Lithium ion battery is now popularly used in portable electronic devices and electric vehicles. Since the battery life of electric vehicles is only a few years, a large amount of lithium ion batteries are reaching their end of life. By the end of 2020, 17.7 GWh of lithium ion batteries had reached the end of life, which equals around 20000 tons of cathode materials. It is estimated that this figure will be increased to more than 140 GWh by 2035. In the fabrication of lithium ion batteries, the cost of cathode materials contributes approximately 32.7% of the total cost. Recycling and reusing the cathode materials from spent lithium ion batteries is promising in reducing the cost of lithium ion batteries and mitigate their environmental impacts. However, recent battery recycling efforts offered a low recovery rate of cathode active material while consuming unsustainable energy and metals. By 2021, the recycling rate of the cathode active material is still low at under 5%. Thus, recycling and recovery technologies of cathode active materials are in urgent needs for further lowering the cost of lithium ion batteries, reducing the use of rare-earth metals, and mitigating the environmental impacts.
Current recycling technologies for spent lithium ion batteries are grouped into hydrometallurgy, pyrometallurgy, and direct recycling. Pyrometallurgical recycling smelts the end-of-life battery materials and recovers some of the useful metals in alloy forms through multistep purification and separation processes. The hydrometallurgical process utilizes acid leaching and solvent extraction and recovers lithium as Li2CO3 and other major materials as polymetallic compounds. While direct recycling recovers the capacity, structure, and morphology of spent cathode active materials without destroying the original structure and yields the reusable high-value materials to the battery industries.
Embodiments described herein relate to a direct recycling method to recover battery cathode materials from spent lithium ion batteries and reuse them in the manufacturing of new lithium ion batteries. We designed a novel direct recycling method to recover the structure and capacity of cathode active materials from spent lithium ion batteries without the high-temperature annealing process and can reuse the relithiated active material in the manufacturing of lithium ion batteries. This method only requires one heating process in the air, which consists of a preheating step to activate the materials and a sintering step to relithiate the materials at moderate temperatures. The performance of the recovered and relithiated cathode active materials can be as good as those of pristine materials. The relithiated materials also possess an outstanding rate capability.
In some embodiments, the mixture is preheated to a temperature below the sintering temperature prior sintering.
In some embodiments, the mixture can be preheated at a temperature of about 140° C. to about 160° C. for a first duration of time and sintered at a temperature of about 300° C. to about 350° C. for a second duration of time. The second duration of time can be substantially longer than the first duration of time.
In some embodiments, the relithiated cathode material can be milled after sintering to prevent agglomeration.
In other embodiments, the method can further include separating relithiated cathode material from the mixture.
In some embodiments, the spent lithium cathode material and particulate lithium source are mixed by milling particles of the lithium cathode material and particulate lithium source.
In some embodiments, the particulate lithium source can include a particulate lithium salt, such as LiNO3.
In some embodiments, the spent lithium cathode material is selected from spent LiCoO2 (LCO), LiMn2O4 (LMO), LiFePO4 (LFP), LiNiMnCoO2 (NMC), LiNiCoAlO2 (NCA) or mixtures thereof.
Other embodiments described herein relate to a relithiated cathode material formed by the method 10. The relithiated cathode material can have a specific capacity, cycling performance, and/or rate capability substantially equal to or better than specific capacity, cycling performance, and/or rate capability of pristine cathode material.
In some embodiments, the method 20 can further include preheating the mixture to a temperature below the sintering temperature prior sintering. For example, the mixture can be preheated at a temperature of about 140° C. to about 160° C. for a first duration of time and sintered at a temperature of about 300° C. to about 350° C. for a second duration of time. The second duration of time can be substantially longer than the first duration of time.
In some embodiments, the relithiated cathode material can be milled after sintering to prevent agglomeration.
In some embodiments, the spent lithium cathode material and particulate lithium source are mixed by milling particles of the lithium cathode material and particulate lithium source.
In some embodiments, the spent cathode electrode is separated from spent lithium ion battery by removing the spent cathode electrode from the spent lithium ion battery in an inert atmosphere and soaking the removed spent cathode electrode in a solvent to remove residual electrolyte from the cathode electrode.
In some embodiments, the solvent combined with spent cathode electrode to form the suspension includes N-methyl-2-pyrrolidone.
In some embodiments, the particulate lithium source can include a particulate lithium salt, such as LiNO3.
In some embodiments, the spent lithium cathode material is selected from spent LiCoO2 (LCO), LiMn2O4 (LMO), LiFePO4 (LFP), LiNiMnCoO2 (NMC), LiNiCoAlO2 (NCA) or mixtures thereof.
The final product is the relithiated cathode active materials with fine particles. The electrochemical performance is tested by the Neware battery tester (Neware Ltd, China). The specific capacity, cycling performance are shown in
The cycling performance is tested at a current density of 0.5C, the long-term cycling performance is tested at a current density of 1C and the rate capability is tested at current densities of 0.1C, 0.2C, 0.5C, 1C, 2C, and 5C. The specific capacity of the spent cathode active material is about 30 mAh/g. After the direct recycling process, the specific capacity comes back to 130 mAh/g at 0.5C, which is consistent with the specific capacity of pristine blend cathode of LMO and NMC. Besides, the relithiated materials possess an outstanding rate capability after the direct recycling process. Thus, the direct recycling method proposed in this patent can recover the structure and capacity with one sintering step, and the relithiated cathode active materials can be directly reused in the manufacturing of new lithium ion batteries.
The application of this method can be extended to most of the dominant cathode materials, including LCO (LiCoO2), LMO (LiMn2O4), LFP (LiFePO4), high nickel NMC (LiNiMnCoO2), and NCA (LiNiCoAlO2). To enhance the stability of long-term cycling performance of relithiated cathode materials, short annealing and tempering processes will be added to the relithiation processes. A coating process is also considered a potential process to eliminate the side reaction of relithiated cathode materials with liquid electrolytes during charging and discharging. The coating materials can be Al2O3, TiO2, Zn, Al pristine NMC (LiNiMnCoO2), etc.
Particle size is also a significant parameter that affect the electrochemical performance of recycled cathode active materials. Therefore, high-speed ball milling and grinding processes will also be integrated in the recycling processes to control the particle size and avoid the agglomerate caused by the sintering process.
From the above description of the invention, those skilled in the art will perceive improvements, changes and modifications. Such improvements, changes and modifications within the skill of the art are intended to be covered by the appended claims. All references, publications, and patents cited in the present application are herein incorporated by reference in their entirety.
This application claims priority from U.S. Provisional Application No. 63/375,735, filed Sep. 15, 2022, the subject matter of which is incorporated herein by reference in its entirety.
This invention was made with government support under 2101129 awarded by the National Science Foundation. The government has certain rights in the invention.
Number | Date | Country | |
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Parent | 63375735 | Sep 2022 | US |
Child | 18467820 | US |