WO2023091087A2 - A recycling method for active materials in lithium or sodium batteries - Google Patents

A recycling method for active materials in lithium or sodium batteries Download PDF

Info

Publication number
WO2023091087A2
WO2023091087A2 PCT/SG2022/050836 SG2022050836W WO2023091087A2 WO 2023091087 A2 WO2023091087 A2 WO 2023091087A2 SG 2022050836 W SG2022050836 W SG 2022050836W WO 2023091087 A2 WO2023091087 A2 WO 2023091087A2
Authority
WO
WIPO (PCT)
Prior art keywords
active material
lithium
tank
solution
redox
Prior art date
Application number
PCT/SG2022/050836
Other languages
French (fr)
Other versions
WO2023091087A3 (en
Inventor
Qing Wang
Feifei Zhang
Original Assignee
National University Of Singapore
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by National University Of Singapore filed Critical National University Of Singapore
Publication of WO2023091087A2 publication Critical patent/WO2023091087A2/en
Publication of WO2023091087A3 publication Critical patent/WO2023091087A3/en

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B3/00Extraction of metal compounds from ores or concentrates by wet processes
    • C22B3/04Extraction of metal compounds from ores or concentrates by wet processes by leaching
    • C22B3/045Leaching using electrochemical processes
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B26/00Obtaining alkali, alkaline earth metals or magnesium
    • C22B26/10Obtaining alkali metals
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B26/00Obtaining alkali, alkaline earth metals or magnesium
    • C22B26/10Obtaining alkali metals
    • C22B26/12Obtaining lithium
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B7/00Working up raw materials other than ores, e.g. scrap, to produce non-ferrous metals and compounds thereof; Methods of a general interest or applied to the winning of more than two metals
    • C22B7/006Wet processes
    • CCHEMISTRY; METALLURGY
    • C25ELECTROLYTIC OR ELECTROPHORETIC PROCESSES; APPARATUS THEREFOR
    • C25BELECTROLYTIC OR ELECTROPHORETIC PROCESSES FOR THE PRODUCTION OF COMPOUNDS OR NON-METALS; APPARATUS THEREFOR
    • C25B1/00Electrolytic production of inorganic compounds or non-metals
    • C25B1/01Products
    • C25B1/02Hydrogen or oxygen
    • C25B1/04Hydrogen or oxygen by electrolysis of water
    • CCHEMISTRY; METALLURGY
    • C25ELECTROLYTIC OR ELECTROPHORETIC PROCESSES; APPARATUS THEREFOR
    • C25BELECTROLYTIC OR ELECTROPHORETIC PROCESSES FOR THE PRODUCTION OF COMPOUNDS OR NON-METALS; APPARATUS THEREFOR
    • C25B1/00Electrolytic production of inorganic compounds or non-metals
    • C25B1/01Products
    • C25B1/14Alkali metal compounds
    • C25B1/16Hydroxides
    • CCHEMISTRY; METALLURGY
    • C25ELECTROLYTIC OR ELECTROPHORETIC PROCESSES; APPARATUS THEREFOR
    • C25BELECTROLYTIC OR ELECTROPHORETIC PROCESSES FOR THE PRODUCTION OF COMPOUNDS OR NON-METALS; APPARATUS THEREFOR
    • C25B1/00Electrolytic production of inorganic compounds or non-metals
    • C25B1/50Processes
    • CCHEMISTRY; METALLURGY
    • C25ELECTROLYTIC OR ELECTROPHORETIC PROCESSES; APPARATUS THEREFOR
    • C25BELECTROLYTIC OR ELECTROPHORETIC PROCESSES FOR THE PRODUCTION OF COMPOUNDS OR NON-METALS; APPARATUS THEREFOR
    • C25B15/00Operating or servicing cells
    • C25B15/08Supplying or removing reactants or electrolytes; Regeneration of electrolytes
    • C25B15/087Recycling of electrolyte to electrochemical cell

Definitions

  • the invention relates to a method recovering valuable elements from an active material of a lithium- and/or sodium-ion battery.
  • Lithium ion batteries are the undisputed choice of power source for portable devices and they are increasingly in demand for applications such as electrical energy storage (EEs) and electric vehicle (EV). LIBs may also be used in the electrical grid for power storage of renewable energy. After 30 years of commercialization and mass production, a myriad of LIBs have been produced. As will be appreciated, this has generated a massive amount of battery waste due to each battery having a limited lifespan. For example, over 1.2 billion smartphones were shipped in 2014 alone. Given that the general lifetime of a battery in such a device is around three years, then this implies that around 24,000 tonnes of lithium-ion battery cathode materials would have needed to be recycled in 2017 -with the recycled lithium material having a market value of roughly $1 billion USD. However, these end-of-life batteries, without proper treatment, may cause critical environmental damage.
  • EEs electrical energy storage
  • EV electric vehicle
  • Lithium and cobalt have been recognised as strategic resources as these elements are relatively rare in the earth’s crust.
  • spent LIBs comprise valuable metals such as Al, Cu, Co, Li, and the concentration of these elements is much higher than that in natural ores. Therefore, without recycling, these batteries would represent a big waste of valuable and scarce materials, such as Li, Co, Ni, etc.
  • this problem will only be made worse by the expansion of LIBs into other applications with widespread use, such as their use in automotive (EVs) and stationary (power grid) energy storage. For sustainable development, it has never been so pressing to recycle the spent batteries and reuse the useful components.
  • Components of the spent end-of-life LIBs include casing, electrolyte, separator and electrode materials.
  • the commonly used cathode materials are oxides compounds such as LiCoO2, LiNixMn y COzO2, LiMr ⁇ C and polyanionic LiFePC .
  • the industrially-implemented recycling technologies are mainly pyrometallurgy and hydrometallurgy.
  • Pyrometallurgy involves using extremely high temperatures to smelt the metals and burn away the remaining components like carbon and the separator material. The formed metal alloy is then treated by hydrometallurgy to obtain various salts. Despite being simple and requiring no extra-sorting and pre-processing, the pyrometallurgical process uses a huge amount of energy and generates a large amount of toxic gases, as well as CO2.
  • the typical hydrometallurgical extraction process consists of the following steps: (1) releasing residual electricity of spent batteries by discharge pre-treatment; (2) removing plastic packaging and casings from the batteries, and separating out the cathode and anode electrodes; (3) scraping cathodic and anodic active materials from the electrodes; (4) dissolving the cathodic active material (such as LiCoO 2 ) using a strong acid (e.g.
  • HCI or H2SO4 and H 2 O 2 to form a solution containing Co 2+ , Li + , SO 4 2 ' ions (leaching process); (5) adding NaOH to the resulting solution to precipitate Co(OH) 2 , leaving Li + , Na + , OH; SO4 2 ' ions in the solution; and then (6) adding Na 2 CO3 to the solution to precipitate I 2CO3 (metal separation process).
  • the above hydrometallurgical extraction process recovers a high proportion of the battery elements and does not require a huge amount of energy. However, it suffers from the following issues. Firstly, the process is complicated and involves many steps. In addition, it requires addition of a large amount of chemicals such as HCI, H 2 SO 4 , H 2 O 2 , NaOH and Na 2 CO 3 . In connection to this addition, it generates a large amount of waste material after I 2CO3 has been precipitated, resulting in secondary pollution. Furthermore, traditional hydrometallurgical extraction processes are unable to effectively extract or leach LiFePO 4 because this material does not dissolve in acid. This is problematic because LiFePO 4 is a widely-used cathode material for electrical energy storage (EEs) and electric vehicle (EV).
  • EEs electrical energy storage
  • EV electric vehicle
  • a redox flow cell comprising a cathode compartment, having a cathode electrode, and an anode compartment, having an anode electrode, separated by an ion selective membrane, where the cathode electrode and anode electrode are attached to a power supply and the redox solution is subjected to an electrochemical reaction on the anode electrode, where the electrochemical reaction on the anode: regenerates the redox mediator, which is then returned to the first tank and reacts with the active material; and enables transport of the lithium or sodium ions through the ion selective membrane into the cathode compartment, which comprises an aqueous catholyte solution that is obtained from a second tank comprising said aqueous catholyte solution;
  • steps (c) and (d) can be repeated until the active material is consumed;
  • the aqueous catholyte solution comprises a hydrogen evolution catalyst to facilitate the production of LiOH or NaOH and hydrogen gas;
  • the valuable element is selected from one or more of the group consisting of Al, Cu, Co, Ni, Fe, Mn, V, and, more particularly, Na and Li.
  • the active material is a cathodic and/or anodic active material. 3. The method according to Clause 2, wherein the cathodic active material is still attached to a cathode electrode of a dismantled lithium- or sodium-ion battery or is provided free from the cathode electrode.
  • the hydrogen evolution catalyst is selected from one or more of the group consisting of Pt, Pd, Ir, Ru, C3N4, a metal alloy (e.g. Pt-Ni-Co and/or Pt-Fe), a metal oxide, a metal sulfide, a metal carbide, a metal nitride, a metal phosphide, and a metal selenide, where the metal in each of the oxide, sulfide, carbide, nitride, phosphide and selenide is selected from one or more of the group selected from Cu, Mn, and more particularly Co, Ni, Mo and W.
  • a metal alloy e.g. Pt-Ni-Co and/or Pt-Fe
  • the redox mediator is selected from one or more of the group consisting of hydroquinonesulfonic acid and, more particularly, ferricyanide (M 3 Fe(CN) 6 ), ferrocyanide (M 4 Fe(CN) 6 ), ferrocene (C HioFe) and derivatives thereof, iodide (Ml) and bromide (MBr), where in each case M is independently selected from the group consisting of Li, Na, K and NH 4 .
  • the redox mediator is selected from one or more of the group consisting of hydroquinonesulfonic acid and, more particularly, ferricyanide (M 3 Fe(CN) 6 ), ferrocyanide (M 4 Fe(CN) 6 ), iodide (Ml), and bromide (MBr), where in each case M is independently selected from the group consisting of Li, Na, K and NH 4 , optionally wherein the derivative of ferrocene is di(ethylsulfonic lithium) ferrocene (Ci4Hi6FeS20eLi2)
  • aqueous catholyte solution is initially selected from one of water or water comprising CO2.
  • the active material is a lithium-ion battery material
  • the aqueous catholyte solution is an aqueous LiOH solution, or an aqueous LiOH solution comprising CO2 with U2CO3 precipitate, optionally wherein the aqueous catholyte solution is an aqueous LiOH solution; or
  • the active material is a sodium-ion battery material
  • the aqueous catholyte solution is an aqueous NaOH solution.
  • the active material is a cathodic active material of a dismantled lithium- or sodium-ion battery.
  • FIG. 1 depicts the schematic of the oxidative redox targeting-based strategy for spent lithium ferrophosphate (LFP) material recycling coupled with hydrogen evolution reaction (HER).
  • FIG. 2 depicts (a) voltage profile of the oxidative leaching process at a current density of 100 mA/cm 2 ; and (b) X-ray diffraction (XRD) patterns show the conversion of LFP to FP after oxidative leaching with [Fe(CN)6] 3- .
  • XRD X-ray diffraction
  • Disclosed herein is an effective approach for lithium- (or sodium-) ion battery material recycling. This may be accomplished by employing a high-throughput electrolytic flow cell to continuously break down the spent battery materials into valuable chemicals under ambient conditions, without consuming additional chemicals.
  • the reacted redox species may be instantaneously regenerated on the anode for subsequent rounds of reactions while Li + (or Na + ) is separated in the form of LiOH (or NaOH) from the cathode compartment.
  • the cathodic process can effectively be carried out with the hydrogen evolution reaction (HER) using an electrocatalyst-modified cathode.
  • the HER reaction With the assistance of an HER electrocatalyst, the HER reaction not only produces OH' for the formation of LiOH at a high-rate, but also generates H 2 as a valuable by-product. More importantly, even with low-cost HER electrocatalysts, such as metal alloys, metal oxides, metal sulfides, metal phosphides, or metal selenides, the current density could be readily increased by one order of magnitude at relatively low operating voltage, which considerably promotes the processing productivity and brings down the size of cell stack and the consequent cost.
  • a method of recovering a valuable element from an active material of a lithium- or sodium-ion battery comprising:
  • a redox flow cell comprising a cathode compartment, having a cathode electrode, and an anode compartment, having an anode electrode, separated by an ion selective membrane, where the cathode electrode and anode electrode are attached to a power supply and the redox solution is subjected to an electrochemical reaction on the anode electrode, where the electrochemical reaction on the anode: regenerates the redox mediator, which is then returned to the first tank and reacts with the active material; and enables transport of the lithium or sodium ions through the ion selective membrane into the cathode compartment, which comprises an aqueous catholyte solution that is obtained from a second tank comprising said aqueous catholyte solution;
  • steps (c) and (d) can be repeated until the active material is consumed;
  • the aqueous catholyte solution comprises a hydrogen evolution catalyst to facilitate the production of LiOH or NaOH and hydrogen gas;
  • the valuable element is selected from one or more of the group consisting of Al, Cu, Co, Ni, Fe, Mn, V, and, more particularly, Na and Li.
  • steps (c) and (d) will occur simultaneously once the process have been set in motion.
  • one of Na and Li will be recovered.
  • further valuable elements such as Al, Cu, Co, Ni, Fe, Mn, V, and combinations thereof may also be recovered.
  • the present invention may be carried out at a high current density, which produces OH’ for the formation of LiOH at a high-rate.
  • the present invention avoids using a sophisticated oxygen depolarized cathode to feed O2 and avoids the consumption of O2.
  • the word “comprising” may be interpreted as requiring the features mentioned, but not limiting the presence of other features.
  • the word “comprising” may also relate to the situation where only the components/features listed are intended to be present (e.g. the word “comprising” may be replaced by the phrases “consists of’ or “consists essentially of”). It is explicitly contemplated that both the broader and narrower interpretations can be applied to all aspects and embodiments of the present invention.
  • the word “comprising” and synonyms thereof may be replaced by the phrase “consisting of’ or the phrase “consists essentially of’ or synonyms thereof and vice versa.
  • the phrase, “consists essentially of” and its pseudonyms may be interpreted herein to refer to a material where minor impurities may be present.
  • the material may be greater than or equal to 90% pure, such as greater than 95% pure, such as greater than 97% pure, such as greater than 99% pure, such as greater than 99.9% pure, such as greater than 99.99% pure, such as greater than 99.999% pure, such as 100% pure.
  • the process above is agnostic to whether the active material is obtained from a cathode and/or an anode. This is because the process can work for active materials of both types, though there may be a preference for cathode active materials.
  • the process described above relate to the recovery of lithium from spent (retired) batteries or from waste materials produced during the manufacturing process.
  • the active materials referred to above may not be capable of functioning in a battery in their current form and so there is a need to recover the lithium and other valuable elements for reuse.
  • the separator divides the cathode compartment from the anode compartment. It can be an electro-active ion conducting membrane (e.g., a lithium or sodium ion conducting membrane).
  • the separator prevents cross-diffusion of the redox mediator and allows for movement of the electro-active ions (e.g., potassium ions, or, more particularly, lithium ions, sodium ions, magnesium ions, aluminum ions, silver ions, copper ions, protons, or a combination thereof; more particularly, the electro-active ions may be potassium ions, or, more particularly, lithium ions, sodium ions, magnesium ions, aluminum ions, copper ions, protons, or a combination thereof).
  • the electro-active ions may be potassium ions, or, more particularly, lithium ions, sodium ions, magnesium ions, aluminum ions, copper ions, protons, or a combination thereof).
  • the separator may be a lithium phosphorus oxynitride glass, a lithium thiophosphate glass, sodium phosphorus oxynitride glass, a sodium thiophosphate glass, a NASICON-type lithium conducting glass ceramic, a NASICON-type sodium conducting glass ceramic, a Garnet-type lithium or sodium conducting glass ceramic, a ceramic nanofiltration membrane, a lithium or sodium ion-exchange membrane, or suitable combinations thereof.
  • Both electrodes in the apparatus i.e. , the cathode and the anode, can be a carbon, a metal, or a combination thereof.
  • these two electrodes Preferably, these two electrodes have high surface area, with or without one or more catalysts, to facilitate the charge collection process. They can be made of a carbon, a metal, or a combination thereof. Examples of an electrode can be found in Skyllas-Kazacos, et. al., Journal of The Electrochemical Society, 158, R55-79 (2011) and Weber, et. al., Journal of Applied Electrochemistry, 41 , 1137-64 (2011).
  • the cathodic active material may come from a depleted (retired) battery or from the manufacturing processes to manufacture such batteries. Any form of the cathodic active material may be used. For example, the cathodic active material may still be attached to a cathode electrode of a dismantled lithium- or sodium-ion battery or is provided free from the cathode electrode.
  • the cathodic active material may be Li x FePO4.
  • a redox mediator refers to a compound present (e.g., dissolved) in the solvent placed in the same tank (i.e. first tank) as the active material that acts as a molecular shuttle to transport the lithium to the electrode in the flow cell to which the tank is connected.
  • Any suitable redox mediator mentioned herein may be used in the method for recovering sodium or, more particularly, lithium ions from a cathodic active material.
  • Particular examples that may be mentioned herein include, but are not limited to, hydroquinonesulfonic acid and, more particularly, ferricyanide (M 3 Fe(CN) 6 ), ferrocyanide (M 4 Fe(CN) 6 ), ferrocene (CioH Fe) and derivatives thereof (e.g. di(ethylsulfonic lithium) ferrocene (Ci4Hi 6 FeS2O6Li 2 )), iodide (Ml) and bromide (MBr), where in each case M is independently selected from the group consisting of Li, Na, K and NH4.
  • the redox mediator may be selected from one or more of the group consisting of ferricyanide (M 3 Fe(CN) s ), ferrocyanide (M 4 Fe(CN) 6 ), iodide (Ml), and bromide (MBr), where in each case M is independently selected from the group consisting of Li, Na, K and NH 4 .
  • M in the redox mediator may preferably be sodium and when seeking to recover lithium from a cathodic active material, M in the redox mediator may preferably be lithium.
  • redox mediator that is compatible with the active material and the solvent used in the tank (i.e. first tank) may be used.
  • Suitable redox mediators that may be mentioned herein include, but are not limited to ferricyanide (M 3 Fe(CN) 6 ), ferrocyanide (M 4 Fe(CN) 6 ), ferrocene (C HioFe) and derivatives thereof, iodide (Ml) and combinations thereof, where in each case M is independently selected from the group consisting of Li, Na, K and NH 4 .
  • M may preferably be Li and when the active material contains sodium, M may be Na. Any suitable concentration of the redox mediators may be used.
  • the total concentration of the redox mediator present in the solvent may be from 0.05 M to 2 M, such as from 0.05 M to 1.5 M, such as from 0.1 M to 1 M, such as from 0.3 M to 0.5 M, such as 0.2 M.
  • ferrocene derivatives having the structure:
  • X is selected from H, F, Cl, Br, I, NO2, COOR, C1.20 alkyl, CF3, and COR, in which R is H or C1.20 alkyl; n is from 0 to 20.
  • ferrocene examples include but are not limited to bromoferrocene, ferrocenylmethyl dimethyl ethyl ammonium bis(trifluoromethanesulfonyl)imide (Fc1 N112-TFSI), /V-(pyridin-2-ylmethylene)-1-(2- (diphenylphosphino) ferrocenyl) ethanamine (FeCp2PPh 2 RCN), 1 ,1-dimethylferrocene (DMFc), tetraferrocene, di(ethylsulfonic sodium) ferrocene (Ci4Hi6FeS20eNa 2 ), and di(trimethanesulfonic sodium) ferrocene (Ci6H 2 2FeS2O6Na 2 ).
  • bromoferrocene ferrocenylmethyl dimethyl ethyl ammonium bis(trifluoromethanesulfonyl)imi
  • the derivatives of ferrocene may be di(trimethanesulfonic sodium) ferrocene (Ci6H 2 2FeS2O6Na 2 ) or di(ethylsulfonic sodium) ferrocene (Ci4Hi 6 FeS 2 O6Na 2 ).
  • redox mediators examples include a metallocene derivative, a triarylamine derivative, a phenothiazine derivative, a phenoxazine derivative, a carbazole derivative, a transition metal complex, an aromatic derivative, a nitroxide radical, a disulfide, or a combination thereof.
  • the metallocene derivative used as a redox mediator may have the following structure:
  • M can be Fe, Co, Ni, Cr, or V; each of the cyclopentadienyl rings, independently, can be substituted with one or more of the following groups: F, Cl, Br, I, NO2, COOR, C1.20 alkyl, CF 3 , and COR, in which R can be H or C1.20 alkyl.
  • the triarylamine derivative used as a redox mediator may have the following structure:
  • each of the phenyl rings can be substituted with one or more of the following groups: SO 3 and, more particularly, F, Cl, Br, I, NO2, COOR, C1-20 alkyl, CF 3 , and COR, in which R can be H or C1.20 alkyl.
  • the phenothiazine derivative and the phenoxazine derivative used as a redox mediator may have the following structure:
  • R a can be H or C1.20 alkyl
  • X can be O or S
  • each of the aromatic moieties is optionally substituted with one or more of the following groups: F, Cl, Br, I, NO2, COOR, R, CF 3 , and COR, in which R can be H or C1.20 alkyl.
  • each of Ri, R2, R3, R4, Rs, and Rs can be C1-20 alkyl, F, Cl, Br, I, NO2, COOR', CF3, COR', OR', OP(OR')(OR"), or NR'R", in which each of R' and R", independently, can be H, C1.20 alkyl.
  • the nitroxide radical used as a redox mediator may have the following structure:
  • each of R1 and R 2 can be C1.20 alkyl or aryl.
  • R1, R 2 , and N together can form a heteroaryl, heteroaraalkyl, or heterocycloalkyl ring.
  • the disulfide used as a redox mediator may the following structure:
  • each of 1 and 2 can be C1.20 alkyl, COOR', CF3, COR', OR', or NR'R", in which each of R' and R", independently, can be H or C1.20 alkyl.
  • any suitable concentration of the redox mediator may be used in the solvent present in the first tank.
  • suitable concentrations include, but are not limited to a total concentration of the redox mediator present in the solvent is from 0.05 M to 3 M, such as from 0.2 M to 0.5 M, such as about 0.4 M.
  • total concentration is intended to mean that the sum of concentrations of redox mediators (when more than one redox mediator is present) fall within the cited range.
  • any suitable solvent may be used in the first tank.
  • the solvent in the first tank may be water.
  • Any suitable solvent may be used in the first tank.
  • the method above also requires a solvent to be present in both the tank containing the active material and the tank that collects the metal ion to be recycled from said active material.
  • a suitable solvent is water, which may be used alone or in combination with an organic solvent suitable for use in a battery.
  • Suitable organic solvents include, but are not limited to a glyme solvent, a cyclic carbonate (such as propylene carbonate, ethylene carbonate, diethyl carbonate butylene carbonate, fluoroethylene carbonate, chloroethylene carbonate, vinylene carbonate, and/or the like), a linear carbonate (such as dimethyl carbonate, diethyl carbonate, ethylmethyl carbonate, and the like), a cyclic ester (such as y-butyrolactone, y- valerolactone, and the like), a linear ester (such as methyl formate, methyl acetate, methyl butyrate, and the like), a cyclic or linear ether other than a glyme (such as tetrahydrofuran (and derivatives thereof), 1 ,3-dioxane, 1 ,4-dioxane, 1 ,2-dimethoxy ethane, 1,4- dibutoxy
  • solvents may be used in any suitable weight ratio with respect to the glyme solvent (e.g. tetraglyme).
  • the additional solvents may be selected from one or more of the group selected from propylene carbonate, ethylene carbonate, diethyl carbonate, dimethyl carbonate, ethyl methyl carbonate, tetrahydrofuran, sulfolane, and acetonitrile.
  • the glyme solvent may be selected from one or more of the group consisting of ethylene glycol dimetheyl ether (monoglyme), diglyme, triglyme, tetraglyme, methyl nonafluorobutyl ether (MFE) and analogues thereof.
  • Analogues of tetraglyme (CH 3 (O(CH 2 ) 2 ) 4 OCH 3 ) that may be mentioned include, but are not limited to, compounds where one or both of its CH 3 end members may be modified to either -C 2 H 5 or to -CH 2 CH 2 CI, or other similar substitutions.
  • the glyme solvent is tetraglyme.
  • the solvent used in first or second tanks may be water alone or water in combination with a glyme solvent (e.g. water and tetraglyme).
  • a glyme solvent e.g. water and tetraglyme
  • the solvent in both tanks may simply be pure water.
  • the solvent in the first tank may be water.
  • the aqueous catholyte solution may be water, or water comprising CO 2 .
  • the aqueous catholyte solution starts to include LiOH and so, after steps (b) and (c) of the method above have been completed, the aqueous catholyte solution may be an aqueous LiOH solution, or an aqueous LiOH solution comprising air and CO 2 with Li 2 CO 3 precipitate.
  • the aqueous catholyte solution starts to include NaOH and so, after steps (b) and (c) of the method above have been completed, the aqueous catholyte solution may be an aqueous NaOH solution, or an aqueous NaOH solution comprising air and CO 2 with Na 2 CO 3 precipitate.
  • the initial solvent used in the method is water and so the LIB and NIB active materials would be expected to result in an aqueous LiOH or NaOH solution, respectively.
  • Any suitable hydrogen evolution catalyst may be used in the catholyte.
  • the hydrogen evolution catalyst may be selected from one or more of the group consisting of Pt, a metal alloy, a metal oxide, a metal sulfide, a metal carbide, a metal nitride, a metal phosphide, and a metal selenide.
  • Any suitable metal alloy may be used in the current invention as the hydrogen evolution catalyst.
  • the metal alloy may be Pt-Ni-Co and/or Pt- Fe.
  • any suitable metal may be used in the metal oxide, a metal sulfide, a metal carbide, a metal nitride, a metal phosphide, and a metal selenide.
  • the metal may be one or more of the group selected from Cu and, more particularly, Co, Ni, Mo and W.
  • the second tank may be fluidly connected to a hydrogen storage tank, which may collect the hydrogen gas from the second tank (e.g. by the hydrogen rising to the top of the second tank and being pumped or otherwise fed into the storage tank).
  • the method disclosed herein is agnostic to the type of active material used - in that it may come from a cathodic active material or an anodic active material.
  • the anodic active material may come from a depleted (retired) battery. Any form of the anodic active material may be used.
  • the anodic active material may still be attached to an anode electrode of a dismantled sodium- or lithium-ion battery or is provided free from the anode electrode.
  • Any suitable material may be used as the anodic active material.
  • the anodic active material may be selected from one or more of Li4Ti 5 0i2, graphite, silicon, hard carbon. It will be appreciated that the graphite, silicon, and hard carbon active materials may be impregnated with sodium or, more particularly, lithium following use in a battery.
  • the process for recovering anodic active material is analogous to the process described hereinbefore for the recovery of cathodic active materials. While the process described herein make use of only a cathodic or anodic active materials separately, it will be appreciated that the same process as described above may be run for a combination of the cathodic and anodic active materials.
  • the active material may be a cathodic active material of a dismantled lithium- or sodium-ion battery.
  • FIG. 1 The general process described above makes use of a flow cell-type arrangement, one embodiment of which is depicted in FIG. 1. It will be appreciated that the general design depicted in this figure is applicable to both cathode and anode active material recovery processes. While the illustration uses a lithium active material, it will be appreciated that a sodium active material may be used instead.
  • the recycling apparatus 100 comprises a redox targeting-based electrolytic flow cell 101 integrated with a H 2 storage tank 115.
  • the redox targeting-based electrolytic flow cell 101 includes a cathodic cell compartment 102 comprising a catholyte tank 110, having a cathode 111, and a cathodic tank 112 comprising water (initially and then aqueous LiOH as the reaction proceeds) 113 and a HER catalyst, where the catholyte tank and the cathodic tank are fluidly connected to one another by a fluid pathway 114.
  • the cathodic tank 112 may also be connected to a hydrogen gas storage tank 115 by a suitable fluid pathway 116.
  • the anodic cell compartment 103 includes an anolyte tank 120, having an anode 121 , and an anodic tank 122 comprising an active material (e.g. LixFePCU) 123 and a redox mediator (e.g. [Fe(CN) 6 ] 3 7 Fe(CN) 6 ] 4 ) in aqueous media, where the anolyte tank and the anodic tank are fluidly connected to one another by a fluid pathway 124.
  • a cation-exchange membrane 130 is disposed between the catholyte 110 and anolyte 120 tanks, which allows cations to move from the anolyte tank to the catholyte tank 110.
  • a current collector is also attached to the catholyte and anolyte tanks. It will be appreciated that the aqueous media in the respective cathodic and anodic sides can circulate through the respective fluid pathways to allow the reaction to occur.
  • the redox mediator e.g. [Fe(CN)6] 3
  • the spent cathode material 123 in this example LixFePC , 0 ⁇ x ⁇ 1
  • the electrolyte containing [Fe(CN)6] 4 ’ and Li + circulates back to the anodic cell compartment 120 for the electrochemical reactions.
  • [Fe(CN)e] 4 ’ is oxidized on the anode 121 coupled with a H2O reduction process (HER) to produce H2 and OH’ on the cathode 111. Meanwhile, lithium ions migrate through the cation-exchange membrane 130 to the cathodic compartment 110 and forms LiOH solution.
  • the redox mediator [Fe(CN)e] 3 ' is regenerated on the anode 121 for a second leaching round, while H2 is continuously produced on the cathode 111 with the assistance of HER electrocatalyst.
  • the hydrogen is then passed into the cathodic tank 112, where it is allowed to bubble to the top of said tank for collection and transfer to the hydrogen storage tank.
  • An analogous process may be used for any active material derived from a cathode or anode active material, which may be lithium- or sodium-ion based.
  • the recycling setup 100 comprises a redox targeting-based electrolytic flow cell 101 integrated with a H 2 storage tank 115.
  • a recycling setup 100 that includes a cathodic cell compartment 102 comprising a catholyte tank 110, having a cathode 111, and a cathodic tank 112 comprising LiOH 113, where the catholyte tank and the cathodic tank are fluidly connected to one another by a fluid pathway 114.
  • the cathodic tank 112 may also include a hydrogen gas storage tank 115 that is connected by a suitable fluid pathway 116 to the cathodic tank 112.
  • the recycling setup 100 also includes an anodic cell compartment 103 comprising an anolyte tank 120, having an anode 121, and an anodic tank 122 comprising Li x FePO4 123, where the anolyte tank and the anodic tank are fluidly connected to one another by a fluid pathway 124.
  • a cationexchange membrane 130 is disposed between the catholyte 110 and anolyte 120 tanks, which allows cations to move from the anolyte tank to the catholyte tank.
  • a current collector is also attached to the catholyte and anolyte tank.
  • the redox mediator [Fe(CN) 6 ] 3 ’ oxidizes the spent cathode material LixFePC , 0 ⁇ x ⁇ 1 , and extract Li + from Li x FePC>4 to form FePC solid and [Fe(CN)e] 4 ' /Li + solution.
  • the electrolyte containing [Fe(CN)6] 4- and Li + circulates back to the anodic cell compartment for the electrochemical reactions.
  • [Fe(CN)s] 4 ' is oxidized on the anode coupled with a H2O reduction process (HER) to produce H2 and OH' on the cathode. Meanwhile, Li + migrates through a cation-exchange membrane to the cathodic cell compartment and forms LiOH solution.
  • the redox mediator [Fe(CN)e] 3 ' is regenerated on the anode for a second leaching round, while H2 is continuously produced on the cathode with the assistance of HER electrocatalyst.
  • the spent LixFePC powder (black mass) consists of conductive agent and binder. 2 g of black mass was immersed into 50 mL of 0.4 M Li 4 Fe(CN) 6 solution in the anodic tank. 50 mL of 0.1 M LiOH was used as the catholyte and HER electrocatalyst (such as Pt, metal alloys, metal oxides, metal sulfides, metal phosphides, or metal selenides) modified carbon felt was used as cathode. Both catholyte and anolyte were pumped flowing through the cell and tanks. The generated H 2 was collected from the cathodic tank and stored into a H 2 storage tank. The electric current density was kept at 100 mA/cm 2 , and voltage changes on the cell were monitored by an Arbin battery testing system.
  • HER electrocatalyst such as Pt, metal alloys, metal oxides, metal sulfides, metal phosphides, or metal selenides
  • the voltage was maintained at around 1.8 V and stopped at a cut-off voltage of 2.3 V at the end of the electrolytic process.
  • a leaching efficiency of around 97% based on the charge capacity was calculated.
  • the black mass was extracted from anolyte and dried.
  • the XRD patterns (FIG. 2b) indicate that all the indexed peaks of pristine olivine LiFePCU vanished after leaching process, instead of the new pattern consistent with that of FePO4. Meanwhile, the catholyte was collected and dried in an oven. White powder of LiOH was obtained after drying overnight. The quantity was nearly consistent with the charge capacity of the cell.
  • suitable redox mediators similar process can be implemented to recycle batteries with LiCoO2, LiNii/sMni/3Coi/3O2 and other cathode materials.

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Materials Engineering (AREA)
  • Organic Chemistry (AREA)
  • Metallurgy (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Electrochemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Geology (AREA)
  • Manufacturing & Machinery (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Mechanical Engineering (AREA)
  • Environmental & Geological Engineering (AREA)
  • Inorganic Chemistry (AREA)
  • Geochemistry & Mineralogy (AREA)
  • General Chemical & Material Sciences (AREA)
  • Sustainable Development (AREA)
  • Secondary Cells (AREA)
  • Manufacture And Refinement Of Metals (AREA)

Abstract

Disclosed herein is a method of method of recovering a valuable element from an active material of a lithium or sodium ion battery. The method requiring an active material comprising lithium or sodium ions, where the active material is added to a redox solution that is formed from a solvent and a redox mediator to form a redox solution in a first tank and then moving the redox solution from the first tank to a redox flow cell having a cathode compartment, which compartment has a cathode electrode, and an anode compartment, having an anode electrode, separated by an ion selective membrane, where the cathode electrode and anode electrode are attached to a power supply and the redox solution is subjected to an electrochemical reaction on the anode electrode, where the electrochemical reaction on the anode: regenerates the redox mediator, which is then returned to the first tank and reacts with the active material; and enables transport of the lithium or sodium ions through the ion selective membrane into the cathode compartment, which comprises an aqueous catholyte solution that is obtained from a second tank, and then capturing the lithium or sodium ions and producing hydrogen in the cathode compartment through an electrochemical reaction on the cathode electrode that produces LiOH or NaOH and hydrogen gas and transferring the resulting aqueous LiOH or NaOH and hydrogen gas in the resulting catholyte solution to a second tank, where: the aqueous catholyte solution comprises a hydrogen evolution catalyst to facilitate the production of LiOH or NaOH and hydrogen gas; and the valuable element is selected from one or more of the group consisting of Al, Cu, Co, Ni, Fe, Mn, V, and, more particularly, Na and Li.

Description

A RECYCLING METHOD FOR ACTIVE MATERIALS IN LITHIUM OR SODIUM BATTERIES
Field of Invention
The invention relates to a method recovering valuable elements from an active material of a lithium- and/or sodium-ion battery.
Background
The listing or discussion of a prior-published document in this specification should not necessarily be taken as an acknowledgement that the document is part of the state of the art or is common general knowledge.
Lithium ion batteries (LIBs) are the undisputed choice of power source for portable devices and they are increasingly in demand for applications such as electrical energy storage (EEs) and electric vehicle (EV). LIBs may also be used in the electrical grid for power storage of renewable energy. After 30 years of commercialization and mass production, a myriad of LIBs have been produced. As will be appreciated, this has generated a massive amount of battery waste due to each battery having a limited lifespan. For example, over 1.2 billion smartphones were shipped in 2014 alone. Given that the general lifetime of a battery in such a device is around three years, then this implies that around 24,000 tonnes of lithium-ion battery cathode materials would have needed to be recycled in 2017 -with the recycled lithium material having a market value of roughly $1 billion USD. However, these end-of-life batteries, without proper treatment, may cause critical environmental damage.
Lithium and cobalt have been recognised as strategic resources as these elements are relatively rare in the earth’s crust. Moreover, spent LIBs comprise valuable metals such as Al, Cu, Co, Li, and the concentration of these elements is much higher than that in natural ores. Therefore, without recycling, these batteries would represent a big waste of valuable and scarce materials, such as Li, Co, Ni, etc. As will be appreciated, this problem will only be made worse by the expansion of LIBs into other applications with widespread use, such as their use in automotive (EVs) and stationary (power grid) energy storage. For sustainable development, it has never been so pressing to recycle the spent batteries and reuse the useful components.
Components of the spent end-of-life LIBs include casing, electrolyte, separator and electrode materials. The commonly used cathode materials are oxides compounds such as LiCoO2, LiNixMnyCOzO2, LiMr^C and polyanionic LiFePC . Currently, the industrially-implemented recycling technologies are mainly pyrometallurgy and hydrometallurgy.
Pyrometallurgy involves using extremely high temperatures to smelt the metals and burn away the remaining components like carbon and the separator material. The formed metal alloy is then treated by hydrometallurgy to obtain various salts. Despite being simple and requiring no extra-sorting and pre-processing, the pyrometallurgical process uses a huge amount of energy and generates a large amount of toxic gases, as well as CO2.
The typical hydrometallurgical extraction process consists of the following steps: (1) releasing residual electricity of spent batteries by discharge pre-treatment; (2) removing plastic packaging and casings from the batteries, and separating out the cathode and anode electrodes; (3) scraping cathodic and anodic active materials from the electrodes; (4) dissolving the cathodic active material (such as LiCoO2) using a strong acid (e.g. HCI or H2SO4) and H2O2 to form a solution containing Co2+, Li+, SO4 2' ions (leaching process); (5) adding NaOH to the resulting solution to precipitate Co(OH)2, leaving Li+, Na+, OH; SO42' ions in the solution; and then (6) adding Na2CO3 to the solution to precipitate I 2CO3 (metal separation process).
The above hydrometallurgical extraction process recovers a high proportion of the battery elements and does not require a huge amount of energy. However, it suffers from the following issues. Firstly, the process is complicated and involves many steps. In addition, it requires addition of a large amount of chemicals such as HCI, H2SO4, H2O2, NaOH and Na2CO3. In connection to this addition, it generates a large amount of waste material after I 2CO3 has been precipitated, resulting in secondary pollution. Furthermore, traditional hydrometallurgical extraction processes are unable to effectively extract or leach LiFePO4 because this material does not dissolve in acid. This is problematic because LiFePO4 is a widely-used cathode material for electrical energy storage (EEs) and electric vehicle (EV).
One strategy that has been attempted to overcome some of the above problems is set out in PCT Patent Publication No. WO 2020/086000. Nevertheless, this method makes use of a sophisticated depolarised cathode and requires a complex flow cell construction, leading to a large footprint for the cell stack, mediocre productivity, as well as increased operating costs. There is therefore a need for a high-throughput, simpler and low-cost process for recycling LIBs that avoids using strong acids and mitigates generation of secondary waste material, which solves one or more problems identified above.
Summary of Invention
Aspects and embodiments of the invention will now be discussed by reference to the following numbered clauses.
1. A method of recovering a valuable element from an active material of a lithium- or sodium-ion battery, respectively, the method comprising:
(a) providing an active material comprising lithium or sodium ions;
(b) adding the active material to a redox solution that comprises a solvent and a redox mediator to form a redox solution comprising lithium or sodium ions in a first tank;
(c) moving the redox solution from the first tank to a redox flow cell comprising a cathode compartment, having a cathode electrode, and an anode compartment, having an anode electrode, separated by an ion selective membrane, where the cathode electrode and anode electrode are attached to a power supply and the redox solution is subjected to an electrochemical reaction on the anode electrode, where the electrochemical reaction on the anode: regenerates the redox mediator, which is then returned to the first tank and reacts with the active material; and enables transport of the lithium or sodium ions through the ion selective membrane into the cathode compartment, which comprises an aqueous catholyte solution that is obtained from a second tank comprising said aqueous catholyte solution;
(d) capturing the lithium or sodium ions and producing hydrogen in the cathode compartment through an electrochemical reaction on the cathode electrode that produces LiOH or NaOH and hydrogen gas and transferring the resulting aqueous LiOH or NaOH and hydrogen gas in the resulting catholyte solution to a second tank, wherein: steps (c) and (d) can be repeated until the active material is consumed; the aqueous catholyte solution comprises a hydrogen evolution catalyst to facilitate the production of LiOH or NaOH and hydrogen gas; and the valuable element is selected from one or more of the group consisting of Al, Cu, Co, Ni, Fe, Mn, V, and, more particularly, Na and Li.
2. The method according to Clause 1 , wherein the active material is a cathodic and/or anodic active material. 3. The method according to Clause 2, wherein the cathodic active material is still attached to a cathode electrode of a dismantled lithium- or sodium-ion battery or is provided free from the cathode electrode.
4. The method according to Clause 2 or Clause 3, wherein the cathodic active material is selected from one or more of NaFePCU, NaCoCh, Na 2(PO4)s, more particularly, LixFePC>4, LixNiaCodAlcOz, LixNiuCovMnwO2, LixCoO2, LixMn2O4, and LixNio 5Mn1.5O4, where 0 <x< 1 , a + b + c = 1 , and u + v + w = 1 , optionally wherein the cathodic active material is LixFePO4.
5. The method according to any one of the preceding clauses, wherein the hydrogen evolution catalyst is selected from one or more of the group consisting of Pt, Pd, Ir, Ru, C3N4, a metal alloy (e.g. Pt-Ni-Co and/or Pt-Fe), a metal oxide, a metal sulfide, a metal carbide, a metal nitride, a metal phosphide, and a metal selenide, where the metal in each of the oxide, sulfide, carbide, nitride, phosphide and selenide is selected from one or more of the group selected from Cu, Mn, and more particularly Co, Ni, Mo and W.
6. The method according to any one of the preceding clauses, wherein the redox mediator is selected from one or more of the group consisting of hydroquinonesulfonic acid and, more particularly, ferricyanide (M3Fe(CN)6), ferrocyanide (M4Fe(CN)6), ferrocene (C HioFe) and derivatives thereof, iodide (Ml) and bromide (MBr), where in each case M is independently selected from the group consisting of Li, Na, K and NH4.
7. The method according to Clause 6, wherein the redox mediator is selected from one or more of the group consisting of hydroquinonesulfonic acid and, more particularly, ferricyanide (M3Fe(CN)6), ferrocyanide (M4Fe(CN)6), iodide (Ml), and bromide (MBr), where in each case M is independently selected from the group consisting of Li, Na, K and NH4, optionally wherein the derivative of ferrocene is di(ethylsulfonic lithium) ferrocene (Ci4Hi6FeS20eLi2)
8. The method according to Clause 6 or Clause 7, wherein the total concentration of the redox mediator present in the solvent is from 0.05 M to 3 M, such as from 0.2 M to 0.5 M, such as about 0.4 M.
9. The method according to any one of the preceding clauses, wherein the second tank is fluidly connected to a hydrogen storage tank, which collects the hydrogen gas from the second tank. 10. The method according to any one of the preceding clauses, wherein the solvent is pure water.
11. The method according to any one of the preceding clauses, wherein the aqueous catholyte solution is initially selected from one of water or water comprising CO2.
12. The method according to any one of the preceding clauses, wherein after steps (b) and (c) have been completed, and:
(i) the active material is a lithium-ion battery material, then the aqueous catholyte solution is an aqueous LiOH solution, or an aqueous LiOH solution comprising CO2 with U2CO3 precipitate, optionally wherein the aqueous catholyte solution is an aqueous LiOH solution; or
(ii) the active material is a sodium-ion battery material, then the aqueous catholyte solution is an aqueous NaOH solution.
13. The method according to any one of Clauses 2 to 12, wherein the anodic active material is still attached to an anode electrode of a dismantled lithium-ion battery or is provided free from the anode electrode.
14. The method according to any one of Clauses 2 to 13, wherein the anodic active material is selected from one or more of Li4Ti50i2, graphite, silicon, hard carbon.
15. The method according to any one of the preceding clauses, wherein the active material is a cathodic active material of a dismantled lithium- or sodium-ion battery.
Drawings
FIG. 1 depicts the schematic of the oxidative redox targeting-based strategy for spent lithium ferrophosphate (LFP) material recycling coupled with hydrogen evolution reaction (HER).
FIG. 2 depicts (a) voltage profile of the oxidative leaching process at a current density of 100 mA/cm2; and (b) X-ray diffraction (XRD) patterns show the conversion of LFP to FP after oxidative leaching with [Fe(CN)6]3-. Description
Disclosed herein is an effective approach for lithium- (or sodium-) ion battery material recycling. This may be accomplished by employing a high-throughput electrolytic flow cell to continuously break down the spent battery materials into valuable chemicals under ambient conditions, without consuming additional chemicals. The reacted redox species may be instantaneously regenerated on the anode for subsequent rounds of reactions while Li+ (or Na+) is separated in the form of LiOH (or NaOH) from the cathode compartment. Surprisingly, the cathodic process can effectively be carried out with the hydrogen evolution reaction (HER) using an electrocatalyst-modified cathode. With the assistance of an HER electrocatalyst, the HER reaction not only produces OH' for the formation of LiOH at a high-rate, but also generates H2 as a valuable by-product. More importantly, even with low-cost HER electrocatalysts, such as metal alloys, metal oxides, metal sulfides, metal phosphides, or metal selenides, the current density could be readily increased by one order of magnitude at relatively low operating voltage, which considerably promotes the processing productivity and brings down the size of cell stack and the consequent cost.
Thus, in a first aspect of the invention, there is provided a method of recovering a valuable element from an active material of a lithium- or sodium-ion battery, respectively, the method comprising:
(a) providing an active material comprising lithium or sodium ions;
(b) adding the active material to a redox solution that comprises a solvent and a redox mediator to form a redox solution comprising lithium or sodium ions in a first tank;
(c) moving the redox solution from the first tank to a redox flow cell comprising a cathode compartment, having a cathode electrode, and an anode compartment, having an anode electrode, separated by an ion selective membrane, where the cathode electrode and anode electrode are attached to a power supply and the redox solution is subjected to an electrochemical reaction on the anode electrode, where the electrochemical reaction on the anode: regenerates the redox mediator, which is then returned to the first tank and reacts with the active material; and enables transport of the lithium or sodium ions through the ion selective membrane into the cathode compartment, which comprises an aqueous catholyte solution that is obtained from a second tank comprising said aqueous catholyte solution;
(d) capturing the lithium or sodium ions and producing hydrogen in the cathode compartment through an electrochemical reaction on the cathode electrode that produces LiOH or NaOH and hydrogen gas and transferring the resulting aqueous LiOH or NaOH and hydrogen gas in the resulting catholyte solution to a second tank, wherein: steps (c) and (d) can be repeated until the active material is consumed; the aqueous catholyte solution comprises a hydrogen evolution catalyst to facilitate the production of LiOH or NaOH and hydrogen gas; and the valuable element is selected from one or more of the group consisting of Al, Cu, Co, Ni, Fe, Mn, V, and, more particularly, Na and Li.
As will be appreciated, steps (c) and (d) will occur simultaneously once the process have been set in motion. In addition, it will be appreciated that one of Na and Li will be recovered. However, depending on the active material used, further valuable elements, such as Al, Cu, Co, Ni, Fe, Mn, V, and combinations thereof may also be recovered.
Advantages associated with this method include, but are not limited to the following.
• An increased current density and production of the desired products. In comparison with a recycling method that uses oxygen reduction reaction (ORR), the present invention may be carried out at a high current density, which produces OH’ for the formation of LiOH at a high-rate.
• Simplification of the flow cell construction, as well as a smaller cell stack. In comparison with the recycling paired with oxygen reduction reaction, the present invention operates with redox flow cells of simple construction and with a smaller size.
• In comparison with the recycling method that uses ORR, the present invention avoids using a sophisticated oxygen depolarized cathode to feed O2 and avoids the consumption of O2.
• Generation of the valuable by-product hydrogen
• This results in a reduced capital and processing costs, and therefore increased profit.
In embodiments herein, the word “comprising” may be interpreted as requiring the features mentioned, but not limiting the presence of other features. Alternatively, the word “comprising” may also relate to the situation where only the components/features listed are intended to be present (e.g. the word “comprising” may be replaced by the phrases “consists of’ or “consists essentially of”). It is explicitly contemplated that both the broader and narrower interpretations can be applied to all aspects and embodiments of the present invention. In other words, the word “comprising” and synonyms thereof may be replaced by the phrase “consisting of’ or the phrase “consists essentially of’ or synonyms thereof and vice versa.
The phrase, “consists essentially of” and its pseudonyms may be interpreted herein to refer to a material where minor impurities may be present. For example, the material may be greater than or equal to 90% pure, such as greater than 95% pure, such as greater than 97% pure, such as greater than 99% pure, such as greater than 99.9% pure, such as greater than 99.99% pure, such as greater than 99.999% pure, such as 100% pure.
As will be appreciated, the process above is agnostic to whether the active material is obtained from a cathode and/or an anode. This is because the process can work for active materials of both types, though there may be a preference for cathode active materials.
As will be appreciated, the process described above relate to the recovery of lithium from spent (retired) batteries or from waste materials produced during the manufacturing process. As such, the active materials referred to above may not be capable of functioning in a battery in their current form and so there is a need to recover the lithium and other valuable elements for reuse.
The separator divides the cathode compartment from the anode compartment. It can be an electro-active ion conducting membrane (e.g., a lithium or sodium ion conducting membrane). The separator prevents cross-diffusion of the redox mediator and allows for movement of the electro-active ions (e.g., potassium ions, or, more particularly, lithium ions, sodium ions, magnesium ions, aluminum ions, silver ions, copper ions, protons, or a combination thereof; more particularly, the electro-active ions may be potassium ions, or, more particularly, lithium ions, sodium ions, magnesium ions, aluminum ions, copper ions, protons, or a combination thereof). For example, the separator may be a lithium phosphorus oxynitride glass, a lithium thiophosphate glass, sodium phosphorus oxynitride glass, a sodium thiophosphate glass, a NASICON-type lithium conducting glass ceramic, a NASICON-type sodium conducting glass ceramic, a Garnet-type lithium or sodium conducting glass ceramic, a ceramic nanofiltration membrane, a lithium or sodium ion-exchange membrane, or suitable combinations thereof.
Both electrodes in the apparatus, i.e. , the cathode and the anode, can be a carbon, a metal, or a combination thereof. Preferably, these two electrodes have high surface area, with or without one or more catalysts, to facilitate the charge collection process. They can be made of a carbon, a metal, or a combination thereof. Examples of an electrode can be found in Skyllas-Kazacos, et. al., Journal of The Electrochemical Society, 158, R55-79 (2011) and Weber, et. al., Journal of Applied Electrochemistry, 41 , 1137-64 (2011).
The cathodic active material may come from a depleted (retired) battery or from the manufacturing processes to manufacture such batteries. Any form of the cathodic active material may be used. For example, the cathodic active material may still be attached to a cathode electrode of a dismantled lithium- or sodium-ion battery or is provided free from the cathode electrode.
Examples of cathodic active materials include, but are not limited to, NaFePCU, NaCoCh, Na 2(PC>4)3, more particularly, LLFePC , LixNiaCofcAlcOa, LixNiuCovMnwO2, LixCoO2, LixMn2O4, and LixNio.5Mn1.5O4, where 0 <x< 1 , a + b + c = 1 , and u + v + w - 1 , and combinations thereof. In a particular embodiment of the invention that may be mentioned herein, the cathodic active material may be LixFePO4.
A redox mediator refers to a compound present (e.g., dissolved) in the solvent placed in the same tank (i.e. first tank) as the active material that acts as a molecular shuttle to transport the lithium to the electrode in the flow cell to which the tank is connected.
Any suitable redox mediator mentioned herein may be used in the method for recovering sodium or, more particularly, lithium ions from a cathodic active material. Particular examples that may be mentioned herein include, but are not limited to, hydroquinonesulfonic acid and, more particularly, ferricyanide (M3Fe(CN)6), ferrocyanide (M4Fe(CN)6), ferrocene (CioH Fe) and derivatives thereof (e.g. di(ethylsulfonic lithium) ferrocene (Ci4Hi6FeS2O6Li2)), iodide (Ml) and bromide (MBr), where in each case M is independently selected from the group consisting of Li, Na, K and NH4. More particularly, the redox mediator may be selected from one or more of the group consisting of ferricyanide (M3Fe(CN)s), ferrocyanide (M4Fe(CN)6), iodide (Ml), and bromide (MBr), where in each case M is independently selected from the group consisting of Li, Na, K and NH4. As will be appreciated when seeking to recover sodium from a cathodic active material, M in the redox mediator may preferably be sodium and when seeking to recover lithium from a cathodic active material, M in the redox mediator may preferably be lithium.
Any suitable redox mediator that is compatible with the active material and the solvent used in the tank (i.e. first tank) may be used. Suitable redox mediators that may be mentioned herein include, but are not limited to ferricyanide (M3Fe(CN)6), ferrocyanide (M4Fe(CN)6), ferrocene (C HioFe) and derivatives thereof, iodide (Ml) and combinations thereof, where in each case M is independently selected from the group consisting of Li, Na, K and NH4. As will be understood, when the active material contains lithium, M may preferably be Li and when the active material contains sodium, M may be Na. Any suitable concentration of the redox mediators may be used. For example, the total concentration of the redox mediator present in the solvent may be from 0.05 M to 2 M, such as from 0.05 M to 1.5 M, such as from 0.1 M to 1 M, such as from 0.3 M to 0.5 M, such as 0.2 M. Derivatives of ferrocene that may be mentioned herein include ferrocene derivatives having the structure:
Figure imgf000012_0001
In the above formulae, X is selected from H, F, Cl, Br, I, NO2, COOR, C1.20 alkyl, CF3, and COR, in which R is H or C1.20 alkyl; n is from 0 to 20.
Specific derivatives of ferrocene that may be mentioned herein include but are not limited to bromoferrocene, ferrocenylmethyl dimethyl ethyl ammonium bis(trifluoromethanesulfonyl)imide (Fc1 N112-TFSI), /V-(pyridin-2-ylmethylene)-1-(2- (diphenylphosphino) ferrocenyl) ethanamine (FeCp2PPh2RCN), 1 ,1-dimethylferrocene (DMFc), tetraferrocene, di(ethylsulfonic sodium) ferrocene (Ci4Hi6FeS20eNa2), and di(trimethanesulfonic sodium) ferrocene (Ci6H22FeS2O6Na2).
In particular embodiments of the invention that may be mentioned herein, the derivatives of ferrocene may be di(trimethanesulfonic sodium) ferrocene (Ci6H22FeS2O6Na2) or di(ethylsulfonic sodium) ferrocene (Ci4Hi6FeS2O6Na2).
Further redox mediators that may be used in the current invention are described below with reference to WO 2013/012391.
Examples of redox mediators are discussed in depth in international application publication number WO 2013/012391, which is hereby incorporated by reference. For example, redox mediators disclosed in WO 2013/012391 include a metallocene derivative, a triarylamine derivative, a phenothiazine derivative, a phenoxazine derivative, a carbazole derivative, a transition metal complex, an aromatic derivative, a nitroxide radical, a disulfide, or a combination thereof.
The metallocene derivative used as a redox mediator may have the following structure:
Figure imgf000013_0001
In the above formula, M can be Fe, Co, Ni, Cr, or V; each of the cyclopentadienyl rings, independently, can be substituted with one or more of the following groups: F, Cl, Br, I, NO2, COOR, C1.20 alkyl, CF3, and COR, in which R can be H or C1.20 alkyl.
The triarylamine derivative used as a redox mediator may have the following structure:
Figure imgf000013_0002
In the above formula, each of the phenyl rings, independently, can be substituted with one or more of the following groups: SO3 and, more particularly, F, Cl, Br, I, NO2, COOR, C1-20 alkyl, CF3, and COR, in which R can be H or C1.20 alkyl.
The phenothiazine derivative and the phenoxazine derivative used as a redox mediator may have the following structure:
Figure imgf000013_0003
Ra can be H or C1.20 alkyl, X can be O or S, each of the aromatic moieties is optionally substituted with one or more of the following groups: F, Cl, Br, I, NO2, COOR, R, CF3, and COR, in which R can be H or C1.20 alkyl.
The aromatic derivative used as a redox mediator may have the following structure:
Figure imgf000013_0004
In these formulas, each of Ri, R2, R3, R4, Rs, and Rs, can be C1-20 alkyl, F, Cl, Br, I, NO2, COOR', CF3, COR', OR', OP(OR')(OR"), or NR'R", in which each of R' and R", independently, can be H, C1.20 alkyl.
The nitroxide radical used as a redox mediator may have the following structure:
Figure imgf000014_0001
In these formulas, each of R1 and R2, independently, can be C1.20 alkyl or aryl. R1, R2, and N together can form a heteroaryl, heteroaraalkyl, or heterocycloalkyl ring.
The disulfide used as a redox mediator may the following structure:
Figure imgf000014_0002
In these formulas, each of 1 and 2, independently, can be C1.20 alkyl, COOR', CF3, COR', OR', or NR'R", in which each of R' and R", independently, can be H or C1.20 alkyl.
Any suitable concentration of the redox mediator may be used in the solvent present in the first tank. Examples of suitable concentrations include, but are not limited to a total concentration of the redox mediator present in the solvent is from 0.05 M to 3 M, such as from 0.2 M to 0.5 M, such as about 0.4 M. When used herein, the term “total concentration” is intended to mean that the sum of concentrations of redox mediators (when more than one redox mediator is present) fall within the cited range.
Any suitable solvent may be used in the first tank. For example, any of the solvents (and combinations of solvents) referred to herein. In particular examples that may be mentioned herein, the solvent in the first tank may be water.
Any suitable solvent may be used in the first tank. As will be appreciated, the method above also requires a solvent to be present in both the tank containing the active material and the tank that collects the metal ion to be recycled from said active material. A suitable solvent is water, which may be used alone or in combination with an organic solvent suitable for use in a battery. Suitable organic solvents that may be mentioned herein include, but are not limited to a glyme solvent, a cyclic carbonate (such as propylene carbonate, ethylene carbonate, diethyl carbonate butylene carbonate, fluoroethylene carbonate, chloroethylene carbonate, vinylene carbonate, and/or the like), a linear carbonate (such as dimethyl carbonate, diethyl carbonate, ethylmethyl carbonate, and the like), a cyclic ester (such as y-butyrolactone, y- valerolactone, and the like), a linear ester (such as methyl formate, methyl acetate, methyl butyrate, and the like), a cyclic or linear ether other than a glyme (such as tetrahydrofuran (and derivatives thereof), 1 ,3-dioxane, 1 ,4-dioxane, 1 ,2-dimethoxy ethane, 1,4- dibutoxyethane, and the like), a nitrile (such as acetonitrile, benzonitrile, and/or the like), dioxolane or a derivative thereof, ethylene sulfide, sulfolane, and sultone or a derivative thereof. These solvents may be used in any suitable weight ratio with respect to the glyme solvent (e.g. tetraglyme). For example, the additional solvents may be selected from one or more of the group selected from propylene carbonate, ethylene carbonate, diethyl carbonate, dimethyl carbonate, ethyl methyl carbonate, tetrahydrofuran, sulfolane, and acetonitrile.
The glyme solvent may be selected from one or more of the group consisting of ethylene glycol dimetheyl ether (monoglyme), diglyme, triglyme, tetraglyme, methyl nonafluorobutyl ether (MFE) and analogues thereof. Analogues of tetraglyme (CH3(O(CH2)2)4OCH3) that may be mentioned include, but are not limited to, compounds where one or both of its CH3 end members may be modified to either -C2H5 or to -CH2CH2CI, or other similar substitutions. In certain embodiments of the invention that may be mentioned herein, the glyme solvent is tetraglyme.
In particular embodiments that may be mentioned herein the solvent used in first or second tanks may be water alone or water in combination with a glyme solvent (e.g. water and tetraglyme). For example, the solvent in both tanks may simply be pure water.
In particular examples that may be mentioned herein, the solvent in the first tank may be water. Initially, the aqueous catholyte solution may be water, or water comprising CO2. When used herein, when water is referred to, it is intended to refer to pure water, that is deionized water. Subsequently, as the method is conducted with a LIB active material, the aqueous catholyte solution starts to include LiOH and so, after steps (b) and (c) of the method above have been completed, the aqueous catholyte solution may be an aqueous LiOH solution, or an aqueous LiOH solution comprising air and CO2 with Li2CO3 precipitate. Alternatively, if the method is conducted with a sodium active material (NIB), the aqueous catholyte solution starts to include NaOH and so, after steps (b) and (c) of the method above have been completed, the aqueous catholyte solution may be an aqueous NaOH solution, or an aqueous NaOH solution comprising air and CO2 with Na2CO3 precipitate. Preferably, the initial solvent used in the method is water and so the LIB and NIB active materials would be expected to result in an aqueous LiOH or NaOH solution, respectively.
As will be appreciated, an important part of the current method is the ability to generate hydrogen, and thereby produce a useful by-product, while also reducing chemical consumption. This is achieved by ensuring that a hydrogen evolution catalyst is present in the catholyte. Any suitable hydrogen evolution catalyst may be used in the catholyte. For example, the hydrogen evolution catalyst may be selected from one or more of the group consisting of Pt, a metal alloy, a metal oxide, a metal sulfide, a metal carbide, a metal nitride, a metal phosphide, and a metal selenide. Any suitable metal alloy may be used in the current invention as the hydrogen evolution catalyst. For example, the metal alloy may be Pt-Ni-Co and/or Pt- Fe. Any suitable metal may be used in the metal oxide, a metal sulfide, a metal carbide, a metal nitride, a metal phosphide, and a metal selenide. For example, the metal may be one or more of the group selected from Cu and, more particularly, Co, Ni, Mo and W.
As will be appreciated, the generation of and accumulation of hydrogen in the cathode compartment and in the second tank is not desirable. To reduce issues (e.g. safety and pressure issues), the second tank may be fluidly connected to a hydrogen storage tank, which may collect the hydrogen gas from the second tank (e.g. by the hydrogen rising to the top of the second tank and being pumped or otherwise fed into the storage tank).
The method disclosed herein is agnostic to the type of active material used - in that it may come from a cathodic active material or an anodic active material. The anodic active material may come from a depleted (retired) battery. Any form of the anodic active material may be used. For example, the anodic active material may still be attached to an anode electrode of a dismantled sodium- or lithium-ion battery or is provided free from the anode electrode. Any suitable material may be used as the anodic active material. For example, the anodic active material may be selected from one or more of Li4Ti50i2, graphite, silicon, hard carbon. It will be appreciated that the graphite, silicon, and hard carbon active materials may be impregnated with sodium or, more particularly, lithium following use in a battery.
The process for recovering anodic active material is analogous to the process described hereinbefore for the recovery of cathodic active materials. While the process described herein make use of only a cathodic or anodic active materials separately, it will be appreciated that the same process as described above may be run for a combination of the cathodic and anodic active materials.
In particular embodiments mentioned herein, the active material may be a cathodic active material of a dismantled lithium- or sodium-ion battery.
The general process described above makes use of a flow cell-type arrangement, one embodiment of which is depicted in FIG. 1. It will be appreciated that the general design depicted in this figure is applicable to both cathode and anode active material recovery processes. While the illustration uses a lithium active material, it will be appreciated that a sodium active material may be used instead.
The recycling apparatus 100 comprises a redox targeting-based electrolytic flow cell 101 integrated with a H2 storage tank 115. The redox targeting-based electrolytic flow cell 101 includes a cathodic cell compartment 102 comprising a catholyte tank 110, having a cathode 111, and a cathodic tank 112 comprising water (initially and then aqueous LiOH as the reaction proceeds) 113 and a HER catalyst, where the catholyte tank and the cathodic tank are fluidly connected to one another by a fluid pathway 114. The cathodic tank 112 may also be connected to a hydrogen gas storage tank 115 by a suitable fluid pathway 116. The anodic cell compartment 103 includes an anolyte tank 120, having an anode 121 , and an anodic tank 122 comprising an active material (e.g. LixFePCU) 123 and a redox mediator (e.g. [Fe(CN)6]37 Fe(CN)6]4 ) in aqueous media, where the anolyte tank and the anodic tank are fluidly connected to one another by a fluid pathway 124. A cation-exchange membrane 130 is disposed between the catholyte 110 and anolyte 120 tanks, which allows cations to move from the anolyte tank to the catholyte tank 110. A current collector is also attached to the catholyte and anolyte tanks. It will be appreciated that the aqueous media in the respective cathodic and anodic sides can circulate through the respective fluid pathways to allow the reaction to occur.
Upon operation, for instance, the redox mediator (e.g. [Fe(CN)6]3 ) oxidizes the spent cathode material 123, in this example LixFePC , 0<x<1, and extracts lithium ions from the LixFePC to form FePO4 as a solid and the salt [Fe(CN)e]47Li+, which is soluble in water. Simultaneously, the electrolyte containing [Fe(CN)6]4’ and Li+ circulates back to the anodic cell compartment 120 for the electrochemical reactions. [Fe(CN)e]4’ is oxidized on the anode 121 coupled with a H2O reduction process (HER) to produce H2 and OH’ on the cathode 111. Meanwhile, lithium ions migrate through the cation-exchange membrane 130 to the cathodic compartment 110 and forms LiOH solution. During the electrochemical process, the redox mediator [Fe(CN)e]3' is regenerated on the anode 121 for a second leaching round, while H2 is continuously produced on the cathode 111 with the assistance of HER electrocatalyst. The hydrogen is then passed into the cathodic tank 112, where it is allowed to bubble to the top of said tank for collection and transfer to the hydrogen storage tank.
An analogous process may be used for any active material derived from a cathode or anode active material, which may be lithium- or sodium-ion based.
Further aspects and embodiments of the invention are provided in the following non-limiting examples.
Examples
Example 1
High-throughput electrolytic flow cell
Based on the “redox-targeting concept”, a novel high-throughput electrolytic flow cell to continuously break down the spent battery materials into valuable chemicals at ambient conditions, without consuming additional chemicals, was developed.
The working principle of the oxidative redox targeting-based strategy for spent LFP material recycling coupled with HER process is illustrated in FIG. 1. The recycling setup 100 comprises a redox targeting-based electrolytic flow cell 101 integrated with a H2 storage tank 115. As shown in FIG. 1 , there is a recycling setup 100 that includes a cathodic cell compartment 102 comprising a catholyte tank 110, having a cathode 111, and a cathodic tank 112 comprising LiOH 113, where the catholyte tank and the cathodic tank are fluidly connected to one another by a fluid pathway 114. The cathodic tank 112 may also include a hydrogen gas storage tank 115 that is connected by a suitable fluid pathway 116 to the cathodic tank 112. The recycling setup 100 also includes an anodic cell compartment 103 comprising an anolyte tank 120, having an anode 121, and an anodic tank 122 comprising LixFePO4 123, where the anolyte tank and the anodic tank are fluidly connected to one another by a fluid pathway 124. A cationexchange membrane 130 is disposed between the catholyte 110 and anolyte 120 tanks, which allows cations to move from the anolyte tank to the catholyte tank. A current collector is also attached to the catholyte and anolyte tank. Upon operation, for instance, the redox mediator [Fe(CN)6]3’ oxidizes the spent cathode material LixFePC , 0<x<1 , and extract Li+ from LixFePC>4 to form FePC solid and [Fe(CN)e]4' /Li+ solution. Simultaneously, the electrolyte containing [Fe(CN)6]4- and Li+ circulates back to the anodic cell compartment for the electrochemical reactions. [Fe(CN)s]4' is oxidized on the anode coupled with a H2O reduction process (HER) to produce H2 and OH' on the cathode. Meanwhile, Li+ migrates through a cation-exchange membrane to the cathodic cell compartment and forms LiOH solution. During the electrochemical process, the redox mediator [Fe(CN)e]3' is regenerated on the anode for a second leaching round, while H2 is continuously produced on the cathode with the assistance of HER electrocatalyst.
The spent LixFePC powder (black mass) consists of conductive agent and binder. 2 g of black mass was immersed into 50 mL of 0.4 M Li4Fe(CN)6 solution in the anodic tank. 50 mL of 0.1 M LiOH was used as the catholyte and HER electrocatalyst (such as Pt, metal alloys, metal oxides, metal sulfides, metal phosphides, or metal selenides) modified carbon felt was used as cathode. Both catholyte and anolyte were pumped flowing through the cell and tanks. The generated H2 was collected from the cathodic tank and stored into a H2 storage tank. The electric current density was kept at 100 mA/cm2, and voltage changes on the cell were monitored by an Arbin battery testing system.
Example 2
Oxidative leaching
The oxidative leaching process was investigated in the system described in Example 1.
Results and discussion
As shown in FIG. 2a, the voltage was maintained at around 1.8 V and stopped at a cut-off voltage of 2.3 V at the end of the electrolytic process. A leaching efficiency of around 97% based on the charge capacity was calculated. After reaction, the black mass was extracted from anolyte and dried. The XRD patterns (FIG. 2b) indicate that all the indexed peaks of pristine olivine LiFePCU vanished after leaching process, instead of the new pattern consistent with that of FePO4. Meanwhile, the catholyte was collected and dried in an oven. White powder of LiOH was obtained after drying overnight. The quantity was nearly consistent with the charge capacity of the cell. With suitable redox mediators, similar process can be implemented to recycle batteries with LiCoO2, LiNii/sMni/3Coi/3O2 and other cathode materials.

Claims

Claims
1. A method of recovering a valuable element from an active material of a lithium- or sodium-ion battery, respectively, the method comprising:
(a) providing an active material comprising lithium or sodium ions;
(b) adding the active material to a redox solution that comprises a solvent and a redox mediator to form a redox solution comprising lithium or sodium ions in a first tank;
(c) moving the redox solution from the first tank to a redox flow cell comprising a cathode compartment, having a cathode electrode, and an anode compartment, having an anode electrode, separated by an ion selective membrane, where the cathode electrode and anode electrode are attached to a power supply and the redox solution is subjected to an electrochemical reaction on the anode electrode, where the electrochemical reaction on the anode: regenerates the redox mediator, which is then returned to the first tank and reacts with the active material; and enables transport of the lithium or sodium ions through the ion selective membrane into the cathode compartment, which comprises an aqueous catholyte solution that is obtained from a second tank comprising said aqueous catholyte solution;
(d) capturing the lithium or sodium ions and producing hydrogen in the cathode compartment through an electrochemical reaction on the cathode electrode that produces LiOH or NaOH and hydrogen gas and transferring the resulting aqueous LiOH or NaOH and hydrogen gas in the resulting catholyte solution to a second tank, wherein: steps (c) and (d) can be repeated until the active material is consumed; the aqueous catholyte solution comprises a hydrogen evolution catalyst to facilitate the production of LiOH or NaOH and hydrogen gas; and the valuable element is selected from one or more of the group consisting of Al, Cu, Co, Ni, Fe, Mn, V, Na and Li.
2. The method according to Claim 1 , wherein the active material is a cathodic and/or anodic active material.
3. The method according to Claim 2, wherein the cathodic active material is still attached to a cathode electrode of a dismantled lithium- or sodium-ion battery or is provided free from the cathode electrode.
4. The method according to Claim 2 or Claim 3, wherein the cathodic active material is selected from one or more of NaFePCU, NaCoCh, NaV2(PC>4)3, more particularly, LixFePCU, LLNiaCofcAIcC , LixNiuCovMnwO2, l_ixCoO2, LixMn2O4, and LixNio 5Mn1.5O4, where 0 <x< 1 , a + b + c = 1 , and u + v + w - 1 , optionally wherein the cathodic active material is LixFePO4.
5. The method according to any one of the preceding claims, wherein the hydrogen evolution catalyst is selected from one or more of the group consisting of Pt, a metal alloy, a metal oxide, a metal sulfide, a metal carbide, a metal nitride, a metal phosphide, and a metal selenide, where the metal in each of the oxide, sulfide, carbide, nitride, phosphide and selenide is selected from one or more of the group is selected from Ni, Co, Cu, Mo and W.
6. The method according to any one of the preceding claims, wherein the redox mediator is selected from one or more of the group consisting of ferricyanide (M3Fe(CN)6), ferrocyanide (M4Fe(CN)6), ferrocene (CioH Fe), hydroquinonesulfonic acid and derivatives thereof, iodide (Ml) and bromide (MBr), where in each case M is independently selected from the group consisting of Li, Na, K and NH4.
7. The method according to Claim 6, wherein the redox mediator is selected from one or more of the group consisting of ferricyanide (M3Fe(CN)e), ferrocyanide (M4Fe(CN)6), iodide (Ml), and bromide (MBr), where in each case M is independently selected from the group consisting of Li, Na, K and NH4, optionally wherein the derivative of ferrocene is di(ethylsulfonic lithium) ferrocene (Ci4HiSFeS2O6Li2)
8. The method according to Claim 6 or Claim 7, wherein the total concentration of the redox mediator present in the solvent is from 0.05 M to 3 M, such as from 0.2 M to 0.5 M, such as about 0.4 M.
9. The method according to any one of the preceding claims, wherein the second tank is fluidly connected to a hydrogen storage tank, which collects the hydrogen gas from the second tank.
10. The method according to any one of the preceding claims, wherein the solvent is pure water.
11. The method according to any one of the preceding claims, wherein the aqueous catholyte solution is initially selected from one of water or water comprising CO2.
12. The method according to any one of the preceding claims, wherein after steps (b) and (c) have been completed, and: (i) the active material is a lithium-ion battery material, then the aqueous catholyte solution is an aqueous LiOH solution, or an aqueous LiOH solution comprising CO2 with U2CO3 precipitate, optionally wherein the aqueous catholyte solution is an aqueous LiOH solution; or
(ii) the active material is a sodium-ion battery material, then the aqueous catholyte solution is an aqueous NaOH solution.
13. The method according to any one of Claims 2 to 12, wherein the anodic active material is still attached to an anode electrode of a dismantled lithium-ion battery or is provided free from the anode electrode.
14. The method according to any one of Claims 2 to 13, wherein the anodic active material is selected from one or more of Li4Ti50i2, graphite, silicon, hard carbon.
15. The method according to any one of the preceding claims, wherein the active material is a cathodic active material of a dismantled lithium- or sodium-ion battery.
PCT/SG2022/050836 2021-11-18 2022-11-18 A recycling method for active materials in lithium or sodium batteries WO2023091087A2 (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
SG10202112820U 2021-11-18
SG10202112820U 2021-11-18

Publications (2)

Publication Number Publication Date
WO2023091087A2 true WO2023091087A2 (en) 2023-05-25
WO2023091087A3 WO2023091087A3 (en) 2023-07-13

Family

ID=86397980

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/SG2022/050836 WO2023091087A2 (en) 2021-11-18 2022-11-18 A recycling method for active materials in lithium or sodium batteries

Country Status (1)

Country Link
WO (1) WO2023091087A2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2023244779A1 (en) * 2022-06-16 2023-12-21 The Regents Of The University Of California Electrochemical extraction of target cations from complex resources

Family Cites Families (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20210078486A (en) * 2018-10-26 2021-06-28 내셔널 유니버시티 오브 싱가포르 Lithium Ion Battery Material Recycling Method
US11715849B2 (en) * 2019-11-01 2023-08-01 Alliance For Sustainable Energy, Llc Methods for cathode recycling of end-of-life lithium batteries

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2023244779A1 (en) * 2022-06-16 2023-12-21 The Regents Of The University Of California Electrochemical extraction of target cations from complex resources

Also Published As

Publication number Publication date
WO2023091087A3 (en) 2023-07-13

Similar Documents

Publication Publication Date Title
CN112996931B (en) Lithium ion battery material recovery method
Yu et al. A redox targeting-based material recycling strategy for spent lithium ion batteries
Du et al. Progresses in sustainable recycling technology of spent lithium‐ion batteries
CN111270072B (en) Recycling method of waste lithium iron phosphate battery positive electrode material
US20220223932A1 (en) Methods of recovering active materials from rechargeable batteries, and related apparatuses
CN104112882A (en) Method for electrochemically extracting lithium from positive electrode material of lithium ion battery
CN106785168A (en) Call Provision, iron, the method for lithium are leached in a kind of failure cobalt acid lithium and lithium iron phosphate positive material
WO2023091087A2 (en) A recycling method for active materials in lithium or sodium batteries
CN115867681A (en) Method for recovering active metal of lithium secondary battery
CN111304679A (en) Device and method for preparing high-purity lithium hexafluorophosphate through electrolysis by electrochemical ion extraction method
Shi et al. Li2CO3 recovery through a carbon-negative electrodialysis of lithium-ion battery leachates
Zhen et al. Redox flow battery
CN112591806A (en) Method for recovering and regenerating anode active material of waste lithium ion battery
Wang et al. Analysis of Direct Recycling Methods for Retired Lithium-ion Batteries from Electric Vehicles
US20210242514A1 (en) Systems and methods for recycling electrodes
CN110289464B (en) Water-based air battery, method for separating and recovering lithium and cobalt elements in lithium cobaltate by using water-based air battery and application of water-based air battery
CN113078382B (en) Lithium battery recovery processing method
KR101069807B1 (en) Method of electro-reduction extraction of cobalt from cathodic active material of lithium battery
Qiu et al. Challenges and perspectives towards direct regeneration of spent LiFePO4 cathode
US20240055680A1 (en) Methods of recovering lithium from a lithium-containing material, and related systems
CN113299937B (en) Method for recycling waste zinc-manganese dry batteries and directly using waste zinc-manganese dry batteries in rechargeable zinc-manganese batteries
KR20190006375A (en) Redox Flow Battery using Sodium-Biphenyl
WO2023229533A1 (en) Spent battery materials recycling method
Gan et al. Continuous Flow Electrochemical Synthesis of Olivine‐Structured NaFePO4 Cathode Material for Sodium‐Ion Batteries from Recycle LiFePO4
KR20240006124A (en) Electrochemical lithium recovery system