In many industrial processes a large amount of hydroxide ions in a base solution is utilized to achieve a desired 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. One method by which the hydroxide ions are produced is by an electrochemical system as disclosed in the above-referenced patent applications, herein incorporated by reference in their entirety. In producing the hydroxide ions electrochemically, a large amount of electrical energy is used; consequently, minimizing the electrical energy used is highly desired.
This invention pertains to a low-voltage, low-energy electrochemical system and method of removing protons, or producing hydroxide ions or both in a cathode electrolyte while dissolving carbon dioxide gas in the cathode electrolyte. In the system, in various embodiments, the cathode electrolyte is partitioned into a first cathode electrolyte compartment and a second cathode electrolyte compartment such that the cathode electrolytes in the two cathode electrolyte compartments are in contact with each other. However, since gas flow between the two cathode electrolyte compartments is restricted, carbon dioxide gas provided to the first cathode electrolyte compartment is prevented from contacting cathode electrolyte in the second cathode electrolyte compartment.
In the system, the cathode is in contact with the cathode electrolyte in the second cathode electrolyte compartment and both the cathode electrolyte and the anode electrolyte are composed of an aqueous solution. In the system, by absorbing carbon dioxide in the cathode electrolyte to form carbonate and bicarbonate ions and also to affect the pH of the cathode electrolyte, the hydroxide ions are produced in the cathode electrolyte with a relatively low voltage across the anode and cathode e.g., a voltage of 3V or less, such as 2V or less, or 1V or less.
In the system, water in the cathode electrolyte is reduced to hydrogen gas and hydroxide ions at the cathode. At the anode, hydrogen gas, provided to the anode from an external source, is oxidized to hydrogen ions. In some embodiments, the hydrogen gas produced at the cathode is directed to the anode for oxidation to hydrogen ions. In the system, a gas, e.g., oxygen or chlorine is not produced at the anode when the low voltage is applied across the anode and cathode. In the system, hydrogen ions produced at the anode migrate into the anode electrolyte to form an acid solution in the anode electrolyte; and, in the system, hydroxide ions produced at the cathode migrate into the cathode electrolyte to produce the base solution in the cathode electrolyte.
In the system, the carbon dioxide gas provided to the cathode electrolyte in the first cathode electrolyte compartment dissolves to produce carbonic acid. Depending on the pH of the cathode electrolyte, the carbonic acid in the cathode electrolyte dissociate into carbonate ions and bicarbonate ions. Thus, in the system, since the cathode electrolyte in the first compartment can mix with the cathode electrolyte in the second cathode electrolyte compartment, mixing of the cathode electrolytes in the two cathode electrolyte compartments will result in the cathode electrolyte comprising carbonic acid, hydroxide ions and/or carbonate ions and/or bicarbonate ions.
In the system, the voltage across the cathode and anode is dependent on several factors including the difference in the pH value of the anode electrolyte and the cathode electrolyte, as well as the ohmic resistances between the cathode and anode. Thus, in various embodiments, by controlling the difference in pH between the cathode electrolyte and the anode electrolyte, e.g., by dissolving more or less carbon dioxide in the cathode electrolyte, the system will produce hydroxide ions and/or carbonate ions and/or bicarbonate ions in the cathode electrolyte while minimizing the voltage across the anode and cathode, thus minimizing the use of electrical energy.
In one embodiment, the invention provides a system comprising a cathode compartment partitioned into a first cathode electrolyte compartment and a second cathode electrolyte compartment by a partition wherein, cathode electrolyte in the second cathode electrolyte compartment is in contact with a cathode, and anode electrolyte in an anode compartment is in contact with an anode.
In another embodiment, the invention provides a method comprising directing a gas into a cathode electrolyte in a first cathode electrolyte compartment; and applying a voltage across a cathode in contact with cathode electrolyte in a second cathode electrolyte compartment that is partitioned from the first cathode electrolyte compartment, and an anode that is in contact with an anode electrolyte.
In various embodiments, by partitioning the cathode electrolyte into the first and second cathode electrolytes compartments, and by restricting carbon dioxide gas to the first cathode electrolyte compartment, contact between the carbon dioxide gas and the cathode and/or with the anode and/or with other electrolytes in the system is restricted. Thus, advantageously, in the system, carbon dioxide gas from a variety of sources, including carbon dioxide from industrial waste gases, e.g., from burning fossil fuels in electrical generating plants and from cement plants, can be utilized. Also, by restricting carbon dioxide gas to the first cathode electrolyte compartment, mixing of carbon dioxide gas with other gases in the system, e.g., mixing of the carbon dioxide with hydrogen gas generated at the cathode, or mixing of carbon dioxide with hydrogen gas supplied to the anode, is avoided.
The following drawings illustrate by way of examples and not by limitation embodiments of the present system and method.
In the following detailed description, unless defined otherwise, all technical and scientific terms have the same meaning as commonly understood by one of ordinary skill in the art to which this invention pertains. Herein, all cited publications and patents are incorporated by reference herein in their entirety. Herein, the date cited for publication may differ from the actual publication dates; thus, an actual publication should be independently confirmed. Herein, the singular “a,” “an,” and “the” include plural references unless the context clearly dictates otherwise.
Herein, exemplary systems and methods are disclosed wherein sodium chloride solution is used in one compartment between the anode electrolyte and cathode electrolyte to produce sodium hydroxide and/or sodium carbonate ions and/or sodium bicarbonate in the cathode electrolyte, and hydrochloric acid in the anode electrolyte. However, as will be appreciated by one ordinarily skilled in the art, the system and method are not limited to the use of sodium chloride solution as disclosed in these exemplary embodiments since the system and method are capable of using an equivalent salt solution, e.g., an aqueous solution of potassium sulfate and the like to produce an equivalent result. Similarly, in preparing the electrolytes for the system, it will be appreciated that water from various sources can be used including seawater, brackish water, brines or naturally occurring fresh water, provided that the water is purified to an acceptable level for use in the system. Therefore, to the extent that such equivalents embody the present system and method, these equivalents are within the scope of the appended claims.
As disclosed in U.S. Provisional Patent Application No. 61/081,299 filed Jul. 16, 2008, titled: “Low Energy pH Modulation for Carbon Sequestration Using Hydrogen Absorptive Metal Catalysts”, herein incorporated by reference in its entirety, in various embodiments, the anode and the cathode of the present system may comprise a noble metal, a transition metal, a platinum group metal, a metal of Groups IVB, VB, VIB, or VIII of the periodic table of elements, alloys of these metals, or oxides of these metals. Exemplary materials include palladium, platinum, iridium, rhodium, ruthenium, titanium, zirconium, chromium, iron, cobalt, nickel, palladium-silver alloys, and palladium-copper alloys. In various embodiments, the cathode and/or the anode may be coated with a reactive coating comprising a metal, a metal alloy, or an oxide, formed by sputtering, electroplating, vapor deposition, or any convenient method of producing a layer of reactive coating on the surface of the cathode and/or anode. In other embodiments, the cathode and/or the anode may comprise a coating designed to provide selective penetration and/or release of certain chemicals or hydroxide ions and/or anti-fouling protection. Exemplary coatings include non-metallic polymers; in specific embodiments herein, an anode fabricated from a 20-mesh Ni gauze material, and a cathode fabricated from a 100-mesh Pt gauze material was used.
In various embodiments, the electrolyte in the cathode compartment is charged with CO2, e.g., by bubbling CO2 into the electrolyte. The source of CO2 may include CO2 in waste gases of an industrial plant such as the flue gas of a fossil fuelled electrical power generating plant. In various embodiments, the system includes a gas mixer/gas absorber that enhances the absorption of CO2 in the cathode electrolyte. In one embodiment, the gas mixer/gas absorber comprised a series of spray nozzles that produced a flat sheet or curtain of liquid through which the gas was directed for absorption; in another embodiment the gas mixer/gas absorber comprised spray absorber that created a mist into which the gas was directed for absorption; other commercially available gas/liquid absorber e.g., an absorber available from Neumann Systems, Colorado, USA may be used. In operation, the cathode and anode compartments are filled with electrolytes and a voltage is applied across the cathode and anode. In various embodiments, the voltage is adjusted to a level to cause production of hydrogen gas at the cathode without producing a gas, e.g., chlorine or oxygen, at the anode. In various embodiments, the system includes a cathode and an anode that facilitate reactions whereby the cathode electrolyte is enriched with hydroxide ions and the anode electrolyte is enriched with hydrogen ions.
Reduction of water at the cathode produces hydroxide ions that migrate into the cathode electrolyte. The production of hydroxide ions in the cathode electrolyte surrounding the cathode may elevate the pH of the cathode electrolyte. In various embodiments, the solution with the elevated pH is used in situ, or is drawn off and utilized in a separate reaction, e.g., to sequester CO2 as described therein. Depending on the balance of the rate of hydroxide ion production versus the rate of carbon dioxide absorption in the cathode electrolyte, it is possible for the pH to remain the same or even decrease, as hydroxide ions are consumed in reaction with protons from dissociation of carbonic acid into carbonate and bicarbonate ions.
Oxidation of hydrogen gas at the anode results in production of hydrogen ions at the anode that desorb from the structure of the anode and migrate into the electrolyte surrounding the anode, resulting in a lowering of the pH of the anode electrolyte. Thus, the pH of the electrolytes in the system can be adjusted by controlling the voltage across the cathode and anode and using electrodes comprised of a material capable of absorbing or desorbing hydrogen ions. In various embodiments, the process generates hydroxide ions in solution with less than a 1:1 ratio of CO2 molecules released into the environment per hydroxide ion generated.
In various embodiments, the system includes an inlet system configured to deliver carbon dioxide gas into the first cathode electrolyte compartment; the carbon dioxide includes carbon dioxide from waste gases of fossil fuelled electrical power generating plants, cement plants and the like. In various embodiments, the carbon dioxide gas delivered to the inlet system may comprise other gases, e.g., oxides of nitrogen (nitrous oxide, nitric oxide) and sulfur gases (sulfur dioxide, hydrogen sulfide); in various embodiments, the system includes a gas treatment system that is capable of removing constituents in the carbon dioxide gas before the gas is utilized in the cathode compartment.
As disclosed in U.S. Provisional Patent Application No. 61/091,729 filed Aug. 25, 2008, titled: “Low Energy Absorption of Hydrogen Ion from an Electrolyte Solution into a Solid Material”, herein incorporated by reference in its entirety, the present method in one embodiment pertains to a low-energy absorption of hydrogen ions from an electrolytic fluid into a solid material. In some embodiments, a hydrogen ion transfer element is configured to transfer hydrogen ions between the cathode electrolyte and anode electrolytes in the system. In various embodiments, the process pertains to removal of protons from bicarbonate ions or carbonic acid in the cathode electrolyte. In various embodiments, hydrogen ions are transferred from one electrolyte solution to another using a hydrogen transfer element that includes a hydrogen storage material such as a palladium membrane, foil, or film. In various embodiments, hydrogen ions are obtained from a proton donor, e.g., carbonic acid, bicarbonate ion, water, and the like and are transferred to a second electrolyte solution. In various embodiments, hydrogen ions and/or carbonate ions are produced by contacting an electrolyte solution with CO2, to remove protons from bicarbonate ions present in the solution. In various embodiments, transferring the hydrogen ions to a second electrolyte solution while contacting a first electrolyte solution with CO2 allows for a greater concentration of bicarbonate ions in the first electrolyte solution.
In various embodiments, the anode electrolyte, enriched with hydrogen ions, can be utilized for a variety of applications including dissolving minerals to produce a solution of divalent cations for use in sequestering carbon dioxide. In various embodiments, the electrolytic cell includes a cathode and/or an anode capable of facilitating reactions to remove hydrogen ions from an electrolytic fluid from a donor molecule in an electrolytic fluid, e.g., to enrich a solution with hydroxide ions or hydrogen ions, where donor molecules of interest include carbonic acid, bicarbonate ions, water, and the like.
The absorption of hydrogen ions from a solution into the structure of a cathode produces an excess of hydroxide ions in the solution surrounding the cathode. In various embodiments, the cathode electrolyte can be used in situ, or drawn off and to utilized in a separate reaction, for a variety of purposes, including the sequestration of CO2 as described therein. In various embodiments, the hydrogen ions can be desorbed from the structure when arranged as an anode to produce excess hydrogen ions in a solution in contact with the anode to lower the pH of the solution.
In some embodiments, the electrolyte solution in a half-cell is charged with ionized forms of CO2 for example, by bubbling CO2 from a source into the electrolyte solution. Ionized forms of CO2 include bicarbonate ions (HCO3−) and carbonate ions (CO3−2). The source of carbon dioxide can be, for instance, a waste feed from an industrial plant such as flue gas from a fossil fuelled electrical power generating plant or a cement plant. The CO2 can be introduced into the electrolyte solution with a sparger, in some embodiments, or by contact with an aqueous liquid spray. In some systems, the reservoir can be enriched with bicarbonate and/or carbonate ions by introducing CO2 gas into the reservoir as hydrogen is removed. In some systems, an electrolyte solution within a reservoir can be flushed to prevent a build-up of hydrogen ions within the reservoir that would oppose the continued transfer of hydrogen ions between the two reservoirs. In some embodiments, the voltage applied across the anode and the cathode is less than 1.24 volts or less than 1.0 volt. The half-cell can include a mixer to help the CO2 absorb and dissolve into the electrolyte solution. In various embodiments, a conductive electrolyte solution can be employed as the electrolyte solution within the reservoir and in some embodiments the electrolyte solution comprises seawater, brine, or brackish water.
As disclosed herein, in various embodiments, hydroxide ions are produced in the cathode electrolyte in a first cathode electrolyte compartment by applying a relatively low voltage, e.g., less than 3V, such as less than 2V, or less than 1V or less than 0.8V or less than 0.6V or less than 0.4V across the cathode and anode while dissolving carbon dioxide in the cathode electrolyte in a second cathode electrolyte compartment. In various embodiments, hydroxide ions are produced from water in the cathode electrolyte in contact with the cathode, and bicarbonate ions and/or carbonate ions are produced in the cathode electrolyte in the first cathode electrolyte compartment by dissolving carbon dioxide gas in the cathode electrolyte in the first cathode electrolyte compartment.
In various embodiments, cathode electrolyte in the first cathode electrolyte compartment is in contact with the cathode electrolyte in the second cathode electrolyte compartment. The cathode electrolyte in the first cathode electrolyte compartment may comprises a gas or a gas dissolved in the cathode electrolyte. For example, the carbon dioxide is present as carbon dioxide gas and/or as dissolved carbon dioxide in the cathode electrolyte. In various embodiments, the carbon dioxide gas is isolated from cathode electrolyte in the second cathode electrolyte compartment.
In various embodiments, the cathode electrolyte in the first cathode electrolyte compartment comprises hydroxide ions, carbonic acid, carbonate ions and/or bicarbonate ions. Similarly, the cathode electrolyte in the second cathode electrolyte compartment comprises dissolved carbon dioxide. In other embodiments, the cathode electrolyte in the second cathode electrolyte compartment comprises hydroxide ions, carbonic acid, carbonate ions and/or bicarbonate ions.
In various embodiments, the system is configured to produce hydroxide ions in the second cathode electrolyte compartment with less than 2V applied across the anode and cathode. The system is also configured to produce hydrogen gas at the cathode. In various embodiments, the system does not produce a gas at the anode; the system, however, is configured to migrate hydroxide ions from the second cathode electrolyte compartment to the first cathode electrolyte compartment. In other embodiments, the system comprises a hydrogen gas delivery system configured to direct hydrogen gas produced at the cathode to the anode. In one embodiment, the first cathode electrolyte compartment is operatively connected to an industrial waste gas system that comprises carbon dioxide. In various embodiments, the carbon dioxide is derived from combusting fossil fuels.
In other embodiments, the cathode compartment is operatively connected to a waste gas treatment system, wherein the waste gas system comprises carbon dioxide. In other embodiments, the cathode compartment is operatively connected to a hydroxide, carbonate and/or bicarbonate precipitation system. In various embodiments, the precipitation system is configured to utilize the cathode electrolyte to produce hydroxide, carbonates and/or divalent cation bicarbonates. In various embodiments, the anode and cathode are operatively connected to an off-peak electrical power-supply system.
In various embodiments, the system comprises an ion exchange membrane located between the anode compartment and the cathode compartment. In various embodiments, the ion exchange membranes comprise a cation exchange membrane separating the cathode electrolyte in the second cathode electrolyte compartment from a third electrolyte. In various embodiments, the ion exchange membrane comprises an anion exchange membrane separating the anode electrolyte from the third electrolyte.
In various embodiments, the third electrolyte comprises sodium ions and chloride ions; the system is configured to migrate sodium ions from the third electrolyte to cathode electrolyte through the cation exchange membrane, and migrate chloride ions from the third electrolyte to the anode electrolyte through the anion exchange membrane.
In various embodiments, the system is configured to produce sodium hydroxide in the cathode electrolyte; and the system is also configured to produce sodium hydroxide, sodium carbonate and/or sodium bicarbonate in the cathode electrolyte. In various embodiments, the system is configured to produce partially desalinated water in the third electrolyte; and the partially desalinated water is operatively connected to a water treatment system. In other embodiments, the cathode electrolyte is operatively connected to a first carbon dioxide gas/liquid contactor configured to dissolve carbon dioxide in the cathode electrolyte; the system is configured to produce a pH differential of between 0 and 14 or greater pH units between the anode and cathode electrolytes.
In various embodiments, by the method, hydroxide ions, carbonic acid, carbonates ions and/or bicarbonate ions are produced in the first cathode electrolyte compartment; and carbonate ions and/or bicarbonate ions are produced in the second cathode electrolyte compartment. In various embodiments, hydrogen gas is produced at the cathode and hydrogen ions are produced at the anode.
In various embodiments, by the method, a gas is not produced at the anode; however, hydrogen gas is produced at the cathode and in some embodiments is directed to the anode. In various embodiments, the voltage across the anode and cathode is less than 2V. By the method, sodium ions are migrated from the third electrolyte to the cathode electrolyte across the cation exchange membrane, and chloride ions are migrated from the third electrolyte to the anode electrolyte across the anion exchange membrane. By the method, sodium carbonate, sodium bicarbonate or sodium hydroxides are produced in the cathode electrolyte, and hydrochloric acid is produced in the anode electrolyte. By the method, acid produced in the anode electrolyte is utilized to dissolve a mafic mineral and/or a cellulose material.
By the method, partially desalinated water is produced in the third electrolyte. In one embodiment, divalent cation hydroxide, carbonate and/or bicarbonate compounds are produced by contacting the cathode electrolyte with a solution comprising divalent cations, e.g., calcium and magnesium ions. In one embodiment, the method includes a step of withdrawing a first portion of the cathode electrolyte; dissolving carbon dioxide in the first portion of cathode electrolyte to produce a first enriched carbonated cathode electrolyte; and replenishing cathode electrolyte with the first enriched carbonated cathode electrolyte. In other embodiments, the method comprises the steps of withdrawing a second portion of the cathode electrolyte; dissolving carbon dioxide in the second portion of cathode electrolyte to produce a second enriched carbonated cathode electrolyte; and contacting the second enriched carbonated cathode electrolyte with a divalent cation solution to produce divalent cation carbonates. In various embodiments, the method includes applying an off-peak electrical power-supply across the cathode and anode to provide the voltage across the anode and cathode.
By the system and method, hydrogen gas is produced at the cathode from water in the cathode electrolyte. In various embodiments, a gas, e.g., oxygen or chlorine is not produced at the anode; in various embodiments, hydrogen gas from an external source is provided to the anode where it is oxidized to hydrogen ions that migrate into the anode electrolyte to produce an acid in the anode electrolyte.
In various embodiments, hydroxide ions produced at the cathode in the second cathode electrolyte compartment migrate into the cathode electrolyte and may cause the pH of the cathode electrolyte to adjust, e.g., the pH of the cathode electrolyte may increase, decrease or remain the same, depending on the rate of removal of cathode electrolyte from the system. In various embodiments, depending on the pH of the cathode electrolyte and the rate of dissolution of carbon dioxide in the first cathode electrolyte compartment, carbon dioxide gas in contact with cathode electrolyte in the first cathode compartment will dissolve in the cathode electrolyte to produce carbonic acid which may dissociate to bicarbonate and/or carbonate ions in the cathode electrolyte, depending on the pH of the cathode electrolyte. Thus, in various embodiments, since the cathode electrolyte in the first and second cathode electrolyte compartment can intermix, the cathode electrolyte may contain carbonic acid, hydroxide ions and/or carbonate ions and/or bicarbonate ions.
In various embodiments, the system includes a hydrogen gas transfer system configured to direct hydrogen gas to the anode where the hydrogen gas is oxidized, without intermixing the hydrogen gas with carbon dioxide present in the cathode electrolyte compartment. In various embodiments, the hydrogen gas produced at the cathode is directed to the anode for oxidation to hydrogen ions.
In various 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 via an outflow stream. In some embodiments, a portion of the withdrawn cathode electrolyte is contacted with carbon dioxide gas in an exogenous carbon dioxide gas/liquid contactor to increase the absorbed carbon dioxide content in the electrolyte solution. In some embodiments, the solution with the absorbed carbon dioxide is returned to the cathode compartment; in other embodiments, the solution with the absorbed carbon dioxide is reacted with a solution comprising divalent cations to produce divalent cation hydroxides, carbonates and/or bicarbonates. In various embodiments, the system and method are configurable for batch, semi-batch or continuous flow operation.
In various embodiments, industrial waste gas containing carbon dioxide is utilized to produce carbonate and bicarbonate ions in the cathode electrolyte. In some embodiments, carbon dioxide is prevented from mixing with other gases in the system, e.g., with hydrogen gas generated at the cathode or with hydrogen gas oxidized at the anode. In other embodiments, carbon dioxide gas is prevented from contacting the cathode and/or anode.
In various embodiments, the pH of the cathode electrolyte is adjusted by producing hydroxide ions from water at the cathode, and allowing the hydroxide ions to migrate into the cathode electrolyte. The pH is also adjusted by dissolving carbon dioxide gas in the cathode electrolyte to produce carbonic acid and carbonic ion species in the electrolyte that react with the hydroxide ions to produce carbonate ions, or bicarbonate ions, or only carbonate ions, or only bicarbonate ions, or mixtures thereof.
With reference to
As is illustrated in a cross-section view in
In positioning partition 103 in the cathode compartment 102, cathode electrolyte in the cathode compartment is partitioned into the first cathode electrolyte compartment 104 and the second cathode electrolyte compartment 106. In various embodiments, partition 103 is configured such that cathode electrolyte in cathode compartment 102 can flow between the first and second electrolyte compartments; however, partition 103 is also configured such that a gas in the first electrolyte compartment 104 is prevented from mixing with other fluids in the system when cathode electrolyte is present in the cathode compartment 102, at least at a depth that the liquid seals the passageway between the downward-tapering channel 107 in the first cathode electrolyte compartment 104 and the second cathode electrolyte compartment 106.
With reference to
With reference to
CO2+H2O<==>H2CO3<==>H++HCO3−<==>H++CO32−
As cathode electrolyte in the first cathode electrolyte compartment 104 may mix with cathode electrolyte in the second cathode electrolyte compartment 106 and vice versa, carbonic acid, bicarbonate and carbonate ions formed in the first cathode electrolyte compartment 104 by absorption of carbon dioxide in the cathode electrolyte may migrate and equilibrate with cathode electrolyte in the second cathode electrolyte compartment 106. Thus, in various embodiments, cathode electrolyte in the first cathode electrolyte compartment may comprise dissolved and un-dissolved carbon dioxide gas, and/or carbonic acid, and/or bicarbonate ions and/or carbonate ions; while cathode electrolyte in the second cathode electrolyte compartment may comprise dissolved carbon dioxide, and/or carbonic acid, and/or bicarbonate ions and/or carbonate ions.
Also with reference to
2H2O+2e−=H2+2OH− (water is electrolyzed at the cathode).
As cathode electrolyte in the first cathode electrolyte compartment can intermix with cathode electrolyte in the second cathode electrolyte compartment, hydroxide ions formed in the second cathode electrolyte compartment may migrate and equilibrate with carbonate and bicarbonate ions in the second cathode electrolyte compartment 106. Thus, in various embodiments, the cathode electrolyte in the first cathode electrolyte compartment may comprise hydroxide ions as well as dissolved and un-dissolved carbon dioxide gas, and/or carbonic acid, and/or bicarbonate ions and/or carbonate ions; while cathode electrolyte in the second cathode electrolyte compartment may comprise hydroxide ions as well as dissolved carbon dioxide, and/or carbonic acid, and/or bicarbonate ions and/or carbonate ions.
In the cathode electrolyte, carbon dioxide gas may dissolve to form carbonic acid, protons, bicarbonate ions, and carbonate ions, depending on the pH of the electrolyte, as follows:
H2O+CO2═H2CO3═H++HCO3−=2H++CO32−
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 first cathode electrolyte compartment 102 (i.e., the first cathode electrolyte compartment 104 and the second cathode electrolyte compartment 106) 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
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:
E°cell=−ΔG°/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 equestion as demonstrated in
Also, for either scenario, the overall cell potential can be determined through the combination of Nernst equations for each half cell reaction:
E=E°−RT ln(Q)/nF
where, E° 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−,
E° 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−,
E° 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)=−0.059 ΔpH.
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 various embodiments, directing CO2 gas 109A into the cathode electrolyte may lower the pH of the cathode electrolyte by producing bicarbonate ions and/or carbonate ions in the cathode electrolyte, and also lower the voltage across the anode and cathode to produce hydroxide, carbonate and/or bicarbonate in the cathode electrolyte.
Thus, as can be appreciated, 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, overvoltage potential refers to the potential (voltage) difference between a half-reaction's thermodynamically determined reduction potential and the potential at which the redox event is experimentally observed. The term is directly related to a cell's voltage efficiency. In an electrolytic cell the overvoltage potential requires more energy than thermodynamically expected to drive a reaction. In each case, the extra or missing 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. It can thus be appreciated that operation of the electrochemical cell with the cathode pH at 7 or greater provides a significant energy savings.
In various embodiments, for different pH values in the cathode electrolyte and the anode electrolyte, hydroxide ions, carbonate ions and/or bicarbonate ions are produced in the cathode electrolyte when the voltage applied across the anode and cathode was less than 3V, 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, or 0.1V. For selected voltages in the above range, the pH difference between the anode electrolyte and the cathode electrolyte was 0, 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11, 12, 13, 14 or greater.
Also, in embodiments wherein it is desired to produce bicarbonate and/or carbonate ions in the cathode electrolyte, the system as illustrated in
In some embodiment as illustrated in
With reference to
Similarly with reference to
In various embodiments, hydroxide ions, carbonate ions and/or bicarbonate ions produced in the cathode electrolyte, and hydrochloric acid produced in the anode electrolyzed are removed from the system, while sodium chloride in the third electrolyte is replenished to maintain continuous operation of the system.
As can be appreciated by one skilled in the art, in various 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 sodium hydroxide 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 various embodiments, hydroxide ions, 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 higher compared to the embodiment when a gas does not form at the anode.
With reference to
In various embodiments, the cathode compartment 102 is operatively connected to a waste gas treatment system (not illustrated) where the base 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, 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 various 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.
In various embodiments, the cathode and anode are also operatively connected to an off-peak electrical power-supply system 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 a base solution in the cathode electrolyte at a relatively lower cost.
In various embodiments, partially desalinated water is produced in the third electrolyte 122 as a result of migration of cations and anions from the third electrolyte to the adjacent anode electrolyte and cathode electrolyte. In various embodiments, the partially desalinated water is operatively connected to a desalination system (not illustrated) where it is further desalinated 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 system produces an acid, e.g., hydrochloric acid in the anode electrolyte. Thus, in various embodiments, the anode compartment is operably connected to a system for dissolving minerals and waste materials comprising divalent cations to produce a solution of divalent cations, e.g., Ca++ and Mg++. In various embodiments, the divalent cation solution is utilized to precipitate hydroxides, carbonates and/or bicarbonates by contacting the divalent cation solution with the present base 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 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, supra, herein incorporated by reference in its entirety.
With reference to
In another embodiment as is illustrated in
With reference to
In various embodiments, the system includes a cathode electrolyte withdrawal and replenishing system (not illustrated) capable of withdrawing all of, or a portion of, the cathode electrolyte from the cathode compartment 102. In various embodiments, the system also includes a salt solution supply system (not shown) for providing a salt solution, e.g., concentrated sodium chloride, as the third electrolyte 122. In various embodiments the system includes a gas supply system (not shown) for supplying carbon dioxide gas 109A to the cathode electrolyte. In various embodiments, the system also includes inlet ports (not shown) for introducing fluids into the cells and outlet ports (not shown) for removing fluids from the cells.
As can be appreciated, in various embodiments and with reference to
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 various 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.
With reference to
Similarly with reference to protons generated at the anode, under the applied voltage across the cathode and anode, the protons will enter the anode electrolyte and migrate to the anion exchange membrane. However, since the anion exchange membrane will block the movement of cations from the anode electrolyte to the third electrolyte, protons in the anode electrolyte will be prevented from migrating to the third electrolyte. Consequently, on applying the voltage across the anode and cathode, the protons produced at the anode will be contained in the anode electrolyte. Thus, depending on the flow rate of fluids into and out of the anode electrolyte the pH of the anode electrolyte will adjust, e.g., the pH may increase, decrease or remain the same.
With reference to the third electrolyte initially charged with a concentrated solution of sodium ion and chloride ions and is contained in an electrochemical cell by the anion exchange membrane and the cation exchange membrane, on applying a voltage across the anode and cathode, anions in the third electrolyte, e.g., chloride ions, will migrate to the anode, while cations, e.g., sodium ions in the third electrolyte, will migrate to the cathode. Since the anion exchange membrane will allow the migration of anions from the third electrolyte to the anode electrolyte, chloride ions present in the third electrolyte will migrate to the anode electrolyte where they will form an acid, e.g., hydrochloric acid, with the protons from the anode.
Further, since the cation exchange membrane will allow migration of cations from the third electrolyte to the cathode electrolyte, sodium ions present in the third electrolyte will migrate to the cathode electrolyte where they will form sodium hydroxide with the hydroxide ions generated at the cathode. Consequently, as is illustrated in
In various embodiments and as is illustrated in
In various embodiments, depending on the ionic species desired in the system, 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, then a potassium salt such as potassium chloride can be utilized in the third electrolyte 122. Similarly, if sulphuric acid is desired in the anode electrolyte, then a sulphate such as sodium sulphate can be utilized in the third electrolyte 122. Likewise, as described in various 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. As can be appreciated, 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 various embodiments the method further includes a step of adding carbon dioxide to the cathode electrolyte; a step of producing carbonic acid, hydroxide ions, carbonate ions and/or bicarbonate ions in the first cathode electrolyte compartment by applying a low voltage as described elsewhere herein, across the anode and cathode; a step of producing carbonate ions and/or bicarbonate ions in the second cathode electrolyte compartment; a step of producing hydrogen gas at the cathode and directing the gas to the anode where it is oxidized to hydrogen ions; a step of producing hydrogen ions at the anode; a step wherein a gas is not produced at the anode on applying the present voltage across the anode and cathode; a step wherein the voltage across the anode and cathode is less than 2V; a step of separating the cathode electrolyte from a third electrolyte by a cation exchange membrane; a step of separating the anode electrolyte from the third electrolyte by an anion exchange membrane; a step wherein the third electrolyte comprises sodium and chloride ions; a step of migrating sodium ions from the third electrolyte to the cathode electrolyte across the cation exchange membrane, and migrating chloride ions from the third electrolyte to the anode electrolyte across the anion exchange membrane; a step wherein the cathode electrolyte comprises sodium carbonate, sodium bicarbonate or sodium hydroxide, and the anode electrolyte comprises hydrochloric acid; a step of producing an acid in the anode electrolyte; a step of utilizing the acid to dissolve a mafic mineral or a cellulose materials; a step of producing partially desalinated water in the third electrolyte; a step comprising processing the partially desalinated water in a water desalination system; a step of contacting the cathode electrolyte with a divalent cation solution to produce divalent cation hydroxide, carbonate and/or bicarbonate compounds; a step wherein the divalent carbonate and/or bicarbonate compounds comprise calcium and magnesium; a step of withdrawing a first portion of the cathode electrolyte; dissolving carbon dioxide in the first portion of cathode electrolyte to produce a first enriched carbonated cathode electrolyte; and replenishing cathode electrolyte with the first enriched carbonated cathode electrolyte; a step of withdrawing a second portion of the cathode electrolyte; dissolving carbon dioxide in the second portion of cathode electrolyte to produce a second enriched carbonated cathode electrolyte; and contacting the second enriched carbonated cathode electrolyte with a divalent cation solution to produce divalent cation carbonates; a step of applying an off-peak electrical power-supply across the cathode and anode to provide the voltage across the anode and cathode.
In various embodiments, hydroxide ions are formed at the cathode and in the cathode electrolyte 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 various embodiments, method 500 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 various embodiments, method 500 further comprises a step of directing carbon dioxide gas into the cathode electrolyte; a step of directing carbon dioxide gas into the cathode electrolyte before or after the cathode electrolyte is placed in contact with the cathode; a step of forming hydrogen gas at the cathode; a step of forming protons at the anode; a step of forming a pH differential of 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11, 12, 13, 14 pH units or greater between the anode and cathode electrolytes without forming a gas at the anode by selectively applying a voltage of between 3V and 0.5V or less across the anode and the cathode; a step of forming hydroxide ions, bicarbonate ions, carbonate ions and/or a combination thereof in the cathode electrolyte; a step of forming sodium hydroxide, sodium bicarbonate or sodium carbonate in the cathode electrolyte; a step of migrating chloride ions from the third electrolyte across the anion exchange membrane to the anode electrolyte; a step of forming an acid in the anode electrolyte; a step of forming hydrochloric acid in the anode electrolyte; a step of migrating cations from the third electrolyte across a cation exchange membrane to the cathode electrolyte; a step of migrating sodium ions from the third electrolyte across the cation exchange membrane to the cathode electrolyte; a step of directing hydrogen gas formed at the cathode to the anode; and a step of removing cathode electrolyte via an outflow and replenishing cathode electrolyte via an inflow stream to the cathode electrolyte.
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, hydroxide ions are produced in the cathode electrolyte with the present voltages. In various embodiments, method 500 in conjunction with the system of
In various embodiments, 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.V7, 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 various 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 various embodiments, the method and system are capable of producing a pH difference of more than 0.5 pH units between the anode electrolyte solution and a cathode electrolyte solution when the two electrolyte solutions are separated, e.g., by one or more ion exchange membranes, and when a voltage of 3V or less, 2.9 V or less or 2.5 V or less, or 2V or less is applied across the anode and cathode. In some embodiments the method and system are capable of producing a pH difference of more than 1.0 pH units, or 2 pH units, or 4 pH units, or 6 pH units, or 8 pH units, or 10 pH units, or 12 pH units, or 14 pH units between a first electrolyte solution and a second electrolyte solution where the first electrolyte solution contacts an anode and the second electrolyte solution contacts a cathode, and the two electrolyte solutions are separated, e.g., by one or more ion exchange membranes, when a voltage of 0.1V or less is applied across the anode and cathode.
In another exemplary result and with reference to
As can be appreciated, the solubility of carbon dioxide in the cathode electrolyte is dependent on the pH of the electrolyte, and the voltage across the cathode and anode is dependent on the pH difference between the anode electrolyte and cathode electrolyte. Thus, as is illustrated in
In some embodiments, divalent cations, e.g., magnesium ions or calcium ions are removed from the cathode electrolyte solution during parts of the process where the cathode and anode electrolytes are in contact with the ion exchange membranes. This is done to prevent scaling of the membranes, if necessary for that particular membrane. Thus, in various embodiments the total concentration of divalent cations in the electrolyte solutions when they are in contact with the ion exchange membrane or membranes for any appreciable time is less than 0.06 mol/kg solution, or less than 0.06 mol/kg solution, or less than 0.04 mol/kg solution, or less than 0.02 mol/kg solution, or less than 0.01 mol/kg solution, or less than 0.005 mol/kg solution, or less than 0.001 mol/kg solution, or less than 0.0005 mol/kg solution, or less than 0.0001 mol/kg solution, or less than 0.00005 mol/kg solution.
In embodiments where carbon dioxide gas is dissolved in the cathode electrolyte, as protons are removed from the cathode electrolyte more carbon dioxide may be dissolved to form carbonic acid, bicarbonate ions and/or carbonate ions. Depending on the pH of the cathode electrolyte the balance is shifted toward bicarbonate ions or toward carbonate ions, as is well understood in the art and as is illustrated in the carbonate speciation diagram, above. In these embodiments the pH of the cathode electrolyte solution may decrease, remain the same, or increase, depending on the rate of removal of protons compared to rate of introduction of carbon dioxide. It will be appreciated that no carbonic acid, hydroxide ions, carbonate ions or bicarbonate ions are formed in these embodiments, or that carbonic acid, hydroxide ions, carbonate ions, bicarbonate ions may not form during one period but form during another period.
In another embodiment, the present 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 various 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, now U.S. Pat. No. 7,735,274, filed on May 23, 2008, herein incorporated by reference in its entirety.
In an alternative embodiment, the present system and method are integrated with a mineral and/or material dissolution and recovery system (not illustrated) wherein the acidic anode electrolyte solution 115 or the basic cathode electrolyte 102 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 various 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, now U.S. Pat. No. 7,735,274, filed on May 23, 2008, herein incorporated by reference in its entirety.
In an alternative embodiment, the present 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, now U.S. Pat. No. 7,887,694, 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 various 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, now U.S. Pat. No. 7,735,274, filed on May 23, 2008, herein incorporated by reference in its entirety.
In another embodiment, the present 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, now U.S. Pat. No. 7,744,761, filed on Jun. 27, 2008, herein incorporated by reference in its entirety.
In an alternative embodiment, the present 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 slurry or suspension comprising carbonates and/or bicarbonates. In various embodiments, the slurry or suspension is disposed of in a location where it is held stable for an extended periods of time, e.g., the 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, now U.S. Pat. No. 7,887,694, filed on Dec. 24, 2008, herein incorporated by reference in its entirety.
While preferred embodiments of the present invention have been illustrated and described herein, it will be obvious to those skilled in the art that such embodiments are provided by way of example only and not by limitation. Numerous variations, changes, and substitutions will now occur to those skilled in the art without departing from the invention. It should be understood that various alternatives to the embodiments of the invention described herein may be employed in practicing the invention. It is intended that the following claims define the scope of the invention and that methods and structures within the scope of these claims and their equivalents be covered thereby.
This application claims priority to commonly assigned and co-pending U.S. Provisional Patent Application No. 61/081,299 filed Jul. 16, 2008, titled: “Low Energy pH Modulation for Carbon Sequestration Using Hydrogen Absorptive Metal Catalysts”, herein incorporated by reference in its entirety. This application claims priority to commonly assigned and co-pending U.S. Provisional Patent Application No. 61/091,729 filed Aug. 25, 2008, titled: “Low Energy Absorption of Hydrogen Ion from an Electrolyte Solution into a Solid Material”, herein incorporated by reference in its entirety. This application claims priority to commonly assigned and co-pending U.S. Provisional Patent Application No. 61/222,456 filed Jul. 1, 2009, titled: “CO2 Utilization In Electrochemical Systems”, herein incorporated by reference in its entirety. This application is a continuation-in-part of commonly assigned PCT Patent Application no. PCT/US09/48511 filed on Jun. 24, 2009, titled: “Low Energy 4-Cell Electrochemical System with Carbon Dioxide Gas,” which is a continuation-in-part of PCT Patent Application no. PCT/US09/032301, filed Jan. 28, 2009,titled: “Low-Energy Electrochemical Bicarbonate Ion Solution,” and a continuation-in-part of PCT Patent Application no. PCT/US08/088242, filed Dec. 23, 2008, titled “Low Energy Electrochemical Hydroxide System and Method,” each of which is incorporated herein by reference in its entirety, and to each of which we claim priority.”
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 | Sell | 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 |
2304391 | Zimmerman | Dec 1942 | A |
2329940 | Ponzer | Sep 1943 | A |
2383674 | Osborne | Aug 1945 | A |
2458039 | Wait | Jan 1949 | A |
2606839 | Evans | Aug 1952 | A |
2810450 | Hartmann | Oct 1957 | A |
2934419 | Cook | Apr 1960 | A |
2967807 | Osborne et al. | Jan 1961 | A |
3046152 | Tsuneyoshi | Jul 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 |
3262865 | Waters, Jr. | Jul 1966 | A |
3264125 | Bourlin et al. | Aug 1966 | 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 |
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 |
3904496 | Harke et al. | Sep 1975 | A |
3907526 | Saleem et al. | Sep 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 |
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 |
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 |
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 |
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 |
4880447 | Bloch | Nov 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 |
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 |
5275794 | Luna | Jan 1994 | A |
5282935 | Cawlfield et al. | Feb 1994 | A |
5318758 | Fujii et al. | Jun 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 |
5470671 | Fletcher et al. | Nov 1995 | A |
5520898 | Pinnavaia et al. | May 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 |
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 |
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 |
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 |
5885478 | Montgomery et al. | Mar 1999 | A |
5897704 | Baglin | Apr 1999 | A |
5925255 | Mukhopadhyay | Jul 1999 | A |
5958353 | Eyal | Sep 1999 | A |
5965201 | Jones, Jr. | Oct 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 |
6186426 | Killer | 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 |
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 |
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 |
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 |
6475460 | Max | Nov 2002 | B1 |
6495013 | Mazur et al. | Dec 2002 | B2 |
6517631 | Bland | Feb 2003 | B1 |
6518217 | Xing et al. | Feb 2003 | B2 |
6537456 | Mukhopadhyay | Mar 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 |
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 |
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 |
7704369 | Olah et al. | Apr 2010 | B2 |
7727374 | Jones | Jun 2010 | B2 |
7735274 | Constantz 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 |
7875163 | Gilliam 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 |
7922809 | Constantz et al. | Apr 2011 | B1 |
7931809 | Constantz et al. | Apr 2011 | B2 |
7933511 | Masuki | Apr 2011 | B2 |
7939336 | Constantz et al. | May 2011 | B2 |
7966250 | Constantz et al. | Jun 2011 | B2 |
7993500 | Gilliam et al. | Aug 2011 | B2 |
8006446 | Constantz et al. | Aug 2011 | 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 |
20030123930 | Jacobs et al. | Jul 2003 | A1 |
20030126899 | Wolken | Jul 2003 | A1 |
20030146163 | Sasowsky et al. | Aug 2003 | A1 |
20030188668 | Bland | Oct 2003 | A1 |
20030213937 | Yaniv | Nov 2003 | A1 |
20030229572 | Raines et al. | Dec 2003 | 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 |
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 |
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 |
20060195002 | Grandjean et al. | Aug 2006 | A1 |
20060196836 | Arakel et al. | Sep 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 |
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 |
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 |
20090081093 | Comrie | Mar 2009 | A1 |
20090081096 | Pellegrin | Mar 2009 | A1 |
20090081112 | Virtanen | Mar 2009 | A1 |
20090090277 | Joshi et al. | Apr 2009 | A1 |
20090101008 | Lackner et al. | Apr 2009 | A1 |
20090107038 | Wan | Apr 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 |
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 | 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 |
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 |
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 | 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 |
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 |
101219330 | Jul 2008 | CN |
101289200 | Oct 2008 | CN |
2653649 | Jun 1978 | DE |
3146326 | Jun 1983 | DE |
3638317 | Jan 1986 | DE |
19523324 | Sep 1994 | DE |
19512163 | Oct 1995 | DE |
19631794 | Aug 1997 | DE |
0522382 | Jan 1993 | EP |
0487102 | Aug 1995 | EP |
0591350 | Nov 1996 | EP |
0628339 | Sep 1999 | EP |
0844905 | Sep 1999 | EP |
1379469 | Mar 2006 | EP |
1650162 | Apr 2006 | EP |
1716911 | Nov 2006 | EP |
1554031 | Dec 2006 | EP |
1571105 | Dec 2007 | 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 | Dec 1982 | JP |
1142093 | Nov 1987 | JP |
63-312988 | Dec 1988 | JP |
03-020491 | Jan 1991 | JP |
03-170363 | Jul 1991 | JP |
04-317721 | Nov 1992 | JP |
7061842 | Mar 1995 | JP |
10287461 | Oct 1998 | JP |
10305212 | Nov 1998 | JP |
2000226402 | Aug 2000 | JP |
03184892 | Jul 2001 | JP |
2003041388 | Jul 2001 | JP |
2002-273163 | Sep 2002 | JP |
2004-174370 | Jun 2004 | JP |
2005-052762 | Mar 2005 | JP |
2006-076825 | Mar 2006 | JP |
2009279530 | Dec 2009 | JP |
7607470 | Jan 1978 | NL |
1819854 | Jun 1993 | SU |
WO 9316216 | Aug 1993 | WO |
WO 9418119 | Aug 1994 | WO |
WO 9634997 | Nov 1996 | WO |
WO 9913967 | Mar 1999 | 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 2006009600 | Jan 2006 | WO |
WO 2006034339 | Mar 2006 | WO |
WO 2006036396 | Apr 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 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 | 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 |
Entry |
---|
Jones, “Principles and Prevention of Corrosion” 2nd edition, pp. 50-52 (1996). |
Allen, L.M. 1992. 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. |
Baer, D.S., et al. 2002. Sensitive absorption measurements in the near-infrared region using off-axis integrated-cavity-output spectroscopy. Appl. Phys. B. 5 pages. |
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. 2004. Multiplex integrated cavity output spectroscopy of cold PAH cations. Chemical Physics Letters. 387: 287-294. |
Bottomley, D.J. et al. 1999. 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. 155: 295-320. |
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/technologies/carbon—seq/index.html>. |
Cerling, T.E. 1984. The stable isotopic composition of modern soil carbonate and its relationship to climate. Earth and Planetary Science Letters. 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>. |
Criss, R.E. 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. |
Ehleringer, J.R., et al. 2002. Stable Isotopes. Volume 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. |
Elswick, E.R., et al. 2007. 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. 22: 2065-2077. |
Fallick, A.E., et al. 1991. A Stable Isotope Study of the Magnesite Deposits Associated with the Alpine-Type Ultramafic Rocks of Yugoslavia. Economic Geology. 86: 847-861. |
Filley, T.R. et al. 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. 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. |
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. 65: 89-103. |
Horkel, K., et al. 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. 2005. Mineral CO2 Sequestration by Steel Slag Carbonation. Environ. Sci. Technol. 39: 9676-9682. |
Huijgen, W.J.J., et al. 2006. Energy Consumption and Net CO2 Sequestration of Aqueous Mineral Carbonation. Ind. Eng. Chem. Res. 45: 9184-9194. |
Huntzinger, D.N. et al. 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. Carbon Dioxide Sequestration in Cement Kiln Dust Through Mineral Carbonation. Michigan Technological University, 2006 [online], [retrieved on Dec. 29, 2009]. <URL: http://www.geo.mtu.edu/˜dnhuntzi/DNHuntzingerETD.pdf>. |
International Search Report dated Mar. 3, 2010 of EP08867440.3. |
International Search Report dated Jan. 4, 2010 of PCT/US09/062795. |
International Search Report dated Jan. 13, 2010 of PCT/US09/059135. |
International Search Report dated Feb. 2, 2010 of PCT/US09/059141. |
International Search Report dated Feb. 24, 2010 of PCT/US09/067764. |
International Search Report dated Mar. 10, 2010 of PCT/US10/022935. |
“Isotopic Signature”, Wikipedia (2010), http://en.wikipedia.org/wiki/Isotopic—signature, Apri1144, 2009, 3 pp. |
Lin, C. et al. Use of Cement Kiln Dust, Fly Ash, and Recycling Technique in Low-Volume Road Rehabilitation. Transportation Research Record, 1992, No. 1345, pp. 19-27 (abstract) [online], [retrieved on Dec. 31, 2009] <URL: http://pubsindex.trb.org/view.aspx?id=370714>. |
McCrea, J.M. 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. 2001. Palaeproterozoic magnesite: lithological and isotopic evidence for playa/sabkha environments. Sedimentology. 48: 379-397. |
Mihalcea, R.M., et al. 1998. Diode-laser absorption measurements of CO2 near 2.0 μm at elevated temperatures. Applied Optics. 37(36): 8341-8347. |
Miljevic, N., et al. 2007. Potential Use of Environmental Isotopes in Pollutant Migration Studies. Environmental Isotopes in Pollutant Studies. 58: 251-262. |
Mook, W.G., et al. 1968. Isotopic Equilibrium between Shells and Their Environment. Science. 159(3817): 874-875. |
Mook, W.G., et al. 1974. Carbon Isotope Fractionation Between Dissolved Bicarbonate and Gaseous Carbon Dioxide. 22:169-176. |
O'Neil, J.R., et al. 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. |
Philp, R.P. 2007. The emergence of stable isotopes in environmental and forensic geochemistry studies: a review. Environ Chem Lett. 5:57-66. |
Power, I.M., et al. 2007. Biologically induced mineralization of dypingite by cyanobacteria from an alkaline wetland near Atlin, British Columbia, Canada. Geochemical Transactions. 8: 16 pages. |
Saad, N. et al. 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). |
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. 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. 2002. Genesis of magnesite deposits in the view of isotope geochemistry. Boletim Paranaense de Geociencias. 50: 59-68. |
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. 26. 161-198. |
Sethi, S. et al. 2006. Existing & Emerging Concentrate Minimization & Disposal Practices for Membrane Systems. Florida Water Resources Journal. pp. 38, 40, 42, 44, 46, 48. |
Sial, A.N., et al. 2000. Carbon isotope fluctuations in Precambrian carbonate sequences of several localities in Brazil. An. Acad. Bras. Ci. 72(4): 539-558. |
Stanley, S.M., et al. 2002. Low-magnesium calcite produced by corallin algae in seawater of Late Cretaceous composition. PNAS. 99(24): 15323-15326. |
U.S. Appl. No. 12/126,776, filed May 23, 2008, Constantz, Brent R., et al, Non-Final Office Action dated Feb. 25, 2010; 21 pp. |
U.S. Appl. No. 12/163,205, filed Jun. 27, 2008, Constantz, Brent R., et al, Non-Final Office Action dated Jan. 27, 2010. |
U.S. Appl. No. 12/163,205, filed Jun. 27, 2008, Constantz, Brent R., et al, Non-Final Office Action dated Mar. 1, 2010. |
U.S. Appl. No. 12/163,205, filed Jun. 27, 2008, Constantz, Brent R., et al, Non-Final Office Action dated Mar. 25, 2010. |
U.S. Appl. No. 12/344,019, filed Dec. 24, 2008, Constantz, Brent R., et al, Non-Final Office Action dated Nov. 16, 2009. |
U.S. Appl. No. 12/344,019, filed Dec. 24, 2008, Constantz, Brent R., et al, Non-Final Office Action dated Mar. 11, 2010. |
U.S. Appl. No. 12/375,632, filed Mar. 5, 2009, Kirk, Donald W. et al, Non-Final Office Action dated Mar. 19, 2010. |
U.S. Appl. No. 12/475,378, filed May 29, 2009, Constantz Brent. et al, Non-Final Office Action dated Mar. 17, 2010. |
U.S. Appl. No. 12/475,378, filed May 29, 2009, Constantz Brent. et al, Non-Final Office Action dated Mar. 2, 2010. |
U.S. Appl. No. 12/486,692, filed Jun. 17, 2009, Constantz Brent. et al, Non-Final Office Action dated Mar. 23, 2010. |
U.S. Appl. No. 12/486,692, filed Jun. 17, 2009, Constantz Brent. et al, Non-Final Office Action dated Mar. 1, 2010. |
U.S. Appl. No. 12/501,217, filed Jul. 10, 2009, Constantz Brent. et al, Non-Final Office Action dated Mar. 12, 2010. |
U.S. Appl. No. 12/604,383, filed Oct. 22 2009, Constantz Brent R. et al, Non-Final Office Action dated Apr. 5, 2010. |
U.S. Appl. No. 12/609,491, filed Oct. 30, 2009, Constantz Brent. et al, Non-Final Office Action dated Mar. 31, 2010. |
Vagin, S.P., et al. 1979. Measurement of the Temperature of Gas Media Containing Carbon Dioxide by the Laser-Probing Method. Plenum. |
Wang, W., et al. 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. 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. 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>. |
Zedef, V., et al. 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. |
U.S. Appl. No. 60/921,598, filed Apr. 3, 2007, Little et al. |
Avery, G.B. et al. 2006. Carbon isotopic characterization of dissolved organic carbon in rainwater: Terrestrial and marine influences. Science Direct. 40(39): 7539-7545. Retrieved from the internet on May 20, 2010. |
Dickens, A. et al. 2004. Reburial of fossil organic carbon in marine sediments. Nature. 427: 336-339. Retrieved from the internet on May 20, 2010. |
Faure, et al. 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). |
Huijgen, W.J.J., et al. 2003. Carbon dioxide sequestration by mineral carbonation. ECN-C-03-016; Energy Research Centre of the Netherlands: Petten; pp. 1-42. |
International Search Report dated May 6, 2010 of EP09716193.9. |
International Search Report dated Jun. 22, 2010 of EP08772151.0. |
International Search Report dated Jul. 7, 2010 of PCT/US10/026880. |
International Search Report dated Jul. 9, 2010 of PCT/US10/025970. |
International Search Report dated May 21, 2010 of PCT/US09/064117. |
Mottana, A. et al. 1979. Der grosse Mineralienfuhrer, BLV Verlagsgesel lschaft mbH, Munchen, XP002577921, p. 194. (in German with English Translation). |
Noda, H., et al. 1990. Electrochemical Reduction of Carbon Dioxide at Various Metal Electrodes in Aqueous Potassium Hydrogen Carbonate Solution. The Chemical Society of Japan. 63: 2459-2462. |
Portier et al. 2005. Modelling 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. 217: 187-199. |
Quay, P.D., et al. 1992. Oceanic Uptake of Fossil Fuel CO$—2$: Carbon- 13 Evidence. Science. 256 (5053): 74-79. |
Schwab, E. 2004. Calciumhydroxid, XP-002577920. Retrieved from the Internet: <URL:http://www.roempp.com/prod/index1.html> (in German with English Translation). |
U.S. Appl. No. 12/344,019, filed Dec. 24, 2008, Constantz, Brent R., et al, Non-Final Office Action dated Jul. 14, 2010. |
U.S. Appl. No. 12/475,378, filed May 29, 2009, Constantz Brent. et al, Final Office Action dated May 5, 2010. |
U.S. Appl. No. 12/486,692, filed Jun. 17, 2009, Constantz Brent. et al, Final Office Action dated May 3, 2010. |
U.S. Appl. No. 12/557,492, filed Sep. 10, 2009, Constantz, Brent R., et al. Non-Final Office Action dated May 6, 2010. |
U.S. Appl. No. 12/604,383, filed Oct. 22 2009, Constantz Brent R. et al, Final Office Action dated Jun. 11, 2010. |
U.S. Appl. No. 12/571,398, filed Sep. 30, 2009, Constantz Brent R. et al, Non-Final Office Action dated May 3, 2010. |
U.S. Appl. No. 12/609,491, filed Oct. 30, 2009, Constantz Brent. et al, Final Office Action dated Jul. 16, 2010. |
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 (2007) 273-281. |
Berg et al., “A 3-Hydroxyproprionate/ 4-Hydroxybutyrate Autotrophic Carbon Dioxide Assimilation Pathway in Archea”; Science Dec. 14, 2007; vol. 318, No. 5857 DOI 10.1126/science 1149976; pp. 1782-1786. |
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. 2002. Brines as possible cation sources for biomimetic carbon dioxide sequestration. American Geophysical Union Abstract #U22A-07. |
CICCS “Aims and Research”; www.nottingham.ac.uk/carbonmanagement/ccs—aims.php 2pp Aug. 3, 2007. |
Druckenmiller et al., “Carbon sequestration using brine of adjusted pH to form mineral carbonates”; Elsevier; www.elsevier.com/locate/fuproc; Fuel Processing Technology 86 (2005) 1599-1614. |
Faverjon, F. et al. 2005. Electrochemical study of a hydrogen diffusion anode-membrane assembly for membrane electrolysis. Electrochimica Acta 51 (3): 386-394. |
Faverjon, F. et al. 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. |
Gain, E. et al. 2002. Ammonium nitrate wastewater treatment by coupled membrane electrolysis and electrodialysis. Journal of Applied Electrochemistry 32: 969-975. |
Genders, D. 1995. Electrochemical Salt Splitting. http://www.electrosynthesis.com/news/mwatts.html (accessed Feb. 5, 2009). |
Goldberg et al., “CO2 Mineral Sequestration Studies in US”; National Energy Technology Laboratory; goldberg@netl.doe.gov; 10pp. |
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. |
Haywood et al., “Carbon dioxide sequestration as stable carbonate minerals—environmental barriers”; Environmental Geology (2001) 41:11-16; Springer-Verlag 2001. |
Hill et al., “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; 5pp. |
Holze, S. et al. 1994. Hydrogen Consuming Anodes for Energy Saving in Sodium Sulphate Electrolysis. Chem. Eng. Technol. 17: 382-389. |
Huijgen, W.J.J., et al. 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. |
International Search Report dated Feb. 19, 2009 of PCT/US08/88242. |
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. |
Lackner, K. “Carbonate Chemistry for Sequestering Fossil Carbon”; Annual Review Energy Environ. 2002 27:193-232. |
Mazrou, S., et al. 1997. Sodium hydroxide and hydrochloric acid generation from sodium chloride and rock salt by electro-electrodialysis. Journal of Applied Electrochemistry 27: 558-567. |
Nayak, V.S. “Nonelectrolytic Production of Caustic Soda and Hydrochloric Acid from Sodium Chloride”; Ind. Eng. Chem. Res. 1996. 35: 3808-3811. |
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. |
Park, A., et al. 2004. CO2 mineral sequestration: physically activated dissolution of serpentine and pH swing process. Chemical Engineering Science 59 (22-23): 5241-5247. |
Rau, G. 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. (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; 4pp. |
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 (2003) pp. 653-663. |
Shell Global Solutions, “ADIP-X and Sulfinol-X—new regenerable acid-gas removal processes”; Shell Global Solutions International; OG 130210370903-En(A); www.shellglobalsoultions.com 2 pp. |
Tececo Pty Ltd, “Eco-Cement”; www.tececo.com/simple.eco-cement.php; Dec. 29, 2008; 6pp. |
“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. |
Cannell, M.G.R. 2003. “Carbon sequestration and biomass energy offset: theoretical, potential and achievable capacities globally, in Europe and the UK.” Biomass and Bioenergy. 24: 97-116. |
Levy, D. “Burnt biomass causes short-term global cooling, long-term warming.” http://news-service.stanford.edn/news/2004/august4/biomass-84.html. 3 pages. |
Turner, J.A. 1999. “A Realizable Renewable Energy Future.” Science. 285 (5428): 687-689. |
Wright, L.L., et al. 1993. “U.S. Carbon Offset Potential Using Biomass Energy Systems.” Water, Air, and Soil Pollution. 70: 483-497. |
Back, M. et al.,“Reactivity of Alkaline Lignite Fly Ashes Towards CO in Water.” Environmental Science & Technology. vol. 42, No. 12 (2008) pp. 4520-4526. |
Huntzinger, D.N. et al.,“Carbon Dioxide Sequestration in Cement Kiln Dust through Mineral Carbonation”; Environmental Science & Technology, vol. 43, No. 6 (2009) pp. 1986-1992. |
International Search Report dated Sep. 17, 2008 of PCT/US2008/068564. |
International Search Report dated Mar. 11, 2009 of PCT/US2008/088318. |
International Search Report dated Mar. 11, 2009 of PCT/2008/088246. |
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. 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/US09/056573. |
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, 2001. SP-199-44. pp. 769-781. |
Lackner, K.S. et al. “Carbon Dioxide Disposal in Carbonate Minerals.” Energy. 1995. 20(11): 1153-1170. |
Montes-Hernandez, G. et al.,“Mineral sequestration of CO2 by aqueous carbonation of coal combustion fly-ash.” Journal of Hazardous Materials vol. 161 (2009). pp. 1347-1354. |
O'Connor, W.K. et al. “Carbon dioxide sequestration: Aqueous mineral carbonation studies using olivine and serpentine.” 2001. Albany Research Center, National Energy Technology Laboratory: Mineral Carbonation Workshop, Pittsburgh, PA. |
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 (2007) 123-137. |
Rakib, M. et al. 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. |
Sadhwani et al., “Case Studies on environmental impact of seawater desalination” Science Direct; http://www.sciencedirect.com/science?—ob=ArticleURL&—udi=B6TFX-4HMX97J-3&—u . . . 3pp. |
Uibu, M. et al. “CO2 mineral sequestration in oil-shale wastes from Estonian power production.” Journal of Environmental Management vol. 90 (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 (2009) pp. 40-58. |
Uliasz-Bochenczyk, A. et al. “Utilization of Carbon Dioxide in Fly Ash and Water Mixtures.” Chemical Engineering Research and Design. 2006. 84(A9): 843-846. |
U.S. Appl. No. 12/375,632, filed Mar. 5, 2009, Kirk, Donald W. et al, Non-Final Office Action dated Sep. 8, 2009. |
“Electrochemical cell”, Wikipedia (2009), http:en.wikipedia.org/wiki/Electrochemical—Cell, Nov. 24, 2009, 5 pp. |
International Search Report dated Dec. 14, 2009 of PCT/US09/061748. |
Bauer, C.F., et al. 1981. Identification and Quantitation of Carbonate Compounds in Coal Fly Ash. American Chemical Society. 15(7): 783-788. |
Bommaraju, T.V. et al. 2001. Brine Electrolysis. <http://electrochem.cwru.edu/encycl/art-b01-brine.htm>. Retrieved on Oct. 6, 2010. pp. 1-25. |
Eurodia. Bipolar Membrane Electrodialysis. Available online as of 2001.; visited Oct. 6, 2010 at http://www.eurodia.com/html/eb.html. |
Gillery et al. Bipolar membrane electrodialysis: the time has fmally 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. |
Golden, D.C., et al. 2001. A Simple Inorganic Process for Formation of Carbonates, Magnetite, and Sulfides in Martian Meteorite ALH84001. American Mineralogist. 86: 370-375. |
Gregerson, J. 1999. Conquering Corrosion (in concrete). Building Design & Construction. 40(8): 50. |
Hassan, A.M. et al. 1989. Corrosion Resistant Materials for Seawater RO Plants. Desalination. 74: 157-170. |
Hein, J.R. et al. 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. |
Horii, Y. et al. 2007. Novel evidence for natural formation of dioxins in ball clay. Chemosphere. 70: 1280-1289. |
International Search Report dated Jan. 20, 2009 of PCT/US2007/010032. |
International Search Report dated Dec. 14, 2010 of EP09812408.4. |
International Search Report dated Jul. 29, 2010 of EP08873036.1. |
International Search Report dated Jan. 4, 2011 of EP09818485.6. |
International Search Report dated Sep. 13, 2010 of PCT/US10/035041. |
Jensen, P. et al. 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. |
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 (2007) (in Chinese, with English translation). |
Lopez-Capel, E. et al. 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. |
Perkins, S. 2004. Sea Change: Carbon Dioxide Imperils Marine Ecosystems. Science News. 166(3): 35. |
Sample, J.C. et al. 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. |
Sakata, M. 1987. Movement and Neutralization of Alkaline Leachate at Coal Ash Disposal Sites. Environ. Sci. Technol. 21(8): 771-777. |
Shaffer, R. 2008. A Devlish Green Angel. Fast Company. N127: 92-97. |
Skrzypek, G. et al. 2006. δ13C analyses of calcium carbonate: comparison between the GasBench and elemental analyzer techniques. Rapid Communications in Mass Spectrometry. 20: 2915-2920. |
Socolow, R. 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. 2004. Experimental and simulation studies on mineral trapping of CO2 with brine. Energy Conversion and Management. 45: 1845-1859. |
Technology for Commercialization of Slag. 1995. New Technology Japan. ISSN: 0385-6542. p35. |
Zhang, C.L. et al. 2001. Temperature-dependent oxygen and carbon isotope fractionations of biogenic siderite. Geochimica et Cosmochimica Acta. 65(14): 2257-2271. |
Constantz, B. 2009. The Risk of Implementing New Regulations on Game-Changing Technology: Sequestering CO2 in the Built Environment. AGU, 90(22), Jt. Assem, Suppl., Abstract. |
Bagotsky, V.S. 2006. Conductive Polymers: Polymers with Ionic Functions. Fundamentals of Electrochemistry. Second Edition. New Jersey: John Wiley & Sons. pp. 454-455. |
Bradfield, D.L. 1984. Conventional Uranium Processing: The Yeelirrie Uranium Project. Practical Hydromet '83—7th Annual Symposium on Uranium and Precious Metals. pp. 39-47. Lakewood, CO. |
Eldorado Beaverlodge Operation. 1960. Canadian Mining Journal. 81(6): 111-138. |
International Search Report dated Apr. 13, 2011 of PCT/US10/57821. |
International Search Report dated Mar. 21, 2011 of EP10739828.1. |
International Search Report dated Mar. 25, 2011 of EP10739829.9. |
International Search Report dated Mar. 25, 2011 of EP10737735.0. |
International Search Report dated Mar. 4, 2011 of EP10737736.8. |
International Search Report dated Apr. 6, 2011 of EP10192919.8. |
International Search Report dated May 18, 2011 of EP09812407.6. |
International Search Report dated Apr. 19, 2011 of PCT/US2010/059835. |
Merritt, R.C. 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. |
Various authors. 2001. “Calcium Carbonate: From the Cretaceous Period Into the 21st Century.” Birkhauser Verlag, pp. 1-54. |
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20100230293 A1 | Sep 2010 | US |
Number | Date | Country | |
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61081299 | Jul 2008 | US | |
61091729 | Aug 2008 | US | |
61222456 | Jul 2009 | US |
Number | Date | Country | |
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Parent | PCT/US2009/048511 | Jun 2009 | US |
Child | 12503557 | US | |
Parent | PCT/US2009/032301 | Jan 2009 | US |
Child | PCT/US2009/048511 | US | |
Parent | PCT/US2008/088242 | Dec 2008 | US |
Child | PCT/US2009/032301 | US |