Back, M. et al.,“Reactivity of Alkaline Lignite Fly Ashes Towards CO in Water.” Environmental Science & Technology. vol. 42, no. May 12, 2008 pp. 4520-4526. |
Baer, D.S., et al. Sensitive absorption measurements in the near-infrared region using off-axis integrated-cavity-output spectroscopy. Appl. Phys. B. May 2002. 5 pages. |
Bagotsky, V.S. “Conductive Polymers: Polymers with Ionic Functions” Fundamentals of Electrochemistry. Dec. 2005 Second Edition. New Jersey: John Wiley & Sons. pp. 454-455. |
Bauer, C.F., et al. Jul., 1981. Identification and Quantitation of Carbonate Compounds in Coal Fly Ash. American Chemical Society. 15(7): 783-788. |
Berg et al., “A 3-Hydroxyproprionate/ 4-Hydroxybutyrate Autotrophic Carbon Dioxide Assimilation Pathway in Archea”; Science 14, Dec. 2007; vol. 318, No. 5857 DOI 10.1126/science 1149976; pp. 1782-1786. |
Biello, D. Cement from CO2: A Concrete Cure for Global Warming? Scientific American Aug. 7, 2008., pp. 1-3 [online] [retrieved on Dec. 29, 2009] <URL: http://www.scientificamerican.com/article.cfm>. |
Biennier, L., et al. Multiplex integrated cavity output spectroscopy of cold PAH cations. Chemical Physics Letters. Mar. 2004; 387: 287-294. |
Biomass Burning: A Hot Issue in Global Change. National Aeronautics and Space Administration. Langley Research Center, Hampton, Virginia. Fact Sheet FS-2001-02-56-LaRC. Feb. 2001. 4 pages. |
Bommaraju, T.V. et al. Nov. 2001 Brine Electrolysis. <http://electrochem.cwru.edu/encycl/art-b01-brine.htm>. Retrieved on Oct. 6, 2010. pp. 1-25. |
Bond, G.M., et al. (2001). CO2 Capture from Coal-Fired Utility Generation Plant Exhausts, and Sequestration by a Biomimetic Route Based on Enzymatic Catalysis—Current Status (paper presented at the First National Conference on Carbon Sequestration, May 14-17, in Washington D.C., USA; Paper Sa.5. |
Bond, G.M., et al. (Dec. 2002). Brines as possible cation sources for biomimetic carbon dioxide sequestration. American Geophysical Union Abstract #U22A-07. |
Bottomley, D.J. et al. The origin and evolution of Canadian Shield brines: evaporation or freezing of seawater? New lithium isotope and geochemical evidence from the Slave craton. Chemical Geology. Jan. 1999; 155: 295-320. |
Bradfield, D.L. Jan. 1984. Conventional Uranium Processing: The Yeelirrie Uranium Project. Practical Hydromet '83—7th Annual Symposium on Uranium and Precious Metals. pp. 39-47. Lakewood, CO. |
Calera. “Investors.” Vinod Khosla. Calera.com website, available online at least as of Feb. 16, 2012. http://calera.com/index.php/about—us/our—team/investors/. |
Cannell, M.G.R. Aug. (2003). “Carbon sequestration and biomass energy offset: theoretical, potential and achievable capacities globally, in Europe and the UK.” Biomass and Bioenergy. 24: 97-116. |
Carbon Sequestration. National Energy Technology Laboratory, Jul. 1, 2008 (online) [retrieved on Dec. 21, 2009] <URL: http://web.archive.org/web/20080701213124/http://www.netl.doe.gov/te chnologies/carbon—seq/index.html>. |
Cerling, T.E. The stable isotopic composition of modern soil carbonate and its relationship to climate. Earth and Planetary Science Letters. Aug. 1984; 71: 229-240. |
Christensen, L.E., et al. Measurement of Sulfur Isotope Compositions by Tunable Laser Spectroscopy of SO2. Analytical Chemistry, Nov. 17, 2007, vol. 79, No. 24, pp. 9261-9268 (abstract) [online] [retrieved on Dec. 30, 2009] <URL: http://pubs.acs.org/doi/abs/10.1021/ac071040p>. |
CICCS “Aims and Research”; www.nottingham.ac.uk/carbonmanagement/ccs—aims.php 2pp Aug. 3, 2007. |
Combes, et al Preparation, physical-chemical characterisation and cytocompatibility of calcium carbonate cements Biomaterials. Mar. 2006; 27(9):1945-1954. |
Constantz, B. “The Risk of Implementing New Regulations on Game-Changing Technology: Sequestering CO2 in the Built Environment” AGU, Sep. 2009; 90(22), Jt. Assem, Suppl., Abstract. |
Criss, R.E. Jan. 1995. Stable Isotope Distribution: Variations from Temperature, Organic and Water-Rock Interactions. Washington University, St. Louis, Department of Earch and Planetary Sciences. American Geophysical Union. pp. 292-307. |
Dickens, A. et al. Reburial of fossil organic carbon in marine sediments. Nature. Jan. 2004; 427: 336-339. Retrieved from the internet on May 20, 2010. |
Druckenmiller, M. et al., “Carbon sequestration using brine of adjusted pH to form mineral carbonates”; Elsevier; www.elsevier.com/locate/fuproc; Fuel Processing Technology 86 (Jan. 2005) 1599-1614. |
Ehleringer, J.R., et al. Jan. 2002. Stable Isotopes. vol. 2, The Earth System: biological and ecological dimensions of global environmental change. pp. 544-550. Edited by Professor Harold A. Mooney and Dr. Josep G. Canadell in Encyclopedia of Global Environmental Change. John Wiley & Sons, Ltd. Chichester. |
Eldorado Beaverlodge Operation. Jun. 1960 Canadian Mining Journal. 81(6): 111-138. |
Electrochemical cell. Wikipedia (2009), http:en.wikipedia.org/wiki/Electrochemical—Cell, Nov. 24, 2009, 5 pp. |
Eloneva et al., “Fixation of CO2 by carbonating calcium derived from blast furnace slag” Energy May 2008 33, pp. 1461-1467. |
Elswick, E.R., et al. Sulfur and carbon isotope geochemistry of coal and derived coal-combustion by-products: An example from an Eastern Kentucky mine and power plant. Applied Geochemistry. Jun. 2007; 22: 2065-2077. |
Eurodia. Bipolar Membrane Electrodialysis. Available online as of Oct. 2001.; visited Oct. 6, 2010 at http://www.eurodia.com/html/eb.html. |
European search report and opinion dated Dec. 20, 2011 for EP Application No. 09767687.8. |
Fallick, A.E., et al. A Stable Isotope Study of the Magnesite Deposits Associated with the Alpine-Type Ultramafic Rocks of Yugoslavia. Economic Geology. Jan. 1991; 86: 847-861. |
Faure, et al. Jan. 1963. The Isotopic Composition of Strontium in Oceanic and Continental Basalts: Application to the Origin of Igneous Rocks. Journal of Petrology. 4(1): 31-50. (abstract only). Http://petrology.oxfordjournals.org/cgi/content/abstract/4/1/31 (retrieved on Jun. 1, 2010). |
Faverjon, F. et al. Aug. 2006. Regeneration of hydrochloric acid and sodium hydroxide from purified sodium chloride by membrane electrolysis using a hydrogen diffusion anode-membrane assembly. Journal of Membrane Science 284 (1-2): 323-330. |
Faverjon, F. et al. Jul. 2005. Electrochemical study of a hydrogen diffusion anode-membrane assembly for membrane electrolysis. Electrochimica Acta 51 (3): 386-394. |
Filley, T.R. et al. Mar. 1997. Application of Isotope-Ratio-Monitoring Gas Chromatography/Mass Spectrometry to Study Carbonization Reactions of FCCU Slurry Oils. Department of Geosciences, Department of Materials Science and Engineering, The Pennsylvania State University, University Park, PA. Abstracts of Papers of the American Chemical Society. 214:65-FUEL Part 1. pp. 938-941. |
Fouke, B.W., et al. May 2000. Depositional Facies and Aqueous-Solid Geochemistry of Travertine-Depositing Hot Springs (Angel Terrace, Mammoth Hot Springs, Yellowstone National Park, U.S.A.). Journal of Sedimentary Research. 70(3): 565-585. |
Gain, E. et al. May 2002 Ammonium nitrate wastewater treatment by coupled membrane electrolysis and electrodialysis. Journal of Applied Electrochemistry 32: 969-975. |
Genders, D. Sep. 1995. Electrochemical Salt Splitting. http://www.electrosynthesis.com/news/mwatts.html (accessed Feb. 5, 2009). |
Gillery et al. Bipolar membrane electrodialysis: the time has finally come! Presented 16th Intl. Forum on Appl. Electrochem; Cleaner Tech.—Challenges and Solutions. Nov. 10-14, 2002. Amelia Island Plantation, FL. 4 pages. Retrieved form the Internet on Aug. 14, 2009. http://www.ameridia.com/html.ebc.html. |
Goldberg et al. Jun. 2009. “CO2 Mineral Sequestration Studies in US”; National Energy Technology Laboratory; goldberg@netl.doe.gov; 10pp. |
Golden, D.C., et al. Jan. 2001. A Simple Inorganic Process for Formation of Carbonates, Magnetite, and Sulfides in Martian Meteorite ALH84001. American Mineralogist. 86: 370-375. |
Graff “Just Catch—CO2 Capture Technology” Aker Kvaerner; Pareto Clean Energy Tech Seminar Oct. 11, 2007 25pp. |
Green Car Congress “PKU Researchers Carry Out Aqueous Fischer-Tropsch Reaction for First Time”; www.greeencarcongress.com/2007/12/pku-researchers.html; Dec. 12, 2007; 2pp. |
Green Car Congress “Researcher Proposes System for Capture of Mobile Source CO2 Emissions Directly from Atmosphere”; www.greeencarcongress.com/2007/10/researcher-prop.html#more; Oct. 8, 2007; 4pp. |
Green Car Congress “Researchers Develop New Method for Ocean Sequestration of Carbon Dioxide Through Accelerated Weathering f Volcanic Rocks”; www.greeencarcongress.com/2007/11/researchers-dev.html#more; Nov. 7, 2007; 3pp. |
Gregerson, J. Aug. 1999. Conquering Corrosion (in concrete). Building Design & Construction. 40(8): 50. |
Groteklaes. “Dolomit”, Roempp, Fachgebiet: Chemie Unterthema: Mineralogie, Geochimie Feb. 2005, Retrieved from the internet: URL: http://www.roempp.com/prod/ [retrieved on Jun. 19, 2012]—with machine English translation. |
Hassan, A.M. et al. Jan. 1989. Corrosion Resistant Materials for Seawater RO Plants. Desalination. 74: 157-170. |
Haywood et al., “Carbon dioxide sequestration as stable carbonate minerals—environmental barriers”; Environmental Geology Aug. 2001 41:11-16; Springer-Verlag 2001. |
Hein, J.R. et al. Feb. 2006. Methanogen c calc te, 13C-depleted b valve shells, and gas hydrate from a mud volcano offshore southern Cal forn a. Geological Society of America. 34(2): 109-112. |
Hill et al. Mar. 18, 2006. “Preliminary Investigation of Carbon Sequestration Potential in Brine from Pennsylvania's Oriskany Sandstone Formation in Indiana County, PA”; The Energy Institute and the Department of Energy & Geo-Environmental Engineering. College of Engineering Research Symposium, Session 3C. 16pp. |
Holdgate, G.R., et al. 2009. Eocene-Miocene carbon-isotope and floral record from brown coal seams in the Gippsland Basin of southeast Australia. Global and Planetary Change. Nov. 2008; 65: 89-103. |
Holze, S. et al. Jan. 1994. Hydrogen Consuming Anodes for Energy Saving in Sodium Sulphate Electrolysis. Chem. Eng. Technol. 17: 382-389. |
Hong, et al. Treatment of Strongly Oxidized Water by Three-cell Electrodialysis Stack. Modern Food Science and Technology. 2005; 21(2):88-90. |
Horii, Y. et al. 2008. Novel evidence for natural formation of dioxins in ball clay. Chemosphere. Sep. 2007; 70: 1280-1289. |
Horkel, K., et al. Jan. 2009. Stable isotopic composition of cryptocrystalline magnesite from deposits in Turkey and Austria. Geophysical Research Abstracts. 11. (abstract only). |
Horner, G. et al. 2004. Isotope selective analysis of CO2 with tunable diode laser (TDL) spectroscopy in the NIR. The Analyst. 129: 772-778. |
Huijgen, W.J.J., et al. Dec. 2005. Carbon dioxide sequestration by mineral carbonation: Literature review update 2003-2004, ECN-C-05-022; Energy Research Centre of the Netherlands: Petten; pp. 1-37. |
Huijgen, W.J.J., et al. Feb. 2003. Carbon dioxide sequestration by mineral carbonation. ECN-C-03-016; Energy Research Centre of the Netherlands: Petten; pp. 1-42. |
Huijgen, W.J.J., et al. Nov. 2005. Mineral CO2 Sequestration by Steel Slag Carbonation. Environ. Sci. Technol. 39: 9676-9682. |
Huijgen, W.J.J., et al. Nov. 2006. Energy Consumption and Net CO2 Sequestration of Aqueous Mineral Carbonation. Ind. Eng. Chem. Res. 45: 9184-9194. |
Huntzinger, D.N. Carbon Dioxide Sequestration in Cement Kiln Dust Through Mineral Carbonation. Michigan Technological University, Jul. 2006 [online], [retrieved on Dec. 29, 2009]. <URL: http://www.geo.mtu.edu/˜dnhuntzi/DNHuntzingerETD.pdf>. |
Huntzinger, D.N. et al. Apr. 2009. A life-cycle assessment of Portland cement manufacturing: comparing the traditional process with alternative technologies. Journal of Cleaner Production. 17: 668-675. |
Huntzinger, D.N. et al.,“Carbon Dioxide Sequestration in Cement Kiln Dust through Mineral Carbonation”; Environmental Science & Technology, vol. 43, No. 6 (Feb. 2009) pp. 1986-1992. |
International search report and written opinion dated May 28, 2013 for PCT/US2011/023730. |
International Search Report dated Jan. 4, 2010 for PCT/US2009/062795. |
International Search Report dated Jan. 4, 2011 of EP 09818485.6. |
International Search Report dated Jan. 13, 2010 for PCT/US2009/059135. |
International Search Report dated Jan. 20, 2009 for PCT/US2007/010032. |
International Search Report dated Feb. 2, 2010 of PCT/US2009/059141. |
International Search Report dated Feb. 19, 2009 of PCT/US2008/088242. |
International Search Report dated Feb. 24, 2010 of PCT/US2009/067764. |
International Search Report dated Mar. 3, 2010 of EP 08867440.3. |
International Search Report dated Mar. 10, 2010 of PCT/US2010/022935. |
International Search Report dated Mar. 11, 2009 of PCT/2008/088246. |
International Search Report dated Mar. 11, 2009 of PCT/US2008/088318. |
International Search Report dated Mar. 21, 2011 of EP 10739828.1. |
International Search Report dated Mar. 25, 2011 of EP10737735.0. |
International Search Report dated Mar. 25, 2011 of EP10739829.9. |
International Search Report dated Apr. 6, 2011 of EP 10192919.8. |
International Search Report dated Apr. 13, 2011 of PCT/US2010/057821. |
International Search Report dated Apr. 19, 2011 of PCT/US2010/059835. |
International Search Report dated May 6, 2010 of EP 09716193.9. |
International Search Report dated May 18, 2011 of EP 09812407.6. |
International Search Report dated May 21, 2010 of PCT/US2009/064117. |
International Search Report dated Jun. 22, 2010 of EP 08772151.0. |
International Search Report dated Jul. 7, 2010 of PCT/US2010/026880. |
International Search Report dated Jul. 9, 2010 of PCT/US2010/025970. |
International Search Report dated Jul. 29, 2010 of EP 08873036.1. |
International Search Report dated Aug. 5, 2009 of PCT/2009/048511. |
International Search Report dated Sep. 8, 2009 of PCT/US2009/045722. |
International Search Report dated Sep. 13, 2010 of PCT/US2010/035041. |
International Search Report dated Sep. 17, 2008 of PCT/US2008/068564. |
International Search Report dated Sep. 17, 2009 of PCT/US2009/050756. |
International Search Report dated Sep. 22, 2009 of PCT/US2009/047711. |
International Search Report dated Oct. 19, 2009 of PCT/US2009/050223. |
International Search Report dated Oct. 30, 2009 of PCT/US2009/056573. |
International Search Report dated Dec. 14, 2009 of PCT/US2009/061748. |
International Search Report dated Dec. 14, 2010 of EP 09812408.4. |
International Search Report dated Mar. 4, 2011 of EP 10737736.8. |
Isotopic Signature Wikipedia (2010), http://en.wikipedia.org/wiki/Isotopic—signature, Apr. 14, 2009, 3 pp. |
Jensen, P. et al. Jul. 1992. ‘Bubbling reefs’ in the Kattegat: submarine landscapes of carbonate-cemented rocks support a diverse ecosystem at methane seeps. Marine Ecology Progress Series. 83: 103-112. |
Jones. 1996. Principles and Prevention of Corrosion. Second Edition. Lebanon, Indiana: Prentice Hall. pp. 50-52. |
Justnes, H. et al. “Pozzolanic, Amorphous Silica Produced from the Mineral Olivine.” Proceedings of the Seventh CANMET/ACI International Conference on Fly Ash, Silica Fume, Slag and Natural Pozzolans in Concrete, Jan. 2001. SP-199-44. pp. 769-781. |
Kohlmann et al., “Carbon Dioxide Emission Control by Mineral Carbonation: The Option for Finland”; INFUB 6th European Conference on Industrial Furnaces and Boilers Estoril Lisbon Portugal, Apr. 2-5, 2002 10pp. |
Kostowskyj et al. 2008. Silver nanowire catalysts for alkaline fuel cells. International Journal of Hydrogen Energy. 33: 5773-5778. |
Lackner, K. “Carbonate Chemistry for Sequestering Fossil Carbon”; Annual Review Energy Environ. Feb. 2002 27:193-232. |
Lackner, K.S. et al. “Carbon Dioxide Disposal in Carbonate Minerals.” Energy. Mar. 1995. 20(11): 1153-1170. |
Levy, D. “Burnt biomass causes short-term global cooling, long-term warming.” http://news-service.stanford.edu/news/2004/august4/biomass-84.html. 3 pages. Aug. 2004. |
Li, et al., “Using Electrolytic Method to Promote CO2 Sequestration in Serpentine by Mineral Carbonation,” Journal of China University of Mining and Technology, 36(6), pp. 817-821 Nov. 2007 (In Chinese, with English translation). |
Lin, C. et al. Use of Cement Kiln Dust, Fly Ash, and Recycling Technique in Low-Volume Road Rehabilitation. Transportation Research Record, Dec. 1992, No. 1345, pp. 19-27 (abstract) [online], [retrieved on Dec. 31, 2009] <URL: http://pubsindex.trb.org/view.aspx?id=370714>. |
Lopez-Capel, E. et al. Aug. 2005. Application of simultaneous thermal analysis mass spectrometry and stable carbon isotope analysis in a carbon sequestration study. Rapid Communications in Mass Spectrometry. 19: 3192-3198. |
Mazrou, S., et al. Sep. 1997. Sodium hydroxide and hydrochloric acid generation from sodium chloride and rock salt by electro-electrodialysis. Journal of Applied Electrochemistry 27: 558-567. |
McCrea, J.M. Jun. 1950. On the Isotopic Chemistry of Carbonates and a Paleotemperature Scale. The Journal of Chemical Physics. 18(6): 849-857. |
Melezhik, V.A., et al. Jan. 2001. Palaeproterozoic magnesite: lithological and isotopic evidence for playa/sabkha environments. Sedimentology. 48: 379-397. |
Merritt, R.C. Jan. 1971. Carbonate Leaching. The Extractive Metallurgy of Uranium: pp. 82-97. Colorado School of Mines Research Institute. Prepared Under Contract with the United States Atomic Energy Commission. |
Metz. 2005. IPCC Special Report on Carbon Dioxide Capture and Storage. Cambridge University. p. 324 <http://books.google.com/books?id=HWgRvPUgyvQC&dq=serpentine+olivine+close+by+cement+plant&source=gbs—navlinks—s> viewed Jul. 15, 2011. |
Mihalcea, R.M., et al. Dec. 1998. Diode-laser absorption measurements of CO2 near 2.0 μm at elevated temperatures. Applied Optics. 37(36): 8341-8347. |
Miljevic, N., et al. Apr. 2007. Potential Use of Environmental Isotopes in Pollutant Migration Studies. Environmental Isotopes in Pollutant Studies. 58: 251-262. |
Miller. “Mixing in Some Carbon.” NY Times, Mar. 21, 2010. Viewed on Feb. 16, 2012 at http://www.nytimes.com/201 0/03/22/business/energy-environment/22cement.html. |
Monteiro, et al. Incorporating carbon sequestration materials in civil infrastructure: A micro and nano-structural analysis. Cement and Concrete Composites. 2013; 40:14-20. |
Montes-Hernandez, G. et al.,“Mineral sequestration of CO2 by aqueous carbonation of coal combustion fly-ash.” Journal of Hazardous Materials vol. 161 May 2009. pp. 1347-1354. |
Mook, W.G., et al. Feb. 1968. Isotopic Equilibrium between Shells and Their Environment. Science. 159(3817): 874-875. |
Mook, W.G., et al. Feb. 1974. Carbon Isotope Fractionation Between Dissolved Bicarbonate and Gaseous Carbon Dioxide. 22:169-176. |
Mottana, A. et al. Jan. 1979. Der grosse Mineralienfuhrer, BLV Verlagsgesel lschaft mbH, Munchen, XP002577921, p. 194. (in German with English Translation). |
Mufson. “Khosla, Gates put up $100 million for Kior.” Washington Post, p. A 12, Oct. 22, 2013. |
Nayak, V.S. “Nonelectrolytic Production of Caustic Soda and Hydrochloric Acid from Sodium Chloride”; Ind. Eng. Chem. Res. Aug. 1996. 35: 3808-3811. |
Noda, H., et al. Sep. 1990. Electrochemical Reduction of Carbon Dioxide at Various Metal Electrodes in Aqueous Potassium Hydrogen Carbonate Solution. The Chemical Society of Japan. 63: 2459-2462. |
O'Connor et al., “Carbon Dioxide Sequestration by Direct Mineral Carbonation: Results From Recent Studies and Current Status”; Albany Research Center, Albany Oregon; Office of Fossil Energy, US Dept. of Energy; 1st Annual DOE Carbon Sequestration Conference, Washington DC, May 2001 12pp. |
O'Connor, W.K. et al. “Carbon dioxide sequestration: Aqueous mineral carbonation studies using olivine and serpentine.” (Aug. 2001). Albany Research Center, National Energy Technology Laboratory: Mineral Carbonation Workshop, Pittsburgh, PA. |
O'Neil, J.R., et al. Mar. 1971. C13 and O18 compositions in some fresh-water carbonates associated with ultramafic rocks and serpentines: western United States*. Geochimica et Cosmochimica Acta. 35: 687-697. |
Park, A., et al. Mar. 2004. CO2 mineral sequestration: physically activated dissolution of serpentine and pH swing process. Chemical Engineering Science 59 (22-23): 5241-5247. |
Perkins, S. Jul. 2004. Sea Change: Carbon Dioxide Imperils Marine Ecosystems. Science News. 166(3): 35. |
Philp, R.P. 2007. The emergence of stable isotopes in environmental and forensic geochemistry studies: a review. Environ Chem Lett. Aug. 2006; 5:57-66. |
Portier et al. 2005. Modeling CO2 solubility in pure water and NaCl-type waters from 0 to 300° C. and from 1 to 300 bar Application to the Utsira Formation at Sleipner. Chemical Geology. Dec. 2004; 217: 187-199. |
Power, I.M., et al. Dec. 2007. Biologically induced mineralization of dypingite by cyanobacteria from an alkaline wetland near Atlin, British Columbia, Canada. Geochemical Transactions. 8: 16 pages. |
Quay, P.D., et al. Apr. 1992. Oceanic Uptake of Fossil Fuel Co$—2$: Carbon—13 Evidence. Science. 256 (5053): 74-79. |
Rahardianto et al., “High recovery membrane desalting of low-salinity brackish water: Integration of accelerated precipitation softening with membrane RO”; Science Direct; Journal of Membrane Science 289 Nov. 2007 123-137. |
Rakib, M. et al. Jan. 1999. Behaviour of Nafion® 350 membrane in sodium sulfate electrochemical splitting: continuous process modelling and pilot scale tests. Journal of Applied Electrochemistry. 29: 1439-1448. |
Rau, G. Oct. 2004. Possible use of Fe/CO2 fuel cells for CO2 mitigation plus H2 and electricity production. Energy Conversion and Management. 45: 2143-2152. |
Raz et al., “Formation of High-Magnesium Calcites via an Amorphous Precursor Phase: Possible Biological Implications”; Advanced Materials; Adv. Mater. Sep. 2000 vol. 12, No. 1; 5pp. |
Rosenthal, E., “Cement Industry is at Center of Climate Change Debate” New York Times; www.nytimes.com/2007/10/26/business/worldbusiness/26cement.html″ref=todayspaper ; Oct. 2007; 4pp. |
Saad, N. et al. Jan. 2009. Measurement of Isotopic CO2 in Dissolved Inorganic Carbons of Water Samples from Various Origins Using Wavelength-Scanned Cavity Ring-Down Spectrophotometer. Geophysical Research Abstracts. 11. (abstract only). |
Sadhwani et al., Nov. 2005. “Case Studies on environmental impact of seawater desalination” Science Direct; http://www.sciencedirect.com/science?—ob=ArticleURL&—udi=B6TFX-4HMX97J-3&—u . . . 3pp. |
Sakata, M. Jan. 1987. Movement and Neutralization of Alkaline Leachate at Coal Ash Disposal Sites. Environ. Sci. Technol. 21(8): 771-777. |
Sample, J.C. et al. Mar. 1995. Isotope Geochemistry of Syntectonic Carbonate Cements and Veins from the Oregon Margin: Implications for the Hydrogelogic Evolution of the Accretionary Wedge. Proceedings of the Ocean Drilling Program, Scientific Results. 146: 137-148. |
Sasakawa, M., et al. Carbonic Isotopic Characterization for the Origin of Excess Methane in Subsurface Seawater. Journal of Geophysical Research, vol. 113 (abstract) [online], Mar. 11, 2008 [retrieved on Jan. 1, 2010] <URL: http://www.agu.org/pubs/crossref/2008/2007JC004217.shtml>. |
Schouten, S., et al. Jun. 2004. Stable Carbon Isotopic Fractionations Associated with Inorganic Carbon Fixation by Anaerobic Ammonium-Oxidizing Bacteria. Applied and Environmental Microbiology. 70(6): 3785-3788. |
Schroll, E. Dec. 2002. Genesis of magnesite deposits in the view of isotope geochemistry. Boletim Paranaense de Geociencias. 50: 59-68. |
Schwab, E. Jan. 2004. Calciumhydroxid, XP-002577920. Retrieved from the Internet: <URL:http://www.roempp.com/prod/indexl.html> (in German with English Translation). |
Serizawa et al., “Cell-compatible properties of calcium carbonates and hydroxyapatite deposited on ultrathin poly (vinyl alcohol)-coated polyethylene films”; J. Biomater. Sci. Polymer Edn., vol. 14, No. 7 Apr. 2003 pp. 653-663. |
Sethi, S. et al. Jun. 2006. Existing & Emerging Concentrate Minimization & Disposal Practices for Membrane Systems. Florida Water Resources Journal. pp. 38, 40, 42, 44, 46, 48. |
Shaffer, R. Aug. 2008 A Devlish Green Angel. Fast Company. N127: 92-97. |
Shaffer. “The King of Green Investing.” Fast Company, Jul. 1, 2008. Viewed on Feb. 16, 2012 at http://www.fastcompany.com/magazine/127/a-devilish-green-angel.html. |
Shell Global Solutions, 2003. “ADIP-X and Sulfinol-X—new regenerable acid-gas removal processes”; Shell Global Solutions International; OG 130210370903- En(A); www.shellglobalsoultions.com 2 pp (presented at the 12th International Oil, Gas, and Petrochemicals Congress, Tehran, Iran Feb. 24-26, 2003). |
Sheppard, S.M.F., et al. 1970. Fractionation of Carbon and Oxygen Isotopes and Magnesium between Coexisting Metamorphic Calcite and Dolomite. Contr. Mineral. And Petrol. Dec. 1969; 26. 161-198. |
Sial, A.N., et al. Jul. 2000. Carbon isotope fluctuations in Precambrian carbonate sequences of several localities in Brazil. An. Acad. Bras. Ci. 72(4): 539-558. |
Skrzypek, G. et al. Jul. 2006. δ13C analyses of calcium carbonate: comparison between the GasBench and elemental analyzer techniques. Rapid Communications in Mass Spectrometry. 20: 2915-2920. |
Socolow, R. Sep. 1997 Fuels Decarbonization and Carbon Sequestration: Report of a Workshop. Center for Energy and Environmental Studies School of Engineering and Applied Science. Princeton University, Princeton, NJ. |
Soong, Y. et al. Jan. 2004. Experimental and simulation studies on mineral trapping of CO2 with brine. Energy Conversion and Management. 45: 1845-1859. |
St. John. “Vinod Khosla: Carbon-Capturing Cement Worth as Much as GE's Power Plant Business.” Greentechmedia, Sep. 15, 2009. Viewed on Feb. 16, 2012 at http://www.greentechmedia.com/green-light/post/vinod-khosla-carbon-capturing-cement-worthas-much-as-ges-power-plant-busin/. |
Stanley, S.M., et al. Sep. 2002. Low-magnesium calcite produced by coralline algae in seawater of Late Cretaceous composition. PNAS. 99(24): 15323-15326. |
Stepkowska, et al. Calcite, Vaterite and Aragonite forming on cement hydration from liquid and gaseous phase. Journal of Thermal Analysis and Calorimetry. 2003; 73:247-269. |
Tari, et al. Colloidal processing of calcium carbonate. Ceramics International. 1998; 24:527-532. |
Tececo Pty Ltd, “Eco-Cement”; www.tececo.com/simple.eco-cement.php; Dec. 29, 2008; 6pp. |
Technology for Commercialization of Slag. Feb. 1995. New Technology Japan. ISSN: 0385-6542. p35. |
Tsuni, et al. Effects of Trace Lanthanum ion on the Stability of Vaterite and Transformation from Vaterite to Calcite in an Aquatic System. Bulletin of the Chemical Society of Japan. 2001; 74(3):479-486. |
Turner, J.A. Jul. 1999. “A Realizable Renewable Energy Future.” Science. 285 (5428): 687-689. |
Uibu, M. et al. “CO2 mineral sequestration in oil-shale wastes from Estonian power production.” Journal of Environmental Management vol. 90 Sep. 2009. pp. 1253-1260. |
Uibu, M. et al.,“Mineral trapping of CO2 via oil shale ash aqueous carbonation: controlling mechanism of process rate and development of continuous-flow reactor system.” Oil Shale. vol. 26, No. 1 (Jan. 2009) pp. 40-58. |
Uliasz-Bochenczyk, A. et al. “Utilization of Carbon Dioxide in Fly Ash and Water Mixtures.” Chemical Engineering Research and Design. Apr. 2006. 84(A9): 843-846. |
Vagin, S.P., et al. Jul. 1979. Measurement of the Temperature of Gas Media Containing Carbon Dioxide by the Laser-Probing Method. Plenum. |
Various authors. 2001. “Calcium Carbonate: From the Cretaceous Period Into the 21st Century.” Birkhauser Verlag, pp. 1-54. <http://books.google.com/books?id=pbkKGa19k5QC&Ipg=PA15&ots=gjUUiWmGIR &dq=vaterite%20limestone&pg=PA54#v=twopage&q&f=true> viewed Jul. 14, 2011. |
Wang, W., et al. Jan. 2005. Effects of biodegradation on the carbon isotopic composition of natural gas—A case study in the bamianhe oil field of the Jiyang Depression, Eastern China. Geochemical Journal. 39(4): 301-309. (abstract) [online] [retrieved on Dec. 29, 2009] <URL: http://www/jstage.jst.go.jp/article/geochemj/39/4/39—301/—article> ab. |
Webber, M.E., et al. Feb. 2001. In situ combustion measurements of CO2 by use of a distributed-feedback diode-laser sensor near 2.0 μm. Applied Optics. 40(6): 821-828. |
Wen-Zhi et al., “Using Electrolytic Method to Promote CO2 Sequestration in Serpentine by Mineral Carbonation”; Journal of China University of Mining and Technology; vol. 36, No. 6; Nov. 2007 (Publication and English Translation). |
Wilson, S.A., et al. Dec. 2009. Carbon Dioxide Fixation within Mine Wastes of Ultramafic-Hosted Ore Deposits: Examples from the Clinton Creek and Cassiar Chrysotile Deposits, Canada. Society of Economic Geologists, Inc. 104: 95-112. |
Winschel, R.A., et al. Stable Carbon Isotope Analysis of Coal/Petroleum Coprocessing Products. Preprints of Papers, American Chemical Society, Division of Fuel Chemistry, Jan. 1, 1988, vol. 33, No. 1, pp. 114-121 [online], [retrieved on Dec. 29, 2009] <URL: http://www.anl.gov/PCS/acsfuel/preprint%20archive/Files/33—1—TORONTO—06-88—0114.PDF>. |
Wright, L.L., et al. Mar. 1993. “U.S. Carbon Offset Potential Using Biomass Energy Systems.” Water, Air, and Soil Pollution. 70: 483-497. |
Zedef, V., et al. Aug. 2000. Genesis of Vein Stockwork and Sedimentary Magnesite and Hydromagnesite Deposits in the Ultramafic Terranes of Southwestern Turkey: A Stable Isotope Study. 95: 429-446. |
Zhang, C.L. et al. Feb. 2001. Temperature-dependent oxygen and carbon isotope fractionations of biogenic siderite. Geochimica et Cosmochimica Acta. 65(14): 2257-2271. |
Donnet, et al. Use of seeds to control precipitation of calcium carbonate and determination of seed nature. Langmuir. Jan. 4, 2005;21(1):100-8. |
European search report and opinion dated Aug. 4, 2014 for EP Application No. 09810860.8. |
Matilla, et al. Production of precipitated calcium carbonate from steel converter slag and other calcium-containing industrial wastes and residues. Advances in inorganic chemistry. 2014; vol. 66, Ch. 10. 347-384. |
Rau, et al. Capturing and sequestering flue-gas CO2 using a wet limestone scrubber. 2nd National Conference on Carbon Sequestration Washington D.C., May 5-8, 2003. http://www.netl.doe.gov/publications/proceedings/03/carbon-seq/pdfs/167.pdf. |
Wei, et al. High Surface Area Calcium Carbonate: Pore Structural Properties and Sulfation Characteristics, Industrial & Engineering Chemistry Research. 1997; 36(6):2141-2148. |
Gomez-Morales, et al. Nucleation of calcium carbonate at different initial pH conditions. Journal of Crystal Growth. 1996; 169(2):331-338. |
Matilla, et al. Reduced Limestone Consumption in Steel Manufacturing Using a pseudo-catalytic calcium lixiviant. Energy Fuels. 2014; 28:4068-4074. |
Rawlins. Geological sequestration of carbon dioxide by hydrous carbonate formation in steelmaking slag. Missouri Curtis Law Wilson Library, Doctoral Dissertations. Paper 1927, Spring 2008. |
Shtepenko, et al. The effect of carbon dioxide on b-dicalcium silicate and Portland cement. Chemical Engineering Journal, vol. 118, Published 2006, pp. 107-118. |
Verdoes, et al. Determination of nucleation and growth rates from induction times in seeded and unseeded precipitation of calcium carbonate. Journal of Crystal Growth. 1992; 118:401-413. |
Number | Date | Country | |
---|---|---|---|
20140332401 A1 | Nov 2014 | US |
Number | Date | Country | |
---|---|---|---|
61151472 | Feb 2009 | US | |
61151484 | Feb 2009 | US | |
61151481 | Feb 2009 | US |
Number | Date | Country | |
---|---|---|---|
Parent | 12991898 | US | |
Child | 14320332 | US |