Feasibility of CO2 desorption and electrolytic regeneration of potassium carbonate solution in an anion exchange membrane cell
Abstract
In this work, an electrolytic process was introduced for coupled regeneration of potassium carbonate (K2CO3) solution and water electrolysis by using an anion exchange membrane cell. The process made the CO2 separation from O2 much easier with respect to the existing cationic exchange membrane process. The solution of K2CO3 was used in the cathode chamber to simulate the solution after absorbing CO2. The solution of sulfuric acid (0.1 mol/L H2SO4) was charged in the anode chamber. The feasibility of the process was discussed. The effects of various operation parameters, including temperature, current density, and electrolysis time, were studied. The results indicate that both the yield rate of CO2 and the current efficiency increase initially and decrease afterward with temperature. The yield rate of CO2 increases while the current efficiency decreases with the current density. A low current density can reduce the energy consumption for producing the same amount of CO2. The processes using anion exchange membrane electrolysis can regenerate the absorbent solution to achieve 89% current efficiency, and the simultaneous production of three pure gases, CO2, H2, and O2, makes this method promising.
Keywords
INTRODUCTION
In the past 40 years, the global climate and environment have been deteriorating, and the temperature has been rising. The use of fossil energy produces a large amount of carbon dioxide (CO2), which makes the total amount of CO2 in the atmosphere continue to rise, resulting in the greenhouse effect, rising sea levels, and frequent extreme weather. In order to improve its status, China has proposed a policy to achieve a carbon peak by 2030 and carbon neutrality by 2060. In 2020, carbon emissions in China reached 9.9 billion tons, of which CO2 emissions from industrial flue gas accounted for the main part.
Pure CO2 is an important chemical raw material, and its separation and purification in flue gas is the premise of its resource utilization. Some processes have been investigated and developed for separation and purification of CO2, such as physical and chemical absorption[1-6], membrane separation[7-10], chemical looping[11-13], and cryogenic separation[14].
Chemical absorption is one of the most widely used methods in comparison with other post-combustion CO2 absorption processes[15]. Among those non-organic-based chemical solvents, including potassium carbonate (K2CO3), sodium carbonate, and aqueous ammonia, K2CO3 is the most effective, economical, and traditional solvent[16]. The hot aqueous solution of K2CO3 has been widely used in the process of removing CO2 such as natural gas sweetening or the production of pure hydrogen for ammonia synthesis[17]. CO2 is separated from the flue gas by chemical reactions between CO2 and K2CO3 solution to produce potassium bicarbonate (KHCO3). The absorbent is regenerated in subsequent steps, and CO2 is desorbed by low pressure or high temperature.
The hot K2CO3 process (Benfield process) requires a considerable amount of heat for regeneration[18]. Martin and Kubic[19] developed an innovative process called Green Freedom for the capture and recovery of atmospheric CO2 through ion-exchange-membrane electrolysis. In the new process, the recovery of captured CO2 is realized by electrolytic stripping. The process was developed to recover CO2 from rich
They concluded that energy requirements can decrease by around 16.6% for electrolytic regeneration processes and 25.8% for the total CO2 capture and compression process using electrolytic regeneration.
However, the present electrolysis process can only obtain a mixture of CO2 (~70%) and O2 in the anode chamber[16,19,20]. It is necessary to separate them by additional processes. In this paper, the authors introduced a modified electrolytic regeneration process by which three pure gases, CO2, O2, and H2, are produced. Our process uses an anionic exchange membrane as compared to a cationic exchange membrane, as reported by other researchers[19,20]. Because of the modification, CO2 and O2 are produced in the anode compartment, yet at two separate positions (membrane and electrode surfaces, respectively), thus making the CO2 separation from O2 much easier with respect to the cationic exchange membrane process. Figure 1 shows a chemical absorption system with the modified electrolytic regeneration process. The CO2-rich solution is pumped into the electrolytic regenerator, in which desorption of CO2 occurs with regeneration of the absorbent solution. The hydrogen as a by-product produced in the process and CO2 can be done via catalytic reactions to form methanol[21]. The electricity used in this process comes from clean energy.
In the paper, the regeneration mechanism of K2CO3 solution after absorption of CO2 using the modified ion-exchange membrane electrolysis process and the effects of various operation parameters, including temperature, current density, and electrolysis time, have been studied.
METHODS
The solution of K2CO3 purchased with a purity of 99% (K2CO3) was used in the cathode chamber to simulate the solution after absorbing CO2. The solution of sulfuric acid (0.1 mol/L H2SO4) was charged in the anode chamber. The solution of 200 mL was used in the experiments. The cells were separated by the anion exchange membrane (Huamotech AEM8040). Titanium plate and Titanium plate with IrO2 coating were used as the cathode and the anode, respectively. The electrolysis reactions were carried out at constant current density with an electrode area of 20 cm2. The whole cell was placed in a water bath to change the experimental temperature. The conductivity of the electrolytic solution was monitored by using a conductivity meter. The concentrations of K2CO3 and KOH in the electrolytic solution were determined by acid-base titration methods. The concentration changes in the electrolyte solutions were monitored by drawing samples at regular intervals and analyzing them by titration, and they were used to calculate the yield of CO2. The yield rate of CO2 and the current efficiency were calculated by Eqs. (4) and (5), respectively.
Where w (mL/h) is the yield rate of CO2, Ct - Ct+1 (mol/L) the concentration changes of CO32- at the interval of 1 h, V (L) the solution volume, 22.4 (L/mol) the molar volume of the gas, η the current efficiency, j
The energy requirement in the bench scale for producing CO2 per unit volume was calculated as Eq. (6).
Where W (kW·h/m3) is the energy requirement in the bench scale for producing CO2 per unit volume, I (A) represents the electrolytic current, and U (V) signifies the average cell voltage after the electrolytic process is stabilized.
RESULTS AND DISCUSSION
Regeneration mechanism
Figure 2 shows an anion exchange membrane cell proposed in this work for electrolytic regeneration of KOH. The sulfuric acid (H2SO4) solution was charged in the anode chamber instead of the absorbent solution. Carbonate ions were transferred into the anode chamber by the AEM and reacted with H+ according to Eq. (7). CO2 was, thus, produced on the surface of the AEM in the anode chamber. The consumed H+ was replenished by water electrolysis, and the simultaneous production of O2, according to Eq. (8), was on the surface of the anode. A partition could be added between the anode and the AEM to avoid the mixture of CO2 and O2. In the cathode chamber, H2 was produced from the water reduction reaction, and the absorbent KOH solvent was regenerated simultaneously according to Eqs. (9)-(11). The overall reaction of the cell can be summarized as Eq. (12).
Figure 2. AEM cell for electrolytic regeneration of KOH with simultaneous H2, O2, and CO2 generation.
It is worth noting that OH- in the cathode chamber was also able to transfer into the anode chamber by the AEM and reacted with H+ to produce H2O, which is the main reason for the decrease of the current efficiency.
Stability of the electrolytic regeneration process
The changes of cell voltage, yield rate of CO2, and current efficiency with electrolysis time were investigated. Figure 3 shows the effect of electrolysis time on the cell voltage. The cell voltage increases with the current density, but the increase is disproportionate. The almost constant cell voltage throughout the electrolysis process indicated that the process was stable.
Figure 4 shows the effect of electrolysis time on the yield rate of CO2. The production rate of CO2 dramatically decreases in the initial 2 h of electrolysis and tends to be stable in the following 3 h. The change of current efficiency with electrolysis time is shown in Figure 5. The current efficiencies are larger than 100% in the initial 2 h and tend to be stable in the following 3 h. In the initial stage, a large number of CO32- exchange with AEM surface groups. The concentration of CO32- in solution is thus reduced, but the exchange process is not the effect of the current.
Effect of temperature
It requires 2 h for the system to be stabilized, as mentioned above. The average values of yield rates of CO2 and current efficiency were calculated by the data obtained from the 3rd to 5th h. Figure 6 shows the effect of temperature on yield rates of CO2 and current efficiency. Both the yield rate of CO2 and the current efficiency increase initially and decrease afterward with temperature. The initial upward stage is due to the increasing conductivity of the solution with temperature [Figure 7]. However, OH- is easier than CO32- to cross the AEM, resulting in a decreased trend with a further increase in temperature. The values of the yield rate of CO2 and the current efficiency reached 129.7 mL/h and 77.6% at the conditions of 30 °C and
Effect of current density and CO32- initial concentration
Figure 8 shows the synergistic influence of current density and CO32- initial concentration on yield rates of CO2 and current efficiency. The larger yield rate of CO2 was obtained in a higher current density in Figure 8A, while the current efficiency has an opposite trend [Figure 8B]. The current efficiency is larger in a lower current density. The reason is that a larger number of OH- ions are produced in a higher current density or a higher CO32- initial concentration, resulting in a decrease of the current efficiency. The current efficiency reached 89% at the current density of 0.01 A/cm2 and the CO32- initial concentration of 0.7 mol/L.
Energy consumption
Figure 9 shows the effects of current density and CO32- initial concentration on energy consumption. The energy consumption increases with current density. A low current density can reduce the energy consumption.
In conclusion, (1) the processes using membrane electrolysis can regenerate the absorbent solution to achieve 89% current efficiency, and the simultaneous production of H2 makes this method promising; (2) CO2 was produced on the surface of the AEM in the anode chamber, while O2 was produced on the surface of the anode. The mixture of CO2 and O2 can be avoided by adding a partition between the anode and the AEM; (3) The effects of various operation parameters, including the temperature, the current density, and CO32- initial concentration, have been studied. Both the yield rate of CO2 and the current efficiency increase initially and decrease afterward with temperature. The yield rate of CO2 increases while the current efficiency decreases with the current density. A low current density can reduce the energy consumption for producing the same amount of CO2.
DECLARATIONS
Acknowledgment
The financial support for this research from the National Natural Science Foundation of China (No. 52074203), the Fundamental Research Funds for the Central Universities under Grants (No. N2225019), and the Natural Science Foundation of Liaoning Province (No. 2022-MS-106) is gratefully acknowledged.
Authors' contributions
Investigation: Wang Y, Yu S
Visualization: Wang Y
Conceptualization, writing - review and editing: Fu D
Availability of data and materials
The corresponding author will provide the datasets used or analyzed during the current work upon reasonable request.
Financial support and sponsorship
This work was supported by the National Natural Science Foundation of China under Grant (No. 52074203), the Fundamental Research Funds for the Central Universities under Grant (N2225019), and the Natural Science Foundation of Liaoning Province (2022-MS-106).
Conflicts of interest
All authors declared that there are no conflicts of interest.
Ethical approval and consent to participate
Not applicable.
Consent for publication
Not applicable.
Copyright
© The Author(s) 2023.
REFERENCES
1. Wang M, Lawal A, Stephenson P, Sidders J, Ramshaw C. Post-combustion CO2 capture with chemical absorption: a state-of-the-art review. Chem Eng Res Des 2011;89:1609-24.
3. Osaka Y, Tsujiguchi T, Kodama A. Experimental investigation on the CO2 separation performance from humid flue gas by TSA process. Sep Purif Technol 2018;207:77-82.
4. Huang C, Liu C, Wu K, et al. CO2 capture from flue gas using an electrochemically reversible hydroquinone/quinone solution. Energy Fuels 2019;33:3380-9.
5. Breault RW, Spenik JL, Shadle LJ, et al. Carbon capture test unit design and development using amine-based solid sorbent. Chem Eng Res Des 2016;112:251-62.
6. Ho MT, Allinson GW, Wiley DE. Reducing the cost of CO2 capture from flue gases using pressure swing adsorption. Ind Eng Chem Res 2008;47:4883-90.
7. Powell CE, Qiao GG. Polymeric CO2/N2 gas separation membranes for the capture of carbon dioxide from power plant flue gases. J Membr Sci 2006;279:1-49.
8. Favre E. Membrane processes and postcombustion carbon dioxide capture: challenges and prospects. Chem Eng J 2011;171:782-93.
9. Ho MT, Allinson GW, Wiley DE. Reducing the cost of CO2 capture from flue gases using membrane technology. Ind Eng Chem Res 2008;47:1562-8.
10. Pohlmann J, Bram M, Wilkner K, Brinkmann T. Pilot scale separation of CO2 from power plant flue gases by membrane technology. Int J Greenh Gas Control 2016;53:56-64.
11. Hossain MM, de Lasa HI. Chemical-looping combustion (CLC) for inherent CO2 separations - a review. Chem Eng Sci 2008;63:4433-51.
12. Lyngfelt A, Leckner B, Mattisson T. A fluidized-bed combustion process with inherent CO2 separation; application of chemical-looping combustion. Chem Eng Sci 2001;56:3101-13.
13. Adánez J, de Diego LF, García-labiano F, Gayán P, Abad A, Palacios JM. Selection of oxygen carriers for chemical-looping combustion. Energy Fuels 2004;18:371-7.
14. Tuinier MJ, van Sint Annaland M, Kramer GJ, Kuipers JAM. Cryogenic CO2 capture using dynamically operated packed beds. Chem Eng Sci 2010;65:114-9.
15. Koronaki I, Prentza L, Papaefthimiou V. Modeling of CO2 capture via chemical absorption processes - an extensive literature review. Renew Sustain Energy Rev 2015;50:547-66.
16. Liu N, Zhao X, Wang Y, Fei W. Electrolytic regeneration of decarbonising potassium carbonate solution. Chin J Chem Eng 2010;18:538-43.
17. Kamps Á, Meyer E, Rumpf B, Maurer G. Solubility of CO2 in aqueous solutions of KCl and in aqueous solutions of K2CO3. J Chem Eng Data 2007;52:817-32.
18. Voldsund M, Jordal K, Anantharaman R. Hydrogen production with CO2 capture. Int J Hydrogen Energy 2016;41:4969-92.
19. Martin FJ, Kubic WL. Green freedom: a concept for producing carbon-neutral synthetic fuels and chemicals. Available from: https://bioage.typepad.com/greencarcongress/docs/GreenFreedom.pdf. [Last accessed on 20 Oct 2023].
20. Zhao X, Liu N, Wang Y, Fei W, Stevens GW. Study on the mechanism and energy consumption of CO2 regeneration process by membrane electrolysis. Ind Eng Chem Res 2011;50:8620-31.
21. Chapel DG, Mariz CL, Emest J. Recovery of CO2 from flue gases: commercial trends. Available from: https://citeseerx.ist.psu.edu/document?repid=rep1&type=pdf&doi=ce589caedf02f08164efb6a9fbca874e8e60cac6. [Last accessed on 20 Oct 2023].
Cite This Article
How to Cite
Fu, D.; Wang Y.; Yu S. Feasibility of CO2 desorption and electrolytic regeneration of potassium carbonate solution in an anion exchange membrane cell. Miner. Miner. Mater. 2023, 2, 11. http://dx.doi.org/10.20517/mmm.2023.19
Download Citation
Export Citation File:
Type of Import
Tips on Downloading Citation
Citation Manager File Format
Type of Import
Direct Import: When the Direct Import option is selected (the default state), a dialogue box will give you the option to Save or Open the downloaded citation data. Choosing Open will either launch your citation manager or give you a choice of applications with which to use the metadata. The Save option saves the file locally for later use.
Indirect Import: When the Indirect Import option is selected, the metadata is displayed and may be copied and pasted as needed.
Comments
Comments must be written in English. Spam, offensive content, impersonation, and private information will not be permitted. If any comment is reported and identified as inappropriate content by OAE staff, the comment will be removed without notice. If you have any queries or need any help, please contact us at support@oaepublish.com.