WO2024045532A1 - Method for recovering and pretreating spent lithium-ion battery - Google Patents
Method for recovering and pretreating spent lithium-ion battery Download PDFInfo
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- WO2024045532A1 WO2024045532A1 PCT/CN2023/079350 CN2023079350W WO2024045532A1 WO 2024045532 A1 WO2024045532 A1 WO 2024045532A1 CN 2023079350 W CN2023079350 W CN 2023079350W WO 2024045532 A1 WO2024045532 A1 WO 2024045532A1
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- H—ELECTRICITY
- H01—ELECTRIC ELEMENTS
- H01M—PROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
- H01M10/00—Secondary cells; Manufacture thereof
- H01M10/54—Reclaiming serviceable parts of waste accumulators
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- H—ELECTRICITY
- H01—ELECTRIC ELEMENTS
- H01M—PROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
- H01M10/00—Secondary cells; Manufacture thereof
- H01M10/05—Accumulators with non-aqueous electrolyte
- H01M10/052—Li-accumulators
- H01M10/0525—Rocking-chair batteries, i.e. batteries with lithium insertion or intercalation in both electrodes; Lithium-ion batteries
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- Y—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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/84—Recycling of batteries or fuel cells
Definitions
- the invention belongs to the technical field of lithium battery recycling, and specifically relates to a method for recycling and preprocessing of waste lithium ion batteries.
- lithium iron phosphate batteries are widely used in electric vehicles and hybrid vehicles due to their low cost and high safety performance.
- the service life of lithium iron phosphate batteries is In 5 to 8 years, lithium iron phosphate will usher in a wave of retirement in recent years. If a large number of used lithium iron phosphate batteries cannot be properly disposed of, it will not only cause serious pollution to the environment, but also cause the loss of scarce lithium resources. Therefore, the recycling and processing of used lithium iron phosphate batteries will be the focus of future research.
- the recycling of used lithium iron phosphate batteries mainly includes two parts: pretreatment and metal recycling.
- the metal recycling part is currently more researched.
- the traditional pretreatment method is to manually sort out the positive and negative electrodes of the battery after discharging and disassembling the battery pack, and then separate the positive and negative active materials from the current collector. This process is difficult to avoid manual participation, has low efficiency, poor safety, and is difficult to Achieve industrialization promotion. Therefore, finding a convenient and efficient method to dispose of used lithium-ion batteries is of great scientific significance and practical value.
- Chinese patent application CN112961984A discloses a process for selective recovery of waste lithium-ion batteries to collect fluids.
- the waste lithium-ion batteries are discharged, dried, and incinerated, and then crushed, screened, and ball milled to obtain ball-milled materials. Take the ball-milled materials. After water washing and magnetic separation, a low magnetic current collector copper and aluminum mixture is obtained.
- the current collector copper and aluminum mixture is slurried and shaken to obtain current collector copper and current collector aluminum respectively. No new impurity ions are introduced during the complete separation process of this process, which greatly simplifies the subsequent impurity removal process, improves the purity of the copper and aluminum current collectors, and increases the sales value of the current collectors.
- the main purpose of this process is to obtain copper and aluminum current collectors, and it does not pay attention to the recovery of positive electrode black powder. It is first incinerated at high temperature and then screened with a large-aperture screen. The incineration process will make the copper current collector brittle, and then it will be crushed. A large amount of copper, aluminum, graphite and other impurities enter the cathode black powder, resulting in a high impurity content in the cathode black powder, which increases the pressure for subsequent recovery of valuable metals and reduces the recovery rate of copper and aluminum current collectors.
- the process of magnetic separation first and then shaker separation also has certain disadvantages, because the material contains The amount of magnetic material is very small, so very few magnetic materials are selected by magnetic separation first, leaving a large amount of material that has not been selected, which will increase unnecessary load and energy consumption of the magnetic separation section.
- the present invention aims to solve at least one of the technical problems existing in the above-mentioned prior art.
- the present invention proposes a method for recycling and pretreatment of used lithium-ion batteries. This method utilizes the inherent density, magnetism, volatilization temperature, toughness and other properties of the battery component materials, and uses the gravity selection and ignition process to realize the recycling of used lithium-ion batteries. Efficient and harmless recycling pretreatment.
- a method for recycling and preprocessing waste lithium-ion batteries which includes the following steps:
- S1 Discharge the used lithium-ion batteries, remove the electrolyte, dry them, and crush the dried batteries to obtain crushed materials;
- S2 The crushed material is sorted on a shaking table to obtain a first mixture containing steel slag, copper flakes, and graphite and a second mixture containing aluminum foil and black powder.
- the second mixture is roasted and screened under an inert atmosphere. , separate aluminum foil and black powder;
- S3 The first mixture undergoes magnetic separation to separate steel slag and a third mixture containing copper flakes and graphite.
- the third mixture is roasted and screened in an inert atmosphere to separate copper flakes and graphite.
- the used lithium-ion battery is at least one of a lithium iron phosphate battery, a ternary lithium battery, a lithium manganate battery or a lithium cobalt oxide battery.
- step S1 the drying temperature is 80-200°C.
- the crushing process includes: first coarse crushing, and then fine crushing. After the fine crushing is completed, sieving is performed. The objects above the sieve are returned to the fine crushing process, and the objects under the sieve are The crushed materials enter the next step of shaking table sorting. Further, the screening is wet screening or dry screening.
- the opening of the coarse fracture is 1-4cm; the opening of the fine fracture is 1-4mm. It should be noted that the coarse crushing opening and fine crushing opening refer to the diameter of the discharge port of the crusher.
- step S1 the particle size of the crushed material is ⁇ 2 mm.
- the shaker in step S2, is a hydraulic shaker with a transverse slope of 1.5°-5°,
- the stroke of the shaker is 15-35mm, and the stroke frequency is 100-150 times/min.
- the greater the bed slope of the shaker the cleaner the separation of heavy substances will be, but the more heavy substances will be mixed into the light substances, so the bed slope must be strictly controlled.
- the magnetic field intensity of the magnetic separation is 600-1500Gs. Within this preferred range, the higher the magnetic field intensity, the better the steel slag separation effect and the higher the separation rate. Furthermore, the equipment used in the magnetic separation is a wet weak magnetic separator.
- the roasting temperature is 300-800°C. Further, the roasting time is 30-240 minutes.
- the higher the baking temperature the better the binder removal effect, and the higher the recovery rate of positive and negative electrode materials.
- the higher the degree of oxidation of copper sheets and aluminum foils the higher the content of copper and aluminum impurities doped in positive and negative electrode materials, so it is necessary to Control the roasting temperature within an appropriate range.
- the aperture of the screen used for screening is 0.025-0.074 mm.
- the inert atmosphere is at least one of nitrogen, argon or helium.
- the steam generated during the drying and roasting process enters the condensation system for recovery through pipelines.
- the present invention first heats and dries the residual electrolyte and moisture, then crushes and screens the whole to control the particle size of the crushed material.
- the crushed material contains steel slag, copper sheets and graphite adhered to the copper sheets, aluminum foil and aluminum foil adhered to the aluminum foil.
- Black powder then use a shaker to separate heavy substances and light substances, then use magnetic separation to separate steel slag, copper flakes and graphite, finally use roasting to burn off the binder, and use screening to separate copper flakes from graphite and aluminum foil.
- Black powder is mainly a mixture of positive electrode powder, carbon powder and a small amount of graphite dropped during the crushing and screening process.
- the positive electrode powder can be dissolved by acid, while graphite and carbon powder can be filtered as insoluble matter. If it falls off, it will have no impact on this process.
- the present invention utilizes the difference in density of different materials, uses water as the medium, and uses a shaking table sorting process to simultaneously separate different materials.
- aluminum foil and black powder are relatively light and float on the top layer under the influence of water flow classification.
- the impact of the transverse water flow is greater, and the graphite and steel slag bonded to the copper sheet are subject to greater longitudinal impact. They can be intercepted at two different directions of the shaker to obtain light and heavy materials; then the strong magnetism of the steel slag and the non-magnetic nature of the copper sheet are used , after magnetic separation, steel slag and Separation of copper sheets.
- the main purpose of the present invention is to obtain higher purity cathode black powder and at the same time achieve efficient recovery of copper, aluminum current collectors and other substances.
- the present invention cleverly places the roasting section at the end, which can avoid the copper current collector becoming brittle due to roasting in the shaking table section and being mixed into the black powder, resulting in excessive copper content in the black powder and a reduction in the copper recovery rate in the copper products. And other issues. Since the amounts of light and heavy materials in the crushed materials are similar, the present invention places the shaker before the magnetic separation, first the shaker selects half of the light materials, and the remaining half of the heavy materials are then subjected to magnetic separation, which greatly reduces the amount of materials entering the magnetic separation section.
- the traditional process generally leaves graphite in the positive electrode black powder.
- the graphite is insoluble in the wet process section and is left in the slag for recovery in the wet process section.
- the present invention can directly obtain most of the graphite products, and only a small amount of graphite is mixed in the positive electrode. Black powder is involved in subsequent leaching.
- the present invention realizes the overall recycling of waste lithium-ion batteries through processes such as crushing, screening, shaking tables, magnetic separation, roasting, and secondary screening.
- the entire process can be completed mechanically without manual disassembly.
- the entire sorting process uses the inherent properties of materials for physical sorting. No chemical reagents are added during the whole process. It has almost no pollution to the environment and no harm to the human body. It is a green and efficient separation method.
- Figure 1 is a process flow diagram of the present invention.
- Step 1 Put the lithium iron phosphate battery that has been fully discharged and drained of the electrolyte into an oven, set the temperature to 150°C, and dry for 3 hours to drain out the moisture and residual electrolyte.
- the generated gas enters the condensation system for recovery through the pipeline; the lithium iron phosphate battery
- the density of each material in the pool is: copper 8.9g/cm 3 , steel 7.85g/cm 3 , aluminum 2.7g/cm 3 , and lithium iron phosphate 1.523g/cm 3 ;
- Step 2 Take out the dried batteries and put them into the jaw crusher for rough crushing. Adjust the opening of the jaw crusher to 2cm;
- Step 3 Put the crushed materials into the roller crusher for fine crushing.
- the opening of the roller crusher is 2mm;
- Step 4 Use a sieve with a mesh size of 2mm to screen the finely crushed materials.
- the material above the screen is returned to the double-roller crusher and continues to be crushed to less than 2mm.
- the material below the screen is processed in the next step;
- Step 5 Set the shaker parameters to a transverse slope of 2.5°, a shaker stroke of 20cm, and a stroke rate of 140 times/min.
- the crushed and qualified materials are pulped to a concentration of 30%, and then slowly put into the shaker. After sorting by the shaker, A first mixture containing steel slag, copper flakes and graphite and a second mixture containing aluminum foil and black powder can be obtained;
- Step 6 Set the magnetic field intensity of the magnetic drum to 800Gs. Pass the first mixture obtained in step 5 through the magnetic drum to separate out the steel slag and the third mixture containing copper flakes and graphite.
- the steel slag recovery rate is 97%;
- Step 7 Put the third mixture obtained in Step 6 into a muffle furnace, set the temperature to 400°C, roast it for 60 minutes in a nitrogen atmosphere, and sieve it with a sieve with a mesh size of 0.038mm.
- the material on the sieve is copper sheet, and the material under the sieve is It is graphite slag, and the copper sheet recovery rate can reach 98%;
- Step 8 Put the second mixture obtained in step 5 into a muffle furnace, set the temperature to 500°C, bake for 40 minutes in a nitrogen atmosphere, and sieve with a sieve with a mesh size of 0.038mm.
- the material above the sieve is aluminum foil, and the material under the sieve is For black powder, the recovery rate of aluminum foil is 97%, and the recovery rate of cathode powder in black powder is 95%.
- a method for recycling and preprocessing used lithium iron phosphate batteries is:
- Step 1 Put the lithium iron phosphate battery that has been fully discharged and drained of the electrolyte into an oven, set the temperature to 180°C, and dry for 2 hours to drain out the moisture and residual electrolyte.
- the generated gas enters the condensation system for recovery through the pipeline;
- Step 2 Take out the dried batteries and put them into the jaw crusher for rough crushing. Adjust the opening of the jaw crusher to 2cm;
- Step 3 Put the crushed materials into the roller crusher for fine crushing.
- the opening of the roller crusher is 2mm;
- Step 4 Use a sieve with a mesh size of 2mm to screen the finely crushed materials.
- the material above the screen is returned to the double-roller crusher and continues to be crushed to less than 2mm.
- the material below the screen is processed in the next step;
- Step 5 Set the shaker parameters to a transverse slope of 3.5°, a shaker stroke of 18cm, and a stroke rate of 140 times/min.
- the crushed and qualified materials are pulped to a concentration of 30%, and then slowly put into the shaker. After sorting by the shaker, A first mixture containing steel slag, copper flakes and graphite and a second mixture containing aluminum foil and black powder can be obtained;
- Step 6 Set the magnetic field intensity of the magnetic drum to 800Gs. Pass the first mixture obtained in step 5 through the magnetic drum to separate out the steel slag and the third mixture containing copper flakes and graphite.
- the steel slag recovery rate is 97%;
- Step 7 Put the third mixture obtained in step 6 into a muffle furnace, set the temperature to 500°C, roast it for 40 minutes in a nitrogen atmosphere, and sieve it with a sieve with a mesh size of 0.038mm.
- the material on the sieve is copper sheet, and the material under the sieve is It is graphite slag, and the copper sheet recovery rate is 97.5%;
- Step 8 Put the second mixture obtained in step 5 into a muffle furnace, set the temperature to 600°C, bake for 40 minutes in a nitrogen atmosphere, and sieve with a sieve with a mesh size of 0.038mm.
- the material above the sieve is aluminum foil, and the material under the sieve is The recovery rate of black powder and aluminum foil is 98%, and the recovery rate of cathode powder in black powder is 94.5%.
- a method for recycling and preprocessing used lithium iron phosphate batteries is:
- Step 1 Put the lithium iron phosphate battery that has been fully discharged and drained of the electrolyte into an oven, set the temperature to 180°C, and dry for 2 hours to drain out the moisture and residual electrolyte.
- the generated gas enters the condensation system for recovery through the pipeline;
- Step 2 Take out the dried batteries and put them into the jaw crusher for rough crushing. Adjust the opening of the jaw crusher to 2cm;
- Step 3 Put the crushed materials into the roller crusher for fine crushing.
- the opening of the roller crusher is 2mm;
- Step 4 Use a sieve with a mesh size of 2mm to screen the finely crushed materials.
- the material above the screen is returned to the double-roller crusher and continues to be crushed to less than 2mm.
- the material below the screen is processed in the next step;
- Step 5 Set the shaker parameters to a transverse slope of 3.5°, a shaker stroke of 23cm, and a stroke rate of 140 times/min.
- the crushed and qualified materials are pulped to a concentration of 30%, and then slowly put into the shaker. After sorting by the shaker, A first mixture containing steel slag, copper flakes and graphite and a second mixture containing aluminum foil and black powder can be obtained;
- Step 6 Set the magnetic field intensity of the magnetic drum to 1500Gs. Pass the first mixture obtained in step 5 through the magnetic drum to separate out the steel slag and the third mixture containing copper flakes and graphite.
- the steel slag recovery rate is 98%;
- Step 7 Put the third mixture obtained in step 6 into a muffle furnace, set the temperature to 500°C, roast it for 40 minutes in a nitrogen atmosphere, and sieve it with a sieve with a mesh size of 0.038mm.
- the material on the sieve is copper sheet, and the material under the sieve is It is graphite slag, and the copper sheet recovery rate is 97%;
- Step 8 Put the second mixture obtained in step 5 into a muffle furnace, set the temperature to 600°C, bake for 120 minutes in a nitrogen atmosphere, and sieve it with a sieve with a mesh size of 0.038mm.
- the material above the sieve is aluminum foil, and the material under the sieve is The recovery rate of black powder and aluminum foil is 96.5%, and the recovery rate of cathode powder in black powder is 96%.
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Abstract
Description
本发明属于锂电池回收技术领域,具体涉及一种废旧锂离子电池回收预处理的方法。The invention belongs to the technical field of lithium battery recycling, and specifically relates to a method for recycling and preprocessing of waste lithium ion batteries.
随着新能源产业的快速发展,磷酸铁锂电池以其低成本和较高的安全性能而被大规模地应用于电动汽车和混合动力汽车中,一般来说,磷酸铁锂电池的使用寿命为5至8年,近年磷酸铁锂将迎来退役潮,届时大量废旧磷酸铁锂电池如不能妥善处理不仅造成环境的严重污染,还会造成稀缺锂资源的流失。因此,废旧磷酸铁锂电池回收处理将是未来的研究重点。With the rapid development of the new energy industry, lithium iron phosphate batteries are widely used in electric vehicles and hybrid vehicles due to their low cost and high safety performance. Generally speaking, the service life of lithium iron phosphate batteries is In 5 to 8 years, lithium iron phosphate will usher in a wave of retirement in recent years. If a large number of used lithium iron phosphate batteries cannot be properly disposed of, it will not only cause serious pollution to the environment, but also cause the loss of scarce lithium resources. Therefore, the recycling and processing of used lithium iron phosphate batteries will be the focus of future research.
废旧磷酸铁锂电池回收主要包括预处理和金属回收两部分,其中金属回收部分目前研究的较多,有多种方法可实现正极活性物质的回收,而对回收预处理方面的研究少之又少。传统的预处理方法是将电池包放电、拆解后,人工分选取出电池正负极,再进行正负极活性物质与集流体分离,此过程难以避免人工参与,效率低,安全性差,难以实现工业化推广。因此寻找一种便捷高效处理废旧锂离子电池的方法具有重大的科学意义和实用价值。The recycling of used lithium iron phosphate batteries mainly includes two parts: pretreatment and metal recycling. Among them, the metal recycling part is currently more researched. There are many methods to realize the recovery of positive active materials, but there is very little research on recycling pretreatment. . The traditional pretreatment method is to manually sort out the positive and negative electrodes of the battery after discharging and disassembling the battery pack, and then separate the positive and negative active materials from the current collector. This process is difficult to avoid manual participation, has low efficiency, poor safety, and is difficult to Achieve industrialization promotion. Therefore, finding a convenient and efficient method to dispose of used lithium-ion batteries is of great scientific significance and practical value.
中国专利申请CN112961984A公开了一种废旧锂离子电池选择性回收集流体的工艺,将废旧锂离子电池进行放电,烘干,焚烧,再进行破碎筛分、球磨,得到球磨后物料,取球磨后物料经过水洗和磁选,得到低磁集流体铜铝混合物,集流体铜铝混合物制浆,摇床,分别得到集流体铜和集流体铝。该工艺全分离过程中未引入新的杂质离子,大大简化了后续的除杂工艺,提高了铜铝集流体的纯度,提高了集流体的销售价值。但是该工艺主要目的是获得铜铝集流体,不重视正极黑粉的回收,其先经过高温焚烧再用大孔径筛网筛分,焚烧过程会使铜集流体变脆,再经过破碎,势必使大量铜、铝、石墨等杂质进入正极黑粉,导致正极黑粉中杂质含量很高,增加后续回收有价金属的压力,而且铜铝集流体回收率也降低。此外该工艺先磁选再摇床分选也存在一定弊端,由于材料中 磁性物质量很少,使得先磁选选出的磁性物质很少,剩下大量的物料未被选走,这样会增加磁选工段不必要的负荷与能耗。Chinese patent application CN112961984A discloses a process for selective recovery of waste lithium-ion batteries to collect fluids. The waste lithium-ion batteries are discharged, dried, and incinerated, and then crushed, screened, and ball milled to obtain ball-milled materials. Take the ball-milled materials. After water washing and magnetic separation, a low magnetic current collector copper and aluminum mixture is obtained. The current collector copper and aluminum mixture is slurried and shaken to obtain current collector copper and current collector aluminum respectively. No new impurity ions are introduced during the complete separation process of this process, which greatly simplifies the subsequent impurity removal process, improves the purity of the copper and aluminum current collectors, and increases the sales value of the current collectors. However, the main purpose of this process is to obtain copper and aluminum current collectors, and it does not pay attention to the recovery of positive electrode black powder. It is first incinerated at high temperature and then screened with a large-aperture screen. The incineration process will make the copper current collector brittle, and then it will be crushed. A large amount of copper, aluminum, graphite and other impurities enter the cathode black powder, resulting in a high impurity content in the cathode black powder, which increases the pressure for subsequent recovery of valuable metals and reduces the recovery rate of copper and aluminum current collectors. In addition, the process of magnetic separation first and then shaker separation also has certain disadvantages, because the material contains The amount of magnetic material is very small, so very few magnetic materials are selected by magnetic separation first, leaving a large amount of material that has not been selected, which will increase unnecessary load and energy consumption of the magnetic separation section.
发明内容Contents of the invention
本发明旨在至少解决上述现有技术中存在的技术问题之一。为此,本发明提出一种废旧锂离子电池回收预处理的方法,该方法利用电池组成材料固有的密度、磁性、挥发温度及韧性等性质,利用重选加火法工艺实现废旧锂离子电池的高效无害化回收预处理。The present invention aims to solve at least one of the technical problems existing in the above-mentioned prior art. To this end, the present invention proposes a method for recycling and pretreatment of used lithium-ion batteries. This method utilizes the inherent density, magnetism, volatilization temperature, toughness and other properties of the battery component materials, and uses the gravity selection and ignition process to realize the recycling of used lithium-ion batteries. Efficient and harmless recycling pretreatment.
根据本发明的一个方面,提出了一种废旧锂离子电池回收预处理的方法,包括以下步骤:According to one aspect of the present invention, a method for recycling and preprocessing waste lithium-ion batteries is proposed, which includes the following steps:
S1:将废旧锂离子电池进行放电、除电解液、烘干,将烘干后的电池进行破碎,得到破碎料;S1: Discharge the used lithium-ion batteries, remove the electrolyte, dry them, and crush the dried batteries to obtain crushed materials;
S2:将所述破碎料进行摇床分选,分别得到含有钢渣、铜片、石墨的第一混合物和含有铝箔、黑粉的第二混合物,所述第二混合物在惰性气氛下焙烧、筛分,分离出铝箔和黑粉;S2: The crushed material is sorted on a shaking table to obtain a first mixture containing steel slag, copper flakes, and graphite and a second mixture containing aluminum foil and black powder. The second mixture is roasted and screened under an inert atmosphere. , separate aluminum foil and black powder;
S3:所述第一混合物经过磁选,分离出钢渣、以及含有铜片和石墨的第三混合物,所述第三混合物在惰性气氛下焙烧、筛分,分离出铜片和石墨。S3: The first mixture undergoes magnetic separation to separate steel slag and a third mixture containing copper flakes and graphite. The third mixture is roasted and screened in an inert atmosphere to separate copper flakes and graphite.
在本发明的一些实施方式中,步骤S1中,所述废旧锂离子电池为磷酸铁锂电池、三元锂电池、锰酸锂电池或钴酸锂电池中的至少一种。In some embodiments of the present invention, in step S1, the used lithium-ion battery is at least one of a lithium iron phosphate battery, a ternary lithium battery, a lithium manganate battery or a lithium cobalt oxide battery.
在本发明的一些实施方式中,步骤S1中,所述烘干的温度为80-200℃。In some embodiments of the present invention, in step S1, the drying temperature is 80-200°C.
在本发明的一些实施方式中,步骤S1中,所述破碎的过程包括:先进行粗破,再细破,细破完成后进行筛分,筛上物返回细破工序,筛下物即为所述破碎料进入下一步摇床分选。进一步地,所述筛分为湿式筛分或干式筛分。In some embodiments of the present invention, in step S1, the crushing process includes: first coarse crushing, and then fine crushing. After the fine crushing is completed, sieving is performed. The objects above the sieve are returned to the fine crushing process, and the objects under the sieve are The crushed materials enter the next step of shaking table sorting. Further, the screening is wet screening or dry screening.
在本发明的一些实施方式中,所述粗破的开口为1-4cm;所述细破的开口为1-4mm。需要说明的是,粗破开口、细破开口指破碎机出料口的口径。In some embodiments of the present invention, the opening of the coarse fracture is 1-4cm; the opening of the fine fracture is 1-4mm. It should be noted that the coarse crushing opening and fine crushing opening refer to the diameter of the discharge port of the crusher.
在本发明的一些实施方式中,步骤S1中,所述破碎料的粒度≤2mm。In some embodiments of the present invention, in step S1, the particle size of the crushed material is ≤ 2 mm.
在本发明的一些实施方式中,步骤S2中,所述摇床为水力摇床,横向坡度为1.5°-5°, 摇床冲程为15-35mm,冲次为100-150次/min。摇床的床面坡度越大,重物质分离得越干净,但也会有越多的重物质混入轻物质中,因此要严格控制床面坡度。In some embodiments of the present invention, in step S2, the shaker is a hydraulic shaker with a transverse slope of 1.5°-5°, The stroke of the shaker is 15-35mm, and the stroke frequency is 100-150 times/min. The greater the bed slope of the shaker, the cleaner the separation of heavy substances will be, but the more heavy substances will be mixed into the light substances, so the bed slope must be strictly controlled.
在本发明的一些实施方式中,步骤S3中,所述磁选的磁场强度为600-1500Gs。在该优选范围内,磁场强度越高,钢渣分离效果越好,分离率越高。进一步地,所述磁选所用设备为湿式弱磁选机。In some embodiments of the present invention, in step S3, the magnetic field intensity of the magnetic separation is 600-1500Gs. Within this preferred range, the higher the magnetic field intensity, the better the steel slag separation effect and the higher the separation rate. Furthermore, the equipment used in the magnetic separation is a wet weak magnetic separator.
在本发明的一些实施方式中,步骤S2和/或步骤S3中,所述焙烧的温度为300-800℃。进一步地,所述焙烧的时间为30-240min。焙烧温度越高,粘结剂去除效果越好,正负极材料回收率越高,但铜片和铝箔氧化程度越高,正负极材料中掺杂的铜、铝杂质含量越高,因此要控制焙烧温度在合适范围。In some embodiments of the present invention, in step S2 and/or step S3, the roasting temperature is 300-800°C. Further, the roasting time is 30-240 minutes. The higher the baking temperature, the better the binder removal effect, and the higher the recovery rate of positive and negative electrode materials. However, the higher the degree of oxidation of copper sheets and aluminum foils, the higher the content of copper and aluminum impurities doped in positive and negative electrode materials, so it is necessary to Control the roasting temperature within an appropriate range.
在本发明的一些实施方式中,步骤S2和/或步骤S3中,所述筛分所用筛网的孔径为0.025-0.074mm。In some embodiments of the present invention, in step S2 and/or step S3, the aperture of the screen used for screening is 0.025-0.074 mm.
在本发明的一些实施方式中,步骤S2和/或步骤S3中,所述惰性气氛为氮气、氩气或氦气中的至少一种。In some embodiments of the present invention, in step S2 and/or step S3, the inert atmosphere is at least one of nitrogen, argon or helium.
在本发明的一些实施方式中,所述烘干、焙烧过程产生的蒸汽通过管道进入冷凝系统回收。In some embodiments of the present invention, the steam generated during the drying and roasting process enters the condensation system for recovery through pipelines.
根据本发明的一种优选的实施方式,至少具有以下有益效果:According to a preferred embodiment of the present invention, it has at least the following beneficial effects:
1、本发明先加热烘干残余电解液和水分,整体破碎和筛分,控制破碎料粒径,破碎料含有钢渣、铜片及粘附于铜片上的石墨、铝箔及粘附于铝箔上的黑粉,再利用摇床实现重物质和轻物质的分选,然后利用磁选实现钢渣、铜片石墨的分离,最后再用焙烧烧掉粘结剂,用筛分实现铜片与石墨、铝箔与正极黑粉分离。黑粉主要是正极粉与碳粉及破碎筛分过程掉落的少量石墨的混合物,后续湿法浸出电池黑粉过程中,正极粉可被酸溶解,而石墨和碳粉可作为不溶物被过滤掉,对本工艺没有影响。1. The present invention first heats and dries the residual electrolyte and moisture, then crushes and screens the whole to control the particle size of the crushed material. The crushed material contains steel slag, copper sheets and graphite adhered to the copper sheets, aluminum foil and aluminum foil adhered to the aluminum foil. Black powder, then use a shaker to separate heavy substances and light substances, then use magnetic separation to separate steel slag, copper flakes and graphite, finally use roasting to burn off the binder, and use screening to separate copper flakes from graphite and aluminum foil. Separate from the positive black powder. Black powder is mainly a mixture of positive electrode powder, carbon powder and a small amount of graphite dropped during the crushing and screening process. During the subsequent wet leaching process of battery black powder, the positive electrode powder can be dissolved by acid, while graphite and carbon powder can be filtered as insoluble matter. If it falls off, it will have no impact on this process.
2、本发明利用不同物质密度差异,以水为介质,用摇床分选工艺同时实现不同材料的分离,在分离过程中,铝箔和黑粉相对较轻,在水流分级影响下浮在最上层,所受横向水流冲击较大,铜片粘结部分石墨和钢渣所受纵向冲击力较大,可在摇床两个不同方位进行拦截获得轻重物料;再利用钢渣的强磁性和铜片的无磁性,磁选后实现钢渣与 铜片的分离。2. The present invention utilizes the difference in density of different materials, uses water as the medium, and uses a shaking table sorting process to simultaneously separate different materials. During the separation process, aluminum foil and black powder are relatively light and float on the top layer under the influence of water flow classification. The impact of the transverse water flow is greater, and the graphite and steel slag bonded to the copper sheet are subject to greater longitudinal impact. They can be intercepted at two different directions of the shaker to obtain light and heavy materials; then the strong magnetism of the steel slag and the non-magnetic nature of the copper sheet are used , after magnetic separation, steel slag and Separation of copper sheets.
3、本发明的主要目的在于获得较高纯度的正极黑粉,与此同时实现铜、铝集流体等物质的高效回收。与传统工艺相比,本发明巧妙地将焙烧段放在最后,可避免在摇床段铜集流体因焙烧变脆混入黑粉中,导致黑粉中铜含量超标,铜产品中铜回收率降低等问题。由于破碎料中轻重物料的量相近,本发明将摇床放在磁选之前,先摇床选出一半轻物质,剩下一半重物质再进行磁选,极大地减少了进入磁选段的料量,减轻磁选工段的负荷,节约了大量能耗。此外,传统工艺一般是将石墨留在正极黑粉中,石墨在湿法段为不溶物,在湿法段被留在渣中回收,本发明可以直接获得大部分石墨产品,仅少量石墨混在正极黑粉中参与后续浸出。3. The main purpose of the present invention is to obtain higher purity cathode black powder and at the same time achieve efficient recovery of copper, aluminum current collectors and other substances. Compared with the traditional process, the present invention cleverly places the roasting section at the end, which can avoid the copper current collector becoming brittle due to roasting in the shaking table section and being mixed into the black powder, resulting in excessive copper content in the black powder and a reduction in the copper recovery rate in the copper products. And other issues. Since the amounts of light and heavy materials in the crushed materials are similar, the present invention places the shaker before the magnetic separation, first the shaker selects half of the light materials, and the remaining half of the heavy materials are then subjected to magnetic separation, which greatly reduces the amount of materials entering the magnetic separation section. , reducing the load on the magnetic separation section and saving a lot of energy consumption. In addition, the traditional process generally leaves graphite in the positive electrode black powder. The graphite is insoluble in the wet process section and is left in the slag for recovery in the wet process section. The present invention can directly obtain most of the graphite products, and only a small amount of graphite is mixed in the positive electrode. Black powder is involved in subsequent leaching.
4、本发明通过破碎、筛分、摇床、磁选、焙烧、二次筛分等工序实现废旧锂离子电池整体回收,整个过程均可由机械完成,无需人工拆解。整个分选过程均是利用材料固有性质进行物理分选,全程不添加化学试剂,对环境几乎无污染、对人体无危害,是一种绿色高效的分离方法。4. The present invention realizes the overall recycling of waste lithium-ion batteries through processes such as crushing, screening, shaking tables, magnetic separation, roasting, and secondary screening. The entire process can be completed mechanically without manual disassembly. The entire sorting process uses the inherent properties of materials for physical sorting. No chemical reagents are added during the whole process. It has almost no pollution to the environment and no harm to the human body. It is a green and efficient separation method.
下面结合附图和实施例对本发明做进一步的说明,其中:The present invention will be further described below in conjunction with the accompanying drawings and examples, wherein:
图1为本发明工艺流程图。Figure 1 is a process flow diagram of the present invention.
以下将结合实施例对本发明的构思及产生的技术效果进行清楚、完整地描述,以充分地理解本发明的目的、特征和效果。显然,所描述的实施例只是本发明的一部分实施例,而不是全部实施例,基于本发明的实施例,本领域的技术人员在不付出创造性劳动的前提下所获得的其他实施例,均属于本发明保护的范围。The concept of the present invention and the technical effects produced will be clearly and completely described below with reference to the embodiments, so as to fully understand the purpose, features and effects of the present invention. Obviously, the described embodiments are only some of the embodiments of the present invention, not all of them. Based on the embodiments of the present invention, other embodiments obtained by those skilled in the art without exerting creative efforts are all protection scope of the present invention.
实施例1Example 1
一种废旧磷酸铁锂电池回收预处理的方法,参照图1,具体过程为:A method for recycling and preprocessing used lithium iron phosphate batteries. Refer to Figure 1. The specific process is:
步骤1,将充分放电并排掉电解液后的磷酸铁锂电池放入烘箱中,设置温度150℃,烘干3h排出水分和残余电解液,产生的气体通过管道进入冷凝系统回收;磷酸铁锂电 池中各物质的密度情况为:铜8.9g/cm3、钢7.85g/cm3、铝2.7g/cm3、磷酸铁锂1.523g/cm3;Step 1: Put the lithium iron phosphate battery that has been fully discharged and drained of the electrolyte into an oven, set the temperature to 150°C, and dry for 3 hours to drain out the moisture and residual electrolyte. The generated gas enters the condensation system for recovery through the pipeline; the lithium iron phosphate battery The density of each material in the pool is: copper 8.9g/cm 3 , steel 7.85g/cm 3 , aluminum 2.7g/cm 3 , and lithium iron phosphate 1.523g/cm 3 ;
步骤2,将烘干好的电池取出,放入颚式破碎机中进行粗破,颚式破碎机开口调节至2cm;Step 2: Take out the dried batteries and put them into the jaw crusher for rough crushing. Adjust the opening of the jaw crusher to 2cm;
步骤3,将破碎后的物料投入对辊破碎机进行细破,对辊磨碎机开口为2mm;Step 3: Put the crushed materials into the roller crusher for fine crushing. The opening of the roller crusher is 2mm;
步骤4,用筛网尺寸2mm的筛子将细碎的物料筛分,筛上物返回对辊破碎机,继续破碎至2mm以下,筛下物进行下一步处理;Step 4: Use a sieve with a mesh size of 2mm to screen the finely crushed materials. The material above the screen is returned to the double-roller crusher and continues to be crushed to less than 2mm. The material below the screen is processed in the next step;
步骤5,摇床参数设置横向坡度2.5°,摇床冲程20cm,冲次140次/min,将破碎合格的物料制浆,浓度为30%,然后缓慢投入摇床,经摇床分选后,可得含钢渣、铜片、石墨的第一混合物以及含铝箔、黑粉的第二混合物;Step 5: Set the shaker parameters to a transverse slope of 2.5°, a shaker stroke of 20cm, and a stroke rate of 140 times/min. The crushed and qualified materials are pulped to a concentration of 30%, and then slowly put into the shaker. After sorting by the shaker, A first mixture containing steel slag, copper flakes and graphite and a second mixture containing aluminum foil and black powder can be obtained;
步骤6,磁滚筒磁场强度设置800Gs,将步骤5得到的第一混合物通过磁滚筒,分离出钢渣以及含铜片、石墨的第三混合物,钢渣回收率为97%;Step 6: Set the magnetic field intensity of the magnetic drum to 800Gs. Pass the first mixture obtained in step 5 through the magnetic drum to separate out the steel slag and the third mixture containing copper flakes and graphite. The steel slag recovery rate is 97%;
步骤7,将步骤6得到的第三混合物放入马弗炉中,设置温度400℃,在氮气气氛下焙烧60min,用筛网尺寸0.038mm筛子筛分,筛上物料为铜片,筛下物料为石墨渣,铜片回收率可达98%;Step 7: Put the third mixture obtained in Step 6 into a muffle furnace, set the temperature to 400°C, roast it for 60 minutes in a nitrogen atmosphere, and sieve it with a sieve with a mesh size of 0.038mm. The material on the sieve is copper sheet, and the material under the sieve is It is graphite slag, and the copper sheet recovery rate can reach 98%;
步骤8,将步骤5得到的第二混合物放入马弗炉中,设置温度500℃,在氮气气氛下焙烧40min,用筛网尺寸0.038mm筛子筛分,筛上物料为铝箔,筛下物料为黑粉,铝箔回收率为97%,黑粉中正极粉的回收率为95%。Step 8: Put the second mixture obtained in step 5 into a muffle furnace, set the temperature to 500°C, bake for 40 minutes in a nitrogen atmosphere, and sieve with a sieve with a mesh size of 0.038mm. The material above the sieve is aluminum foil, and the material under the sieve is For black powder, the recovery rate of aluminum foil is 97%, and the recovery rate of cathode powder in black powder is 95%.
表1实施例1中各产物的元素含量
Table 1 Element content of each product in Example 1
实施例2Example 2
一种废旧磷酸铁锂电池回收预处理的方法,具体过程为:A method for recycling and preprocessing used lithium iron phosphate batteries. The specific process is:
步骤1,将充分放电并排掉电解液后的磷酸铁锂电池放入烘箱中,设置温度180℃,烘干2h排出水分和残余电解液,产生的气体通过管道进入冷凝系统回收;Step 1: Put the lithium iron phosphate battery that has been fully discharged and drained of the electrolyte into an oven, set the temperature to 180°C, and dry for 2 hours to drain out the moisture and residual electrolyte. The generated gas enters the condensation system for recovery through the pipeline;
步骤2,将烘干好的电池取出,放入颚式破碎机中进行粗破,颚式破碎机开口调节至2cm;Step 2: Take out the dried batteries and put them into the jaw crusher for rough crushing. Adjust the opening of the jaw crusher to 2cm;
步骤3,将破碎后的物料投入对辊破碎机进行细破,对辊磨碎机开口2mm;Step 3: Put the crushed materials into the roller crusher for fine crushing. The opening of the roller crusher is 2mm;
步骤4,用筛网尺寸2mm的筛子将细碎的物料筛分,筛上物返回对辊破碎机,继续破碎至2mm以下,筛下物进行下一步处理;Step 4: Use a sieve with a mesh size of 2mm to screen the finely crushed materials. The material above the screen is returned to the double-roller crusher and continues to be crushed to less than 2mm. The material below the screen is processed in the next step;
步骤5,摇床参数设置横向坡度3.5°,摇床冲程18cm,冲次140次/min,将破碎合格的物料制浆,浓度为30%,然后缓慢投入摇床,经摇床分选后,可得含钢渣、铜片、石墨的第一混合物以及含铝箔、黑粉的第二混合物;Step 5: Set the shaker parameters to a transverse slope of 3.5°, a shaker stroke of 18cm, and a stroke rate of 140 times/min. The crushed and qualified materials are pulped to a concentration of 30%, and then slowly put into the shaker. After sorting by the shaker, A first mixture containing steel slag, copper flakes and graphite and a second mixture containing aluminum foil and black powder can be obtained;
步骤6,磁滚筒磁场强度设置800Gs,将步骤5得到的第一混合物通过磁滚筒,分离出钢渣以及含铜片、石墨的第三混合物,钢渣回收率为97%;Step 6: Set the magnetic field intensity of the magnetic drum to 800Gs. Pass the first mixture obtained in step 5 through the magnetic drum to separate out the steel slag and the third mixture containing copper flakes and graphite. The steel slag recovery rate is 97%;
步骤7,将步骤6得到的第三混合物放入马弗炉中,设置温度500℃,在氮气气氛下焙烧40min,用筛网尺寸0.038mm筛子筛分,筛上物料为铜片,筛下物料为石墨渣,铜片回收率为97.5%;Step 7: Put the third mixture obtained in step 6 into a muffle furnace, set the temperature to 500°C, roast it for 40 minutes in a nitrogen atmosphere, and sieve it with a sieve with a mesh size of 0.038mm. The material on the sieve is copper sheet, and the material under the sieve is It is graphite slag, and the copper sheet recovery rate is 97.5%;
步骤8,将步骤5得到的第二混合物放入马弗炉中,设置温度600℃,在氮气气氛下焙烧40min,用筛网尺寸0.038mm筛子筛分,筛上物料为铝箔,筛下物料为黑粉,铝箔回收率为98%,黑粉中正极粉的回收率为94.5%。Step 8: Put the second mixture obtained in step 5 into a muffle furnace, set the temperature to 600°C, bake for 40 minutes in a nitrogen atmosphere, and sieve with a sieve with a mesh size of 0.038mm. The material above the sieve is aluminum foil, and the material under the sieve is The recovery rate of black powder and aluminum foil is 98%, and the recovery rate of cathode powder in black powder is 94.5%.
表2实施例2中各产物的元素含量
Table 2 Element content of each product in Example 2
实施例3Example 3
一种废旧磷酸铁锂电池回收预处理的方法,具体过程为:A method for recycling and preprocessing used lithium iron phosphate batteries. The specific process is:
步骤1,将充分放电并排掉电解液后的磷酸铁锂电池放入烘箱中,设置温度180℃,烘干2h排出水分和残余电解液,产生的气体通过管道进入冷凝系统回收;Step 1: Put the lithium iron phosphate battery that has been fully discharged and drained of the electrolyte into an oven, set the temperature to 180°C, and dry for 2 hours to drain out the moisture and residual electrolyte. The generated gas enters the condensation system for recovery through the pipeline;
步骤2,将烘干好的电池取出,放入颚式破碎机中进行粗破,颚式破碎机开口调节至2cm;Step 2: Take out the dried batteries and put them into the jaw crusher for rough crushing. Adjust the opening of the jaw crusher to 2cm;
步骤3,将破碎后的物料投入对辊破碎机进行细破,对辊磨碎机开口2mm;Step 3: Put the crushed materials into the roller crusher for fine crushing. The opening of the roller crusher is 2mm;
步骤4,用筛网尺寸2mm的筛子将细碎的物料筛分,筛上物返回对辊破碎机,继续破碎至2mm以下,筛下物进行下一步处理;Step 4: Use a sieve with a mesh size of 2mm to screen the finely crushed materials. The material above the screen is returned to the double-roller crusher and continues to be crushed to less than 2mm. The material below the screen is processed in the next step;
步骤5,摇床参数设置横向坡度3.5°,摇床冲程23cm,冲次140次/min,将破碎合格的物料制浆,浓度为30%,然后缓慢投入摇床,经摇床分选后,可得含钢渣、铜片、石墨的第一混合物以及含铝箔、黑粉的第二混合物;Step 5: Set the shaker parameters to a transverse slope of 3.5°, a shaker stroke of 23cm, and a stroke rate of 140 times/min. The crushed and qualified materials are pulped to a concentration of 30%, and then slowly put into the shaker. After sorting by the shaker, A first mixture containing steel slag, copper flakes and graphite and a second mixture containing aluminum foil and black powder can be obtained;
步骤6,磁滚筒磁场强度设置1500Gs,将步骤5得到的第一混合物通过磁滚筒,分离出钢渣以及含铜片、石墨的第三混合物,钢渣回收率为98%;Step 6: Set the magnetic field intensity of the magnetic drum to 1500Gs. Pass the first mixture obtained in step 5 through the magnetic drum to separate out the steel slag and the third mixture containing copper flakes and graphite. The steel slag recovery rate is 98%;
步骤7,将步骤6得到的第三混合物放入马弗炉中,设置温度500℃,在氮气气氛下焙烧40min,用筛网尺寸0.038mm筛子筛分,筛上物料为铜片,筛下物料为石墨渣,铜片回收率为97%;Step 7: Put the third mixture obtained in step 6 into a muffle furnace, set the temperature to 500°C, roast it for 40 minutes in a nitrogen atmosphere, and sieve it with a sieve with a mesh size of 0.038mm. The material on the sieve is copper sheet, and the material under the sieve is It is graphite slag, and the copper sheet recovery rate is 97%;
步骤8,将步骤5得到的第二混合物放入马弗炉中,设置温度600℃,在氮气气氛下焙烧120min,用筛网尺寸0.038mm筛子筛分,筛上物料为铝箔,筛下物料为黑粉,铝箔回收率为96.5%,黑粉中正极粉的回收率为96%。Step 8: Put the second mixture obtained in step 5 into a muffle furnace, set the temperature to 600°C, bake for 120 minutes in a nitrogen atmosphere, and sieve it with a sieve with a mesh size of 0.038mm. The material above the sieve is aluminum foil, and the material under the sieve is The recovery rate of black powder and aluminum foil is 96.5%, and the recovery rate of cathode powder in black powder is 96%.
表3实施例3中各产物的元素含量
Table 3 Element content of each product in Example 3
上面结合附图对本发明实施例作了详细说明,但是本发明不限于上述实施例,在所属技术领域普通技术人员所具备的知识范围内,还可以在不脱离本发明宗旨的前提下作出各种变化。此外,在不冲突的情况下,本发明的实施例及实施例中的特征可以相互组合。 The embodiments of the present invention have been described in detail above with reference to the accompanying drawings. However, the present invention is not limited to the above embodiments. Within the scope of knowledge possessed by those of ordinary skill in the art, various modifications can be made without departing from the purpose of the present invention. Variety. In addition, the embodiments of the present invention and the features in the embodiments may be combined with each other without conflict.
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| CN202211038996.6A CN115483466B (en) | 2022-08-29 | 2022-08-29 | Method for recycling and pretreatment of waste lithium-ion batteries |
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| PCT/CN2023/079350 Ceased WO2024045532A1 (en) | 2022-08-29 | 2023-03-02 | Method for recovering and pretreating spent lithium-ion battery |
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| Country | Link |
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| CN (1) | CN115483466B (en) |
| WO (1) | WO2024045532A1 (en) |
Cited By (2)
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|---|---|---|---|---|
| CN118017065A (en) * | 2024-04-10 | 2024-05-10 | 烟台大为环保科技有限公司 | Method and equipment for recycling black powder of waste lithium batteries |
| CN119542596A (en) * | 2024-11-25 | 2025-02-28 | 常州厚丰新能源有限公司 | A method and device for regenerating and recovering copper-containing battery negative electrode material |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN115483466B (en) * | 2022-08-29 | 2025-09-30 | 广东邦普循环科技有限公司 | Method for recycling and pretreatment of waste lithium-ion batteries |
| CN116273445B (en) * | 2023-02-20 | 2024-02-02 | 湖南五创循环科技股份有限公司 | Method for improving separation efficiency of mixed materials of waste lithium manganate batteries |
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| Publication number | Publication date |
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| CN115483466A (en) | 2022-12-16 |
| CN115483466B (en) | 2025-09-30 |
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