High efficiency zinc-iodine adsorption-aided flow battery with a low cost membrane
11552324 · 2023-01-10
Assignee
Inventors
Cpc classification
Y02E60/10
GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
Y02C20/40
GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
H01M4/1397
ELECTRICITY
Y02E60/50
GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
H01M8/0202
ELECTRICITY
H01M8/188
ELECTRICITY
B01J20/20
PERFORMING OPERATIONS; TRANSPORTING
International classification
H01M8/18
ELECTRICITY
B01J20/20
PERFORMING OPERATIONS; TRANSPORTING
H01M8/0202
ELECTRICITY
H01M4/1397
ELECTRICITY
Abstract
A flow battery system and methods are provided for eliminating crossover issues of active materials in redox flow batteries. A solid adsorbent with large specific surface area is disposed in an electrolyte of at least one half-cell, in contact with the electrolyte. During a charging process, the active material in a charged state is captured and stored on surfaces of the adsorbent, so that concentrations of the active material in the electrolyte in the charged state is reduced and the crossover is inhibited. During a discharging process, the active material is desorbed from the adsorbent to the electrolyte and pumped into the stack for reaction. The flow battery stack can have a microporous membrane separator. The electrolyte of the flow battery includes zinc iodide as active material and polyethylene glycol (PEG) as an additive.
Claims
1. A flow battery system, comprising: an anolyte comprising a first active material having a charged state A.sub.c and a discharged state A.sub.d; a catholyte comprising a second active material having a charged state B.sub.c and discharged state B.sub.d; an anode configured to be in contact with the anolyte; a cathode configured to be in contact with the catholyte; a separator interposed between the anode and the cathode; and a plurality of solid adsorbents with a specific surface area larger than 20 m.sup.2 g.sup.−1.
2. The flow battery system of claim 1, wherein the plurality of solid adsorbents is disposed in one or both of the anolyte and the catholyte, and wherein during charging, the charged active material A.sub.c and/or B.sub.c is adsorbed on surfaces of the adsorbents and stored in the anolyte and/or the catholyte, and during discharging, A.sub.c and/or B.sub.c is desorbed from surfaces of the adsorbents to the anolyte and/or the catholyte, and the discharged active material A.sub.d and/or B.sub.d is dissolved in the anolyte and/or the catholyte.
3. The flow battery system of claim 2, wherein the anolyte or catholyte is disposed in a tank having a filter structure to keep the solid adsorbents within the tank.
4. The flow battery system of claim 3, wherein the adsorbent comprises activated carbon in a form of a particle, a pellet, fabric, or porous bulk.
5. The flow battery system of claim 3, wherein the adsorbent comprises silica gel in a form of a particle, a pellet, fabric, or porous bulk.
6. The flow battery system of claim 3, wherein the adsorbent comprises zeolite in a form of a particle, a pellet, fabric, or porous bulk.
7. The flow battery system of claim 3, wherein the adsorbent comprises polymer matrix in a form of a particle, a pellet, fabric, or porous bulk.
8. The flow battery system of claim 3, wherein the adsorbent comprises transition metal oxides and sulfides including any of Sc, Ti, V, Cr, Mn, Fe, Co, Ni, Cu, and Zn, in a form of a particle, a pellet, fabric, or porous bulk.
9. The flow battery system of claim 3, wherein the adsorbent comprises metal-organic frameworks (MOF) in a form of a particle, a pellet, fabric, or porous bulk.
10. The flow battery system of claim 3, wherein the cathode active material comprises halogen including any of Cl/C1.sup.−, Br/Br.sup.−, and I/I.sup.−.
11. The flow battery system of claim 10, wherein the anolyte and catholyte each comprises zinc iodide.
12. The flow battery system of claim 11, wherein the anolyte and catholyte each comprises supporting cations including any of Li.sup.+, Na.sup.+, K.sup.+, and NH.sub.4.sup.+.
13. The flow battery system of claim 12, wherein the anolyte and/or the catholyte comprises a polyethylene glycol (PEG) additive.
14. The flow battery system of claim 3, wherein the cathode active material comprises metal ions including any of V.sup.4+/V.sup.5+, Mn.sup.2+/Mn.sup.3+, Fe.sup.2+/Fe.sup.3+, Co.sup.2+/Co.sup.3+, and Ce.sup.3+/Ce.sup.4+.
15. The flow battery system of claim 3, wherein the cathode active material comprises organic molecules including any of 2,5-di-tert-butyl-1,4-bis(2-methoxyethoxy)benzene, 4-hydrocy-TEMPO, and ferrocene derivatives.
16. The flow battery system of claim 3, wherein the anode active material comprises sulfide/polysulfide.
17. The flow battery system of claim 3, wherein the anode active material comprises transition metal ions including any of Ti.sup.3+/Ti.sup.4+, V.sup.2+/V.sup.3+ and Cr.sup.2+/Cr.sup.3+.
18. The flow battery system of claim 3, wherein the cathode active material comprises organic molecules including anthraquinone and methylviologen.
19. The flow battery system of claim 3, wherein the separator is a micro-porous membrane.
20. The flow battery system of claim 3, wherein the separator is an anion/cation exchange membrane.
Description
BRIEF DESCRIPTION OF THE DRAWINGS
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DETAILED DISCLOSURE OF THE INVENTION
(13) Embodiments of the subject invention provide novel and advantageous flow battery systems and methods for eliminating crossover of active materials in redox flow batteries. Crossover refers to transportation of redox active species across ion exchange membrane leading to self-discharge, irreversible reaction, low coulombic efficiency, and capacity decay.
(14) This invention solves the crossover problem by having adsorbents disposed in the electrolyte tank in contact with the electrolyte, as shown in
(15) The adsorbents configurations for controlling the crossover issue can be applied to many different types of flow battery systems. The adsorbent can be either activated carbon, silica gel, zeolite, metal sulfide, polymer matrix, or metal-organic frameworks, and the adsorbing active materials can include halogen, sulfide/polysulfide, transition metal ions, and organic molecules. The form of adsorbent can be either a particle, a pellet, fabric or porous bulk. The electrolyte tank may have a filter structure to keep all the adsorbents in the electrolyte tank without being flushed into the external tubes and the stack.
(16) Utilization of low-cost high-conductivity separators facilitates controlling of crossover. In some embodiments, the anolyte and the catholyte may have a same composition. With adsorbents in tank, a high coulombic efficiency can be achieved with porous non-selective separator, providing advantages of high conductivity and low cost.
(17) In one embodiment, a zinc-iodine adsorption-aided flow battery (ZIAB) system comprises activated carbon (AC) as adsorbents in a container and a low-cost porous separator. The I.sub.3-/I.sub.2Br— is catholyte of the ZIAB system is adsorbed and stored by the activated carbon in a form of solid I.sub.2 in the container during the charging processes of the ZIAB system, while the solid I.sub.2 is dissolved into the catholyte when a concentration of I.sub.3-/I.sub.2Br— decreases during the discharging processes.
(18) As a result, the concentration of the I.sub.3-/I.sub.2Br— in catholyte is reduced at high SOC, inhibiting the crossover issue. Since the iodine is stored as solid I.sub.2 in the container, utilizations of the iodine as high as almost 100% in catholyte can be realized. Further, a high coulombic efficiency of 95% can be achieved with the AC in the container when polyethylene glycol (PEG) is used as an electrolyte additive.
(19) Moreover, the activated carbon limits precipitation reactions of iodine in the container, inhibiting the pipe-blocking problem caused by the solid iodine. Thus, the subject invention offers advantages of decoupled energy and power for a flow battery, leading to low-cost, scalable, and reliable energy storage applications.
(20) When the term “about” is used herein, in conjunction with a numerical value, it is understood that the value can be in a range of 90% of the value to 110% of the value, i.e. the value can be +/−10% of the stated value. For example, “about 1 kg” means from 0.90 kg to 1.1 kg.
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(22) In one embodiment, the anolyte and catholyte of the flow battery system have a composition of zinc, bromide and iodide salt as shown in Table 1. The AC particles are immersed in a container such as a tank containing the catholyte and flowed through by the catholyte. A filter may be installed at the outlet of the catholyte container, inhibiting carbon particles from getting into the pipelines of the flow battery system.
(23) TABLE-US-00001 TABLE 1 Composition of Electrolytes Activated Sample Salt A Salt B carbon PEG K-C0 ZnBr.sub.2 1M KI 2M 0 0 K-C90 ZnBr.sub.2 1M KI 2M 228 g/L 0 K-P-C0 ZnBr.sub.2 1M KI 2M 0 1% vol K-C90 ZnBr.sub.2 1M KI 2M 228 g/L 1% vol A-P-C0 ZnI.sub.2 1M NH.sub.4Br 2M 0 1% vol A-P-C45 ZnI.sub.2 1M NH.sub.4Br 2M 114 g/L 1% vol A-P-C90 ZnI.sub.2 1M NH.sub.4Br 2M 228 g/L 1% vol
(24) During the charging processes of the Zn—I adsorption-aided flow battery system, the I.sub.3.sup.−/I.sub.2Br.sup.− formed is carried from the cathode to the catholyte container and adsorbed by the AC as shown in Equation (4), thereby limiting a concentration of the I.sub.2Br.sup.− in the catholyte and inhibiting the crossover by diffusion.
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(26) During the discharging processes of the Zn—I adsorption-aided flow battery system, when the concentration of I.sub.2Br.sup.− decreases, the I.sub.2 on surfaces of the AC are dissolved by the bromide in the catholyte, flowing into the stack of the Zn—I adsorption-aided flow battery system for the discharge processes.
(27) Moreover, with the adsorption-based flow battery system and methods, a high coulombic efficiency can be achieved. and a low-cost, non-selective porous separator can be employed. Furthermore, the issue of I.sub.2leakage to the environment can be inhabited. As the porous separator allows migration of I.sup.− from the anolyte to the catholyte of the Zn—I adsorption-aided flow battery system, the in the anolyte leads to an increase of the capacity of the flow battery system.
(28) In one embodiment, the anolyte and/or catholyte container contains a filter structure as shown in
(29) Now referring to
(30) To illustrate the effects of the adsorption employed by the subject invention, performance of one Zn—I adsorption-aided flow battery system with the AC in the container is compared with performance of one Zn—I adsorption-aided flow battery system without the AC in the container. Each side of the two battery systems contains 15 mL 2M KI with 1M ZnBr.sub.2 electrolyte, and the AC weights 80% of the iodine element.
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(32) Remarkable differences in cycling performances of the two battery systems are observed in
(33) There is a 6.4 Ah L.sup.−1 difference between the 1.sup.st and the 2.sup.nd charging capacity, which is not observed in subsequent cycles. The difference may be attributed to the irreversible AC adsorption of iodine in the 1.sup.st cycle.
(34) It is also noted that such CE is achieved with high areal Zn plating capacity over 75 mAh cm.sup.−2 and long discharging time over 3 hours 45 minutes. In the 2.sup.nd cycle, the coulombic efficiency of the battery system without the AC drops to <10%, while the charging voltage also dramatically drops, which may be due to a serious formation of dendrite on the Zn electrode as shown in
(35) The 1.sup.st-cycle charging voltage of the battery system without the AC is higher than that of the battery system with the AC, which may be contributed by a higher concentration of I.sub.3.sup.−/I.sub.2Br.sup.− in catholyte. The hypothesis was verified by the UV-vis adsorption test of the fully charged electrolyte shown in
(36) Moreover, the adsorption peak of iodine commonly seen in an iodine flow battery is not observed for the battery system with the AC, proving the effectiveness of iodine adsorption by the AC in the container of the battery system. The discharge capacity of the AC is greater than 30 Ah L.sup.−1, considering both anolyte volume and the catholyte volume. It is noted that the theoretical capacity of iodine in catholyte is only 26.8 Wh L.sup.−1, indicating that the iodine in the anolyte also contributes to the capacity increase.
(37) Although the AC adsorption significantly improves the performance of Zn—I battery with porous membrane, the low CE, low energy efficiency and dendrite issue still cannot satisfy the requirements of realistic applications. To overcome the challenges, polyethylene glycol (PEG) as additive is introduced to the flow battery system of the subject invention.
(38) It is well known that PEG as electrolyte additive can suppress Zn dendrite formation and hydrogen evolution, which is commonly used in Zn plating and Zn flow batteries[6-8]. However, in the Zn—I flow batteries, PEG forms complex with I.sub.3.sup.− at high SOC and the complex is an insoluble dark semisolid precipitation blocking ionic tunnels in the microporous separator, causing resistance increase for ionic transfer. The AC adsorbent in the tank limits the concentration of I.sub.3.sup.−/I.sub.2Br.sup.− in electrolyte, which controls the thickness of PEG-I complex deposition. The mechanism of PEG additive in adsorption-aided Zn—I flow battery is shown in
(39) As shown in
(40) The separator-blocking problem by PEG can be solved by the AC adsorption of the subject invention. In one embodiment, the AC is added into the catholyte tank of the flow cell with 1% vol PEG.sub.400 (weighting 90% of iodine in catholyte). As shown in
(41) In one embodiment, referring to
(42) At high SOC, PEG-I complex formed in the catholyte container may fix more free-I.sub.3.sup.−/I.sub.2Br.sup.− on surfaces of the AC, further suppressing the crossover issue. A CE greater than 95% can be achieved for current densities in a range of 20-40 mA cm.sup.−2 as shown in
(43) In one embodiment, to further improve rate performance of the flow battery system, ammonium bromide (NH.sub.4Br), instead of KBr, may be adopted as supporting electrolyte for its better ionic conductivity. The voltage efficiency of the flow battery system drops from 82.9% to 62.3%, when the current density increases from 20 mA cm.sup.−2 to 80 mA cm.sup.−2 as shown in
(44) To evaluate the economic impacts of the adsorption-aided flow battery system, a cost model described by R. M. Darling et al.[9], with mineral price information published by the U. S. Geological Survey (USGC) is utilized. The calculation is based on the assumption of building a 2-h energy storage system, which is a favored configuration for energy storage application for solar power and wind farms. The estimated costs of battery component are listed in Table 2.
(45) TABLE-US-00002 TABLE 2 Estimated Battery Components Cost and Performance ZIBB- Unit VRFB Nafion ZIAB Faraday Constant Ah M.sup.−1 26.80 26.80 26.80 Discharge Time H 2 2 2 OCV V 1.4 1.354 1.354 Number of Electrons 1 2 2 Additional Cost $ kW.sup.−1 50 50 50 BOP Cost $ kW.sup.−1 145 145 145 Separator Area Cost $ m.sup.−2 225 225 49 Resistance mΩ m.sup.2 0.05 0.1 0.1 Areal Cost Factor $ mΩ 11.25 22.5 4.901961 Positive material cost $ kg.sup.−1 64.47 22.46 23.86 Negative material cost $ kg.sup.−1 64.47 0.258 0.258 Electrolyte Cost $ kg.sup.−1 0.1 0.1 0.1 Active material:Electrolyte 0.1 0.66 0.66 mass ratio Positive molecular weight g M.sup.−1 51 254 254 Negative molecular weight g M.sup.−1 51 66 66 Positive DOD % 0.8 0.8 0.8 Negative DOD % 0.8 0.53 0.53 System efficiency % 0.94 0.94 0.94 Voltage efficiency % 0.9 0.9 0.9 Coulombic efficiency % 0.97 0.99 0.95
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(47) Although the energy cost is increased by 10.6% due to the extra cost of the activated carbon adsorbent, the system cost of the Zn—I flow battery with the adsorption-aided design is decreased by 15.3%, showing the economic competitiveness of the system and methods of the subject invention.
(48) Materials
(49) ZnI.sub.2 (Aladdin Chemical Reagent Co. Ltd., 98%), ZnBr2 (Xinbao Fine Chemical Factory, 98%), KI (Aladdin Chemical Reagent Co. Ltd., 99%), NH.sub.4Br (Aladdin Chemical Reagent Co. Ltd., 99%), Activated carbon by wood (Fuzhou Y H-Carbon Co. Ltd., #8-25, I value 950-1000), PEG (Aladdin Chemical Reagent Co. Ltd., Mn 400), PTFE porous separator (Haining Yibo Filter Co. Ltd., pore size 0.1 μm hydrophilic), Polymer nonwoven cloth (Mitsubishi Paper Mills Co. Ltd., 150 μm), Zn plate (Hebei Shengshida Metal Co. Ltd., 0.1 mm), and copper foam (Shanghai Yinfu Metal Co. Ltd., 2 mm) are used as received. Carbon felt (Beijing Jinglong Te Tan Co. Ltd., 3 mm) was heated in air at 500° C. for 5 hours. All the electrolytes are prepared with deionized water.
(50) Flow Battery Assembly
(51) A schematic representation of the flow stack internal structure of the flow cell is shown in
(52) Electrochemical Tests
(53) The battery testing station is a model CT3001A supplied by Wuhan Lanhe Technology Co. Ltd. For the test of electrolyte sample K—C0 in
(54) All patents, patent applications, provisional applications, and publications referred to or cited herein are incorporated by reference in their entirety, including all figures and tables, to the extent they are not inconsistent with the explicit teachings of this specification.
(55) It should be understood that the examples and embodiments described herein are for illustrative purposes only and that various modifications or changes in light thereof will be suggested to persons skilled in the art and are to be included within the spirit and purview of this application and the scope of the appended claims. In addition, any elements or limitations of any invention or embodiment thereof disclosed herein can be combined with any and/or all other elements or limitations (individually or in any combination) or any other invention or embodiment thereof disclosed herein, and all such combinations are contemplated with the scope of the invention without limitation thereto.
REFERENCES
(56) 1. Li, B., et al., Ambipolar zinc-polyiodide electrolyte for a high-energy density aqueous redox flow battery. Nature Communications, 2015. 6. 2. Xie, C. X., et al., A Long Cycle Life, Self-Healing Zinc-Iodine Flow Battery with High Power Density. Angewandte Chemie-International Edition, 2018. 57(35): p. 11171-11176. 3. Weng, G. M., et al., Unlocking the capacity of iodide for high-energy-density zinc/polyiodide and lithium/polyiodide redox flow batteries. Energy & Environmental Science, 2017. 10(3): p. 735-741. 4. Pan, H., et al., Controlling solid-liquid conversion reactions for a highly reversible aqueous zinc-iodine battery. ACS Energy Letters, 2017. 2(12): p. 2674-2680. 5. Xie, C., et al., Highly stable zinc-iodine single flow batteries with super high energy density for stationary energy storage. Energy & Environmental Science, 2019. 12(6): p. 1834-1839. 6. Ballesteros, J., et al., Zinc electrodeposition in the presence of polyethylene glycol 20000. Electrochimica Acta, 2007. 52(11): p. 3686-3696. 7. Kim, J.-W., J.-Y. Lee, and S.-M. Park, Effects of organic additives on zinc electrodeposition at iron electrodes studied by EQCM and in situ STM. Langmuir, 2004. 20(2): p. 459-466. 8. Sun, K. E., et al., Suppression of dendrite formation and corrosion on zinc anode of secondary aqueous batteries. ACS applied materials & interfaces, 2017. 9(11): p. 9681-9687. 9. Darling, R. M., et al., Pathways to low-cost electrochemical energy storage: a comparison of aqueous and nonaqueous flow batteries. Energy & Environmental Science, 2014. 7(11): p. 3459-3477.