CN115172923B - Method for recycling battery powder through low-temperature pyrolysis - Google Patents
Method for recycling battery powder through low-temperature pyrolysis Download PDFInfo
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- 238000000197 pyrolysis Methods 0.000 title claims abstract description 106
- 238000000034 method Methods 0.000 title claims abstract description 50
- 239000000843 powder Substances 0.000 title claims abstract description 38
- 238000004064 recycling Methods 0.000 title claims description 8
- 239000000463 material Substances 0.000 claims abstract description 48
- 238000006243 chemical reaction Methods 0.000 claims abstract description 24
- 239000011888 foil Substances 0.000 claims abstract description 15
- 239000010926 waste battery Substances 0.000 claims abstract description 7
- JRBRVDCKNXZZGH-UHFFFAOYSA-N alumane;copper Chemical compound [AlH3].[Cu] JRBRVDCKNXZZGH-UHFFFAOYSA-N 0.000 claims abstract description 6
- 238000010438 heat treatment Methods 0.000 claims description 12
- HBBGRARXTFLTSG-UHFFFAOYSA-N Lithium ion Chemical compound [Li+] HBBGRARXTFLTSG-UHFFFAOYSA-N 0.000 claims description 11
- 229910001416 lithium ion Inorganic materials 0.000 claims description 11
- 238000011049 filling Methods 0.000 claims description 9
- 239000002245 particle Substances 0.000 claims description 9
- 230000035484 reaction time Effects 0.000 claims description 4
- WHXSMMKQMYFTQS-UHFFFAOYSA-N Lithium Chemical compound [Li] WHXSMMKQMYFTQS-UHFFFAOYSA-N 0.000 claims description 2
- 229910052744 lithium Inorganic materials 0.000 claims description 2
- 229910000625 lithium cobalt oxide Inorganic materials 0.000 claims description 2
- GELKBWJHTRAYNV-UHFFFAOYSA-K lithium iron phosphate Chemical compound [Li+].[Fe+2].[O-]P([O-])([O-])=O GELKBWJHTRAYNV-UHFFFAOYSA-K 0.000 claims description 2
- BFZPBUKRYWOWDV-UHFFFAOYSA-N lithium;oxido(oxo)cobalt Chemical compound [Li+].[O-][Co]=O BFZPBUKRYWOWDV-UHFFFAOYSA-N 0.000 claims description 2
- 238000012216 screening Methods 0.000 claims description 2
- QHGJSLXSVXVKHZ-UHFFFAOYSA-N dilithium;dioxido(dioxo)manganese Chemical compound [Li+].[Li+].[O-][Mn]([O-])(=O)=O QHGJSLXSVXVKHZ-UHFFFAOYSA-N 0.000 claims 1
- 238000007599 discharging Methods 0.000 claims 1
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 abstract description 18
- 229910052782 aluminium Inorganic materials 0.000 abstract description 17
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 abstract description 11
- 229910052802 copper Inorganic materials 0.000 abstract description 10
- 239000010949 copper Substances 0.000 abstract description 10
- 238000003795 desorption Methods 0.000 abstract description 10
- 230000003647 oxidation Effects 0.000 abstract description 4
- 238000007254 oxidation reaction Methods 0.000 abstract description 4
- 229920000642 polymer Polymers 0.000 abstract description 4
- 238000000926 separation method Methods 0.000 abstract description 2
- 239000007789 gas Substances 0.000 description 12
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 10
- 239000002699 waste material Substances 0.000 description 8
- 230000000052 comparative effect Effects 0.000 description 7
- 239000002932 luster Substances 0.000 description 7
- 238000012544 monitoring process Methods 0.000 description 7
- 239000011149 active material Substances 0.000 description 5
- 239000012670 alkaline solution Substances 0.000 description 5
- 229910002092 carbon dioxide Inorganic materials 0.000 description 5
- 239000011230 binding agent Substances 0.000 description 4
- 238000001816 cooling Methods 0.000 description 4
- 229910052751 metal Inorganic materials 0.000 description 4
- 239000002184 metal Substances 0.000 description 4
- 239000002033 PVDF binder Substances 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 239000003792 electrolyte Substances 0.000 description 3
- 229920002981 polyvinylidene fluoride Polymers 0.000 description 3
- 239000003832 thermite Substances 0.000 description 3
- 239000011203 carbon fibre reinforced carbon Substances 0.000 description 2
- 239000006258 conductive agent Substances 0.000 description 2
- 229920000620 organic polymer Polymers 0.000 description 2
- 239000003960 organic solvent Substances 0.000 description 2
- 238000007789 sealing Methods 0.000 description 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 1
- 101001121408 Homo sapiens L-amino-acid oxidase Proteins 0.000 description 1
- 102100026388 L-amino-acid oxidase Human genes 0.000 description 1
- 229910032387 LiCoO2 Inorganic materials 0.000 description 1
- 229910052493 LiFePO4 Inorganic materials 0.000 description 1
- 229910002993 LiMnO2 Inorganic materials 0.000 description 1
- 229910003005 LiNiO2 Inorganic materials 0.000 description 1
- 206010024769 Local reaction Diseases 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 238000007133 aluminothermic reaction Methods 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 238000009835 boiling Methods 0.000 description 1
- 239000001569 carbon dioxide Substances 0.000 description 1
- 238000006555 catalytic reaction Methods 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 239000011530 conductive current collector Substances 0.000 description 1
- 239000011889 copper foil Substances 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 239000010439 graphite Substances 0.000 description 1
- 229910002804 graphite Inorganic materials 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 238000009776 industrial production Methods 0.000 description 1
- 150000002500 ions Chemical class 0.000 description 1
- 238000002386 leaching Methods 0.000 description 1
- 229910002102 lithium manganese oxide Inorganic materials 0.000 description 1
- VLXXBCXTUVRROQ-UHFFFAOYSA-N lithium;oxido-oxo-(oxomanganiooxy)manganese Chemical compound [Li+].[O-][Mn](=O)O[Mn]=O VLXXBCXTUVRROQ-UHFFFAOYSA-N 0.000 description 1
- URIIGZKXFBNRAU-UHFFFAOYSA-N lithium;oxonickel Chemical compound [Li].[Ni]=O URIIGZKXFBNRAU-UHFFFAOYSA-N 0.000 description 1
- 238000006386 neutralization reaction Methods 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 239000007774 positive electrode material Substances 0.000 description 1
- 238000002203 pretreatment Methods 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 150000003254 radicals Chemical class 0.000 description 1
- 239000002893 slag Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000000243 solution Substances 0.000 description 1
- 238000005979 thermal decomposition reaction Methods 0.000 description 1
- 229910052723 transition metal Inorganic materials 0.000 description 1
- 150000003624 transition metals Chemical class 0.000 description 1
Classifications
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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
-
- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B15/00—Obtaining copper
- C22B15/0002—Preliminary treatment
- C22B15/0004—Preliminary treatment without modification of the copper constituent
- C22B15/0006—Preliminary treatment without modification of the copper constituent by dry processes
-
- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B21/00—Obtaining aluminium
- C22B21/0038—Obtaining aluminium by other processes
- C22B21/0069—Obtaining aluminium by other processes from scrap, skimmings or any secondary source aluminium, e.g. recovery of alloy constituents
-
- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B7/00—Working up raw materials other than ores, e.g. scrap, to produce non-ferrous metals and compounds thereof; Methods of a general interest or applied to the winning of more than two metals
- C22B7/001—Dry processes
-
- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B7/00—Working up raw materials other than ores, e.g. scrap, to produce non-ferrous metals and compounds thereof; Methods of a general interest or applied to the winning of more than two metals
- C22B7/005—Separation by a physical processing technique only, e.g. by mechanical breaking
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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
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E60/00—Enabling technologies; Technologies with a potential or indirect contribution to GHG emissions mitigation
- Y02E60/10—Energy storage using 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
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P10/00—Technologies related to metal processing
- Y02P10/20—Recycling
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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
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- Geology (AREA)
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Abstract
本发明公开了一种低温热解脱附回收电池粉的方法,将废旧电池破碎料在混合气氛及气压为3‑8MPa、温度为120‑150℃下进行反应,混合气氛为CO2、NO、O2的混合气体,将所得反应物料在负压及310‑360℃下进行反应,然后分选得到铜铝箔和电池粉。本发明采用低温高压热解及中温负压热解的联合工艺,全过程的温度控制在400℃以下,即可达到与集流体分离的目的,既实现了聚合物的断链,又避免了铜铝的氧化。
The invention discloses a method for recovering battery powder by low-temperature pyrolysis and desorption, wherein the waste battery crushed material is reacted in a mixed atmosphere with a pressure of 3-8 MPa and a temperature of 120-150°C, wherein the mixed atmosphere is a mixed gas of CO2 , NO, and O2 , and the obtained reaction materials are reacted at a negative pressure and 310-360°C, and then the copper-aluminum foil and the battery powder are sorted. The invention adopts a combined process of low-temperature and high-pressure pyrolysis and medium-temperature and negative-pressure pyrolysis, and the temperature of the whole process is controlled below 400°C, so as to achieve the purpose of separation from the current collector, realize the chain breaking of the polymer, and avoid the oxidation of copper and aluminum.
Description
技术领域Technical Field
本发明属于电池回收技术领域,具体涉及一种低温热解脱附回收电池粉的方法。The invention belongs to the technical field of battery recycling, and in particular relates to a method for recycling battery powder by low-temperature thermal desorption.
背景技术Background Art
锂离子电池结构复杂,由外壳、隔膜、正极、负极等多个部件组成,在回收废旧电池过程中,有必要通过一系列方法使其不同部件分离。其中,负极由石墨、黏结剂、导电剂和集流体铜箔组成,正极由活性物质粉末、黏结剂以及导电剂涂覆在集流体铝箔上制成,正极活性物质粉末主要有LiCoO2,LiNiO2,LiMnO2,LiFePO4以及LiNixCoyMn1-x-yO2等。Lithium-ion batteries have a complex structure, consisting of multiple parts such as the outer shell, diaphragm, positive electrode, and negative electrode. In the process of recycling used batteries, it is necessary to separate the different parts through a series of methods. Among them, the negative electrode is composed of graphite, binder, conductive agent and current collector copper foil, and the positive electrode is made of active material powder, binder and conductive agent coated on the current collector aluminum foil. The positive electrode active material powder mainly includes LiCoO2 , LiNiO2 , LiMnO2 , LiFePO4 and LiNixCoyMn1 -xyO2 , etc.
废旧锂离子电池回收的前处理过程通常需要一定的技术手段使活性物质粉末从集流体上脱附分离。The pre-treatment process of recycling waste lithium-ion batteries usually requires certain technical means to desorb and separate the active material powder from the current collector.
目前,分离活性材料与集流体主要从三个方面入手:①根据金属铝可以溶解在碱性溶液中的特性,将正极卷芯浸泡在碱性溶液中可以达到正极粉末与集流体分离的目的,该方法具有能耗低、操作性强等优势,但集流体铝箔以离子的形式进入溶液中,需要进一步进行回收处理。此外,该过程需要大量的碱溶液,为防止碱液产生二次污染,需要进行中和处理,这样将需要额外的成本开销,为避免引入的碱液对粉料产生污染,在过滤过程中,要对脱附活性物质进行充分冲洗或酸中和;②采用有机溶剂溶解粘结剂PVDF,使集流体金属箔可以固体的形式得到回收,但有机溶剂价格通常昂贵,不太适合大模工业应用;③于空气中直接加热到特定温度可以使黏结剂失活以达到分离集流体铝箔的目的,也是目前报道最多的锂电池回收热解预处理工艺。At present, the separation of active materials and current collectors mainly starts from three aspects: ① Based on the characteristic that metal aluminum can be dissolved in alkaline solution, the positive electrode core can be immersed in alkaline solution to achieve the purpose of separating positive electrode powder from current collector. This method has the advantages of low energy consumption and strong operability, but the current collector aluminum foil enters the solution in the form of ions and needs further recycling. In addition, this process requires a large amount of alkaline solution. In order to prevent secondary pollution from the alkaline solution, neutralization treatment is required, which will require additional cost expenditure. In order to avoid the introduction of alkaline solution to pollute the powder, the desorbed active material must be fully rinsed or acid-neutralized during the filtration process; ② The binder PVDF is dissolved by organic solvents so that the current collector metal foil can be recovered in solid form, but the price of organic solvents is usually expensive and not suitable for large-scale industrial applications; ③ Directly heating to a specific temperature in the air can inactivate the binder to achieve the purpose of separating the current collector aluminum foil, which is also the most reported lithium battery recycling pyrolysis pretreatment process.
热解预处理工艺在现有的工业生产中使用的较为广泛,但其中也存在一些较大的问题,如:①常规热解的温度在500℃以上,由于物料种类复杂,在此温度下,电解液及隔膜出现燃烧,极易造成热解炉内局部反应剧烈,造成温度失控,电池中的铝金属在600℃以上时会发生铝热反应,导致瞬间温度急剧上升,烧穿热解炉,带来较大的安全风险;②在此温度下,电池中的金属铜铝被大量氧化,导致电池粉中杂质含量高,且在后续酸液浸出时,氧化物溶解,产生大量的铜铝渣,给后续净化提纯带来了较大压力。The pyrolysis pretreatment process is widely used in existing industrial production, but there are also some major problems, such as: ① The temperature of conventional pyrolysis is above 500°C. Due to the complex types of materials, at this temperature, the electrolyte and diaphragm will burn, which can easily cause violent local reactions in the pyrolysis furnace and cause temperature out of control. The aluminum metal in the battery will undergo a thermite reaction at above 600°C, resulting in a sharp rise in instantaneous temperature, burning through the pyrolysis furnace, and posing a greater safety risk; ② At this temperature, the metallic copper and aluminum in the battery are oxidized in large quantities, resulting in a high impurity content in the battery powder, and during the subsequent acid leaching, the oxides dissolve to produce a large amount of copper and aluminum slag, which brings great pressure to the subsequent purification.
发明内容Summary 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,本发明提出一种低温热解脱附回收电池粉的方法,该方法能使废旧电池活性材料在较低温度下即可达到与集流体分离的目的。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 recovering battery powder by low-temperature pyrolysis desorption, which can separate the active materials of waste batteries from the current collector at a relatively low temperature.
根据本发明的一个方面,提出了一种低温热解脱附回收电池粉的方法,包括以下步骤:According to one aspect of the present invention, a method for recovering battery powder by low-temperature pyrolysis is proposed, comprising the following steps:
S1:废旧电池经放电、拆解、破碎,得到破碎料;S1: Waste batteries are discharged, disassembled and crushed to obtain crushed materials;
S2:将所述破碎料在混合气氛及气压为3-8MPa、温度为120-150℃下进行反应,所述混合气氛为CO2、NO、O2的混合气体,其体积比为100:(10-15):(0-2);S2: reacting the crushed material in a mixed atmosphere with a pressure of 3-8 MPa and a temperature of 120-150° C., wherein the mixed atmosphere is a mixed gas of CO2, NO, and O2 in a volume ratio of 100:(10-15):(0-2);
S3:将步骤S2所得反应物料在负压及310-360℃下进行反应,然后分选得到铜铝箔和电池粉。S3: reacting the reaction materials obtained in step S2 under negative pressure at 310-360° C., and then sorting to obtain copper-aluminum foil and battery powder.
在本发明的一些实施方式中,步骤S1中,所述破碎料的粒度为5cm以下。In some embodiments of the present invention, in step S1, the particle size of the crushed material is less than 5 cm.
在本发明的一些实施方式中,步骤S1中,所述废旧电池为三元锂离子电池、磷酸铁锂电池、钴酸锂电池、锰酸锂电池或镍酸锂电池中的至少一种。In some embodiments of the present invention, in step S1, the waste battery is at least one of a ternary lithium-ion battery, a lithium iron phosphate battery, a lithium cobalt oxide battery, a lithium manganese oxide battery or a lithium nickel oxide battery.
在本发明的一些实施方式中,步骤S2中,所述反应的时间为3-5h。In some embodiments of the present invention, in step S2, the reaction time is 3-5 hours.
在本发明的一些实施方式中,步骤S2中,所述反应在热解炉中进行,控制所述破碎料在所述热解炉中的填充率为5-15%。In some embodiments of the present invention, in step S2, the reaction is carried out in a pyrolysis furnace, and the filling rate of the crushed material in the pyrolysis furnace is controlled to be 5-15%.
在本发明的一些实施方式中,步骤S3中,所述负压的压力为-0.01~-0.08MPa。In some embodiments of the present invention, in step S3, the negative pressure is -0.01 to -0.08 MPa.
在本发明的一些实施方式中,步骤S3中,所述反应的时间为1-3h。In some embodiments of the present invention, in step S3, the reaction time is 1-3 hours.
在本发明的一些实施方式中,步骤S2所述反应结束后,以0.1-0.5MPa/min的速率释放热解炉内的压力至常压,再启动真空泵抽至所述负压。In some embodiments of the present invention, after the reaction in step S2 is completed, the pressure in the pyrolysis furnace is released to normal pressure at a rate of 0.1-0.5 MPa/min, and then the vacuum pump is started to evacuate to the negative pressure.
在本发明的一些实施方式中,步骤S3中,以5-10℃/min的升温速率加热至反应温度。In some embodiments of the present invention, in step S3, heating is performed to the reaction temperature at a heating rate of 5-10°C/min.
在本发明的一些实施方式中,步骤S3所得铜铝箔中,铜含量不低于45wt%,铝含量不低于35wt%。In some embodiments of the present invention, the copper content of the copper-aluminum foil obtained in step S3 is not less than 45wt%, and the aluminum content is not less than 35wt%.
在本发明的一些实施方式中,步骤S3所得电池粉中,铝含量不高于0.5wt%。In some embodiments of the present invention, the aluminum content in the battery powder obtained in step S3 is not higher than 0.5 wt %.
在本发明的一些实施方式中,步骤S3中,所述分选的过程为:使用双层筛网进行筛分,得到的上层为所述铜铝箔,底层为所述电池粉。In some embodiments of the present invention, in step S3, the sorting process is: using a double-layer sieve for screening, and the upper layer obtained is the copper-aluminum foil, and the bottom layer is the battery powder.
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, at least the following beneficial effects are achieved:
1、本发明方案中,针对废旧电池在较高热解温度下极易出现安全隐患及铜铝大面积被氧化的问题,采用低温高压热解及中温负压热解的联合工艺,并使全过程的温度控制在400℃以下,中温负压热解在无氧条件下进行,避免了破碎料中电解液及隔膜的燃烧,导致温度失控的现象,保护了热解炉,降低了铜铝氧化的程度。1. In the scheme of the present invention, in order to solve the problem that waste batteries are prone to safety hazards and large-area oxidation of copper and aluminum at high pyrolysis temperatures, a combined process of low-temperature and high-pressure pyrolysis and medium-temperature and negative-pressure pyrolysis is adopted, and the temperature of the whole process is controlled below 400°C. The medium-temperature and negative-pressure pyrolysis is carried out under anaerobic conditions, which avoids the combustion of electrolyte and diaphragm in the crushed material and the phenomenon of temperature runaway, protects the pyrolysis furnace, and reduces the degree of copper and aluminum oxidation.
2、在高压混合气体通入的情况下,利用NO作为单电子自由基,在100℃以上时具备较高的活性,在痕量氧的催化下,可随机的进攻有机聚合物中的碳碳键,使聚合物断链形成小分子化合物,降低了聚合物的热分解温度,参考以下反应式:2. When high-pressure mixed gas is introduced, NO is used as a single-electron free radical, which has high activity above 100°C. Under the catalysis of trace oxygen, it can randomly attack the carbon-carbon bonds in organic polymers, causing the polymer chains to break to form small molecular compounds, thereby reducing the thermal decomposition temperature of the polymer. Refer to the following reaction formula:
·NO+[-CH2-CF2-]→R1-CH2-N=O+R2-CF2-N=O。·NO+[-CH 2 -CF 2 -]→R1-CH 2 -N=O+R 2 -CF 2 -N=O.
利用PVDF对二氧化碳特有的吸收特性,可出现较大的体积膨胀,对PVDF造成一定的机械损伤,利于NO更深入的对碳碳键进行断链。By utilizing PVDF's unique absorption characteristics for carbon dioxide, a large volume expansion can occur, causing certain mechanical damage to PVDF, which is conducive to NO's deeper chain breaking of carbon-carbon bonds.
在本发明较低的温度下,实现了聚合物的断链,并避免了铜铝的氧化,更避免了铝热反应的发生。At a relatively low temperature, the polymer chain is broken, the oxidation of copper and aluminum is avoided, and the occurrence of thermite reaction is avoided.
3、在负压热解时,断链后的有机聚合物在稍高温度下,即可分解及碳化,无需加热到500℃以上,且其中的电解液等在负压下极易达到沸点,并以气态进入废气处理系统,同时,铜铝不会被氧化,铝热反应更不会发生,达到了电池粉与铜铝箔分离脱附的目的。3. During negative pressure pyrolysis, the organic polymer after chain breaking can be decomposed and carbonized at a slightly higher temperature without heating to above 500°C. The electrolyte in it can easily reach the boiling point under negative pressure and enter the exhaust gas treatment system in gaseous state. At the same time, copper and aluminum will not be oxidized, and thermite reaction will not occur, thus achieving the purpose of separating and desorbing battery powder from copper and aluminum foil.
附图说明BRIEF DESCRIPTION OF THE DRAWINGS
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 with reference to the accompanying drawings and embodiments, wherein:
图1为本发明的工艺流程图。Fig. 1 is a process flow chart of the present invention.
具体实施方式DETAILED DESCRIPTION
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 following will be combined with the embodiments to clearly and completely describe the concept of the present invention and the technical effects produced, so as to fully understand the purpose, characteristics and effects of the present invention. Obviously, the described embodiments are only part 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 creative work are all within the scope of protection of the present invention.
实施例1Example 1
一种低温热解脱附回收电池粉的方法,参照图1,具体过程为:A method for recovering battery powder by low-temperature pyrolysis and desorption, referring to FIG1 , the specific process is as follows:
步骤1,废旧三元锂离子电池经放电、拆解后,破碎成粒度为5cm以下的破碎料;Step 1, after the waste ternary lithium-ion batteries are discharged and disassembled, they are crushed into crushed materials with a particle size of less than 5 cm;
步骤2,将破碎料加入热解炉中,控制热解炉填充率为5%,并通入高压混合气体,密闭,控制热解炉内气压为3MPa,温度为120℃,持续5h,高压混合气体CO2、NO、O2的混合气体,体积比为100:10:0.1;Step 2, add the crushed material into the pyrolysis furnace, control the filling rate of the pyrolysis furnace to 5%, and introduce high-pressure mixed gas, close the furnace, control the pressure in the pyrolysis furnace to 3MPa, the temperature to 120℃, and continue for 5h. The high-pressure mixed gas is a mixed gas of CO2 , NO, and O2 , with a volume ratio of 100:10:0.1;
步骤3,反应结束后,以0.1MPa/min释放炉内压力至常压,并启动真空泵抽负压,控制热解炉内压力为-0.01MPa,并以5℃/min的升温速率升温至310℃,持续3h;Step 3: After the reaction is completed, the pressure in the furnace is released to normal pressure at a rate of 0.1 MPa/min, and the vacuum pump is started to extract negative pressure, the pressure in the pyrolysis furnace is controlled to be -0.01 MPa, and the temperature is increased to 310°C at a heating rate of 5°C/min for 3 hours;
步骤4,热解反应结束后,将热解炉中的物料使用双层筛网进行筛分,得到上层为热解后的铜铝箔、底层为热解过程中脱下的电池粉。Step 4, after the pyrolysis reaction is completed, the material in the pyrolysis furnace is screened using a double-layer screen to obtain an upper layer of copper and aluminum foil after pyrolysis and a bottom layer of battery powder removed during the pyrolysis process.
监测热解炉内情况:在高压热解时,仅观测到破碎料表层似有液滴溶出,体积出现微微膨胀,未观测到其它明显变化;在负压热解时,炉内温度保持恒定,粉料明显脱落,出现金属光泽。Monitoring the situation in the pyrolysis furnace: During high-pressure pyrolysis, only droplets were observed to dissolve out of the surface of the crushed material, and the volume expanded slightly, and no other obvious changes were observed; during negative-pressure pyrolysis, the temperature in the furnace remained constant, the powder fell off obviously, and a metallic luster appeared.
实施例2Example 2
一种低温热解脱附回收电池粉的方法,具体过程为:A method for recovering battery powder by low-temperature pyrolysis desorption, the specific process is as follows:
步骤1,废旧三元锂离子电池经放电、拆解后,破碎成粒度为5cm以下的破碎料;Step 1, after the waste ternary lithium-ion batteries are discharged and disassembled, they are crushed into crushed materials with a particle size of less than 5 cm;
步骤2,将破碎料加入热解炉中,控制热解炉填充率为10%,并通入高压混合气体,密闭,控制热解炉内气压为5MPa,温度为130℃,持续4h;高压混合气体CO2、NO、O2的混合气体,体积比为100:13:1;Step 2, adding the crushed material into the pyrolysis furnace, controlling the filling rate of the pyrolysis furnace to 10%, and introducing high-pressure mixed gas, sealing, controlling the pressure in the pyrolysis furnace to 5MPa, the temperature to 130°C, and continuing for 4h; the high-pressure mixed gas is a mixed gas of CO2, NO, and O2, with a volume ratio of 100:13:1;
步骤3,反应结束后,以0.3MPa/min释放炉内压力至常压,并启动真空泵抽负压,控制热解炉内压力为-0.04MPa,并以8℃/min的升温速率升温至340℃,持续2h;Step 3: After the reaction is completed, the pressure in the furnace is released to normal pressure at 0.3 MPa/min, and the vacuum pump is started to extract negative pressure, the pressure in the pyrolysis furnace is controlled to be -0.04 MPa, and the temperature is increased to 340°C at a heating rate of 8°C/min for 2 hours;
步骤4,热解反应结束后,将热解炉中的物料使用双层筛网进行筛分,得到上层为热解后的电池料、底层为热解过程中脱下的电池粉。Step 4, after the pyrolysis reaction is completed, the material in the pyrolysis furnace is screened using a double-layer screen to obtain an upper layer of battery material after pyrolysis and a bottom layer of battery powder removed during the pyrolysis process.
监测热解炉内情况:在高压热解时,仅观测到破碎料表层似有液滴溶出,体积出现微微膨胀,未观测到其它明显变化;在负压热解时,炉内温度保持恒定,粉料明显脱落,出现金属光泽。Monitoring the situation in the pyrolysis furnace: During high-pressure pyrolysis, only droplets were observed to dissolve out of the surface of the crushed material, and the volume expanded slightly, and no other obvious changes were observed; during negative-pressure pyrolysis, the temperature in the furnace remained constant, the powder fell off obviously, and a metallic luster appeared.
实施例3Example 3
一种低温热解脱附回收电池粉的方法,具体过程为:A method for recovering battery powder by low-temperature thermal desorption, the specific process is as follows:
步骤1,废旧三元锂离子电池经放电、拆解后,破碎成粒度为5cm以下的破碎料;Step 1, after the waste ternary lithium-ion batteries are discharged and disassembled, they are crushed into crushed materials with a particle size of less than 5 cm;
步骤2,将破碎料加入热解炉中,控制热解炉填充率为15%,并通入高压混合气体,密闭,控制热解炉内气压为8MPa,温度为150℃,持续3h;高压混合气体CO2、NO、O2的混合气体,体积比为100:15:2;Step 2, adding the crushed material into the pyrolysis furnace, controlling the filling rate of the pyrolysis furnace to 15%, and introducing high-pressure mixed gas, sealing, controlling the pressure in the pyrolysis furnace to 8MPa, the temperature to 150°C, and continuing for 3h; the high-pressure mixed gas is a mixed gas of CO2, NO, and O2, with a volume ratio of 100:15:2;
步骤3,反应结束后,以0.5MPa/min释放炉内压力至常压,并启动真空泵抽负压,控制热解炉内压力为-0.08MPa,并以10℃/min的升温速率升温至360℃,持续1h;Step 3: After the reaction is completed, the pressure in the furnace is released to normal pressure at a rate of 0.5 MPa/min, and the vacuum pump is started to extract negative pressure, the pressure in the pyrolysis furnace is controlled to be -0.08 MPa, and the temperature is increased to 360°C at a heating rate of 10°C/min for 1 hour;
步骤4,热解反应结束后,将热解炉中的物料使用双层筛网进行筛分,得到上层为热解后的电池料、底层为热解过程中脱下的电池粉。Step 4, after the pyrolysis reaction is completed, the material in the pyrolysis furnace is screened using a double-layer screen to obtain an upper layer of battery material after pyrolysis and a bottom layer of battery powder removed during the pyrolysis process.
监测热解炉内情况:在高压热解时,仅观测到破碎料表层似有液滴溶出,体积出现微微膨胀,未观测到其它明显变化;在负压热解时,炉内温度保持恒定,粉料明显脱落,出现金属光泽。Monitoring the situation in the pyrolysis furnace: During high-pressure pyrolysis, only droplets were observed to dissolve out of the surface of the crushed material, and the volume expanded slightly, and no other obvious changes were observed; during negative-pressure pyrolysis, the temperature in the furnace remained constant, the powder fell off obviously, and a metallic luster appeared.
对比例1Comparative Example 1
一种热解脱附回收电池粉的方法,与实施例1的区别在于,不进行低温高压热解,具体过程为:A method for recovering battery powder by pyrolysis desorption is different from Example 1 in that low-temperature and high-pressure pyrolysis is not performed. The specific process is as follows:
步骤1,废旧三元锂离子电池经放电、拆解后,破碎成粒度为5cm以下的破碎料;Step 1, after the waste ternary lithium-ion batteries are discharged and disassembled, they are crushed into crushed materials with a particle size of less than 5 cm;
步骤2,将破碎料加入热解炉中,控制热解炉填充率为5%;Step 2, adding the crushed material into the pyrolysis furnace, and controlling the filling rate of the pyrolysis furnace to be 5%;
步骤3,启动真空泵抽负压,控制热解炉内压力为-0.01MPa,并以5℃/min的升温速率升温至310℃,持续3h;Step 3, start the vacuum pump to draw negative pressure, control the pressure in the pyrolysis furnace to -0.01 MPa, and heat up to 310°C at a heating rate of 5°C/min for 3 hours;
步骤4,热解反应结束后,将热解炉中的物料使用双层筛网进行筛分,得到上层为热解后的电池料、底层为热解过程中脱下的电池粉。Step 4, after the pyrolysis reaction is completed, the material in the pyrolysis furnace is screened using a double-layer screen to obtain an upper layer of battery material after pyrolysis and a bottom layer of battery powder removed during the pyrolysis process.
监测热解炉内情况:在负压热解时,炉内温度保持恒定,碎料表层出现熔融态液滴,冷却后团聚,未出现明显的金属光泽。Monitoring the conditions in the pyrolysis furnace: During negative pressure pyrolysis, the temperature in the furnace remains constant, molten droplets appear on the surface of the crushed materials, and agglomerate after cooling, without showing obvious metallic luster.
对比例2Comparative Example 2
一种热解脱附回收电池粉的方法,与实施例2的区别在于,不进行低温高压热解,具体过程为:A method for recovering battery powder by pyrolysis desorption is different from Example 2 in that low-temperature and high-pressure pyrolysis is not performed. The specific process is as follows:
步骤1,废旧三元锂离子电池经放电、拆解后,破碎成粒度为5cm以下的破碎料;Step 1, after the waste ternary lithium-ion batteries are discharged and disassembled, they are crushed into crushed materials with a particle size of less than 5 cm;
步骤2,将破碎料加入热解炉中,控制热解炉填充率为10%;Step 2, adding the crushed material into the pyrolysis furnace, and controlling the filling rate of the pyrolysis furnace to be 10%;
步骤3,启动真空泵抽负压,控制热解炉内压力为-0.04MPa,并以8℃/min的升温速率升温至340℃,持续2h;Step 3, start the vacuum pump to draw negative pressure, control the pressure in the pyrolysis furnace to -0.04 MPa, and heat up to 340°C at a heating rate of 8°C/min for 2 hours;
步骤4,热解反应结束后,将热解炉中的物料使用双层筛网进行筛分,得到上层为热解后的电池料、底层为热解过程中脱下的电池粉。Step 4, after the pyrolysis reaction is completed, the material in the pyrolysis furnace is screened using a double-layer screen to obtain an upper layer of battery material after pyrolysis and a bottom layer of battery powder removed during the pyrolysis process.
监测热解炉内情况:在负压热解时,炉内温度保持恒定,碎料表层出现熔融态液滴,冷却后团聚,未出现明显的金属光泽。Monitoring the conditions in the pyrolysis furnace: During negative pressure pyrolysis, the temperature in the furnace remains constant, molten droplets appear on the surface of the crushed materials, and agglomerate after cooling, without showing obvious metallic luster.
对比例3Comparative Example 3
一种热解脱附回收电池粉的方法,与实施例3的区别在于,不进行低温高压热解,具体过程为:A method for recovering battery powder by pyrolysis desorption, which differs from Example 3 in that low-temperature and high-pressure pyrolysis is not performed, and the specific process is as follows:
步骤1,废旧三元锂离子电池经放电、拆解后,破碎成粒度为5cm以下的破碎料;Step 1, after the waste ternary lithium-ion batteries are discharged and disassembled, they are crushed into crushed materials with a particle size of less than 5 cm;
步骤2,将破碎料加入热解炉中,控制热解炉填充率为15%;Step 2, adding the crushed material into the pyrolysis furnace, and controlling the filling rate of the pyrolysis furnace to be 15%;
步骤3,启动真空泵抽负压,控制热解炉内压力为-0.08MPa,并以10℃/min的升温速率升温至360℃,持续1h;Step 3, start the vacuum pump to draw negative pressure, control the pressure in the pyrolysis furnace to -0.08MPa, and heat up to 360°C at a heating rate of 10°C/min for 1h;
步骤4,热解反应结束后,将热解炉中的物料使用双层筛网进行筛分,得到上层为热解后的电池料、底层为热解过程中脱下的电池粉。Step 4, after the pyrolysis reaction is completed, the material in the pyrolysis furnace is screened using a double-layer screen to obtain an upper layer of battery material after pyrolysis and a bottom layer of battery powder removed during the pyrolysis process.
监测热解炉内情况:在负压热解时,炉内温度保持恒定,碎料表层出现熔融态液滴,冷却后团聚,未出现明显的金属光泽。Monitoring the conditions in the pyrolysis furnace: During negative pressure pyrolysis, the temperature in the furnace remains constant, molten droplets appear on the surface of the crushed materials, and they agglomerate after cooling, without showing obvious metallic luster.
对比例4Comparative Example 4
一种热解脱附回收电池粉的方法,与实施例2的区别在于,不进行低温高压热解,且提高步骤3的热解温度,具体过程为:A method for recovering battery powder by pyrolysis desorption is different from that in Example 2 in that low-temperature and high-pressure pyrolysis is not performed and the pyrolysis temperature of step 3 is increased. The specific process is as follows:
步骤1,废旧三元锂离子电池经放电、拆解后,破碎成粒度为5cm以下的破碎料;Step 1, after the waste ternary lithium-ion batteries are discharged and disassembled, they are crushed into crushed materials with a particle size of less than 5 cm;
步骤2,将破碎料加入热解炉中,控制热解炉填充率为10%;Step 2, adding the crushed material into the pyrolysis furnace, and controlling the filling rate of the pyrolysis furnace to be 10%;
步骤3,启动真空泵抽负压,控制热解炉内压力为-0.04MPa,并以8℃/min的升温速率升温至450℃,持续1h;Step 3, start the vacuum pump to draw negative pressure, control the pressure in the pyrolysis furnace to -0.04 MPa, and heat up to 450°C at a heating rate of 8°C/min for 1 hour;
步骤4,热解反应结束后,将热解炉中的物料使用双层筛网进行筛分,得到上层为热解后的电池料、底层为热解过程中脱下的电池粉。Step 4, after the pyrolysis reaction is completed, the material in the pyrolysis furnace is screened using a double-layer screen to obtain an upper layer of battery material after pyrolysis and a bottom layer of battery powder removed during the pyrolysis process.
监测热解炉内情况:在负压热解时,炉内温度达到450℃后,出现火苗,温度不受控制,自行升高,迅速出现火星四溅的现象,物料呈现通红的熔融态,冷却后,也未出现明显的金属光泽。Monitoring the situation inside the pyrolysis furnace: During negative pressure pyrolysis, when the temperature inside the furnace reaches 450°C, flames appear, the temperature becomes uncontrolled and rises on its own, sparks quickly fly, and the material appears in a red molten state. After cooling, no obvious metallic luster appears.
对实施例1-3和对比例1-4所得电池粉和金属箔进行检测,其结果如表1所示。The battery powder and metal foil obtained in Examples 1-3 and Comparative Examples 1-4 were tested, and the results are shown in Table 1.
表1Table 1
对比例1-3中,金属箔残留大量的过渡金属,说明热解温度不足,热解反应难以完全发生;对比例4明显出现了铝热反应,所有的铝基本上都被氧化进入黑粉中,没有得到成型的铝箔。In Comparative Examples 1-3, a large amount of transition metal remained in the metal foil, indicating that the pyrolysis temperature was insufficient and the pyrolysis reaction was difficult to occur completely; in Comparative Example 4, an aluminothermic reaction obviously occurred, and basically all the aluminum was oxidized into the black powder, and no formed aluminum foil was obtained.
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 are described in detail above in conjunction with the accompanying drawings, but the present invention is not limited to the above embodiments. Various changes can be made within the knowledge of ordinary technicians in the relevant technical field without departing from the purpose of the present invention. In addition, the embodiments of the present invention and the features in the embodiments can be combined with each other without conflict.
Claims (10)
Priority Applications (7)
Application Number | Priority Date | Filing Date | Title |
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CN202210716640.7A CN115172923B (en) | 2022-06-23 | 2022-06-23 | Method for recycling battery powder through low-temperature pyrolysis |
ES202390219A ES2995435A1 (en) | 2022-06-23 | 2022-09-20 | Method for recovering battery powder by low-temperature pyrolysis desorption |
HU2400037A HU231613B1 (en) | 2022-06-23 | 2022-09-20 | Method for recovering battery powder by low-temperature pyrolysis desorption |
PCT/CN2022/119978 WO2023245889A1 (en) | 2022-06-23 | 2022-09-20 | Method for recovering battery powder by low-temperature pyrolysis desorption |
MX2023014862A MX2023014862A (en) | 2022-06-23 | 2022-09-20 | METHOD TO RECOVER BATTERY DUST BY DESORPTION BY PYROLYSIS AT LOW TEMPERATURE. |
GB2318191.0A GB2624545A (en) | 2022-06-23 | 2022-09-20 | Method for recovering battery powder by low-temperature pyrolysis desorption |
DE112022002405.4T DE112022002405T5 (en) | 2022-06-23 | 2022-09-20 | METHOD FOR RECOVERY OF BATTERY POWDER BY LOW TEMPERATURE PYROLYSIS DESORPTION |
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CN115911635A (en) * | 2022-12-22 | 2023-04-04 | 广东邦普循环科技有限公司 | Low-copper aluminum fluoride-free black powder and preparation method thereof |
WO2024207144A1 (en) * | 2023-04-03 | 2024-10-10 | 广东邦普循环科技有限公司 | Method for removing pvdf in waste lithium battery in whole industry chain of lithium batteries |
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CN112139203A (en) * | 2020-08-24 | 2020-12-29 | 广东邦普循环科技有限公司 | Vacuum cracking method and cracking equipment for power battery |
CN113764758A (en) * | 2021-07-26 | 2021-12-07 | 广东邦普循环科技有限公司 | Method for recycling, pyrolyzing and controlling temperature of waste lithium battery and application |
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CN103730704B (en) * | 2014-01-20 | 2016-03-16 | 赣州市豪鹏科技有限公司 | A kind of processing method of waste secondary battery |
CN105489959A (en) * | 2014-09-30 | 2016-04-13 | 上海比亚迪有限公司 | Recycling method for lithium ion secondary battery negative electrode material |
CN104659437B (en) * | 2015-02-04 | 2017-01-11 | 广州鹏辉能源科技股份有限公司 | Method for efficiently recycling waste battery current collector |
JP6859598B2 (en) * | 2016-03-18 | 2021-04-14 | 三菱マテリアル株式会社 | How to recover valuables from used lithium-ion batteries |
CN109599602B (en) * | 2018-11-30 | 2021-07-13 | 成都尤尼瑞克科技有限公司 | Method for resource utilization of waste positive electrode material of lithium battery |
CN111799522B (en) * | 2019-04-09 | 2023-01-10 | 锂源(深圳)科学研究有限公司 | Method for recovering positive electrode material, positive electrode material obtained by the method, and use of the positive electrode material |
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CN111313121B (en) * | 2020-03-31 | 2024-07-09 | 长沙矿冶研究院有限责任公司 | Method and system for preparing anode and cathode waste powder by crushing lithium battery |
CN113161640B (en) * | 2021-02-03 | 2022-10-18 | 顺尔茨环保(北京)有限公司 | System and method for recycling black powder through multistage pyrolysis of waste lithium batteries |
CN114147043B (en) * | 2021-09-30 | 2024-05-10 | 湖南江冶新能源科技股份有限公司 | Sorting method for recycling anode and cathode powder of waste lithium batteries |
CN114381603B (en) * | 2022-01-17 | 2024-07-05 | 湖南江冶机电科技股份有限公司 | Method for fully recycling valuable metal components of waste lithium batteries by hydrodynamic separation wet stripping polar powder |
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CN112139203A (en) * | 2020-08-24 | 2020-12-29 | 广东邦普循环科技有限公司 | Vacuum cracking method and cracking equipment for power battery |
CN113764758A (en) * | 2021-07-26 | 2021-12-07 | 广东邦普循环科技有限公司 | Method for recycling, pyrolyzing and controlling temperature of waste lithium battery and application |
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ES2995435A1 (en) | 2025-02-10 |
HUP2400037A1 (en) | 2024-06-28 |
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GB202318191D0 (en) | 2024-01-10 |
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