Recovery of Metals from Materials Containing Lithium and Iron
20240313285 ยท 2024-09-19
Inventors
Cpc classification
H01M4/5825
ELECTRICITY
C22B7/005
CHEMISTRY; METALLURGY
C22B3/1616
CHEMISTRY; METALLURGY
Y02P10/20
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
C22B3/22
CHEMISTRY; METALLURGY
Y02W30/84
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
International classification
C22B3/22
CHEMISTRY; METALLURGY
C22B7/00
CHEMISTRY; METALLURGY
Abstract
Methods for recycling lithium and iron containing material, such as batteries, include selectively leaching lithium from the material by disposing the material in a powder form in a solution comprising formic acid and hydrogen peroxide, filtering the solution to obtain a first leach liquor comprising lithium and a residue comprising iron phosphate and carbon, subjecting the first leach liquor to a first precipitation to remove residual iron from the leach liquor and obtain a second leach liquor, and subjecting the second leach liquor to a second precipitation, wherein lithium is precipitated and a third leach liquor is obtained. The third leach liquor may be subjected to a third precipitation using trisodium phosphate or sodium carbonate. The material may be a battery cathode, such as a lithium iron phosphate battery cathode.
Claims
1. A method for recovering one or more metals from a lithium and iron containing material, comprising: selectively leaching lithium from the material by disposing the material in a powder form in a mixture comprising formic acid at a concentration equal to or less than about 3.0 mol/L and an oxidizing reagent at a concentration that maintains an oxidative potential in the mixture; filtering the mixture to obtain a first leach liquor comprising lithium and a residue comprising iron phosphate and carbon; subjecting the first leach liquor to a first precipitation at a first selected pH and a first selected temperature to remove residual iron from the leach liquor and obtain a second leach liquor; subjecting the second leach liquor to a second precipitation at a second selected pH and a second selected temperature, wherein lithium is precipitated, and a third leach liquor is obtained.
2. The method of claim 1, wherein the material also contains one or more other metals selected from one or more base metals, cobalt, nickel, and manganese; and the one or more other metals are precipitated from the first leach liquor during the first precipitation.
3. The method of claim 1, comprising subjecting the third leach liquor to a third precipitation at a third selected pH and a third selected temperature, wherein lithium is precipitated.
4. The method of claim 1, wherein the first precipitation is carried out at a pH of about 9.0 and a temperature of about 60? C., wherein iron(III) hydroxide is precipitated.
5. The method of claim 1, wherein at least one of the second selected pH and the second selected temperature is higher than the first selected pH and the first selected temperature.
6. The method of claim 1, wherein the second precipitation is carried out at a pH of about 11.0 and a temperature of about 100? C.
7. The method of claim 1, wherein at least one of the third selected pH and the third selected temperature is higher than the second selected pH and the second selected temperature.
8. The method of claim 3, wherein the third precipitation is carried out at a pH of about 12.5 and a temperature of about 100? C.
9. The method of claim 3, comprising adding a trisodium phosphate solution to the third leach liquor for the third precipitation.
10. The method of claim 9, comprising saturating the third leach liquor with trisodium phosphate.
11. The method of claim 9, comprising: in situ precipitation of lithium phosphate at pH of about 11 and temperature of about 100? C.; and precipitation of lithium phosphate at pH of about 12.5 and temperature of about 100? C. using the trisodium phosphate solution.
12. The method of claim 3, comprising adding a sodium carbonate solution to the third leach liquor for the third precipitation.
13. The method of claim 12, comprising saturating the third leach liquor with sodium carbonate.
14. The method of claim 12, comprising: in situ precipitation of lithium phosphate at pH of about 11 and temperature of about 100? C.; and precipitation of lithium carbonate at pH of about 11 and temperature of about 100? C. using the sodium carbonate solution.
15. The method of claim 1, wherein the concentration of formic acid is equal to or less than about 1.5 mol/L.
16. The method of claim 1, wherein the oxidizing reagent comprises at least one of hydrogen peroxide. ozone, oxygen, oxygen enriched gas, and sodium persulfate.
17. The method of claim 1, wherein the oxidizing reagent comprises hydrogen peroxide.
18. The method of claim 17, wherein the concentration of hydrogen peroxide is about 5 to about 10%.
19. The method of claim 1, wherein the mixture comprises up to about 65% pulp density of the material.
20. The method of claim 1, wherein the material is a black mass.
21. The method of claim 1, wherein the material is a black mass of a battery containing lithium.
22. The method of claim 1, wherein the material comprises LFP containing material derived from a LFP battery.
Description
BRIEF DESCRIPTION OF THE DRAWINGS
[0043] For a greater understanding of the invention, and to show more clearly how it may be carried into effect, embodiments will be described, by way of example, with reference to the accompanying drawings, wherein:
[0044]
[0045]
[0046]
[0047]
[0048]
[0049]
[0050]
[0051]
DETAILED DESCRIPTION OF EMBODIMENTS
[0052] According to a broad aspect, the invention provides methods for efficient, economically viable, and environmentally friendly recovering of metals, particularly lithium and iron, from materials such as but not limited to batteries. The methods are based on selective leaching of lithium from the materials.
[0053] Embodiments described herein provide sustainable methods for efficient, economically viable, and environmentally friendly recycling of material containing lithium and iron. As a non-limiting example, such material may be derived from lithium iron phosphate (LFP) batteries or black mass bearing LFP. The material may be in the form of a black mass, typically a powder or granulated particles prepared by shredding, grinding, pulverizing, etc., items containing lithium and iron, and, depending on the items, other metals. In the case of LFP batteries, the material may be black mass prepared from the battery cathodes, and other metals such as, for example, one or more base metals (e.g., copper, lead, aluminum, zinc), cobalt, nickel, and manganese may also be present. According to embodiments, metals may be recovered by selective leaching of lithium from the material with formic acid, and two or more precipitation steps in which iron and other metals are precipitated in a first precipitation at a selected pH.
[0054] Whereas formic acid has been proposed for the recycling of spent lithium-ion batteries (LIBs) based on LiCoO.sub.2 (LCO) (Zheng at al., 2018) and LiNi.sub.1/3Co.sub.1/3Mn.sub.1/3O.sub.2 (Gao et al., 2017), there are drawbacks of those approaches including non-selective leaching of lithium wherein one or more other metals are present in the leachate (e.g., cobalt, nickel, manganese), high formic acid consumption, low solid to liquid ratio, the need for a high reaction temperature, incomplete recovery of lithium due to co-precipitation with the one or more other metals, and overall high cost. No previous work has explored use of formic acid for selective leaching of lithium from spent LFP batteries.
[0055] Embodiments described herein provide selective leaching of lithium from LFP containing materials or black mass comprising LFP material with low formic acid consumption, high solid to liquid ratio, a low reaction temperature, and substantially complete recovery of lithium without co-precipitation of iron or other metals. Consequently, the methods using formic acid are efficient, economically viable, and environmentally friendly.
[0056] According to certain embodiments, LFP containing materials or black mass material is treated with formic acid as a leaching reagent with hydrogen peroxide or other reagent as an oxidant under controlled parameters of formic acid and hydrogen peroxide concentration, pulp density, temperature, and duration. For example, formic acid may be used at a concentration up to about 1.5 mol/L, or about 2.0 mol/L, or about 3.0 mol/L, hydrogen peroxide may be used at a concentration up to about 10%. Hydrogen peroxide improves the leaching efficiency and minimize impurities including iron to enhance selectivity of lithium leaching. Other reagents may be used as oxidants, including gases such as ozone, oxygen, and oxygen enriched gas at a flow rate of about 0.1 to 1 L/min per liter of slurry, i.e., a flow rate that maintains an oxidative potential in the mixture, sodium persulfate (Na.sub.2S.sub.2O.sub.8) at a concentration up to about 10%, or other strong oxidants. Under certain conditions the hydrogen peroxide or other reagent may act as a reducing agent. For example, hydrogen peroxide acts as an oxidant in oxidizing iron (II) to iron (III), whereas it acts to reduce cobalt (III) to cobalt (II). The LFP containing materials or black mass may be added at a pulp density in which the mixture or slurry remains suitably liquid and mixable (i.e., preferably not a paste or not saturated with cathode material), e.g., up to about 60%, or about 65% pulp density. The process may be carried out at a temperature range of about 30-70? C., or about 5-100? C., or greater, and for duration ranges of at least about 10 min, wherein a pregnant leach liquor is produced that includes lithium. Depending on the material (LFP containing material, black mass) being processed, the pregnant leach liquor may also include trace amounts of iron, and other metals that may be present in the material (e.g., one or more base metals, cobalt, nickel, and manganese), and a residue may be produced that includes iron phosphate and carbon, as shown in the embodiments of
[0057] In one embodiment, leaching conditions that produce favourable results, that is, selective leaching of lithium, include formic acid at a concentration equal to or less than about 1.5 mol/L, e.g., about 1.0 to 1.5 mol/L, or 1.0 to 1.2 mol/L, hydrogen peroxide at a concentration of about 5%, a pulp density of about 10-20%, and temperature of about 30-50? C.
[0058] In another embodiment, leaching conditions may include formic acid at a concentration of about 1.0 to 1.2 mol/L, hydrogen peroxide at a concentration of about 5%, a pulp density of about 10%, and temperature of about 30? C.
[0059] In other embodiments, leaching conditions may include formic acid at a concentration of about 0.5 to 1.5 mol/L, hydrogen peroxide at a concentration of about 0.2 to 10%, a pulp density of about 10 to 40%, and temperature of about 30 to 50? C.
[0060] In implementations where the material includes lithium and other metals, such as, for example, one or more of the above-mentioned one or more base metals, cobalt, nickel, and manganese, the pregnant leach liquor may be subjected to an initial precipitation carried out at pH of about 2 to about 10.5, or about 2 to about 9, and temperature of about 50? C. to about 70? C. Under these conditions there is little or no precipitation of lithium, and substantially complete precipitation of any of the one or more base metals, cobalt, nickel, and manganese, as well as residual iron, if present, as shown in the embodiments of
[0061] According to embodiments, precipitation of lithium as Li.sub.3PO.sub.4 or Li.sub.2CO.sub.3 from the pregnant leach liquor may be carried out in one or more steps under conditions of elevated pH, e.g., pH 10-13, and elevated temperature, e.g., up to about 100? C. In some embodiments, precipitation of Li.sub.3PO.sub.4 or Li.sub.2CO.sub.3 is carried out in two steps, e.g., firstly, in situ precipitation of Li.sub.3PO.sub.4 at pH of about 11 and temperature of about 100? C., and secondly at an elevated pH of about 12.5 at about 100? C. using a Na.sub.3PO.sub.4 solution, or at pH of about 11 and temperature of about 100? C. using a Na.sub.2CO.sub.3 solution. In some embodiments, the Na.sub.3PO.sub.4 solution or the Na.sub.2CO.sub.3 solution may be added at a high molar ratio (i.e., at excessive amounts, greater than the required stoichiometric amount, e.g., at 1 mol/L or 2 mol/L) or they may be saturated solutions. As non-limiting examples, Na.sub.3PO.sub.4 may be added at a PO.sub.4.sup.2?:Li.sup.+ molar ratio of 1.33:3, and Na.sub.2CO.sub.3 may be added at a Na:Li molar ratio of 1:1. According to embodiments, mass balance may indicate >99.5% recovery of lithium with high purity products.
[0062] Thus, embodiments described herein may include selective leaching with in situ precipitation of Li.sub.3PO.sub.4 in a first step followed by precipitation of remaining lithium as Li.sub.3PO.sub.4 or Li.sub.2CO.sub.3 using a high molar ratio solution or saturated solution of trisodium phosphate or sodium carbonate, respectively. The resulting liquor is rich in sodium and formate ions and, e.g., may be recycled as sodium oxalate to reduce the environmental load.
[0063] As noted above, LFP material subjected to methods for recovering lithium according to the embodiments may be in the form of a black mass. For recovering one or more metals including lithium from an LFP battery, the black mass may be obtained by disassembling a LFP battery to obtain the cathode, removing metal (e.g., aluminum) foil from the cathode, and grinding, pulverizing, etc. the cathode to a powdered, particulate, or granular, etc. form (hereinafter referred to as powder). Although methods are provided herein for obtaining LFP battery cathode powder, the powder (i.e., black mass) may be procured from facilities and operations that process spent LFP batteries.
[0064] Embodiments significantly improve the recovery of pure metal products from LFP battery cathodes, with economic and environmental benefits through recyclability and recirculation of the reagents used. The methods may be scaled up and applied to industrial processes.
[0065] The invention will be further described by way of the following non-limiting Examples.
EXAMPLES
Materials
[0066] Spent LFP batteries with LiFePO.sub.4/C as cathode material were procured from a local industry. Formic acid (HCOOH), hydrogen peroxide (50 wt % H.sub.2O.sub.2), sodium hydroxide (NaOH), trisodium phosphate (Na.sub.3PO.sub.4.Math.12H.sub.2O), and sodium carbonate (Na.sub.2CO.sub.3) were purchased from Sigma Aldrich, USA. Deionized water was used to prepare solutions. Sodium hydroxide solution was used to adjust the pH of leach liquor.
Pre-Treatment of Spent LFP Batteries
[0067] Spent LFP batteries were initially dipped in 1.0 mol/L sodium chloride solution for complete discharging to avoid short circuiting. Afterwards, batteries were dismantled in order to separate anode (coated on copper foil) and cathode (coated on aluminum foil). The cathode material was separated from aluminum foil by maintaining cathodes in a solution of 1.5% sodium hydroxide for 0.5 h under ultrasound using a VWR? Ultrasonic Cleaner (VWR International, Mississauga, Ontario) with 10% (w/v) pulp density. The cathode material was then washed with deionized water and dried in an oven at 60? C. for 48 h. The dried cathode material was crushed and sieved through 74 ?m sieve (200 US Mesh) to obtain a fine powder (i.e., black mass). A definite amount of cathode powder was digested in a definite volume of aqua regia and the resulting solution was analyzed for elements concentration using inductively coupled plasma-optical emission spectrometry (ICP-OES). The major elemental contents (wt %) were found to be 32.50% Fe, 4.35% Li, and 18.05% P. For black mass derived from LFP battery cathodes, other metals such as cobalt, nickel, and manganese may be present at about 5 wt % or less.
General Procedure
[0068]
[0069] All leaching experiments were performed in a 500 mL round bottom flask over a magnetic stirrer (500 rpm speed) with a temperature controlling probe using formic acid as a lixiviant and hydrogen peroxide as an oxidant for the desired time period. The flask was fitted with a condenser to avoid volume loss via evaporation at high temperatures. Once the reaction was complete, the flask was immediately removed and the contents subjected to filtration. The metals content was then checked in the liquor. The residues left were washed with deionized water and then placed in an oven for drying at 60? C. for 48 h. After analyzing the metals concentration, the leaching efficiency (LE) of each metal was calculated using the following formula
where C, V, m, and w % are the metal concentrations in leach liquor, volume of leach liquor, mass of cathode powder, and mass fraction of metal in cathode powder, respectively. All experiments were done in triplicate and the standard deviation was found to be ?5% throughout the study.
Characterization Techniques
[0070] The concentration of elements in the digested and leach liquors were analyzed using microwave plasma atomic emission spectroscopy (MP-AES, Agilent 4200) and ICP-OES techniques. The spent cathode powder, residue after leaching, and recovered lithium products were characterized through powder X-ray diffraction (XRD) using X'Pert Pro Philips powder diffractometer employing Cu-Ku radiation (?=1.54 ?). Surface morphologies were also studied with a field emission scanning electron microscope (FE-SEM, Quanta 650).
Effect of Formic Acid Concentration
[0071] The formic acid concentration was varied from 0.25 to 1.25 mol/L to observe its effect on the selective leaching of lithium. The other experimental conditions, i.e., pulp density (10% w/v), H.sub.2O.sub.2 concentration (5% v/v), temperature (T=50? C.), and reaction time (t=1 h) were kept constant throughout the experiment. As shown in
Effect of Hydrogen Peroxide Concentration
[0072] The amount of hydrogen peroxide added initially to the reaction system significantly affected leaching efficiency. It is clear from
Effect of Pulp Density
[0073]
Effect of Temperature
[0074] The reaction temperature was varied from 30? C. to 70? C. using 1.0 mol/L HCOOH, 5% H.sub.2O.sub.2, and 10% pulp density for one hour to observe change in leaching efficiency of lithium and iron.
Effect of Reaction Time
[0075] A variation in reaction time from 2 min to 70 min at optimized leaching conditions, i.e., 1.0 mol/L HCOOH, 5% H.sub.2O.sub.2, 10% pulp density and 50? C. temperature was done to study time effect. As shown in
Recovery of Lithium from Pregnant Leach Liquor
[0076] The above-noted optimized conditions for selective leaching of lithium were used to produce bulk amounts of leach liquor for recovery of lithium products. Those leaching conditions, i.e., 10% pulp density, 1.0 mol/L HCOOH with 5% H.sub.2O.sub.2, at 30? C. for 0.5 h were used to produce 500 mL of leach liquor. It is to be understood that these are suggested optimized conditions, as it will be readily apparent to those of ordinary skill that one or more of the parameters may be varied and the same or better results obtained. Accordingly, the suggested optimized conditions are an embodiment and the invention is not limited thereto.
[0077] The concentrations of Li, Fe, and P were found to be 3950 mg/L, 101 mg/L and 381 mg/L, respectively, in the pregnant leach liquor. Iron was precipitated as iron hydroxide at pH=9.0 and 60? C. temperature. The leach liquor was filtered and analyzed for its metal contents. The pH was raised to 11 using NaOH solution and lithium was in situ precipitated as Li.sub.3PO.sub.4 at 100? C. by the leached phosphate present in the reaction system. White precipitates thus obtained were filtered, washed with hot deionized water and dried in an oven at 80? C. for 24 h. The leach liquor remaining after filtration of precipitates was subjected to analysis and lithium concentration was found to be 3704 mg/L. The filtrate remaining was adjusted to pH 12.5 by adding NaOH solution. Lithium precipitation was accelerated by adding a small amount of solid Na.sub.3PO.sub.4 followed by 1.0 mol/L Na.sub.3PO.sub.4 solution and keeping PO.sub.4.sup.3?/Li.sup.+ molar ratio 1.33:3 (Song et al., 2018) with continuous stirring at 100? C. for satisfactory precipitation results (
TABLE-US-00001 TABLE 1 Concentrations of Li and Fe at different stages of the process Stage of Process Li (mg/L) Fe (mg/L) Pregnant leach liquor 3950 101 After Fe precipitation 3944 After in situ Li.sub.3PO.sub.4 precipitation 3704 After Li.sub.3PO.sub.4 precipitation 9
[0078] In another embodiment the leach solution was processed according to the above procedures up to the second precipitation and then saturated Na.sub.2CO.sub.3 was added and the third precipitation was carried out at the pH and temperature used in the second precipitation to obtain lithium carbonate.
Characterization of Recovered Products
[0079] The recovered lithium phosphate and lithium carbonate were characterized using an XRD technique and purity was evaluated using MP-AES analysis of the solution of product in 5% nitric acid.
[0080]
[0081] XRD pattern of in situ precipitated Li.sub.3PO.sub.4 (
FE-SEM Analysis
[0082] The morphology of recovered products was investigated using FE-SEM technique and is presented in
Reagent Consumption
[0083] The reagent consumption, that is, the minimum amounts of the reagents required to recover substantially 100% of the lithium from LFP battery cathodes, are given in Table 2.
TABLE-US-00002 TABLE 2 Reagent consumption per mole of lithium recovered Amount Reagent (moles) Lixiviant (1.0 mol/L formic acid) 1.76 Hydrogen peroxide 50 wt %, (5% used for reaction) 1.55 Na.sub.3PO.sub.412H.sub.2O (1.0 mol/L solution) 0.45 Na.sub.2CO.sub.3 saturated solution 0.43
However, for optimal results excessive (i.e., greater than the required stoichiometric amount) or saturated Na.sub.2CO.sub.3 solution may be used to obtain lithium carbonate from leach liquor.
Further Embodiments
[0084] It is expected that methods described herein may be adapted for recovering other metals, for example platinum groups metals, from materials such as printed circuit boards and automobile catalysts, and recovering copper from low-grade copper ore, etc.
EQUIVALENTS
[0085] It will be appreciated that modifications may be made to the embodiments described herein without departing from the scope of the invention. Accordingly, the invention should not be limited by the specific embodiments set forth but should be given the broadest interpretation consistent with the teachings of the description as a whole.
REFERENCES
[0086] Bian, D.; Sun, Y.; Li, S.; Tian, Y.; Yang, Z.; Fan, X.; Zhang, W. A Novel Process to Recycle Spent LiFePO.sub.4 for Synthesizing LiFePO.sub.4/C Hierarchical Microflowers. Electrochim. Acta 2016, 190, 134-140. https://doi.org/10.1016/j.electacta.2015.12.114. [0087] Byeon, P.; Bae, H. B.; Chung, H. S.; Lee, S. G.; Kim, J. G.; Lee, H. J.; Choi, J. W.; Chung, S. Y. Atomic-Scale Observation of LiFePO.sub.4 and LiCoO.sub.2 Dissolution Behavior in Aqueous Solutions. Adv. Funct. Mater. 2018, 28 (45), 1804564. [0088] Cai, G.; Fung, K. Y.; Ng, K. M.; Wibowo, C. Process Development for the Recycle of Spent Lithium Ion Batteries by Chemical Precipitation. Ind. Eng. Chem. Res. 2014, 53 (47), 18245-18259. https://doi.org/10.1021/ie5025326. [0089] Gao, W., et al. Lithium Carbonate Recovery from Cathode Scrap of Spent Lithium-Ion Battery: A Closed-Loop Process. Environ. Sci. Technol. 2017, 51, 1662-1669. DOI: 10.1021/acs.est.6b03320.(14) [0090] Goodenough, J. B.; Kim, Y. Challenges for Rechargeable Li Batteries. Chem. Mater. 2010, 22 (3), 587-603. https://doi.org/10.1021/cm901452z. [0091] He, K.; Zhang, Z. Y.; Zhang, F. S. A Green Process for Phosphorus Recovery from Spent LiFePO.sub.4 Batteries by Transformation of Delithiated LiFePO.sub.4 Crystal into NaFeS.sub.2. J. Hazard. Mater. 2020, 395, 122614. https://doi.org/10.1016/j.jhazmat.2020.122614. [0092] Jiang, L. G.; Liang, B.; Xue, Q.; Yin, C. W. Characterization of Phosphorus Leaching from Phosphate Waste Rock in the Xiangxi River Watershed, Three Gorges Reservoir, China. Chemosphere 2016, 150, 130-138. https://doi.org/10.1016/j.chemosphere.2016.02.008. [0093] Kavanagh, L.; Keohane, J.; Cabellos, G. G.; Lloyd, A.; Cleary, J. Global Lithium Sources-Industrial Use and Future in the Electric Vehicle Industry: A Review. Resources 2018, 7 (3), 1-29. https://doi.org/10.3390/resources7030057. [0094] Li, H.; Xing, S.; Liu, Y.; Li, F.; Guo, H.; Kuang, G. Recovery of Lithium, Iron, and Phosphorus from Spent LiFePO.sub.4 Batteries Using Stoichiometric Sulfuric Acid Leaching System. ACS Sustain. Chem. Eng. 2017, 5 (9), 8017-8024. https://doi.org/10.1021/acssuschemeng.7b01594. [0095] Li, Z.; Liu, D. F.; Xiong, J.; He, L.; Zhao, Z.; Wang, D. Selective Recovery of Lithium and Iron Phosphate/Carbon from Spent Lithium Iron Phosphate Cathode Material by Anionic Membrane Slurry Electrolysis. Waste Manag. 2020, 107, 1-8. https://doi.org/10.1016/j.wasman.2020.03.017. [0096] Shin, E. J.; Kim, S.; Noh, J. K.; Byun, D.; Chung, K. Y.; Kim, H. S.; Cho, B. W. A Green Recycling Process Designed for LiFePO.sub.4 Cathode Materials for Li-Ion Batteries. J. Mater. Chem. A 2015, 3 (21), 11493-11502. https://doi.org/10.1039/c5ta02540k. [0097] Song, Y.; Zhao, Z. Recovery of Lithium from Spent Lithium-Ion Batteries Using Precipitation and Electrodialysis Techniques. Sep. Purif Technol. 2018, 206, 335-342. https://doi.org/10.1016/j.seppur.2018.06.022. [0098] Song, Y. J. Recovery of Lithium as Li.sub.3PO.sub.4 from Waste Water in a LIB Recycling Process. J. Korean Inst. Met. Mater. 2018, 56 (10), 755-762. https://doi.org/10.3365/KJMM.2018.56.10.755. [0099] Yang, Y.; Meng, X.; Cao, H.; Lin, X.; Liu, C.; Sun, Y.; Zhang, Y.; Sun, Z. Selective Recovery of Lithium from Spent Lithium Iron Phosphate Batteries: A Sustainable Process. Green Chem. 2018, 20 (13), 3121-3133. https://doi.org/10.1039/c7gc03376a. [0100] Zheng, Y.; Song, W.; Mo, W. T.; Zhou, L.; Liu, J. W. Lithium Fluoride Recovery from Cathode Material of Spent Lithium-Ion Battery. RSC Adv. 2018, 8 (16), 8990-8998. https://doi.org/10.1039/c8ra00061a.