The present disclosure relates to a method of producing a substantially pure gaseous carbon dioxide (CO2), by separating gaseous mixture of carbon dioxide (CO2) and oxygen (O2) after an electrolytic regeneration of a spent aqueous scrubbing liquid from a process of scrubbing a gas, such as flue gas comprising carbon dioxide. The substantially pure carbon dioxide is then compressed to a liquid CO2 for transport. The CO2 may be extracted from flue gas, ambient air or other sources.
Carbon dioxide (CO2) is a gas that when emitted into the atmosphere is damaging to the climate as it contributes to the green-house effect and rise in global temperature. It is for example produced as a by-product when fossil fuel, e.g. coal, gasoline or diesel, is burned. Coal- and gas-fired power plants accounts for a large share of CO2 emissions. It is a goal for many sectors to lower carbon dioxide emissions.
Emitted gases resulting from combustion and comprising CO2 are typically denoted flue gases or exhaust gases. Depleting such emitted gases of CO2 by lowering the CO2 content in the emitted gases, can be done by so called scrubbing of the gases, i.e. removing the CO2 from the gas stream by absorbing/dissolving CO2 in a liquid.
As described in U.S. Pat. No. 11,219,860, the CO2 withdrawn from the scrubbing process, or from an anode chamber of an electrolytic cell, after regeneration of a scrubbing liquid, is then conventionally compressed, or cooled and compressed to be transported of site for other downstream uses. However, the process of cooling and compressing gaseous CO2 into a liquid carbon dioxide requires a substantial amount of power. There is an imperative need for improved scrubbing systems that preferably require less power for the CO2 capture and compression. The method in accordance with the present disclosure, may be obtained using the method and system disclosed in U.S. Pat. No. 11,219,860.
It is in view of the above considerations and others that the embodiments described in this disclosure have been made. It is an object of the present disclosure, to provide an improved method of preparing a substantially pure gaseous carbon dioxide, and a system and uses thereof.
The disclosure is defined by the appended independent claims. Embodiments are set forth in the appended dependent claims and in the following description.
Accordingly, there is provided a method of preparing a substantially pure gaseous carbon dioxide from a gaseous mixture of carbon dioxide (CO2) and oxygen (O2), wherein said gaseous mixture is withdrawn from an anode chamber of an electrolytic cell, and wherein said electrolytic cell is fed a spent aqueous scrubbing liquid from a scrubber, wherein said scrubber scrubs a gas, having a first carbon dioxide concentration with a first alkaline, aqueous scrubbing liquid, wherein said spent aqueous scrubbing liquid is regenerated in the electrolytic cell by electrolysis, wherein the regeneration further comprises generating a gaseous mixture of oxygen and carbon dioxide (CO2) in the anode chamber; and wherein said gaseous mixture comprises between 66 and 80% v/v carbon dioxide and between 20% v/v and 34% v/v oxygen, the method comprising the steps of: treating said gaseous mixture of oxygen and carbon dioxide (CO2) to remove at least 50% oxygen from said mixture.
The aqueous scrubbing liquid may be circulated between the electrolytic cell and the scrubber, where the scrubbing liquid may be a first alkaline, where a first spent aqueous scrubbing liquid is fed to an electrolytic cell, and a first regenerated aqueous scrubbing liquid is fed back to the scrubber from the electrolytic cell, after regeneration in the electrolytic cell. The treatment of the gaseous mixture of oxygen and carbon dioxide to remove oxygen from said mixture may be performed using a gas separator device, where the gas separator device may be a sorbent/solvent gas separator, a membrane separator and/or a cryogenic distillation separator, or any suitable method/device for treating the stream to separate O2 from a CO2 rich stream and create a CO2 rich stream that has a reduced O2 content.
The regeneration of the scrubbing liquid in the electrolytic cell results in a generation of a gaseous mixture of oxygen and carbon dioxide
This means that at least a substantial amount of oxygen is removed from the mixture. By removing oxygen, i.e. separating O2 from the CO2 of the gaseous mixture form the anode chamber of the electrolytic cell, an increased efficiency is obtained in the CO2 compression stage. The decrease in efficiency correlates with decrease in gas volume that is to be compressed. e.g. if there is 20% v/v O2 in 80% v/v CO2 the energy consumption can be reduced to 80% of the original value.
The carbon capture reaction in the scrubbing step takes place automatically. The operation of the scrubber is thereby an automatic process and requires no power apart from one needed to circulate the liquids. The regeneration process of the first scrubbing liquid that take place in the cathode and anode chambers of the electrolytic cell are electrochemical reactions, which inherently require electrical power. The electrochemical process regenerates the solvent, produces hydrogen at the cathode and a mixture of carbon dioxide (CO2) and oxygen at the anode. The regeneration thus comprises generating gaseous hydrogen in the cathode chamber and a gaseous mixture of oxygen and carbon dioxide in the anode chamber by electrolysis.
In accordance with the present disclosure the percentages of concentrations of liquids or gas may be defined by % v/v i.e. a volume concentration of a solution, where a solution having 80% CO2 and 20% O2 may be seen as a solution of 100 units of a volume, has 80 units of CO2 and 20 units O2, where the units may be ml, litres,
According to the first aspect wherein at least 60% of the oxygen is removed from the gaseous mixture, or at least 70% of the oxygen is removed from the gaseous mixture, or at least 80% of the oxygen is removed from the gaseous mixture, or at least 90% of the oxygen is removed from the gaseous mixture, or at least 95% of the oxygen is removed from the gaseous mixture, or at least 99% of the oxygen is removed from the gaseous mixture. This means that substantially all of the oxygen may be removed before compression, which even further increased the energy saved during the compression stage.
According to the first aspect, the method may further comprise the step of compressing said oxygen depleted gaseous mixture into a substantially pure liquid carbon dioxide. This means that the liquid carbon may easily be transported for other downstream uses. The gas having a first carbon dioxide concentration is any one of a flue gas, an exhaustive gas, air.
According to one alternative of the first aspect wherein the step of treating said gaseous mixture to remove at least 50% oxygen from said mixture comprises: flowing said gaseous mixture through a heating device, thereby consuming said oxygen and creating an output flow of carbon dioxide and dihydrogen oxide (H2O). The heating device may be a separate burner, or for instance a generator producing district heating and power, and the full flow of the gaseous mixture of carbon dioxide and oxygen could be used instead of air. The carbon dioxide and water may thus be further separated by condensation, and the pure CO2 can be further cleaned, cooled and compressed for transport.
The heating device may be fed with a fuel, and wherein said fuel is any one of hydrogen, natural gas or biogas and said hydrogen may be a gaseous hydrogen withdrawn from a cathode chamber of said electrolytic cell.
According to another alternative of the first aspect, the step of treating said gaseous mixture to remove at least 50% oxygen from said mixture may comprise utilising said gaseous mixture as an oxidizer in a processes step of scrubbing a flue gas for CO2.
Through this treatment, if all the oxidant is oxygen mixed with carbon dioxide, the flue gas will intermittently consist of pure CO2, which can thus be cooled and compressed directly for transport with limited pre-treatment.
According to yet another alternative of the first aspect the step of treating said gaseous mixture to remove at least 50% oxygen from said mixture comprises utilising said gaseous mixture as an oxidizing agent in an aerobic biological treatment process.
By an aerobic biological treatment process is meant for instance a wastewater purification process, and through this treatment the oxygen is depleted during the wastewater purification process and the purified CO2 can be collected, cooled and compressed for transport.
According to a second aspect there is provided a system for scrubbing a gas, such as flue gas or exhaustive gas, comprising carbon dioxide to deplete the flue gas of carbon dioxide, the system comprising:
According to a third aspect, a regeneration arrangement is provided for regenerating a spent aqueous scrubbing liquid to provide alkaline, aqueous scrubbing liquid, the regeneration arrangement comprising an electrolytic cell, comprising an anode chamber comprising an anode inlet for receiving the spent aqueous scrubbing liquid and an anode outlet for withdrawing oxygen and carbon dioxide, and the cathode chamber comprises an outlet for withdrawing regenerated aqueous scrubbing liquid;
According to one alternative of the systems according to the second or third aspect, the gas separator device may be a heating device. By heating device is meant a device such as a burner, an engine or a generator.
According to another alternative, the gas separator device may be an aerobic biological process facility such as a wastewater treatment plant.
According to the second and third aspects, at least 50% of the oxygen is removed from the gaseous mixture of carbon dioxide and oxygen withdrawn from the anode chamber by or in the gas separator device. Alternatively, at least 60% of the oxygen is removed from the gaseous mixture, or at least 70% of the oxygen is removed from the gaseous mixture, or at least 80% of the oxygen is removed from the gaseous mixture, or at least 90% of the oxygen is removed from the gaseous mixture, or at least 95% of the oxygen is removed from the gaseous mixture, or at least 99% of the oxygen is removed from the gaseous mixture.
Although the present disclosure has been described above with reference to specific embodiments, it is not intended to be limited to the specific form set forth herein. Rather, the disclosure is limited only by the accompanying claims and other embodiments than the specific embodiments described above are equally possible within the scope of these appended claims.
In the claims, the term “comprises/comprising” does not exclude the presence of other elements or steps. Additionally, although individual features may be included in different claims, these may possibly advantageously be combined, and the inclusion in different claims does not imply that a combination of features is not feasible and/or advantageous.
In addition, singular references do not exclude a plurality. The terms “a”, “an”, “first”, “second” etc. do not preclude a plurality.
These and other aspects, features and advantages of which the disclosure is capable of will be apparent and elucidated from the following description of embodiments of the present disclosure, reference being made to the accompanying drawings.
With reference to
The gas which is scrubbed in the scrubber may for instance be a flue gas or an exhaustive gas. One alternative is to utilise the scrubber and regeneration in a vehicle. Another option could be so called DAC (direct air capture) applications, where CO2 is captured from the ambient air and a stream of concentrated CO2 is generated. The gas enters the scrubber through the scrubber inlet 213. To deplete the flue gas from carbon dioxide CO2, the scrubbing method can be described as follows. The gas is scrubbed in the scrubber 210 in a counter flow manner with a first alkaline, aqueous scrubbing liquid to dissolve carbon dioxide CO2 as hydrogen carbonate HCO3— and/or as carbonate CO32— in the first alkaline, aqueous scrubbing liquid. A first spent aqueous scrubbing liquid comprising dissolved hydrogen carbonate HCO3— and/or carbonate CO32— results. The first spent aqueous scrubbing liquid has a pH from about 7 to about 11, or usually from about 7 to about 9, when it leaves at the outlet 211″ for withdrawing spent aqueous scrubbing liquid of the scrubber 210. The first spent aqueous scrubbing liquid is then fed to an anode chamber 313 of an electrolytic cell 310 via an anode inlet 313′. The electrolytic cell 310 has apart from the anode chamber 313 also a cathode chamber 312. The anode chamber 313 and the cathode chamber 312 are separated by a membrane 311. This membrane 311 may be semi-permeable membrane, being permeable to cations, but essentially impermeable to anions. Thus, the membrane cation-exchange membrane. The electrolysis increases the pH of the first spent aqueous scrubbing liquid in the cathode chamber 312. In the anode chamber 313, the electrolysis further depletes the first spent aqueous scrubbing liquid of hydrogen carbonate HCO3— and of carbonate CO32— by decreasing the pH-value to release gaseous carbon dioxide. The outlet 211″ for spent aqueous scrubbing liquid of the scrubber 210 is in flow communication with the inlet 313′ for the spent aqueous scrubbing liquid of the anode chamber 313. Moreover, the outlet 312″ for regenerated aqueous scrubbing liquid of the cathode chamber 312 is flow communication with the inlet 212′ for the alkaline, aqueous scrubbing liquid of the scrubber 210.
One can say that the first spent aqueous scrubbing liquid is regenerated by generating gaseous hydrogen H2 and dissolved hydroxide ions OH− in the cathode chamber 312 and a gaseous mixture of oxygen O2 and carbon dioxide CO2 in the anode chamber 313 by electrolysis. This is indicated by the upwards pointing arrows from the cathode outlet 312″ and the anode outlet 313″ in
The gaseous mixture of carbon dioxide and oxygen withdrawn from the anode chamber 313 is transported to a separation device 340, where oxygen is removed from the gaseous mixture, such that a stream of substantially pure gaseous CO2 is obtained. The substantially pure gaseous CO2 may then be transferred to a compression unit 330, where the gaseous CO2 is converted into a substantially pure liquid CO2.
Furthermore, the regeneration arrangement 300 also comprises a first gas separator device 340 for separating oxygen O2 and carbon dioxide CO2 withdrawn from the anode chamber 313 from liquid. The first gas separator 340 is arranged upstream the second compressor unit 330.
The composition of the gaseous mixture is typically around 75% v/v CO2 and 25% v/v O2. When the system 100 operates, the oxygen O2 and carbon dioxide CO2 are separated in the first gas separator device 340 leaving a substantially pure gaseous CO2 stream which may be compressed in the first compressor unit 330. An advantage of providing CO2 in a liquid phase is that it is practical during transportation. According to the disclosure oxygen is thus removed from the gaseous mixture before the carbon dioxide is compressed.
According to the disclosure oxygen is thus removed from the gaseous mixture before the carbon dioxide is compressed.
At least 50% of the oxygen is removed from the gaseous mixture, as this allows for a substantial energy saving when compressing the carbon dioxide into a liquid carbon dioxide.
According to an alternative embodiment least 60% of the oxygen is removed from said mixture.
According to one embodiment at least 80% of the oxygen is removed from said mixture.
According to one embodiment at least 90% of the oxygen is removed from said mixture.
According to one embodiment at least 95% of the oxygen is removed from said mixture.
According to one embodiment at least 99% of the oxygen is removed from said gaseous mixture.
The gas separator device 340 may according to one embodiment may be a heating device. The heating device may for instance be a burner where the oxygen in the gaseous mixture is used as an oxygen source instead of air, leaving a pure CO2 steam of gas and water which can be collected, cleaned and handled downstream of the separator device. The heating device may also be a generator, such as for instance for obtaining central or district heating and power, using either biogas, natural gas or H2 gas as input and the full flow from the anode chamber outlet of the gaseous mixture of CO2/O2 is used as an oxygen source. One alternative is to use the H2 gas from the cathode chamber of the electrolyser cell as input.
According to another embodiment, the separator device 340 provides the gaseous mixture of carbon dioxide and oxygen as an oxidizer or oxidizing agent in the process where the gas is scrubbed for CO2 if all the oxidant is O2 mixed with CO2 the flue gas will intermittently consist of pure CO2 and it can thus be compressed directly with limited pre-treatment. As an example, a gas fired generator may be fueled with methane and a mixture of CO2/O2 instead of air, which leads to the exhaust gas being is pure CO2 and water. The exhaust gas created is therefore pure CO2, as no nitrogen from the air is injected creating NOx and N2 in the exhaust.
According to a third embodiment the separator device 340 is a biological aerobic process, such as for instance a wastewater treatment plant, which is either in flow connection to the regeneration arrangement, or where the gaseous mixture of oxygen and carbon dioxide is transported. The gaseous mixture is utilised in the wastewater treatment process, such that the oxygen in the gaseous mixture is consumed as an oxidizing agent, for instance through various enzymatic and bacterial reactions in the wastewater process. The purified CO2 may then be collected and compressed.
Now turning to the regeneration arrangement 300 in
The regeneration arrangement 300 also comprises a second gas separator 380 for separating gaseous hydrogen H2 and, for instance, liquid aqueous potassium hydroxide KOH, withdrawn from the cathode chamber 312.
Furthermore, the regeneration arrangement 300 has a separator 350, such as a filter. For instance, the filter may be a reversed osmosis filter. This concentrator 350 is arranged downstream of the first gas separator unit 340. It is to be noted that the electrolytic cell may be sensitive to impurities in the fluid flowing through the anode and cathode chambers. Hence, there may also be a separate cleaning unit (not shown), which serves to remove impurities such as for instance nitrogen oxides NOx and sulfur oxides SOx from the spent aqueous scrubbing liquid before it enters the electrolytic cell 310. As an example, the cleaning unit may include a filter to remove particulate matter. It should be noted that in
The solvent is then regenerated in the regeneration arrangement 300 using electrochemistry. In general, the electrochemical reaction can be split into two parts; the anode reaction and the cathode reaction. These reactions will be described below.
In the anode chamber 313, O2 and CO2 are generated in two different steps. First, O2 is generated at the anode together with 4 H+. Then, the H+ decreases the pH-value of the solvent and releases CO2. Simultaneously, O2 is generated at the anode and the two gases are mixed in a ratio of 4:1, CO2 to O2. The overall reaction at the anode chamber 313 is:
4×HCO3→O2+4×CO2+2×H2O+4e−
The reaction at the anode is:
2×H2O→O2+4×H++4e−
This reaction decreases the pH-value locally. This decrease in pH-value pushes the
HCO3—/CO2 equilibrium to the right, such that:
4×H++4×HCO3→4×CO2+4×H2O
which results in the release of gaseous CO2 from the solvent.
At the cathode, H2 is produced together with OH. This reaction both generates valuable H2 for downstream applications and regenerates the alkaline solvent comprising hydroxide ions (OH) for the carbon capture process. The cathode chamber reaction 312 is:
4×H2O+4→2×H2+4×OH−.
The electrochemical reaction in the electrolytic cell 310 requires electrical power. The actual power consumption will depend on the technical implementation of the process of the system 100. Assuming 100% efficiency, the minimum current required for the process can be calculated using Faraday's law of thermodynamics: I=mFz/tM. With the parameters as listed in Table 1 below, the current can be calculated.
The current can thus be calculated to I=2. 18×109 A. With a minimum voltage of 2 V assumed, the theoretical minimum power consumption for 1 ton of CO2 will be:
For real chemical reactions, a higher energy consumption is expected. As suggested by a model based on experiments the ultimate power consumption for the capture of CO2 and regeneration of the solvent is predicted to 5.88 GJ per 1 ton of CO2. This process regenerates the solvent, produces H2 at the cathode 312 and a mixture of CO2 and O2 at the anode. Further energy is required for the separation of the CO2 and O2 from the first gas separator 340.
CO2 and H2 is typically produced in a ratio of 2:1. If the downstream application is methanol production, the suitable stoichiometric ratio is 1:3 and additional H2 is required for this process. Commercial electrolysis equipment produces H2 with an energy consumption of 55 kWh/kg. For 1 ton of CO2, the H2 requirements are therefore (mco2Mco2)×3=68182 mol, which equals: 68182 mol×2 g/mol×55 kWh/kg=7500 kWh=26.98 GJ. The carbon capture regeneration process produced H2 corresponding to 4.5 GJ, and the remaining energy requirements for H2 production is therefore: 26.98 GJ−4.50 GJ=22.48 GJ. The power consumption of the carbon capture process is determined primarily by the electrochemical cell. The purification of CO2 requires additional energy.
Efficiency Gain in CO2 Compressor when CO2 is Removed from the Gas Stream.
The liquefaction or compression of CO2 requires energy, where the energy may be in the form of electricity for a compressor. Typically, CO2 is transported in its liquid state at 15 bars and −30 C. The optimized compression and liquefaction of pure CO2 typically has an energy cost of app. 110 wh/kg CO2. If other components are present in the CO2 the cost of compression will increase due to increased volume and weight.
The CO2 stream exiting system 100 according to the present disclosure may contain a CO2 and O2 mixture with a CO2 content between 66% v/v and 80% v/v, thus the energy required to compress the CO2 stream will be higher than that of pure CO2.
Tests and calculations performed based on a diabatic compression and subsequent condensation shows that the optimal energy requirement for compressing a CO2 mixture stream having both CO2 and O2, where the content of CO2 is around 80% v/v and O2 is approximately 20% v/v, is approximately 160 wh/kg CO2. Thus the 20% v/v O2 in the CO2 mixture stream increases the energy consumption from approximately 110 wh/kg CO2 to 160 wh/kg CO2, which is an increase of at least 50 wh/kg.
Thus, a reduction of the O2 content of the CO2 mixture stream will give a significant reduction in the energy usage, and thereby reduce the cost for compressing the CO2 exiting the system 100 of the present disclosure.
In the following, a CO2 capture from a power plant generating 10 MW heat and power from biomass is presented in relation to three process steps: “scrubber”, “regeneration” and “separation”. Overall, the process requires a large amount of electrical energy. This is positive, as electrification of the carbon capture process is highly wanted and completely new. Some of the energy may be recovered as heat for district heating.
To verify the applicability of the process using the system 100 as described herein, laboratory tests have been performed.
In the laboratory tests, a standard electrolysis cell from EC Electrocell, model Electro MP Cell was used. The electrolysis cell was provided with a Nafion 117 membrane. In operating the cell, a 1,5 M KHCO3 solution was circulated over the anode side from a combined degassing/circulation tank. The liquid was circulated at 1.5 L/min. Similarly, a 1.5 M KOH solution was circulated over the cathode side from a combined degassing/circulation tank. The liquid was circulated at 1.5 L/min. Standard flowmeters and lab pumps were used. Gas flow from the degassing tanks were measured by an Aalborg GFM gas flow meter. CO2 contents were measured using a Guardian NG from Edinburgh Sensors. A standard heat plate was used to keep a constant temperature of the liquid at 40 degrees Celsius during the experiments. The pH and temperature were measured in the circulation tanks using standard online pH and temperature meters. The current density applied to the electrolyser were varied between 1-4 kA/m2, using a standard power converter.
Details with Data from Single Cell Tests
To verify the applicability of the process using system 100 as described herein, tests have been performed. The test was performed on commercially available components from Electrocell that typically is used for KOH and chlorine production. The cell was of the type Electro MP Cell, from Electrocell A/S, Vennelystvej 1, DK-6880 Tarm, with the following configuration, the anode being titanium coated with MMO, the cathode being out of a Nickel alloy and the membrane being a Nafion 424 membrane.
The test was performed on a 0.6 M KHCO3 solution that is equivalent to absorber liquid that is fully loaded with CO2, the absorber liquid is circulated on the anode side of the cell with 1.5 l/min. The CO2 content of the absorber liquid is dependent on the effectiveness of the Scrubber, and where the tests have been performed the absorber liquid had absorbed at least 90% of possible CO2 absorption possible by the absorption liquid.
On the Cathode a 4.5 M KOH is circulated with 1.5 l/min, and the KOH concentration is increased, bleeding out liquid from the cathode is equivalent to lean absorber liquid. The temperature of the cell and liquid streams is set to 70 C. A voltage is then applied to the cell and increased until a current of 15 A is reached, for full current voltage relation of the cell, as seen in
The amount of CO2 released from the anode is measured with a mass flow meter and CO2 sensor, as seen in
Number | Date | Country | Kind |
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22160299.8 | Mar 2022 | EP | regional |
This application is a national stage application under 35 U.S.C. § 371, of PCT/EP2023/055416, filed on Mar. 3, 2023 and which claims the benefit under 35 U.S.C. § 119 (a) of European Application No. 22160299.8 filed on Mar. 4, 2022, the contents of both are incorporated by reference herein in their entirety.
Filing Document | Filing Date | Country | Kind |
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PCT/EP2023/055416 | 3/3/2023 | WO |