CN115679103A - A recycling process for positive electrode materials of decommissioned ternary lithium batteries - Google Patents
A recycling process for positive electrode materials of decommissioned ternary lithium batteries Download PDFInfo
- Publication number
- CN115679103A CN115679103A CN202110875809.9A CN202110875809A CN115679103A CN 115679103 A CN115679103 A CN 115679103A CN 202110875809 A CN202110875809 A CN 202110875809A CN 115679103 A CN115679103 A CN 115679103A
- Authority
- CN
- China
- Prior art keywords
- positive electrode
- hydrothermal
- battery
- filtered product
- regeneration process
- Prior art date
- Legal status (The legal status 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 status listed.)
- Pending
Links
- 229910052744 lithium Inorganic materials 0.000 title claims abstract description 64
- WHXSMMKQMYFTQS-UHFFFAOYSA-N Lithium Chemical compound [Li] WHXSMMKQMYFTQS-UHFFFAOYSA-N 0.000 title claims abstract description 60
- 238000000034 method Methods 0.000 title claims abstract description 46
- 239000007774 positive electrode material Substances 0.000 title claims abstract description 35
- 238000004064 recycling Methods 0.000 title claims abstract description 20
- 239000000047 product Substances 0.000 claims abstract description 44
- 239000002699 waste material Substances 0.000 claims abstract description 26
- 239000000706 filtrate Substances 0.000 claims abstract description 22
- 239000003480 eluent Substances 0.000 claims abstract description 20
- JRKICGRDRMAZLK-UHFFFAOYSA-L peroxydisulfate Chemical compound [O-]S(=O)(=O)OOS([O-])(=O)=O JRKICGRDRMAZLK-UHFFFAOYSA-L 0.000 claims abstract description 16
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 34
- 239000007788 liquid Substances 0.000 claims description 31
- 238000001914 filtration Methods 0.000 claims description 22
- 238000000137 annealing Methods 0.000 claims description 21
- 239000002904 solvent Substances 0.000 claims description 20
- 239000013543 active substance Substances 0.000 claims description 19
- 239000001763 2-hydroxyethyl(trimethyl)azanium Substances 0.000 claims description 17
- 235000019743 Choline chloride Nutrition 0.000 claims description 17
- LYCAIKOWRPUZTN-UHFFFAOYSA-N Ethylene glycol Chemical compound OCCO LYCAIKOWRPUZTN-UHFFFAOYSA-N 0.000 claims description 17
- SGMZJAMFUVOLNK-UHFFFAOYSA-M choline chloride Chemical compound [Cl-].C[N+](C)(C)CCO SGMZJAMFUVOLNK-UHFFFAOYSA-M 0.000 claims description 17
- 229960003178 choline chloride Drugs 0.000 claims description 17
- OKKJLVBELUTLKV-UHFFFAOYSA-N Methanol Chemical compound OC OKKJLVBELUTLKV-UHFFFAOYSA-N 0.000 claims description 15
- 238000010438 heat treatment Methods 0.000 claims description 14
- 238000003756 stirring Methods 0.000 claims description 14
- KWYUFKZDYYNOTN-UHFFFAOYSA-M potassium hydroxide Substances [OH-].[K+] KWYUFKZDYYNOTN-UHFFFAOYSA-M 0.000 claims description 13
- 230000008929 regeneration Effects 0.000 claims description 13
- 238000011069 regeneration method Methods 0.000 claims description 13
- 238000005188 flotation Methods 0.000 claims description 11
- 239000000654 additive Substances 0.000 claims description 10
- 230000000996 additive effect Effects 0.000 claims description 10
- 150000003839 salts Chemical class 0.000 claims description 10
- 229920006395 saturated elastomer Polymers 0.000 claims description 10
- 238000002791 soaking Methods 0.000 claims description 10
- PEDCQBHIVMGVHV-UHFFFAOYSA-N Glycerine Chemical compound OCC(O)CO PEDCQBHIVMGVHV-UHFFFAOYSA-N 0.000 claims description 9
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims description 9
- XGZVUEUWXADBQD-UHFFFAOYSA-L lithium carbonate Chemical compound [Li+].[Li+].[O-]C([O-])=O XGZVUEUWXADBQD-UHFFFAOYSA-L 0.000 claims description 8
- 229910052808 lithium carbonate Inorganic materials 0.000 claims description 8
- XSQUKJJJFZCRTK-UHFFFAOYSA-N Urea Chemical compound NC(N)=O XSQUKJJJFZCRTK-UHFFFAOYSA-N 0.000 claims description 6
- 150000001875 compounds Chemical class 0.000 claims description 6
- HBBGRARXTFLTSG-UHFFFAOYSA-N Lithium ion Chemical compound [Li+] HBBGRARXTFLTSG-UHFFFAOYSA-N 0.000 claims description 5
- 229910001416 lithium ion Inorganic materials 0.000 claims description 5
- LCPVQAHEFVXVKT-UHFFFAOYSA-N 2-(2,4-difluorophenoxy)pyridin-3-amine Chemical group NC1=CC=CN=C1OC1=CC=C(F)C=C1F LCPVQAHEFVXVKT-UHFFFAOYSA-N 0.000 claims description 3
- BVKZGUZCCUSVTD-UHFFFAOYSA-L Carbonate Chemical compound [O-]C([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-L 0.000 claims description 3
- WQZGKKKJIJFFOK-GASJEMHNSA-N Glucose Natural products OC[C@H]1OC(O)[C@H](O)[C@@H](O)[C@@H]1O WQZGKKKJIJFFOK-GASJEMHNSA-N 0.000 claims description 3
- TVXBFESIOXBWNM-UHFFFAOYSA-N Xylitol Natural products OCCC(O)C(O)C(O)CCO TVXBFESIOXBWNM-UHFFFAOYSA-N 0.000 claims description 3
- WQZGKKKJIJFFOK-VFUOTHLCSA-N beta-D-glucose Chemical compound OC[C@H]1O[C@@H](O)[C@H](O)[C@@H](O)[C@@H]1O WQZGKKKJIJFFOK-VFUOTHLCSA-N 0.000 claims description 3
- 239000004202 carbamide Substances 0.000 claims description 3
- 239000012153 distilled water Substances 0.000 claims description 3
- 239000008103 glucose Substances 0.000 claims description 3
- HEBKCHPVOIAQTA-UHFFFAOYSA-N meso ribitol Natural products OCC(O)C(O)C(O)CO HEBKCHPVOIAQTA-UHFFFAOYSA-N 0.000 claims description 3
- USHAGKDGDHPEEY-UHFFFAOYSA-L potassium persulfate Chemical compound [K+].[K+].[O-]S(=O)(=O)OOS([O-])(=O)=O USHAGKDGDHPEEY-UHFFFAOYSA-L 0.000 claims description 3
- CHQMHPLRPQMAMX-UHFFFAOYSA-L sodium persulfate Substances [Na+].[Na+].[O-]S(=O)(=O)OOS([O-])(=O)=O CHQMHPLRPQMAMX-UHFFFAOYSA-L 0.000 claims description 3
- 239000000811 xylitol Substances 0.000 claims description 3
- HEBKCHPVOIAQTA-SCDXWVJYSA-N xylitol Chemical compound OC[C@H](O)[C@@H](O)[C@H](O)CO HEBKCHPVOIAQTA-SCDXWVJYSA-N 0.000 claims description 3
- 229960002675 xylitol Drugs 0.000 claims description 3
- 235000010447 xylitol Nutrition 0.000 claims description 3
- 235000013877 carbamide Nutrition 0.000 claims description 2
- 238000001035 drying Methods 0.000 claims description 2
- 229960001031 glucose Drugs 0.000 claims description 2
- 235000001727 glucose Nutrition 0.000 claims description 2
- 229940045136 urea Drugs 0.000 claims description 2
- PUPZLCDOIYMWBV-UHFFFAOYSA-N (+/-)-1,3-Butanediol Chemical compound CC(O)CCO PUPZLCDOIYMWBV-UHFFFAOYSA-N 0.000 claims 1
- 238000004140 cleaning Methods 0.000 claims 1
- 238000007599 discharging Methods 0.000 claims 1
- 239000012530 fluid Substances 0.000 claims 1
- WGCNASOHLSPBMP-UHFFFAOYSA-N hydroxyacetaldehyde Natural products OCC=O WGCNASOHLSPBMP-UHFFFAOYSA-N 0.000 claims 1
- 238000012216 screening Methods 0.000 claims 1
- 238000010008 shearing Methods 0.000 claims 1
- 238000005987 sulfurization reaction Methods 0.000 claims 1
- 229910052751 metal Inorganic materials 0.000 abstract description 9
- 239000002184 metal Substances 0.000 abstract description 9
- 239000011149 active material Substances 0.000 abstract description 6
- 239000000463 material Substances 0.000 abstract description 6
- 150000002739 metals Chemical class 0.000 abstract description 6
- 238000011084 recovery Methods 0.000 abstract description 5
- 230000007613 environmental effect Effects 0.000 abstract description 2
- 238000000605 extraction Methods 0.000 abstract description 2
- 239000000243 solution Substances 0.000 description 32
- 238000010828 elution Methods 0.000 description 26
- WMFOQBRAJBCJND-UHFFFAOYSA-M Lithium hydroxide Chemical compound [Li+].[OH-] WMFOQBRAJBCJND-UHFFFAOYSA-M 0.000 description 22
- CDQSJQSWAWPGKG-UHFFFAOYSA-N butane-1,1-diol Chemical compound CCCC(O)O CDQSJQSWAWPGKG-UHFFFAOYSA-N 0.000 description 17
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 description 10
- 229910052782 aluminium Inorganic materials 0.000 description 10
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 10
- 239000011888 foil Substances 0.000 description 10
- 238000000926 separation method Methods 0.000 description 10
- 239000008367 deionised water Substances 0.000 description 8
- 229910021641 deionized water Inorganic materials 0.000 description 8
- 239000011259 mixed solution Substances 0.000 description 7
- 230000000052 comparative effect Effects 0.000 description 6
- 208000028659 discharge Diseases 0.000 description 5
- 230000000694 effects Effects 0.000 description 5
- 238000001027 hydrothermal synthesis Methods 0.000 description 5
- 229910000029 sodium carbonate Inorganic materials 0.000 description 5
- 229910052723 transition metal Inorganic materials 0.000 description 5
- 150000003624 transition metals Chemical class 0.000 description 5
- 239000000203 mixture Substances 0.000 description 4
- 239000011734 sodium Substances 0.000 description 4
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 description 2
- 239000002033 PVDF binder Substances 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 238000009854 hydrometallurgy Methods 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 229920002981 polyvinylidene fluoride Polymers 0.000 description 2
- BWHMMNNQKKPAPP-UHFFFAOYSA-L potassium carbonate Chemical compound [K+].[K+].[O-]C([O-])=O BWHMMNNQKKPAPP-UHFFFAOYSA-L 0.000 description 2
- 238000009853 pyrometallurgy Methods 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- PWHULOQIROXLJO-UHFFFAOYSA-N Manganese Chemical compound [Mn] PWHULOQIROXLJO-UHFFFAOYSA-N 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 239000010405 anode material Substances 0.000 description 1
- 239000011230 binding agent Substances 0.000 description 1
- 239000010406 cathode material Substances 0.000 description 1
- 229910017052 cobalt Inorganic materials 0.000 description 1
- 239000010941 cobalt Substances 0.000 description 1
- GUTLYIVDDKVIGB-UHFFFAOYSA-N cobalt atom Chemical compound [Co] GUTLYIVDDKVIGB-UHFFFAOYSA-N 0.000 description 1
- 238000004090 dissolution Methods 0.000 description 1
- 239000007772 electrode material Substances 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 150000002500 ions Chemical class 0.000 description 1
- 229910052748 manganese Inorganic materials 0.000 description 1
- 239000011572 manganese Substances 0.000 description 1
- 229910052759 nickel Inorganic materials 0.000 description 1
- 229910000027 potassium carbonate Inorganic materials 0.000 description 1
- 239000002244 precipitate Substances 0.000 description 1
- 239000002002 slurry Substances 0.000 description 1
- 229910000314 transition metal oxide Inorganic materials 0.000 description 1
Images
Classifications
-
- 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
Landscapes
- Secondary Cells (AREA)
- Battery Electrode And Active Subsutance (AREA)
- Manufacture And Refinement Of Metals (AREA)
Abstract
本发明提供了一种退役三元锂电池正极材料循环再生工艺,包括以下步骤:A)将废旧三元锂电池的正极片经过处理后,得到正极活性物质;B)用洗脱剂对所述正极活性物质进行处理后过滤,得到滤液和过滤产物,所述洗脱剂选自过硫酸盐的溶液;C)将所述过滤产物进行水热再硫化后退火处理,得到正极活性物质;D)调节所述滤液的pH,回收金属锂。本发明使用的洗脱剂,能够有效的分离出正极材料活性物质中的有价金属,且能重复使用,降低了回收成本。另外,使用水热再硫化对洗脱产物进行处理,避免了对有价金属的逐个萃取,优化回收工艺的同时,也防止了使用萃取剂对环境造成污染,使用的材料对比现有的方法更加廉价易得,也做到了节能环保。The invention provides a recycling process for positive electrode materials of decommissioned ternary lithium batteries, comprising the following steps: A) treating the positive electrode sheets of waste ternary lithium batteries to obtain positive electrode active materials; The positive active material is filtered after treatment to obtain a filtrate and a filtered product, and the eluent is selected from a persulfate solution; C) the filtered product is subjected to hydrothermal resulfurization and then annealed to obtain a positive active material; D) The pH of the filtrate is adjusted to recover lithium metal. The eluent used in the invention can effectively separate the valuable metals in the active material of the positive electrode material, and can be reused, reducing the recovery cost. In addition, hydrothermal resulfurization is used to treat the eluted products, which avoids the extraction of valuable metals one by one, optimizes the recovery process, and prevents the use of extractants from polluting the environment. The materials used are more efficient than existing methods. It is cheap and easy to get, and it also achieves energy saving and environmental protection.
Description
技术领域technical field
本发明属于锂离子电池技术领域,具体涉及一种退役三元锂电池正极材料循环再生工艺。The invention belongs to the technical field of lithium ion batteries, and in particular relates to a process for recycling positive electrode materials of decommissioned ternary lithium batteries.
背景技术Background technique
锂离子电池因其体积小、质量轻、比容量高等优点而被广泛使用于手机移动端、相机、电动汽车等领域,在锂电池大量使用以后,退役锂电池的回收利用成了我们需要解决的问题。有效的回收退役锂电池,减少了镍、钴、锰等有价金属对环境的污染,同时也能缓解资源短缺的问题。如今对于退役锂电池的回收主要分为火法冶金和湿法冶金两种,火法冶金能耗大,回收成本较高;湿法冶金操作流程冗长,需逐个分离有价金属,同时,萃取剂的使用会对环境造成污染,加大回收的成本。节能环保的回收退役锂电池,成了当今研究的重点。Lithium-ion batteries are widely used in mobile phones, cameras, electric vehicles and other fields due to their small size, light weight, and high specific capacity. After lithium batteries are used in large quantities, the recycling of retired lithium batteries has become a problem we need to solve question. Effective recycling of decommissioned lithium batteries reduces the pollution of nickel, cobalt, manganese and other valuable metals to the environment, and can also alleviate the problem of resource shortage. Nowadays, the recycling of decommissioned lithium batteries is mainly divided into pyrometallurgy and hydrometallurgy. Pyrometallurgy consumes a lot of energy and the recycling cost is high; hydrometallurgy has a long operation process and needs to separate valuable metals one by one. Excessive use will pollute the environment and increase the cost of recycling. Energy-saving and environment-friendly recycling of decommissioned lithium batteries has become the focus of current research.
发明内容Contents of the invention
有鉴于此,本发明要解决的技术问题在于提供一种退役三元锂电池正极材料循环再生工艺,本发明提供的工艺流程简单,可以有效回收活性物质并再生。In view of this, the technical problem to be solved by the present invention is to provide a recycling process for positive electrode materials of decommissioned ternary lithium batteries. The process flow provided by the present invention is simple, and active materials can be effectively recovered and regenerated.
本发明提供了一种退役三元锂电池正极材料循环再生工艺,包括以下步骤:The present invention provides a recycling process for positive electrode materials of decommissioned ternary lithium batteries, comprising the following steps:
A)将废旧三元锂电池的正极片经过处理后,得到正极活性物质;A) After treating the positive electrode sheet of the waste ternary lithium battery, the positive electrode active material is obtained;
B)用洗脱剂对所述正极活性物质进行处理后过滤,得到滤液和过滤产物,所述洗脱剂选自过硫酸盐的溶液;B) filtering the positive active material after treatment with an eluent to obtain a filtrate and a filtered product, the eluent being selected from a persulfate solution;
C)将所述过滤产物进行水热再硫化后退火处理,得到正极活性物质;C) annealing the filtered product after hydrothermal resulfurization to obtain a positive active material;
D)调节所述滤液的pH,回收金属锂。D) adjusting the pH of the filtrate to recover lithium metal.
优选的,步骤A)包括以下步骤:Preferably, step A) comprises the following steps:
A1)将废旧三元锂电池浸泡在饱和食盐水中进行放电处理;A1) Soak the waste ternary lithium battery in saturated salt water for discharge treatment;
将放电后的废旧三元锂电池用清水清洗干净并烘干;Clean the discharged waste ternary lithium battery with clean water and dry it;
将烘干后的电池剪切破碎成电池切片;Cut and break the dried battery into battery slices;
通过浮选法分离电池正极片、负极片、外壳和隔膜;Separation of battery positive electrode, negative electrode, casing and separator by flotation;
A2)将所述正极片置于处理液中进行加热搅拌,然后过滤,得到过滤产物;A2) placing the positive electrode sheet in the treatment solution for heating and stirring, and then filtering to obtain a filtered product;
将所述过滤产物进行筛分,得到正极活性物质。The filtered product is sieved to obtain a positive electrode active material.
优选的,所述处理液包括溶剂和溶质,所述溶剂选自乙二醇、甘油、丁二醇中的一种或多种,所述溶质选自木糖醇、葡萄糖、尿素、氯化胆碱中的一种或多种;Preferably, the treatment liquid includes a solvent and a solute, the solvent is selected from one or more of ethylene glycol, glycerol, butanediol, and the solute is selected from xylitol, glucose, urea, cholerin One or more of alkalis;
所述处理液中溶质与溶剂的摩尔比为(1.5~2.5):1,所述正极片与处理液的固液质量体积比为1g:(20~25)ml。The molar ratio of the solute to the solvent in the treatment solution is (1.5-2.5):1, and the solid-to-liquid mass-volume ratio of the positive electrode sheet to the treatment solution is 1g:(20-25)ml.
优选的,步骤A2)中,所述加热搅拌的温度为150~200℃,时间为3~5h。Preferably, in step A2), the temperature of the heating and stirring is 150-200° C., and the time is 3-5 hours.
优选的,所述过硫酸盐选自过硫酸钠或过硫酸钾;Preferably, the persulfate is selected from sodium persulfate or potassium persulfate;
所述过硫酸盐的溶液中的溶剂选自甲醇、乙二醇、蒸馏水中的一种或多种;The solvent in the solution of the persulfate is selected from one or more of methanol, ethylene glycol, distilled water;
所述过硫酸盐的溶液的浓度为0.2~1mol/L。The concentration of the persulfate solution is 0.2˜1 mol/L.
优选的,所述正极活性物质与所述洗脱剂的固液质量体积比为1g:(20~100)ml。Preferably, the solid-to-liquid mass-volume ratio of the positive electrode active material to the eluent is 1g:(20-100)ml.
优选的,步骤B)中,所述处理的温度为30~90℃,时间为2~8h。Preferably, in step B), the temperature of the treatment is 30-90° C., and the treatment time is 2-8 hours.
优选的,所述过滤产物与水热再硫化的添加剂的固液质量体积比为1g:(5~20)ml,所述水热再硫化的添加剂选自NaOH、LiOH、KOH中的一种或多种,所述水热再硫化的添加剂中OH-的浓度为2~4.5mol/L;Preferably, the solid-to-liquid mass volume ratio of the filtered product and the additive for hydrothermal resulfurization is 1 g: (5-20) ml, and the additive for hydrothermal resulfurization is selected from one of NaOH, LiOH, KOH or Various, the concentration of OH- in the additive for hydrothermal resulfurization is 2-4.5mol/L;
所述水热再硫化的温度为150~250℃,时间为1~6h。The temperature of the hydrothermal resulfurization is 150-250° C., and the time is 1-6 hours.
优选的,所述退火操作中加入含锂化合物,退火温度为500~900℃,退火时间为2~10h。Preferably, a lithium-containing compound is added in the annealing operation, the annealing temperature is 500-900° C., and the annealing time is 2-10 h.
优选的,回收金属锂的方法:Preferably, the method for reclaiming metal lithium:
调节pH至10~12,加入水溶性碳酸盐,使得锂离子以碳酸锂沉淀出来。Adjust the pH to 10-12, and add water-soluble carbonate, so that lithium ions are precipitated as lithium carbonate.
与现有技术相比,本发明提供了一种退役三元锂电池正极材料循环再生工艺,包括以下步骤:A)将废旧三元锂电池的正极片经过处理后,得到正极活性物质;B)用洗脱剂对所述正极活性物质进行处理后过滤,得到滤液和过滤产物,所述洗脱剂选自过硫酸盐的溶液;C)将所述过滤产物进行水热再硫化后退火处理,得到正极活性物质;D)调节所述滤液的pH,回收金属锂。本发明使用的洗脱剂,能够有效的分离出正极材料活性物质中的有价金属,且能重复使用,降低了回收成本。另外,使用水热再硫化对洗脱产物进行处理,避免了对有价金属的逐个萃取,优化回收工艺的同时,也防止了使用萃取剂对环境造成污染,使用的材料对比现有的方法更加廉价易得,进一步降低了回收费用,也做到了节能环保。Compared with the prior art, the present invention provides a recycling process for the cathode material of a decommissioned ternary lithium battery, comprising the following steps: A) treating the positive electrode sheet of the waste ternary lithium battery to obtain the positive electrode active material; B) treating the positive active material with an eluent and then filtering to obtain a filtrate and a filtered product, the eluent being selected from a persulfate solution; C) annealing the filtered product after hydrothermal resulfurization, Obtaining the positive electrode active material; D) adjusting the pH of the filtrate to reclaim metal lithium. The eluent used in the invention can effectively separate the valuable metals in the active material of the positive electrode material, and can be reused, reducing the recovery cost. In addition, hydrothermal resulfurization is used to treat the eluted products, which avoids the extraction of valuable metals one by one, optimizes the recovery process, and prevents the use of extractants from polluting the environment. The materials used are more efficient than existing methods. It is cheap and easy to obtain, which further reduces the recycling cost, and also achieves energy saving and environmental protection.
附图说明Description of drawings
图1为本发明提供的退役三元锂电池正极材料循环再生工艺流程图;Fig. 1 is the process flow diagram of recycling and regeneration of positive electrode material of decommissioned ternary lithium battery provided by the present invention;
图2为实施例1的电池循环效率图;Fig. 2 is the battery cycle efficiency figure of embodiment 1;
图3为实施例2的电池循环效率图;Fig. 3 is the battery cycle efficiency figure of embodiment 2;
图4为实施例3的电池循环效率图;Fig. 4 is the battery cycle efficiency figure of embodiment 3;
图5为实施例4的电池循环效率图。FIG. 5 is a graph of battery cycle efficiency of Example 4. FIG.
具体实施方式Detailed ways
本发明提供了一种退役三元锂电池正极材料循环再生工艺,包括以下步骤:The present invention provides a recycling process for positive electrode materials of decommissioned ternary lithium batteries, comprising the following steps:
A)将废旧三元锂电池的正极片经过处理后,得到正极活性物质;A) After treating the positive electrode sheet of the waste ternary lithium battery, the positive electrode active material is obtained;
B)用洗脱剂对所述正极活性物质进行处理后过滤,得到滤液和过滤产物,所述洗脱剂选自过硫酸盐的溶液;B) filtering the positive active material after treatment with an eluent to obtain a filtrate and a filtered product, the eluent being selected from a persulfate solution;
C)将所述过滤产物进行水热再硫化后退火处理,得到正极活性物质;C) annealing the filtered product after hydrothermal resulfurization to obtain a positive active material;
D)调节所述滤液的pH,回收金属锂。D) adjusting the pH of the filtrate to recover lithium metal.
本发明首先从废旧三元锂电池中分离正极活性物质,具体包括以下步骤:The present invention first separates the positive active material from the waste ternary lithium battery, specifically comprising the following steps:
A1)将废旧三元锂电池浸泡在饱和食盐水中进行放电处理;A1) Soak the waste ternary lithium battery in saturated salt water for discharge treatment;
将放电后的废旧三元锂电池用清水清洗干净并烘干;Clean the discharged waste ternary lithium battery with clean water and dry it;
将烘干后的电池剪切破碎成电池切片;Cut and break the dried battery into battery slices;
通过浮选法分离电池正极片、负极片、外壳和隔膜;Separation of battery positive electrode, negative electrode, casing and separator by flotation;
A2)将所述正极片置于处理液中进行加热搅拌,然后过滤,得到过滤产物;A2) placing the positive electrode sheet in the treatment solution for heating and stirring, and then filtering to obtain a filtered product;
将所述过滤产物进行筛分,得到正极活性物质。The filtered product is sieved to obtain a positive electrode active material.
其中,所述电池切片的尺寸为1~2cm;Wherein, the size of the battery slice is 1-2 cm;
本发明对所述浮选法的具体方法并没有特殊限制,本领域技术人员公知的方法即可。The present invention has no special limitation on the specific method of the flotation method, and any method known to those skilled in the art will suffice.
所述处理液包括溶剂和溶质,所述溶剂选自乙二醇、甘油、丁二醇中的一种或多种,所述溶质选自木糖醇、葡萄糖、尿素、氯化胆碱中的一种或多种;在本发明的一些具体实施方式中,所述处理液为氯化胆碱和丁二醇的混合液。Described treatment liquid comprises solvent and solute, and described solvent is selected from one or more in ethylene glycol, glycerol, butanediol, and described solute is selected from xylitol, glucose, urea, choline chloride One or more; In some specific embodiments of the present invention, the treatment solution is a mixed solution of choline chloride and butanediol.
所述处理液中溶质与溶剂的摩尔比为(1.5~2.5):1,优选为1.5:1、2.0:1、2.5:1,或(1.5~2.5):1之间的任意值,所述正极片与处理液的固液质量体积比为1g:(20~25)ml,优选为1g:20ml、1g:22.5ml、1g:25ml,或1g:(20~25)ml之间的任意值。The molar ratio of solute and solvent in the treatment liquid is (1.5~2.5):1, preferably 1.5:1, 2.0:1, 2.5:1, or any value between (1.5~2.5):1. The solid-to-liquid mass-volume ratio of the positive electrode sheet to the treatment solution is 1g: (20-25)ml, preferably 1g: 20ml, 1g: 22.5ml, 1g: 25ml, or any value between 1g: (20-25)ml .
在本发明中,固液质量体积比都以g:ml为单位。In the present invention, the mass-to-volume ratio of solid to liquid is expressed in units of g:ml.
所述加热搅拌的温度为150~200℃,优选为150、160、175、190、200,或150~200℃之间的任意值,时间为3~5h,优选为3、3.5、4、4.5、5,或3~5h之间的任意值。The heating and stirring temperature is 150-200°C, preferably 150, 160, 175, 190, 200, or any value between 150-200°C, and the time is 3-5h, preferably 3, 3.5, 4, 4.5 , 5, or any value between 3 and 5h.
加热搅拌处理完成后,进行过滤,过滤后将滤渣进行筛分,将较大的铝箔与正极活性物质进行分离。After the heating and stirring treatment is completed, filter is performed, and after filtering, the filter residue is sieved to separate the larger aluminum foil from the positive electrode active material.
得到正极活性物质后,用洗脱剂对所述正极活性物质进行处理后过滤,得到滤液和过滤产物,所述洗脱剂选自过硫酸盐的溶液。After the positive electrode active material is obtained, the positive electrode active material is treated with an eluent and then filtered to obtain a filtrate and a filtered product, and the eluent is selected from a persulfate solution.
所述洗脱剂包括溶剂和溶质,所述溶剂选自甲醇、乙二醇、蒸馏水中的一种或多种,所述溶质选自过硫酸盐中一种或多种,优选的,所述过硫酸盐选自过硫酸钠或过硫酸钾;Described eluent comprises solvent and solute, and described solvent is selected from one or more in methanol, ethylene glycol, distilled water, and described solute is selected from one or more in persulfate, preferably, described The persulfate is selected from sodium persulfate or potassium persulfate;
所述正极活性物质与所述洗脱剂的固液质量体积比为1g:(20~100)ml,优选为1g:20ml、1g:40ml、1g:60ml、1g:80ml、1g:100ml,或1g:(20~100)ml之间的任意值,洗脱剂的浓度为0.2~1mol/L,优选为0.2mol/L、0.4mol/L、0.6mol/L、0.8mol/L、1.0mol/L,或0.2~1mol/L之间的任意值。The solid-to-liquid mass volume ratio of the positive electrode active material to the eluent is 1g:(20-100)ml, preferably 1g:20ml, 1g:40ml, 1g:60ml, 1g:80ml, 1g:100ml, or 1g: Any value between (20~100)ml, the concentration of eluent is 0.2~1mol/L, preferably 0.2mol/L, 0.4mol/L, 0.6mol/L, 0.8mol/L, 1.0mol /L, or any value between 0.2 and 1mol/L.
在本发明中,将所述正极活性物质进行洗脱剂浸泡处理,进行过滤,得到浸泡液和过滤产物。其中,所述浸泡处理的温度为30~90℃,优选为30、50、60、80、90,或30~90℃之间的任意值,时间为2~8h,优选为2、4、6、8,或2~8h之间的任意值。In the present invention, the positive electrode active material is soaked in an eluent and filtered to obtain a soaking solution and a filtered product. Wherein, the temperature of the soaking treatment is 30-90°C, preferably 30, 50, 60, 80, 90, or any value between 30-90°C, and the time is 2-8 hours, preferably 2, 4, 6 hours , 8, or any value between 2 and 8h.
烘干过滤产物后,进行水热再硫化。所述烘干的温度为80~150℃,优选为80、100、120、150,或80~150℃之间的任意值。After the filtered product is dried, hydrothermal resulfurization is carried out. The drying temperature is 80-150°C, preferably 80, 100, 120, 150, or any value between 80-150°C.
在本发明中,所述过滤产物与水热再硫化的添加剂的固液质量体积比为1g:(5~20)ml,优选为1g:5ml、1g:10ml、1g:15ml、1g:20ml,或1g:(5~20)ml之间的任意值。In the present invention, the solid-to-liquid mass volume ratio of the filtered product and the hydrothermal resulfurization additive is 1g: (5-20) ml, preferably 1g: 5ml, 1g: 10ml, 1g: 15ml, 1g: 20ml, Or 1g: any value between (5-20)ml.
所述水热再硫化的添加剂选自NaOH、LiOH、KOH中的一种或多种,所述水热再硫化的添加剂中OH-的浓度为2~4.5mol/L,优选为2、2.5、3、3.5、4、4.5,或2~4.5mol/L之间的任意值;The additive for hydrothermal resulfurization is selected from one or more of NaOH, LiOH, and KOH, and the concentration of OH- in the additive for hydrothermal resulfurization is 2 to 4.5 mol/L, preferably 2, 2.5, 3, 3.5, 4, 4.5, or any value between 2 and 4.5mol/L;
所述水热再硫化的温度为150~250℃,优选为150、170、200、230、250,或150~250℃之间的任意值,时间为1~6h,优选为1、2、3、5、6,或1~6h之间的任意值。The temperature of the hydrothermal resulfurization is 150-250°C, preferably 150, 170, 200, 230, 250, or any value between 150-250°C, and the time is 1-6 hours, preferably 1, 2, 3 hours , 5, 6, or any value between 1 and 6h.
将水热再硫化产物烘干后,进行退火处理,得到正极材料活性物质。After the hydrothermal resulfurization product is dried, it is annealed to obtain the positive electrode material active material.
所述退火操作中加入含锂化合物,所述退火的温度为500~1000℃,优选为500、600、700、800、900、1000,或500~1000℃之间的任意值,退火时间为2~10h,优选为2、4、6、8、10,或2~10之间的任意值。所述含锂化合物选自Li2CO3或者LiOH,所述含锂化合物的添加量相比过滤产物为过量,在本发明中,所述含锂化合物的添加量占所述过滤产物的摩尔百分比为3%~5%,优选为3%。A lithium-containing compound is added in the annealing operation, the annealing temperature is 500-1000°C, preferably 500, 600, 700, 800, 900, 1000, or any value between 500-1000°C, and the annealing time is 2 ~10h, preferably 2, 4, 6, 8, 10, or any value between 2-10. The lithium-containing compound is selected from Li2CO3 or LiOH , and the amount of the lithium-containing compound added is excessive compared to the filtered product. In the present invention, the added amount of the lithium-containing compound accounts for the molar percentage of the filtered product 3% to 5%, preferably 3%.
调节洗脱处理后反应液的pH至10~12,优选为10、11、12,或10~12之间的任意值,加入水溶性碳酸盐,优选为碳酸钠或碳酸钾,使得锂离子以碳酸锂沉淀出来,回收金属锂。Adjust the pH of the reaction solution after the elution treatment to 10-12, preferably 10, 11, 12, or any value between 10-12, and add a water-soluble carbonate, preferably sodium carbonate or potassium carbonate, so that lithium ions Precipitate with lithium carbonate, recover metal lithium.
参见图1,图1为本发明提供的退役三元锂电池正极材料循环再生工艺流程图。Referring to Fig. 1, Fig. 1 is a flow chart of the process flow chart of recycling the anode material of decommissioned ternary lithium battery provided by the present invention.
活性物质的分离上,本发明使用粘结剂溶解液,相对比高温灼烧和NMP、DMF溶剂溶解,降低了能耗和对环境的污染。在将正极材料活性物质提取出来后,用洗脱剂处理,将复杂的过渡金属氧化物分离出来,用水热再硫化直接再生,得到活性物质,不使用强酸和萃取剂的条件下,简化了回收的流程,减少了对环境造成的污染,同时,使用的水热添加剂对比现有方法更加廉价,也降低了回收的成本,使整个回收过程节能环保。For the separation of active substances, the present invention uses a binder solution, which reduces energy consumption and environmental pollution compared with high-temperature burning and NMP and DMF solvent dissolution. After the active material of the positive electrode material is extracted, it is treated with an eluent to separate the complex transition metal oxides, and then directly regenerated by hydrothermal resulfurization to obtain the active material. It simplifies the recovery without using strong acid and extractant. The process reduces the pollution to the environment. At the same time, the hydrothermal additive used is cheaper than the existing method, which also reduces the cost of recycling, making the entire recycling process energy-saving and environmentally friendly.
为了进一步理解本发明,下面结合实施例对本发明提供的退役三元锂电池正极材料循环再生工艺进行说明,本发明的保护范围不受以下实施例的限制。In order to further understand the present invention, the recycling process of the positive electrode material of the decommissioned ternary lithium battery provided by the present invention will be described below in conjunction with the examples, and the scope of protection of the present invention is not limited by the following examples.
实施例1.Example 1.
1、将废旧三元锂电池NCM523浸泡在饱和食盐水中进行放电处理12h;1. Soak the waste ternary lithium battery NCM523 in saturated salt water for 12 hours;
2、将放电后的废旧三元锂电池NCM523用清水反复洗涤多次并烘干;2. Wash the discharged waste ternary lithium battery NCM523 repeatedly with clean water several times and dry it;
3、将烘干后的电池剪切破碎成电池切片,切片直径为1厘米;3. Cut and break the dried battery into battery slices with a diameter of 1 cm;
4、通过浮选法分离极片、外壳、隔膜;4. Separation of pole piece, shell and diaphragm by flotation method;
5、将正极片浸泡在由氯化胆碱和丁二醇混合均匀的溶剂中,氯化胆碱和丁二醇的摩尔比为2:1,加热温度为180℃,浸泡并搅拌5h,固液质量体积比(g:ml)为1:20;5. Soak the positive electrode sheet in a solvent that is uniformly mixed with choline chloride and butanediol. The molar ratio of choline chloride and butanediol is 2:1, and the heating temperature is 180°C. Soak and stir for 5 hours. Liquid mass volume ratio (g:ml) is 1:20;
6、浸泡过滤后将滤渣进行筛分,将较大的铝箔与活性物质进行分离;6. After soaking and filtering, the filter residue is screened to separate the larger aluminum foil from the active substance;
7、将活性物质用K2S2O8溶液中进行浸泡,K2S2O8浓度为0.2mol/L,洗脱温度为60℃,时间为4h,固液质量体积比为(g:ml)为1:50;7. Soak the active substance in K 2 S 2 O 8 solution, the K 2 S 2 O 8 concentration is 0.2mol/L, the elution temperature is 60°C, the time is 4h, and the solid-liquid mass volume ratio is (g: ml) is 1:50;
8、洗脱过滤后将滤液和过滤产物进行分离;8. After elution and filtration, the filtrate and the filtered product are separated;
9、将过滤产物与LiOH溶液一并放入反应釜中,进行水热反应,其中,LiOH溶液的浓度为4mol/L,水热反应的温度为220℃,时间为3h,固液质量体积比(g:ml)为1:20;9. Put the filtered product and LiOH solution into the reactor together for hydrothermal reaction, wherein the concentration of LiOH solution is 4mol/L, the temperature of the hydrothermal reaction is 220°C, the time is 3h, the mass-volume ratio of solid to liquid (g:ml) is 1:20;
10、将水热产物用去离子水反复冲洗并放入60℃真空干燥箱中烘干,然后与3%物质的量过量的Li2CO3混合进行退火,退火温度为850℃,时间为4h;10. Rinse the hydrothermal product repeatedly with deionized water and dry it in a vacuum oven at 60°C, then mix it with 3% excess Li 2 CO 3 for annealing, the annealing temperature is 850°C, and the time is 4h ;
11、调节滤液的pH为11,加入碳酸钠,使得锂以碳酸锂的形式沉淀出来,用去离子水反复冲洗后烘干。11. Adjust the pH of the filtrate to be 11, add sodium carbonate to precipitate lithium in the form of lithium carbonate, rinse with deionized water repeatedly and then dry.
实施例2.Example 2.
1、将废旧三元锂电池NCM523浸泡在饱和食盐水中进行放电处理12h;1. Soak the waste ternary lithium battery NCM523 in saturated salt water for 12 hours;
2、将放电后的废旧三元锂电池NCM523用清水反复洗涤多次并烘干;2. Wash the discharged waste ternary lithium battery NCM523 repeatedly with clean water several times and dry it;
3、将烘干后的电池剪切破碎成电池切片,切片直径为1厘米;3. Cut and break the dried battery into battery slices with a diameter of 1 cm;
4、通过浮选法分离极片、外壳、隔膜;4. Separation of pole piece, shell and diaphragm by flotation method;
5、将正极片浸泡在由氯化胆碱和丁二醇混合均匀的溶剂中,氯化胆碱和丁二醇的摩尔比为2:1,加热温度为180℃,浸泡并搅拌5h,固液质量体积比(g:ml)为1:20;5. Soak the positive electrode sheet in a solvent that is uniformly mixed with choline chloride and butanediol. The molar ratio of choline chloride and butanediol is 2:1, and the heating temperature is 180°C. Soak and stir for 5 hours. Liquid mass volume ratio (g:ml) is 1:20;
6、浸泡过滤后将滤渣进行筛分,将较大的铝箔与活性物质进行分离;6. After soaking and filtering, the filter residue is screened to separate the larger aluminum foil from the active substance;
7、将活性物质用K2S2O8溶液中进行浸泡,K2S2O8浓度为0.2mol/L,洗脱温度为70℃,时间为4h,固液质量体积比为(g:ml)为1:50;7. Soak the active substance in K 2 S 2 O 8 solution, the K 2 S 2 O 8 concentration is 0.2mol/L, the elution temperature is 70°C, the time is 4h, and the solid-liquid mass volume ratio is (g: ml) is 1:50;
8、洗脱过滤后将滤液和过滤产物进行分离;8. After elution and filtration, the filtrate and the filtered product are separated;
9、将过滤产物与LiOH和KOH的混合溶液一并放入反应釜中,进行水热反应,混合溶液中,LiOH溶液的浓度为0.1mol/L,KOH溶液的浓度为3.9mol/L,水热反应的温度为220℃,时间为3h,固液质量体积比(g:ml)为1:20;9. Put the filtered product and the mixed solution of LiOH and KOH into the reactor together for hydrothermal reaction. In the mixed solution, the concentration of LiOH solution is 0.1mol/L, the concentration of KOH solution is 3.9mol/L, water The temperature of the thermal reaction is 220°C, the time is 3 hours, and the solid-liquid mass-volume ratio (g:ml) is 1:20;
10、将水热产物用去离子水反复冲洗并放入60℃真空干燥箱中烘干,然后与3%物质的量过量的Li2CO3混合进行退火,退火温度为850℃,时间为5h;10. Rinse the hydrothermal product repeatedly with deionized water and dry it in a vacuum oven at 60°C, then mix it with 3% excess Li 2 CO 3 for annealing, the annealing temperature is 850°C, and the time is 5h ;
11、调节滤液的pH为11,加入碳酸钠,使得锂以碳酸锂的形式沉淀出来,用去离子水反复冲洗后烘干。11. Adjust the pH of the filtrate to be 11, add sodium carbonate to precipitate lithium in the form of lithium carbonate, rinse with deionized water repeatedly and then dry.
实施例3.Example 3.
1、将废旧三元锂电池NCM523浸泡在饱和食盐水中进行放电处理12h;1. Soak the waste ternary lithium battery NCM523 in saturated salt water for 12 hours;
2、将放电后的废旧三元锂电池NCM523用清水反复洗涤多次并烘干;2. Wash the discharged waste ternary lithium battery NCM523 repeatedly with clean water several times and dry it;
3、将烘干后的电池剪切破碎成电池切片,切片直径为1厘米;3. Cut and break the dried battery into battery slices with a diameter of 1 cm;
4、通过浮选法分离极片、外壳、隔膜;4. Separation of pole piece, shell and diaphragm by flotation method;
5、将正极片浸泡在由氯化胆碱和丁二醇混合均匀的溶剂中,氯化胆碱和丁二醇的摩尔比为2:1,加热温度为180℃,浸泡并搅拌5h,固液质量体积比(g:ml)为1:20;5. Soak the positive electrode sheet in a solvent that is uniformly mixed with choline chloride and butanediol. The molar ratio of choline chloride and butanediol is 2:1, and the heating temperature is 180°C. Soak and stir for 5 hours. Liquid mass volume ratio (g:ml) is 1:20;
6、浸泡过滤后将滤渣进行筛分,将较大的铝箔与活性物质进行分离;6. After soaking and filtering, the filter residue is screened to separate the larger aluminum foil from the active substance;
7、将活性物质用K2S2O8溶液中进行浸泡,K2S2O8浓度为0.2mol/L,洗脱温度为70℃,时间为5h,固液质量体积比为(g:ml)为1:50;7. Soak the active substance in K 2 S 2 O 8 solution, the K 2 S 2 O 8 concentration is 0.2mol/L, the elution temperature is 70°C, the time is 5h, and the solid-liquid mass volume ratio is (g: ml) is 1:50;
8、洗脱过滤后将滤液和过滤产物进行分离;8. After elution and filtration, the filtrate and the filtered product are separated;
9、将过滤产物与LiOH和KOH的混合溶液一并放入反应釜中,进行水热反应,混合溶液中,LiOH溶液的浓度为0.1mol/L,KOH溶液的浓度为3.9mol/L,水热反应的温度为220℃,时间为4h,固液质量体积比(g:ml)为1:20;9. Put the filtered product and the mixed solution of LiOH and KOH into the reactor together for hydrothermal reaction. In the mixed solution, the concentration of LiOH solution is 0.1mol/L, the concentration of KOH solution is 3.9mol/L, water The temperature of the thermal reaction is 220°C, the time is 4 hours, and the solid-liquid mass-volume ratio (g:ml) is 1:20;
10、将水热产物用去离子水反复冲洗并放入60℃真空干燥箱中烘干,然后与3%物质的量过量的Li2CO3混合进行退火,退火温度为850℃,时间为5h;10. Rinse the hydrothermal product repeatedly with deionized water and dry it in a vacuum oven at 60°C, then mix it with 3% excess Li 2 CO 3 for annealing, the annealing temperature is 850°C, and the time is 5h ;
11、调节滤液的pH为11,加入碳酸钠,使得锂以碳酸锂的形式沉淀出来,用去离子水反复冲洗后烘干。11. Adjust the pH of the filtrate to be 11, add sodium carbonate to precipitate lithium in the form of lithium carbonate, rinse with deionized water repeatedly and then dry.
实施例4.Example 4.
1、将废旧三元锂电池NCM523浸泡在饱和食盐水中进行放电处理12h;1. Soak the waste ternary lithium battery NCM523 in saturated salt water for 12 hours;
2、将放电后的废旧三元锂电池NCM523用清水反复洗涤多次并烘干;2. Wash the discharged waste ternary lithium battery NCM523 repeatedly with clean water several times and dry it;
3、将烘干后的电池剪切破碎成电池切片,切片直径为1厘米;3. Cut and break the dried battery into battery slices with a diameter of 1 cm;
4、通过浮选法分离极片、外壳、隔膜;4. Separation of pole piece, shell and diaphragm by flotation method;
5、将正极片浸泡在由氯化胆碱和丁二醇混合均匀的溶剂中,氯化胆碱和丁二醇的摩尔比为2:1,加热温度为180℃,浸泡并搅拌5h,固液质量体积比(g:ml)为1:20;5. Soak the positive electrode sheet in a solvent that is uniformly mixed with choline chloride and butanediol. The molar ratio of choline chloride and butanediol is 2:1, and the heating temperature is 180°C. Soak and stir for 5 hours. Liquid mass volume ratio (g:ml) is 1:20;
6、浸泡过滤后将滤渣进行筛分,将较大的铝箔与活性物质进行分离;6. After soaking and filtering, the filter residue is screened to separate the larger aluminum foil from the active substance;
7、将活性物质用Na2S2O8溶液中进行浸泡,Na2S2O8浓度为0.2mol/L,洗脱温度为70℃,时间为5h,固液质量体积比为(g:ml)为1:50;7. Soak the active substance in Na 2 S 2 O 8 solution, the concentration of Na 2 S 2 O 8 is 0.2mol/L, the elution temperature is 70°C, the time is 5h, and the solid-liquid mass volume ratio is (g: ml) is 1:50;
8、洗脱过滤后将滤液和过滤产物进行分离;8. After elution and filtration, the filtrate and the filtered product are separated;
9、将过滤产物与LiOH和KOH的混合溶液一并放入反应釜中,进行水热反应,混合溶液中,LiOH溶液的浓度为0.1mol/L,KOH溶液的浓度为3.9mol/L,水热反应的温度为220℃,时间为4h,固液质量体积比(g:ml)为1:20;9. Put the filtered product and the mixed solution of LiOH and KOH into the reactor together for hydrothermal reaction. In the mixed solution, the concentration of LiOH solution is 0.1mol/L, the concentration of KOH solution is 3.9mol/L, water The temperature of the thermal reaction is 220°C, the time is 4 hours, and the solid-liquid mass-volume ratio (g:ml) is 1:20;
10、将水热产物用去离子水反复冲洗并放入60℃真空干燥箱中烘干,然后与3%物质的量过量的Li2CO3混合进行退火,退火温度为850℃,时间为5h;10. Rinse the hydrothermal product repeatedly with deionized water and dry it in a vacuum oven at 60°C, then mix it with 3% excess Li 2 CO 3 for annealing, the annealing temperature is 850°C, and the time is 5h ;
11、调节滤液的pH为11,加入碳酸钠,使得锂以碳酸锂的形式沉淀出来,用去离子水反复冲洗后烘干。11. Adjust the pH of the filtrate to be 11, add sodium carbonate to precipitate lithium in the form of lithium carbonate, rinse with deionized water repeatedly and then dry.
对上述回收材料进行电池的组装,具体步骤为:To assemble the battery from the above recycled materials, the specific steps are:
将材料以80wt%回收材料、10wt%Super P和10wt%PVDF制备成浆料涂覆在铝箔上并在110℃真空烘箱中烘干12h,其中PVDF是溶解在NMP中的形式添加。将烘干的铝箔冲压成直径为12mm的圆片,采用CR2032型硬币半电池,在手套箱中组装。The material was prepared as a slurry with 80wt% recycled material, 10wt% Super P and 10wt% PVDF, coated on aluminum foil and dried in a vacuum oven at 110°C for 12h, where PVDF was added in the form of dissolving NMP. The dried aluminum foil was punched into a disc with a diameter of 12 mm, and a CR2032 coin half cell was used for assembly in a glove box.
结果参见图2~图5,图2为实施例1的电池循环效率图;图3为实施例2的电池循环效率图;图4为实施例3的电池循环效率图;图5为实施例4的电池循环效率图。由图4可知,在以1C倍率进行充放电循环,回收电极材料组装的电池首圈放电比容量均能达到170mAh/g,经历50圈循环以后放电比容量仍能达到168mAh/g,容量保持率可以达到98.8%;首次效率为92.96%,循环过后效率可以达到99%以上。Result is referring to Fig. 2~Fig. 5, and Fig. 2 is the battery cycle efficiency figure of embodiment 1; Fig. 3 is the battery cycle efficiency figure of embodiment 2; Fig. 4 is the battery cycle efficiency figure of embodiment 3; Fig. 5 is embodiment 4 The battery cycle efficiency diagram. It can be seen from Figure 4 that when the charge-discharge cycle is performed at a rate of 1C, the first-cycle discharge specific capacity of the battery assembled with recycled electrode materials can reach 170mAh/g, and the discharge specific capacity can still reach 168mAh/g after 50 cycles. It can reach 98.8%; the first-time efficiency is 92.96%, and the efficiency can reach more than 99% after the cycle.
对比例1.Comparative example 1.
1、将废旧三元锂电池NCM523浸泡在饱和食盐水中进行放电处理12h;1. Soak the waste ternary lithium battery NCM523 in saturated salt water for 12 hours;
2、将放电后的废旧三元锂电池NCM523用清水反复洗涤多次并烘干;2. Wash the discharged waste ternary lithium battery NCM523 repeatedly with clean water several times and dry it;
3、将烘干后的电池剪切破碎成电池切片,切片直径为1厘米;3. Cut and break the dried battery into battery slices with a diameter of 1 cm;
4、通过浮选法分离极片、外壳、隔膜;4. Separation of pole piece, shell and diaphragm by flotation method;
5、将正极片浸泡在由氯化胆碱和丁二醇混合均匀的溶剂中,氯化胆碱和丁二醇的摩尔比为2:1,加热温度为180℃,浸泡并搅拌5h,固液质量体积比(g:ml)为1:20;5. Soak the positive electrode sheet in a solvent that is uniformly mixed with choline chloride and butanediol. The molar ratio of choline chloride and butanediol is 2:1, and the heating temperature is 180°C. Soak and stir for 5 hours. Liquid mass volume ratio (g:ml) is 1:20;
6、浸泡过滤后将滤渣进行筛分,将较大的铝箔与活性物质进行分离;6. After soaking and filtering, the filter residue is screened to separate the larger aluminum foil from the active substance;
7、将活性物质用H2C2O4溶液中进行浸泡,H2C2O4浓度为0.2mol/L,洗脱温度为70℃,时间为4h,固液质量体积比为(g:ml)为1:50;7. Soak the active substance in H 2 C 2 O 4 solution, the concentration of H 2 C 2 O 4 is 0.2mol/L, the elution temperature is 70°C, the time is 4h, and the solid-liquid mass volume ratio is (g: ml) is 1:50;
8、洗脱过滤后将滤液和过滤产物进行分离;8. After elution and filtration, the filtrate and the filtered product are separated;
对于锂的洗脱效果有所欠缺,影响后续再生过程。The elution effect of lithium is lacking, which affects the subsequent regeneration process.
对比例2.Comparative example 2.
1、将废旧三元锂电池NCM523浸泡在饱和食盐水中进行放电处理12h;1. Soak the waste ternary lithium battery NCM523 in saturated salt water for 12 hours;
2、将放电后的废旧三元锂电池NCM523用清水反复洗涤多次并烘干;2. Wash the discharged waste ternary lithium battery NCM523 repeatedly with clean water several times and dry it;
3、将烘干后的电池剪切破碎成电池切片,切片直径为1厘米;3. Cut and break the dried battery into battery slices with a diameter of 1 cm;
4、通过浮选法分离极片、外壳、隔膜;4. Separation of pole piece, shell and diaphragm by flotation method;
5、将正极片浸泡在由氯化胆碱和丁二醇混合均匀的溶剂中,氯化胆碱和丁二醇的摩尔比为2:1,加热温度为180℃,浸泡并搅拌5h,固液质量体积比(g:ml)为1:20;5. Soak the positive electrode piece in a solvent that is uniformly mixed with choline chloride and butanediol. The molar ratio of choline chloride and butanediol is 2:1, and the heating temperature is 180°C. Soak and stir for 5 hours. Liquid mass volume ratio (g:ml) is 1:20;
6、浸泡过滤后将滤渣进行筛分,将较大的铝箔与活性物质进行分离;6. After soaking and filtering, the filter residue is screened to separate the larger aluminum foil from the active substance;
7、将活性物质用(NH4)2S2O8溶液中进行浸泡,(NH4)2S2O8浓度为0.2mol/L,洗脱温度为70℃,时间为5h,固液质量体积比为(g:ml)为1:50;7. Soak the active substance in (NH 4 ) 2 S 2 O 8 solution, the concentration of (NH 4 ) 2 S 2 O 8 is 0.2mol/L, the elution temperature is 70°C, the time is 5h, the solid-liquid mass The volume ratio (g:ml) is 1:50;
8、洗脱过滤后将滤液和过滤产物进行分离;8. After elution and filtration, the filtrate and the filtered product are separated;
洗脱过程过渡金属溶解严重,影响后续再生过程。During the elution process, the transition metal dissolves seriously, which affects the subsequent regeneration process.
对比例3Comparative example 3
1、将废旧三元锂电池NCM523浸泡在饱和食盐水中进行放电处理12h;1. Soak the waste ternary lithium battery NCM523 in saturated salt water for 12 hours;
2、将放电后的废旧三元锂电池NCM523用清水反复洗涤多次并烘干;2. Wash the discharged waste ternary lithium battery NCM523 repeatedly with clean water several times and dry it;
3、将烘干后的电池剪切破碎成电池切片,切片直径为1厘米;3. Cut and break the dried battery into battery slices with a diameter of 1 cm;
4、通过浮选法分离极片、外壳、隔膜;4. Separation of pole piece, shell and diaphragm by flotation method;
5、将正极片浸泡在由氯化胆碱和丁二醇混合均匀的溶剂中,氯化胆碱和丁二醇的摩尔比为2:1,加热温度为180℃,浸泡并搅拌5h,固液质量体积比(g:ml)为1:20;5. Soak the positive electrode piece in a solvent that is uniformly mixed with choline chloride and butanediol. The molar ratio of choline chloride and butanediol is 2:1, and the heating temperature is 180°C. Soak and stir for 5 hours. Liquid mass volume ratio (g:ml) is 1:20;
6、浸泡过滤后将滤渣进行筛分,将较大的铝箔与活性物质进行分离;6. After soaking and filtering, the filter residue is screened to separate the larger aluminum foil from the active substance;
7、将活性物质用100ml的K2S2O8溶液中进行浸泡,K2S2O8浓度为0.2mol/L,加入甲醇10ml,洗脱温度为60℃,时间为4h,固液质量体积比为(g:ml)为1:50;7. Soak the active substance in 100ml of K 2 S 2 O 8 solution, the concentration of K 2 S 2 O 8 is 0.2mol/L, add 10ml of methanol, the elution temperature is 60°C, the time is 4h, the solid-liquid mass The volume ratio (g:ml) is 1:50;
8、洗脱过滤后将滤液和过滤产物进行分离;8. After elution and filtration, the filtrate and the filtered product are separated;
洗脱过程中过渡金属溶解严重,影响后续再生过程。During the elution process, the transition metal dissolves seriously, which affects the subsequent regeneration process.
对过滤产物进行ICP测试,测得离子浓度,计算洗脱效果,结果见表1.The ICP test was carried out on the filtered product, the ion concentration was measured, and the elution effect was calculated. The results are shown in Table 1.
表1 过滤产物的洗脱效果Table 1 The elution effect of the filtered product
由表1可知,Na2S2O8、Na2S2O8和(NH4)2S2O8均对三元材料中锂具有很好的洗脱效果,但(NH4)2S2O8对其他过渡金属也存在洗脱,在过硫酸盐溶液中加入少量甲醇提升锂的洗脱率,但同时会增大过渡金属的洗脱率,H2C2O4溶液对锂的洗脱效果没有上述过硫酸盐好,且过渡金属的洗脱率也较高。It can be seen from Table 1 that Na 2 S 2 O 8 , Na 2 S 2 O 8 and (NH 4 ) 2 S 2 O 8 all have good elution effects on lithium in ternary materials, but (NH 4 ) 2 S 2 O 8 also elutes other transition metals. Adding a small amount of methanol to the persulfate solution improves the elution rate of lithium, but at the same time it increases the elution rate of transition metals. The H 2 C 2 O 4 solution for lithium The elution effect is not as good as the above-mentioned persulfates, and the elution rate of transition metals is also higher.
以上所述仅是本发明的优选实施方式,应当指出,对于本技术领域的普通技术人员来说,在不脱离本发明原理的前提下,还可以做出若干改进和润饰,这些改进和润饰也应视为本发明的保护范围。The above is only a preferred embodiment of the present invention, it should be pointed out that for those skilled in the art, without departing from the principle of the present invention, some improvements and modifications can also be made, and these improvements and modifications are also It should be regarded as the protection scope of the present invention.
Claims (10)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN202110875809.9A CN115679103A (en) | 2021-07-30 | 2021-07-30 | A recycling process for positive electrode materials of decommissioned ternary lithium batteries |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN202110875809.9A CN115679103A (en) | 2021-07-30 | 2021-07-30 | A recycling process for positive electrode materials of decommissioned ternary lithium batteries |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN115679103A true CN115679103A (en) | 2023-02-03 |
Family
ID=85060103
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN202110875809.9A Pending CN115679103A (en) | 2021-07-30 | 2021-07-30 | A recycling process for positive electrode materials of decommissioned ternary lithium batteries |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN115679103A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN119253111A (en) * | 2024-09-27 | 2025-01-03 | 广东华菁新能源科技有限公司 | A method for recycling lithium iron phosphate positive electrode sheets suitable for retired lithium-ion power batteries |
Citations (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN107579246A (en) * | 2017-09-01 | 2018-01-12 | 安普瑞斯(无锡)有限公司 | A kind of preparation method of the high-pressure solid cobalt nickel lithium manganate ternary material of lithium ion battery |
| CN109022793A (en) * | 2017-06-12 | 2018-12-18 | 长沙矿冶研究院有限责任公司 | A method of the Selectively leaching lithium from the anode material waste powder of at least one of the manganese of nickel containing cobalt |
| CN109075407A (en) * | 2016-05-20 | 2018-12-21 | 魁北克电力公司 | The method for recycling electrode material of lithium battery |
| CN109904548A (en) * | 2019-03-22 | 2019-06-18 | 郑州中科新兴产业技术研究院 | A method of synthesizing rich lithium material from waste and old lithium ion battery |
| CN111600089A (en) * | 2020-06-01 | 2020-08-28 | 宁波大学 | A process for recycling and recycling cathode material of waste ternary lithium battery |
| CN112117507A (en) * | 2020-11-19 | 2020-12-22 | 中南大学 | A method for efficient recovery and regeneration of cathode materials of waste lithium-ion batteries |
| CN112830526A (en) * | 2021-01-04 | 2021-05-25 | 赣州有色冶金研究所 | Method for regenerating ternary precursor by utilizing nickel-cobalt-manganese slag |
| CN112897492A (en) * | 2021-01-25 | 2021-06-04 | 中南大学 | Method for regenerating and recycling high-impurity lithium iron phosphate waste powder |
-
2021
- 2021-07-30 CN CN202110875809.9A patent/CN115679103A/en active Pending
Patent Citations (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN109075407A (en) * | 2016-05-20 | 2018-12-21 | 魁北克电力公司 | The method for recycling electrode material of lithium battery |
| CN109022793A (en) * | 2017-06-12 | 2018-12-18 | 长沙矿冶研究院有限责任公司 | A method of the Selectively leaching lithium from the anode material waste powder of at least one of the manganese of nickel containing cobalt |
| CN107579246A (en) * | 2017-09-01 | 2018-01-12 | 安普瑞斯(无锡)有限公司 | A kind of preparation method of the high-pressure solid cobalt nickel lithium manganate ternary material of lithium ion battery |
| CN109904548A (en) * | 2019-03-22 | 2019-06-18 | 郑州中科新兴产业技术研究院 | A method of synthesizing rich lithium material from waste and old lithium ion battery |
| CN111600089A (en) * | 2020-06-01 | 2020-08-28 | 宁波大学 | A process for recycling and recycling cathode material of waste ternary lithium battery |
| CN112117507A (en) * | 2020-11-19 | 2020-12-22 | 中南大学 | A method for efficient recovery and regeneration of cathode materials of waste lithium-ion batteries |
| CN112830526A (en) * | 2021-01-04 | 2021-05-25 | 赣州有色冶金研究所 | Method for regenerating ternary precursor by utilizing nickel-cobalt-manganese slag |
| CN112897492A (en) * | 2021-01-25 | 2021-06-04 | 中南大学 | Method for regenerating and recycling high-impurity lithium iron phosphate waste powder |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN119253111A (en) * | 2024-09-27 | 2025-01-03 | 广东华菁新能源科技有限公司 | A method for recycling lithium iron phosphate positive electrode sheets suitable for retired lithium-ion power batteries |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN108899604B (en) | Method for preparing ternary positive electrode material precursor by utilizing waste lithium battery positive electrode piece | |
| CN105990617A (en) | Method for recycling and regenerating waste lithium ion battery electrode materials | |
| CN113562717B (en) | Method for recycling and regenerating waste lithium iron phosphate batteries at low temperature | |
| CN104466292B (en) | The method of Call Provision lithium metal from the used Li ion cell of lithium cobaltate cathode material | |
| CN106785177A (en) | A kind of method for being reclaimed from waste and old nickel-cobalt-manganese ternary lithium ion battery, preparing nickel cobalt manganese aluminium quaternary positive electrode | |
| CN109256596B (en) | Method and system for reversely preparing aluminum-doped ternary precursor | |
| CN105576314A (en) | Recycling method of positive electrode piece of lithium ion battery | |
| CN108285977A (en) | A kind of method of waste lithium ion cell anode material recovery | |
| CN103035977A (en) | Method for separating and recovering lithium from waste lithium ion battery | |
| CN111600089A (en) | A process for recycling and recycling cathode material of waste ternary lithium battery | |
| CN108103323B (en) | A kind of recycling method of positive electrode material of nickel-cobalt-manganese waste battery | |
| CN112186287A (en) | Ball-milling spray regeneration method for waste lithium ion battery anode material | |
| CN111261969A (en) | A method for recycling and regenerating cathode material of waste lithium iron phosphate battery | |
| CN111321297B (en) | Method for recovering valuable metals from waste lithium ion batteries | |
| CN116706304B (en) | A method for regenerating lithium-rich layered oxide cathode materials from spent lithium batteries | |
| CN104466293B (en) | The renovation process of lithium ion cell anode material lithium cobaltate waste material | |
| CN112591806A (en) | Method for recovering and regenerating anode active material of waste lithium ion battery | |
| CN110563046B (en) | Method for recycling waste lithium ion battery anode material | |
| CN114530641A (en) | Method for recycling waste lithium ion battery cathode | |
| CN115528340B (en) | A method for regenerating positive electrode materials of waste lithium-ion batteries | |
| CN110176647B (en) | Gradient utilization method for waste lithium ion battery negative electrode material | |
| CN117210685A (en) | Method for recycling valuable metals in retired lithium ion battery by using recyclable chelating agent | |
| CN108306071A (en) | A kind of waste lithium ion cell anode material recovery technique | |
| CN115679103A (en) | A recycling process for positive electrode materials of decommissioned ternary lithium batteries | |
| CN116119690A (en) | Method for selectively recycling lithium from waste lithium battery |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| PB01 | Publication | ||
| PB01 | Publication | ||
| SE01 | Entry into force of request for substantive examination | ||
| SE01 | Entry into force of request for substantive examination |