WO2024229788A1 - Method for repairing and regenerating positive electrode material by recovering waste battery in full-chain integrated manner - Google Patents
Method for repairing and regenerating positive electrode material by recovering waste battery in full-chain integrated manner Download PDFInfo
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- WO2024229788A1 WO2024229788A1 PCT/CN2023/093431 CN2023093431W WO2024229788A1 WO 2024229788 A1 WO2024229788 A1 WO 2024229788A1 CN 2023093431 W CN2023093431 W CN 2023093431W WO 2024229788 A1 WO2024229788 A1 WO 2024229788A1
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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
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- 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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- the present invention belongs to the field of resource recycling technology, for example, a method for recycling waste batteries and repairing and regenerating positive electrode materials in an integrated whole-chain manner.
- lithium iron phosphate batteries have stood out among lithium-ion power batteries due to their advantages such as good thermal stability, high safety performance and excellent cycle stability.
- life of power batteries is limited, and the number of retired lithium iron phosphate power batteries is increasing year by year. If they cannot be effectively utilized, it will cause waste of resources and environmental pollution.
- "Full-chain integrated recycling" as the main means of circular economy can effectively solve the above problems.
- the valuable components of lithium iron phosphate batteries are mainly present in the positive electrode materials, so the full-chain integrated recycling of lithium iron phosphate batteries is mainly to recycle and reuse waste lithium iron phosphate positive electrode materials.
- the commonly used recycling methods for lithium iron phosphate positive electrode materials are pyrometallurgical recycling and wet recycling. Both methods separate and extract valuable metals from waste positive electrode materials, which are energy-intensive and require a large amount of acid and alkali reagents, and the overall recycling cost is high. Since the price of lithium iron phosphate is relatively low compared to ternary positive electrode materials and the valuable metal content is low, the economic benefits of recycling using traditional methods are not high.
- CN114006070A discloses a method for high-temperature pyrolysis and pneumatic stripping and sorting of waste lithium batteries.
- the waste gas generated by pyrolysis is treated by high-temperature incineration, rapid cooling, water washing, alkali washing and other processes before being discharged in compliance with emission standards.
- This method not only consumes energy, but also causes a large amount of carbon dioxide emissions, which is not conducive to the realization of the dual carbon goals.
- CN115312903A discloses a method for regenerating waste lithium iron phosphate to prepare rate-type lithium iron phosphate, comprising adding water to waste lithium iron phosphate powder and ferrous disulfide in a molar ratio to prepare a slurry and mixing; Lithium powder and hydrogen ions are added to the acid solution in molar ratio, and water is added according to the solid-liquid ratio to adjust the slurry and stir; the mixed slurry is transferred to an autoclave, sealed and introduced with oxidizing gas, heated and stirred for reaction, and then kept warm; the filtrate after the reaction is filtered, phosphorus source and lithium source are added to the filtrate, and the temperature is increased and kept warm after adding a dispersant; the slurry is filtered and washed after insulation and cooling, and sprayed to obtain a spray material; the spray material is sintered under a protective atmosphere to obtain a carbon-coated lithium iron phosphate positive electrode material.
- the regeneration method can replenish lithium for waste positive electrode materials, restore the material morphology, composition and electrochemical properties, and realize the regeneration of positive electrode materials.
- the entire regeneration process consumes less reagents, has a short process and low environmental pollution.
- the performance of the regenerated positive electrode material is not very ideal. This is because, although the waste positive electrode material has been replenished with lithium, the positive electrode material has poor conductivity, and the outer carbon coating layer has defects during the cycle. It is difficult to completely restore or improve the conductivity of the positive electrode material by only replenishing lithium, so the electrochemical performance of the regenerated positive electrode material is not ideal.
- the electrolyte is also one of the main components of waste lithium-ion batteries. During the pyrolysis of battery fragments, the electrolyte decomposes and produces a large amount of organic gas. Currently, the direct combustion of organic gas is generally used for treatment.
- the purpose of the present invention is to provide a method for recycling waste batteries and repairing and regenerating positive electrode materials in an integrated manner.
- the present invention not only utilizes the organic gas generated by the decomposition of the electrolyte, but also restores the performance of the lithium iron phosphate positive electrode material.
- the entire reaction process only consumes silicon dioxide while fixing the tail gas, with low reagent consumption and low cost.
- the embodiments of the present disclosure provide a method for recycling waste batteries and repairing and regenerating positive electrode materials in an integrated manner, wherein the repair and regeneration method comprises the following steps:
- waste battery described in the embodiment of the present disclosure After the waste battery described in the embodiment of the present disclosure is discharged, it is disassembled and crushed to obtain pre-treated battery fragments, and the battery fragments are pyrolyzed to obtain waste positive electrode material powder and waste gas.
- the carbon capture flow can fix carbon in the coating layer of the regenerated lithium iron phosphate, and will not produce carbon dioxide emissions, which is beneficial to reducing carbon emissions.
- the fluorine circulation flow can realize the recycling of HF, and does not require further collection and treatment of harmful gases, which is beneficial to reducing environmental pollution.
- the regenerated silicon carbide-coated lithium iron phosphate can repair the damage of the carbon coating layer of the waste lithium iron phosphate, and the coating surface is smoother, and the material has excellent electrochemical properties. The entire reaction process only consumes silicon dioxide while fixing the exhaust gas, with low reagent consumption and low cost.
- the waste batteries in step (1) include any one of waste lithium iron phosphate batteries, waste lithium cobalt oxide batteries or waste ternary batteries, or a combination of at least two of them.
- the temperature of the pyrolysis treatment in step (1) is 400-600°C, for example, 400°C, 450°C, 500°C, 550°C or 600°C.
- the pyrolysis treatment time is 3 to 8 hours, for example: 3 hours, 4 hours, 5 hours, 6 hours, 7 hours or 8 hours.
- the lithium supplementation calcination treatment in step (2) includes testing the lithium deficiency of the positive electrode material powder by inductively coupled plasma mass spectrometry (ICP testing), determining the amount of lithium source added, and adding the positive electrode material to the positive electrode material.
- ICP testing inductively coupled plasma mass spectrometry
- the material powder is mixed with the lithium source, ball-milled and then calcined.
- the positive electrode material powder is lithium iron phosphate
- a reducing agent is added.
- the reducing agent includes any one of sucrose, glucose, cellulose or elemental carbon, or a combination of at least two thereof.
- the amount of the reducing agent added is 1-5% of the mass of the positive electrode material powder, for example: 1%, 2%, 3%, 4% or 5%, etc. Preferably, it is 2-3%.
- the lithium source includes any one of lithium hydroxide, lithium carbonate, lithium nitrate, lithium oxalate, lithium acetate, lithium dihydrogen phosphate, or lithium hydrogen phosphate, or a combination of at least two thereof.
- the ball milling time is 0.5 to 2 h, for example, 0.5 h, 0.8 h, 1 h, 1.5 h or 2 h.
- the calcination temperature is 650-800°C, for example, 650°C, 680°C, 700°C, 750°C or 800°C.
- the calcination time is 1 to 5 hours, for example, 1 hour, 2 hours, 3 hours, 4 hours or 5 hours.
- the calcination atmosphere is nitrogen and/or argon.
- the organic gas in step (3) is obtained by condensing and recovering the waste gas obtained by the pyrolysis in step (1), and collecting it after removing the acidic gas.
- the organic gas includes any one of C 2 H 4 , CH 4 or C 2 H 6 or a combination of at least two thereof.
- the volume ratio of the organic gas to silicon tetrafluoride in step (3) is 1:(1-5), for example: 1:1, 1:2, 1:3, 1:4 or 1:5, etc.
- the flow rate of the mixed gas in step (3) is 50 to 100 mL/min, for example, 50 mL/min, 60 mL/min, 70 mL/min, 80 mL/min, 90 mL/min or 100 mL/min.
- the electron energy of the plasma coating treatment is 20-30 eV, for example, 20 eV, 22 eV, 25 eV, 38 eV or 30 eV.
- the temperature of the plasma coating treatment is 350-500° C., for example, 350° C., 380° C., 400° C., 450° C. or 500° C.
- the waste gas obtained by the plasma coating treatment is recovered using SiO2 , and the obtained silicon tetrafluoride gas is dried and recycled.
- the mass fraction of the silicon carbide coating layer is 0.1-2%, for example: 0.1%, 0.5%, 0.8%, 1%, 1.5% or 2%.
- the repair and regeneration method comprises the following steps:
- step (3) The organic gas collected in step (2) and silicon tetrafluoride are mixed in a volume ratio of 1:(1-5) to obtain a mixed gas, and the mixed gas is introduced into a plasma reactor at a flow rate of 50-100 mL/min.
- the powder obtained by lithium supplementation calcination is subjected to plasma coating treatment under the conditions of an electron energy of 20-30 eV and a constant temperature zone temperature of 350-500° C. to obtain a silicon carbide coated positive electrode material, and the obtained waste gas is recovered using SiO2 , and the obtained silicon tetrafluoride gas is dried and recycled.
- the present invention has the following beneficial effects:
- the carbon capture flow can fix carbon in the coating layer of the regenerated lithium iron phosphate, and will not generate carbon dioxide emissions, which is beneficial to reducing carbon emissions.
- the fluorine circulation flow can realize the recycling of HF, and does not require further collection and treatment of harmful gases, which is beneficial to reducing environmental pollution.
- the regenerated silicon carbide coated lithium iron phosphate can repair the damage of the carbon coating of the waste lithium iron phosphate, and the coated surface is smoother.
- the material has excellent electrochemical properties. The entire reaction process only consumes silicon dioxide while fixing the exhaust gas, with low reagent consumption and low cost.
- the lithium iron phosphate battery regenerated by the method disclosed in the present invention has a 0.1C gram capacity of more than 152.79 mAh/g, a coulombic efficiency of more than 96.41%, a 1C gram capacity of more than 138.09 mAh/g, and a compaction density of more than 2.511 g/ cm3 .
- FIG1 is a schematic diagram of the process flow of the repair and regeneration method described in Example 1 of the present disclosure.
- FIG. 2 is an XRD diagram of the silicon carbide coated positive electrode material obtained in Example 1 of the present disclosure.
- This embodiment provides a method for repairing and regenerating a positive electrode material of a battery, and the method comprises the following steps:
- step (1) discharging, disassembling and crushing the retired power batteries, subjecting the obtained battery fragments to pyrolysis treatment at 600° C. for 4 h, subjecting the waste gas after pyrolysis to step (2), and collecting the waste lithium iron phosphate positive electrode powder;
- This embodiment provides a method for repairing and regenerating a positive electrode material of a battery, and the method comprises the following steps:
- step (1) discharging, disassembling and crushing the retired power batteries, subjecting the obtained battery fragments to pyrolysis treatment at 620° C. for 4 h, subjecting the waste gas after pyrolysis to step (2), and collecting the waste lithium iron phosphate positive electrode powder;
- the Fe/Li ratio of the waste lithium iron phosphate was determined by ICP testing.
- the lithium source was lithium hydroxide, and the reducing agent was sucrose.
- the amount of reducing agent added was 3.2% of the mass of the waste lithium iron phosphate powder.
- the waste lithium iron phosphate powder after uniform mixing is placed in a nitrogen atmosphere and calcined at 780°C for 2.5 hours.
- the electrolyte waste gas is condensed and recovered, the acid gas is removed, and the organic gas (main components are C 2 H 4 , CH 4 , C 2 H 6, etc.) is collected in turn;
- This comparative example provides a method for repairing and regenerating a positive electrode material of a battery, and the repairing and regenerating method comprises the following steps:
- This comparative example directly uses silicon carbide solid phase coating of commercial lithium iron phosphate positive electrode material.
- the lithium iron phosphate prepared in the embodiment and the comparative example, the conductive agent acetylene black, and the binder PVDF were mixed in a mass ratio of 90:5:5, and an appropriate amount of N-methyl pyrrolidone was added to coat the slurry.
- the test results are shown in Table 1:
- the lithium iron phosphate battery regenerated by the method described in the present invention has a 0.1C gram capacity of more than 152.79 mAh/g, a coulombic efficiency of more than 96.41%, a 1C gram capacity of more than 138.09 mAh/g, and a compaction density of more than 2.511 g/ cm3 .
- Example 1 By comparing Example 1 with Examples 3-4, it can be seen that in the repair and regeneration method disclosed in the present invention, the amount of the reducing agent added will affect the effect of preparing the silicon carbide coated positive electrode material.
- the effect of preparing the silicon carbide coated positive electrode material is better when the amount of the reducing agent added is controlled to 2-3% of the mass of the positive electrode material powder. If the amount of raw agent added is too large, the carbon coating of the regenerated lithium iron phosphate will be too thick, which will reduce its capacity.
- the electron energy of the plasma coating treatment will affect the effect of obtaining the silicon carbide coated positive electrode material.
- the electron energy of the plasma coating treatment is controlled at 20-30 eV, and the effect of obtaining the silicon carbide coated positive electrode material is better. If the electron energy is too large, although the reaction is promoted, the reaction proceeds rapidly and non-specific reactions may occur, reducing the gram capacity and rate performance, and slightly reducing the coulombic efficiency. If the electron energy is too small and the proportion of organic gas is too small, the reaction rate is slow and the product selectivity is affected, the overall electrochemical performance is reduced, and it cannot be ensured that the reaction can occur or the reaction rate is slow.
- Example 1 By comparing Example 1 with Examples 7-8, it can be seen that in the repair and regeneration method disclosed in the present invention, the volume ratio of organic gas to silicon fluoride will affect the effect of preparing the silicon carbide coated positive electrode material.
- the volume ratio of organic gas to silicon fluoride is controlled between 1:1 and 1:5, the effect of preparing the silicon carbide coated positive electrode material is better. If the proportion of organic gas is too large, although it promotes the occurrence of the reaction, it will produce a thicker carbon coating layer and reduce the gram capacity of the repair material. If the proportion of organic gas is too small, the reaction rate is slow and the product selectivity is affected.
- Example 1 From the comparison between Example 1 and Comparative Example 1, it can be seen that the use of silicon carbide to coat the regenerated lithium iron phosphate can repair the defects of the surface coating layer of the waste lithium iron phosphate, which is beneficial to the recovery of its electrochemical performance.
- Example 1 By comparing Example 1 with Comparative Example 2, it can be seen that the silicon carbide coated positive electrode material recovered by the repair method of the present disclosure has a similar effect to the silicon carbide coated positive electrode material prepared from commercial lithium iron phosphate, indicating that the repair and recovery method of the present application has a better recovery effect, and the carbon capture flow can fix carbon in the coating layer of the regenerated lithium iron phosphate, and will not generate carbon dioxide emissions, which is beneficial to reducing carbon emissions.
- the fluorine circulation flow can achieve The current recycling of HF does not require further collection and treatment of harmful gases, which is beneficial to reducing environmental pollution.
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Abstract
Description
本公开属于资源回收技术领域,例如一种全链条一体化回收废旧电池修复再生正极材料的方法。The present invention belongs to the field of resource recycling technology, for example, a method for recycling waste batteries and repairing and regenerating positive electrode materials in an integrated whole-chain manner.
随着新能源汽车产业的快速发展,磷酸铁锂电池由于具有诸如热稳定性好、安全性能高和循环稳定性优异等优点,在锂离子动力电池中脱颖而出。然而动力电池寿命有限,磷酸铁锂动力电池退役量逐年增加,若不能进行有效地利用,会造成资源的浪费和环境的污染。“全链条一体化回收”作为循环经济的主要手段,能够有效解决上述问题。With the rapid development of the new energy vehicle industry, lithium iron phosphate batteries have stood out among lithium-ion power batteries due to their advantages such as good thermal stability, high safety performance and excellent cycle stability. However, the life of power batteries is limited, and the number of retired lithium iron phosphate power batteries is increasing year by year. If they cannot be effectively utilized, it will cause waste of resources and environmental pollution. "Full-chain integrated recycling" as the main means of circular economy can effectively solve the above problems.
磷酸铁锂电池的有价成分主要存在于正极材料中,因此磷酸铁锂电池的全链条一体化回收主要是对废旧磷酸铁锂正极材料进行回收再利用。磷酸铁锂正极材料常用的回收利用手段为火法回收和湿法回收,这两种方式都是将有价金属从废旧正极材料分离提取,能耗高且需要消耗大量的酸碱试剂,整体回收成本高昂。由于磷酸铁锂价格相对三元正极材料低廉,且有价金属含量较低,因此采用传统方式回收经济效益不高。The valuable components of lithium iron phosphate batteries are mainly present in the positive electrode materials, so the full-chain integrated recycling of lithium iron phosphate batteries is mainly to recycle and reuse waste lithium iron phosphate positive electrode materials. The commonly used recycling methods for lithium iron phosphate positive electrode materials are pyrometallurgical recycling and wet recycling. Both methods separate and extract valuable metals from waste positive electrode materials, which are energy-intensive and require a large amount of acid and alkali reagents, and the overall recycling cost is high. Since the price of lithium iron phosphate is relatively low compared to ternary positive electrode materials and the valuable metal content is low, the economic benefits of recycling using traditional methods are not high.
CN114006070A公开了一种废旧锂电池高温热解及气动力剥离分选的方法,热解产生的废气通过高温焚烧、急冷、水洗、碱洗等工序处理后,达标排放。这一方式不仅消耗了能源,还会造成大量二氧化碳的排放,不利于双碳目标的实现。CN114006070A discloses a method for high-temperature pyrolysis and pneumatic stripping and sorting of waste lithium batteries. The waste gas generated by pyrolysis is treated by high-temperature incineration, rapid cooling, water washing, alkali washing and other processes before being discharged in compliance with emission standards. This method not only consumes energy, but also causes a large amount of carbon dioxide emissions, which is not conducive to the realization of the dual carbon goals.
CN115312903A公开了一种废旧磷酸铁锂再生制备倍率型磷酸铁锂的方法,将废旧磷酸铁锂粉和二硫化亚铁按摩尔比加水调浆混匀;向浆料按废旧磷酸铁 锂粉和氢离子按摩尔比加入酸溶液,按固液比加水调浆搅拌;将混合浆料转移至高压釜内,密封后通入氧化性气体,升温搅拌反应后保温;将反应后滤液过滤,滤液中补加磷源和锂源,加分散剂后升温保温;将保温冷却后浆料抽滤洗涤,喷雾得到喷雾料;将喷雾料在保护性气氛下烧结处理得到碳包覆磷酸铁锂正极材料。再生手段能够对废旧正极材料进行补锂,恢复材料形貌成分和电化学性能,实现正极材料的再生,整个再生过程试剂消耗少、流程短且环境污染低。但再生的正极材料性能并不十分理想,这是因为,虽对废旧正极材料进行了补锂操作,但正极材料导电性差,外层碳包覆层在循环过程中存在缺损,仅进行补锂难以完全恢复或提高正极材料的导电性,因此再生的正极材料电化学性能并不理想。CN115312903A discloses a method for regenerating waste lithium iron phosphate to prepare rate-type lithium iron phosphate, comprising adding water to waste lithium iron phosphate powder and ferrous disulfide in a molar ratio to prepare a slurry and mixing; Lithium powder and hydrogen ions are added to the acid solution in molar ratio, and water is added according to the solid-liquid ratio to adjust the slurry and stir; the mixed slurry is transferred to an autoclave, sealed and introduced with oxidizing gas, heated and stirred for reaction, and then kept warm; the filtrate after the reaction is filtered, phosphorus source and lithium source are added to the filtrate, and the temperature is increased and kept warm after adding a dispersant; the slurry is filtered and washed after insulation and cooling, and sprayed to obtain a spray material; the spray material is sintered under a protective atmosphere to obtain a carbon-coated lithium iron phosphate positive electrode material. The regeneration method can replenish lithium for waste positive electrode materials, restore the material morphology, composition and electrochemical properties, and realize the regeneration of positive electrode materials. The entire regeneration process consumes less reagents, has a short process and low environmental pollution. However, the performance of the regenerated positive electrode material is not very ideal. This is because, although the waste positive electrode material has been replenished with lithium, the positive electrode material has poor conductivity, and the outer carbon coating layer has defects during the cycle. It is difficult to completely restore or improve the conductivity of the positive electrode material by only replenishing lithium, so the electrochemical performance of the regenerated positive electrode material is not ideal.
除了正极材料外,电解液也是废旧锂离子电池的主要成分之一。在电池碎片的热解过程中,电解液分解产生大量的有机气体。现今一般采用直接燃烧有机气体的方式处理。In addition to the cathode material, the electrolyte is also one of the main components of waste lithium-ion batteries. During the pyrolysis of battery fragments, the electrolyte decomposes and produces a large amount of organic gas. Currently, the direct combustion of organic gas is generally used for treatment.
发明内容Summary of the invention
以下是对本文详细描述的主题的概述。本概述并非是为了限制权利要求的保护范围。The following is a summary of the subject matter described in detail herein. This summary is not intended to limit the scope of the claims.
本公开的目的在于提供一种全链条一体化回收废旧电池修复再生正极材料的方法,本公开既利用了电解液分解产生的有机气体,又恢复了磷酸铁锂正极材料的性能,且整个反应过程在固定尾气的同时仅需消耗二氧化硅,试剂消耗少,成本低廉。The purpose of the present invention is to provide a method for recycling waste batteries and repairing and regenerating positive electrode materials in an integrated manner. The present invention not only utilizes the organic gas generated by the decomposition of the electrolyte, but also restores the performance of the lithium iron phosphate positive electrode material. The entire reaction process only consumes silicon dioxide while fixing the tail gas, with low reagent consumption and low cost.
为达到此公开目的,本公开采用以下技术方案:In order to achieve the purpose of this disclosure, the present disclosure adopts the following technical solutions:
第一方面,本公开实施例提供了一种全链条一体化回收废旧电池修复再生正极材料的方法,所述修复再生方法包括以下步骤: In a first aspect, the embodiments of the present disclosure provide a method for recycling waste batteries and repairing and regenerating positive electrode materials in an integrated manner, wherein the repair and regeneration method comprises the following steps:
(1)对废弃电池放电后进行热解分选得到正极材料粉末;(1) discharging the waste batteries and performing pyrolysis separation to obtain positive electrode material powder;
(2)对正极材料粉末进行补锂煅烧处理;(2) performing lithium supplementation calcination treatment on the positive electrode material powder;
(3)将有机气体和四氟化硅混合,得到混合气体,使用所述混合气体对补锂煅烧得到的粉末进行等离子体包覆处理,得到碳化硅包覆正极材料,得到的废气利用SiO2进行回收,得到的四氟化硅气体干燥处理后循环利用。(3) Mixing an organic gas and silicon tetrafluoride to obtain a mixed gas, using the mixed gas to perform plasma coating treatment on the powder obtained by lithium supplementation calcination to obtain a silicon carbide coated positive electrode material, recovering the obtained waste gas using SiO2 , and drying the obtained silicon tetrafluoride gas for recycling.
本公开实施例所述废弃电池放电后,经拆解及破碎处理后得到预处理的电池碎片,对所述电池碎片进行热解处理得到废旧正极材料粉末和废气。After the waste battery described in the embodiment of the present disclosure is discharged, it is disassembled and crushed to obtain pre-treated battery fragments, and the battery fragments are pyrolyzed to obtain waste positive electrode material powder and waste gas.
本公开实施例所述修复再生方法中,碳捕集流能够将碳固定于再生磷酸铁锂的包覆层中,不会产生二氧化碳排放,有利于降低碳排放,氟循环流能够实现HF的循环利用,不需要有害气体的进一步收集处理过程,有利于降低环境污染,再生的碳化硅包覆磷酸铁锂能够修复废旧磷酸铁锂碳包覆层的损伤,并且包覆表面更光滑,材料电化学性能优异,整个反应过程在固定尾气的同时仅需消耗二氧化硅,试剂消耗少,成本低廉。In the repair and regeneration method described in the embodiment of the present disclosure, the carbon capture flow can fix carbon in the coating layer of the regenerated lithium iron phosphate, and will not produce carbon dioxide emissions, which is beneficial to reducing carbon emissions. The fluorine circulation flow can realize the recycling of HF, and does not require further collection and treatment of harmful gases, which is beneficial to reducing environmental pollution. The regenerated silicon carbide-coated lithium iron phosphate can repair the damage of the carbon coating layer of the waste lithium iron phosphate, and the coating surface is smoother, and the material has excellent electrochemical properties. The entire reaction process only consumes silicon dioxide while fixing the exhaust gas, with low reagent consumption and low cost.
本公开实施例所述废气利用SiO2进行回收的反应方程式为:SiO2+4HF=SiF4+2H2O。The reaction equation for recycling the waste gas using SiO 2 in the embodiment of the present disclosure is: SiO 2 +4HF=SiF 4 +2H 2 O.
在一个实施例中,步骤(1)所述废弃电池包括废弃磷酸铁锂电池、废旧钴酸锂电池或废旧三元电池中的任意一种或至少两种的组合。In one embodiment, the waste batteries in step (1) include any one of waste lithium iron phosphate batteries, waste lithium cobalt oxide batteries or waste ternary batteries, or a combination of at least two of them.
在一个实施例中,步骤(1)所述热解处理的温度为400~600℃,例如:400℃、450℃、500℃、550℃或600℃等。In one embodiment, the temperature of the pyrolysis treatment in step (1) is 400-600°C, for example, 400°C, 450°C, 500°C, 550°C or 600°C.
在一个实施例中,所述热解处理的时间为3~8h,例如:3h、4h、5h、6h、7h或8h等。In one embodiment, the pyrolysis treatment time is 3 to 8 hours, for example: 3 hours, 4 hours, 5 hours, 6 hours, 7 hours or 8 hours.
在一个实施例中,步骤(2)所述补锂煅烧处理包括通过电感耦合等离子体质谱仪测试(ICP测试)正极材料粉末的贫锂量,确定锂源加入量,将正极材 料粉末和锂源混合,球磨后进行煅烧。In one embodiment, the lithium supplementation calcination treatment in step (2) includes testing the lithium deficiency of the positive electrode material powder by inductively coupled plasma mass spectrometry (ICP testing), determining the amount of lithium source added, and adding the positive electrode material to the positive electrode material. The material powder is mixed with the lithium source, ball-milled and then calcined.
在一个实施例中,所述正极材料粉末为磷酸铁锂时,加入还原剂。In one embodiment, when the positive electrode material powder is lithium iron phosphate, a reducing agent is added.
在一个实施例中,所述还原剂包括蔗糖、葡萄糖、纤维素或单质碳中的任意一种或至少两种的组合。In one embodiment, the reducing agent includes any one of sucrose, glucose, cellulose or elemental carbon, or a combination of at least two thereof.
在一个实施例中,所述还原剂的添加量为所述正极材料粉末质量的1~5%,例如:1%、2%、3%、4%或5%等。优选为2~3%。In one embodiment, the amount of the reducing agent added is 1-5% of the mass of the positive electrode material powder, for example: 1%, 2%, 3%, 4% or 5%, etc. Preferably, it is 2-3%.
在一个实施例中,锂源包括氢氧化锂、碳酸锂、硝酸锂、草酸锂、醋酸锂、磷酸二氢锂或磷酸氢二锂中的任意一种或至少两种的组合。In one embodiment, the lithium source includes any one of lithium hydroxide, lithium carbonate, lithium nitrate, lithium oxalate, lithium acetate, lithium dihydrogen phosphate, or lithium hydrogen phosphate, or a combination of at least two thereof.
在一个实施例中,所述球磨的时间为0.5~2h,例如:0.5h、0.8h、1h、1.5h或2h等。In one embodiment, the ball milling time is 0.5 to 2 h, for example, 0.5 h, 0.8 h, 1 h, 1.5 h or 2 h.
在一个实施例中,所述煅烧的温度为650~800℃,例如:650℃、680℃、700℃、750℃或800℃等。In one embodiment, the calcination temperature is 650-800°C, for example, 650°C, 680°C, 700°C, 750°C or 800°C.
在一个实施例中,所述煅烧的时间为1~5h,例如:1h、2h、3h、4h或5h等。In one embodiment, the calcination time is 1 to 5 hours, for example, 1 hour, 2 hours, 3 hours, 4 hours or 5 hours.
在一个实施例中,所述煅烧的气氛为氮气和/或氩气。In one embodiment, the calcination atmosphere is nitrogen and/or argon.
在一个实施例中,步骤(3)所述有机气体由对步骤(1)所述热解得到的废气进行冷凝回收、除酸性气体后收集得到。In one embodiment, the organic gas in step (3) is obtained by condensing and recovering the waste gas obtained by the pyrolysis in step (1), and collecting it after removing the acidic gas.
在一个实施例中,所述有机气体包括C2H4、CH4或C2H6中的任意一种或至少两种的组合。In one embodiment, the organic gas includes any one of C 2 H 4 , CH 4 or C 2 H 6 or a combination of at least two thereof.
在一个实施例中,步骤(3)所述有机气体和四氟化硅的体积比为1:(1~5),例如:1:1、1:2、1:3、1:4或1:5等。In one embodiment, the volume ratio of the organic gas to silicon tetrafluoride in step (3) is 1:(1-5), for example: 1:1, 1:2, 1:3, 1:4 or 1:5, etc.
在一个实施例中,步骤(3)所述混合气体的流速为50~100mL/min,例如:50mL/min、60mL/min、70mL/min、80mL/min、90mL/min或100mL/min等。 In one embodiment, the flow rate of the mixed gas in step (3) is 50 to 100 mL/min, for example, 50 mL/min, 60 mL/min, 70 mL/min, 80 mL/min, 90 mL/min or 100 mL/min.
在一个实施例中,所述等离子体包覆处理的电子能量为20~30eV,例如:20eV、22eV、25eV、38eV或30eV等。In one embodiment, the electron energy of the plasma coating treatment is 20-30 eV, for example, 20 eV, 22 eV, 25 eV, 38 eV or 30 eV.
在一个实施例中,所述等离子体包覆处理的温度为350~500℃,例如:350℃、380℃、400℃、450℃或500℃等。In one embodiment, the temperature of the plasma coating treatment is 350-500° C., for example, 350° C., 380° C., 400° C., 450° C. or 500° C.
在一个实施例中,所述等离子体包覆处理得到的废气利用SiO2进行回收,得到的四氟化硅气体干燥处理后循环利用。In one embodiment, the waste gas obtained by the plasma coating treatment is recovered using SiO2 , and the obtained silicon tetrafluoride gas is dried and recycled.
在一个实施例中,以所述碳化硅包覆正极材料的质量为100%计,碳化硅包覆层的质量分数为0.1~2%,例如:0.1%、0.5%、0.8%、1%、1.5%或2%等。In one embodiment, based on the mass of the silicon carbide coated positive electrode material being 100%, the mass fraction of the silicon carbide coating layer is 0.1-2%, for example: 0.1%, 0.5%, 0.8%, 1%, 1.5% or 2%.
作为本公开的可选方案,所述修复再生方法包括以下步骤:As an optional solution of the present disclosure, the repair and regeneration method comprises the following steps:
(1)对废弃电池放电后进行热解处理得到废气和正极材料粉末;(1) discharging the waste battery and performing pyrolysis treatment to obtain waste gas and positive electrode material powder;
(2)通过ICP测试正极材料粉末的贫锂量,确定锂源加入量,将正极材料粉末、锂源和还原剂混合,在650~800℃下煅烧1~5h,所述还原剂的添加量为所述正极材料粉末质量的1~5%,对废气进行冷凝回收、除酸性气体和收集有机气体处理;(2) testing the lithium deficiency of the positive electrode material powder by ICP, determining the amount of lithium source added, mixing the positive electrode material powder, the lithium source and the reducing agent, calcining at 650-800° C. for 1-5 hours, wherein the amount of the reducing agent added is 1-5% of the mass of the positive electrode material powder, and condensing and recovering the waste gas, removing acidic gas and collecting organic gas for treatment;
(3)将步骤(2)收集的有机气体和四氟化硅按照体积比为1:(1~5)混合,得到混合气体,将所述混合气体以50~100mL/min的流速通入等离子体反应器中,在电子能量为20~30eV,调节恒温区温度为350~500℃的条件下对补锂煅烧得到的粉末在进行等离子体包覆处理,得到碳化硅包覆正极材料,得到的废气利用SiO2进行回收,得到的四氟化硅气体干燥处理后循环利用。(3) The organic gas collected in step (2) and silicon tetrafluoride are mixed in a volume ratio of 1:(1-5) to obtain a mixed gas, and the mixed gas is introduced into a plasma reactor at a flow rate of 50-100 mL/min. The powder obtained by lithium supplementation calcination is subjected to plasma coating treatment under the conditions of an electron energy of 20-30 eV and a constant temperature zone temperature of 350-500° C. to obtain a silicon carbide coated positive electrode material, and the obtained waste gas is recovered using SiO2 , and the obtained silicon tetrafluoride gas is dried and recycled.
相对于现有技术,本公开具有以下有益效果:Compared with the prior art, the present invention has the following beneficial effects:
(1)本公开所述修复再生方法中,碳捕集流能够将碳固定于再生磷酸铁锂的包覆层中,不会产生二氧化碳排放,有利于降低碳排放,氟循环流能够实现HF的循环利用,不需要有害气体的进一步收集处理过程,有利于降低环境污染, 再生的碳化硅包覆磷酸铁锂能够修复废旧磷酸铁锂碳包覆层的损伤,并且包覆表面更光滑,材料电化学性能优异,整个反应过程在固定尾气的同时仅需消耗二氧化硅,试剂消耗少,成本低廉。(1) In the repair and regeneration method disclosed in the present invention, the carbon capture flow can fix carbon in the coating layer of the regenerated lithium iron phosphate, and will not generate carbon dioxide emissions, which is beneficial to reducing carbon emissions. The fluorine circulation flow can realize the recycling of HF, and does not require further collection and treatment of harmful gases, which is beneficial to reducing environmental pollution. The regenerated silicon carbide coated lithium iron phosphate can repair the damage of the carbon coating of the waste lithium iron phosphate, and the coated surface is smoother. The material has excellent electrochemical properties. The entire reaction process only consumes silicon dioxide while fixing the exhaust gas, with low reagent consumption and low cost.
(2)本公开所述方法再生得到的磷酸铁锂制得电池0.1C克容量可达152.79mAh/g以上,库伦效率可达96.41%以上,1C克容量可达138.09mAh/g以上,压实密度可达2.511g/cm3以上。(2) The lithium iron phosphate battery regenerated by the method disclosed in the present invention has a 0.1C gram capacity of more than 152.79 mAh/g, a coulombic efficiency of more than 96.41%, a 1C gram capacity of more than 138.09 mAh/g, and a compaction density of more than 2.511 g/ cm3 .
在阅读并理解了附图和详细描述后,可以明白其他方面。Other aspects will be apparent upon reading and understanding the drawings and detailed description.
附图用来提供对本文技术方案的进一步理解,并且构成说明书的一部分,与本申请的实施例一起用于解释本文的技术方案,并不构成对本文技术方案的限制。The accompanying drawings are used to provide further understanding of the technical solution of this article and constitute a part of the specification. Together with the embodiments of the present application, they are used to explain the technical solution of this article and do not constitute a limitation on the technical solution of this article.
图1是本公开实施例1所述修复再生方法的工艺流程示意图。FIG1 is a schematic diagram of the process flow of the repair and regeneration method described in Example 1 of the present disclosure.
图2是本公开实施例1制得碳化硅包覆正极材料的XRD图。FIG. 2 is an XRD diagram of the silicon carbide coated positive electrode material obtained in Example 1 of the present disclosure.
下面通过具体实施方式来进一步说明本公开的技术方案。本领域技术人员应该明了,所述实施例仅仅是帮助理解本公开,不应视为对本公开的具体限制。The technical solution of the present disclosure is further described below through specific implementation methods. Those skilled in the art should understand that the embodiments are only to help understand the present disclosure and should not be regarded as specific limitations of the present disclosure.
实施例1Example 1
本实施例提供了一种电池正极材料的修复再生方法,所述修复再生方法包括以下步骤:This embodiment provides a method for repairing and regenerating a positive electrode material of a battery, and the method comprises the following steps:
(1)对退役动力电池进行放电、拆解及破碎处理,得到的电池碎片在600℃下进行4h的热解处理,热解后废气进行步骤(2)处理,收集废旧磷酸铁锂正极粉末; (1) discharging, disassembling and crushing the retired power batteries, subjecting the obtained battery fragments to pyrolysis treatment at 600° C. for 4 h, subjecting the waste gas after pyrolysis to step (2), and collecting the waste lithium iron phosphate positive electrode powder;
(2)通过ICP测试确定废旧磷酸铁锂的Fe/Li比值,向废旧磷酸铁锂正极材料中混入锂源与还原剂,在球磨机中球磨1h,使得Fe/Li=1:1.05,锂源为氢氧化锂,还原剂为蔗糖,还原剂添加量为废旧磷酸铁锂粉末质量的3%。将混合均匀后的废旧磷酸铁锂粉末置于氮气气氛下,750℃煅烧3h,将电解液废气依次进行冷凝回收、除酸性气体以及收集有机气体(主要成分为C2H4、CH4、C2H6等);(2) Determine the Fe/Li ratio of waste lithium iron phosphate by ICP test, mix lithium source and reducing agent into waste lithium iron phosphate positive electrode material, and ball mill for 1 hour in a ball mill to make Fe/Li=1:1.05, the lithium source is lithium hydroxide, the reducing agent is sucrose, and the amount of reducing agent added is 3% of the mass of waste lithium iron phosphate powder. The mixed waste lithium iron phosphate powder is placed in a nitrogen atmosphere and calcined at 750℃ for 3 hours, and the electrolyte waste gas is condensed and recovered, the acid gas is removed, and the organic gas (main components are C2H4 , CH4 , C2H6 , etc.) is collected in turn;
(3)常压下将有机气体与氟化硅气体混合,控制气体流速为60mL/min,有机气体与氟化硅的体积比为1:2,将补锂煅烧得到的粉末均匀地铺在瓷舟上,瓷舟置于反应器恒温区,随后将混合气体通入等离子体反应器中。设置等离子反应器所产生的电子能量为25eV,调节恒温区温度为400℃,反应2h,得到碳化硅包覆磷酸铁锂(碳化硅质量分数为1%),所述碳化硅包覆磷酸铁锂的XRD图如图2所示,收集废气,利用SiO2进行回收,反应方程式如下:SiO2+4HF=SiF4+2H2O,所得到的四氟化硅气体干燥处理后回用。(3) Mix the organic gas with the silicon fluoride gas under normal pressure, control the gas flow rate to 60 mL/min, and the volume ratio of the organic gas to the silicon fluoride is 1:2. Evenly spread the powder obtained by calcining the lithium supplement on a porcelain boat, place the porcelain boat in the constant temperature zone of the reactor, and then pass the mixed gas into the plasma reactor. Set the electron energy generated by the plasma reactor to 25 eV, adjust the temperature of the constant temperature zone to 400 ° C, react for 2 hours, and obtain silicon carbide-coated lithium iron phosphate (silicon carbide mass fraction is 1%). The XRD diagram of the silicon carbide-coated lithium iron phosphate is shown in Figure 2. Collect the waste gas and recycle it using SiO 2. The reaction equation is as follows: SiO 2 +4HF=SiF 4 +2H 2 O. The obtained silicon tetrafluoride gas is dried and reused.
实施例2Example 2
本实施例提供了一种电池正极材料的修复再生方法,所述修复再生方法包括以下步骤:This embodiment provides a method for repairing and regenerating a positive electrode material of a battery, and the method comprises the following steps:
(1)对退役动力电池进行放电、拆解及破碎处理,得到的电池碎片在620℃下进行4h的热解处理,热解后废气进行步骤(2)处理,收集废旧磷酸铁锂正极粉末;(1) discharging, disassembling and crushing the retired power batteries, subjecting the obtained battery fragments to pyrolysis treatment at 620° C. for 4 h, subjecting the waste gas after pyrolysis to step (2), and collecting the waste lithium iron phosphate positive electrode powder;
(2)通过ICP测试确定废旧磷酸铁锂的Fe/Li比值,向废旧磷酸铁锂正极材料中混入锂源与还原剂,在球磨机中球磨1h,使得Fe/Li=1:1.02,锂源为氢氧化锂,还原剂为蔗糖,还原剂添加量为废旧磷酸铁锂粉末质量的3.2%。将混 合均匀后的废旧磷酸铁锂粉末置于氮气气氛下,780℃煅烧2.5h,将电解液废气依次进行冷凝回收、除酸性气体以及收集有机气体(主要成分为C2H4、CH4、C2H6等);(2) The Fe/Li ratio of the waste lithium iron phosphate was determined by ICP testing. A lithium source and a reducing agent were mixed into the waste lithium iron phosphate positive electrode material, and the mixture was ball-milled in a ball mill for 1 hour to make Fe/Li = 1:1.02. The lithium source was lithium hydroxide, and the reducing agent was sucrose. The amount of reducing agent added was 3.2% of the mass of the waste lithium iron phosphate powder. The waste lithium iron phosphate powder after uniform mixing is placed in a nitrogen atmosphere and calcined at 780°C for 2.5 hours. The electrolyte waste gas is condensed and recovered, the acid gas is removed, and the organic gas (main components are C 2 H 4 , CH 4 , C 2 H 6, etc.) is collected in turn;
(3)常压下将有机气体与氟化硅气体混合,控制气体流速为70mL/min,有机气体与氟化硅的体积比为1:3,将补锂煅烧得到的粉末均匀地铺在瓷舟上,瓷舟置于反应器恒温区,随后将混合气体通入等离子体反应器中。设置等离子反应器所产生的电子能量为27eV,调节恒温区温度为380℃,反应2h,得到碳化硅包覆磷酸铁锂(碳化硅质量分数为1.1%),收集废气,利用SiO2进行回收,反应方程式如下:SiO2+4HF=SiF4+2H2O,所得到的四氟化硅气体干燥处理后回用。(3) Mix the organic gas with the silicon fluoride gas under normal pressure, control the gas flow rate to 70 mL/min, and the volume ratio of the organic gas to the silicon fluoride to be 1:3. Evenly spread the powder obtained by calcining the lithium supplement on a porcelain boat, place the porcelain boat in the constant temperature zone of the reactor, and then pass the mixed gas into the plasma reactor. Set the electron energy generated by the plasma reactor to 27 eV, adjust the temperature of the constant temperature zone to 380 ° C, react for 2 hours, and obtain silicon carbide-coated lithium iron phosphate (silicon carbide mass fraction is 1.1%). Collect the waste gas and recycle it using SiO 2. The reaction equation is as follows: SiO 2 +4HF=SiF 4 +2H 2 O. The obtained silicon tetrafluoride gas is dried and reused.
实施例3Example 3
本实施例与实施例1区别仅在于,还原剂添加量为废旧磷酸铁锂粉末质量的1%,其他条件与参数与实施例1完全相同。The only difference between this embodiment and embodiment 1 is that the amount of reducing agent added is 1% of the mass of the waste lithium iron phosphate powder, and the other conditions and parameters are exactly the same as those in embodiment 1.
实施例4Example 4
本实施例与实施例1区别仅在于,还原剂添加量为废旧磷酸铁锂粉末质量的5%,其他条件与参数与实施例1完全相同。The only difference between this embodiment and embodiment 1 is that the amount of reducing agent added is 5% of the mass of the waste lithium iron phosphate powder, and the other conditions and parameters are exactly the same as those in embodiment 1.
实施例5Example 5
本实施例与实施例1区别仅在于,步骤(3)所述电子能量为15eV,其他条件与参数与实施例1完全相同。The only difference between this embodiment and embodiment 1 is that the electron energy in step (3) is 15 eV, and the other conditions and parameters are exactly the same as those in embodiment 1.
实施例6Example 6
本实施例与实施例1区别仅在于,步骤(3)所述电子能量为35eV,其他条件与参数与实施例1完全相同。 The only difference between this embodiment and embodiment 1 is that the electron energy in step (3) is 35 eV, and the other conditions and parameters are exactly the same as those in embodiment 1.
实施例7Example 7
本实施例与实施例1区别仅在于,步骤(3)所述有机气体与氟化硅的体积比为2:1,其他条件与参数与实施例1完全相同。The only difference between this embodiment and embodiment 1 is that the volume ratio of the organic gas to silicon fluoride in step (3) is 2:1, and the other conditions and parameters are exactly the same as those in embodiment 1.
实施例8Example 8
本实施例与实施例1区别仅在于,步骤(3)所述有机气体与氟化硅的体积比为1:10,其他条件与参数与实施例1完全相同。The only difference between this embodiment and embodiment 1 is that the volume ratio of the organic gas to silicon fluoride in step (3) is 1:10, and the other conditions and parameters are exactly the same as those in embodiment 1.
对比例1Comparative Example 1
本对比例提供了一种电池正极材料的修复再生方法,所述修复再生方法包括以下步骤:This comparative example provides a method for repairing and regenerating a positive electrode material of a battery, and the repairing and regenerating method comprises the following steps:
S1:对退役动力电池进行放电、拆解及破碎处理;S1: Discharge, dismantle and crush retired power batteries;
S2:对经过S1预处理后的电池碎片进行热解处理,热解后废气进行冷凝回收处理,收集废旧磷酸铁锂正极粉末;S2: Pyrolysis treatment is performed on the battery fragments pre-treated by S1, and the waste gas after pyrolysis is condensed and recovered to collect the waste lithium iron phosphate positive electrode powder;
S3:通过ICP测试确定废旧磷酸铁锂的Fe/Li比值,向废旧磷酸铁锂正极材料中混入锂源与还原剂,在球磨机中球磨1h,使得Fe/Li=1:1.05,锂源为氢氧化锂,还原剂为蔗糖,还原剂添加量为废旧磷酸铁锂粉末质量的10%。将混合均匀后的废旧磷酸铁锂粉末置于氮气气氛下,750℃煅烧3h。得到修复再生的碳包覆磷酸铁锂。S3: Determine the Fe/Li ratio of waste lithium iron phosphate by ICP test, mix lithium source and reducing agent into waste lithium iron phosphate positive electrode material, and ball mill for 1h in a ball mill to make Fe/Li=1:1.05, the lithium source is lithium hydroxide, the reducing agent is sucrose, and the amount of reducing agent added is 10% of the mass of waste lithium iron phosphate powder. Place the mixed waste lithium iron phosphate powder in a nitrogen atmosphere and calcine at 750℃ for 3h. Obtain repaired and regenerated carbon-coated lithium iron phosphate.
对比例2Comparative Example 2
本对比例直接采用碳化硅固相包覆商用磷酸铁锂正极材料。This comparative example directly uses silicon carbide solid phase coating of commercial lithium iron phosphate positive electrode material.
性能测试:Performance Test:
将实施例和对比例制备的材料磷酸铁锂与导电剂乙炔黑、粘结剂PVDF质量比按90:5:5充分搅拌混均,加入适量的N甲基本吡咯烷酮,将浆料涂覆 于铝箔片上,真空干燥中120℃度干燥12h制成正极片;以金属锂片为负极组装成半电池,测试电化学性能,测试结果如表1所示:The lithium iron phosphate prepared in the embodiment and the comparative example, the conductive agent acetylene black, and the binder PVDF were mixed in a mass ratio of 90:5:5, and an appropriate amount of N-methyl pyrrolidone was added to coat the slurry. On an aluminum foil, dry at 120°C for 12 hours in a vacuum dryer to form a positive electrode sheet; assemble a half-cell with a metal lithium sheet as the negative electrode, and test the electrochemical performance. The test results are shown in Table 1:
表1
Table 1
由表1可以看出,由实施例1-2可得,本公开所述方法再生得到的磷酸铁锂制得电池0.1C克容量可达152.79mAh/g以上,库伦效率可达96.41%以上,1C克容量可达138.09mAh/g以上,压实密度可达2.511g/cm3以上。As can be seen from Table 1, from Examples 1-2, the lithium iron phosphate battery regenerated by the method described in the present invention has a 0.1C gram capacity of more than 152.79 mAh/g, a coulombic efficiency of more than 96.41%, a 1C gram capacity of more than 138.09 mAh/g, and a compaction density of more than 2.511 g/ cm3 .
由实施例1和实施例3-4对比可得,本公开所述修复再生方法中,所述还原剂的添加量会影响制得碳化硅包覆正极材料的效果,将还原剂的添加量控制在所述正极材料粉末质量的2~3%,制得碳化硅包覆正极材料的效果较好,若还 原剂的添加量过大,再生磷酸铁锂的碳包覆层过厚,会使得其容量下降,若还原剂的添加量过低,无法完全还原废旧磷酸铁锂中铁元素的价态,并且难以初步修复缺损的碳包覆层,导致修复磷酸铁锂的电化学性能和循环稳定性难以满足商用需求。By comparing Example 1 with Examples 3-4, it can be seen that in the repair and regeneration method disclosed in the present invention, the amount of the reducing agent added will affect the effect of preparing the silicon carbide coated positive electrode material. The effect of preparing the silicon carbide coated positive electrode material is better when the amount of the reducing agent added is controlled to 2-3% of the mass of the positive electrode material powder. If the amount of raw agent added is too large, the carbon coating of the regenerated lithium iron phosphate will be too thick, which will reduce its capacity. If the amount of reducing agent added is too low, the valence state of the iron element in the waste lithium iron phosphate cannot be completely reduced, and it is difficult to initially repair the defective carbon coating, resulting in the electrochemical performance and cycle stability of the repaired lithium iron phosphate being difficult to meet commercial needs.
由实施例1和实施例5-6对比可得,本公开所述修复再生方法中,等离子体包覆处理的电子能量会影响制得碳化硅包覆正极材料的效果,将等离子体包覆处理的电子能量控制在20~30eV,制得碳化硅包覆正极材料的效果较好,若电子能量过大,虽促进反应的发生,但反应快速进行,可能产生非特异性反应,降低克容量和倍率性能,库伦效率略有降低,若电子能量过小,有机气体占比过小,则反应速率缓慢且产物选择性受到影响,电化学性能总体降低,不能确保反应能够发生或反应速率缓慢。By comparing Example 1 with Examples 5-6, it can be seen that in the repair and regeneration method disclosed in the present invention, the electron energy of the plasma coating treatment will affect the effect of obtaining the silicon carbide coated positive electrode material. The electron energy of the plasma coating treatment is controlled at 20-30 eV, and the effect of obtaining the silicon carbide coated positive electrode material is better. If the electron energy is too large, although the reaction is promoted, the reaction proceeds rapidly and non-specific reactions may occur, reducing the gram capacity and rate performance, and slightly reducing the coulombic efficiency. If the electron energy is too small and the proportion of organic gas is too small, the reaction rate is slow and the product selectivity is affected, the overall electrochemical performance is reduced, and it cannot be ensured that the reaction can occur or the reaction rate is slow.
由实施例1和实施例7-8对比可得,本公开所述修复再生方法中,有机气体与氟化硅的体积比会影响制得碳化硅包覆正极材料的效果,将有机气体与氟化硅的体积比控制在1:1~1:5之间,制得碳化硅包覆正极材料的效果较好,若有机气体占比过大,虽促进反应的发生,但会产生较厚的碳包覆层,降低修复材料的克容量,若有机气体占比过小,则反应速率缓慢且产物选择性受到影响。By comparing Example 1 with Examples 7-8, it can be seen that in the repair and regeneration method disclosed in the present invention, the volume ratio of organic gas to silicon fluoride will affect the effect of preparing the silicon carbide coated positive electrode material. When the volume ratio of organic gas to silicon fluoride is controlled between 1:1 and 1:5, the effect of preparing the silicon carbide coated positive electrode material is better. If the proportion of organic gas is too large, although it promotes the occurrence of the reaction, it will produce a thicker carbon coating layer and reduce the gram capacity of the repair material. If the proportion of organic gas is too small, the reaction rate is slow and the product selectivity is affected.
由实施例1和对比例1对比可得,采用碳化硅包覆再生磷酸铁锂能够修复废旧磷酸铁锂表面包覆层的缺陷,有利于其恢复电化学性能。From the comparison between Example 1 and Comparative Example 1, it can be seen that the use of silicon carbide to coat the regenerated lithium iron phosphate can repair the defects of the surface coating layer of the waste lithium iron phosphate, which is beneficial to the recovery of its electrochemical performance.
由实施例1和对比例2对比可得,本公开所述修复方法回收得到的碳化硅包覆正极材料相较于商用磷酸铁锂制得碳化硅包覆正极材料效果相近,说明本申请所述修复回收方法回收效果较好,且碳捕集流能够将碳固定于再生磷酸铁锂的包覆层中,不会产生二氧化碳排放,有利于降低碳排放,氟循环流能够实 现HF的循环利用,不需要有害气体的进一步收集处理过程,有利于降低环境污染。 By comparing Example 1 with Comparative Example 2, it can be seen that the silicon carbide coated positive electrode material recovered by the repair method of the present disclosure has a similar effect to the silicon carbide coated positive electrode material prepared from commercial lithium iron phosphate, indicating that the repair and recovery method of the present application has a better recovery effect, and the carbon capture flow can fix carbon in the coating layer of the regenerated lithium iron phosphate, and will not generate carbon dioxide emissions, which is beneficial to reducing carbon emissions. The fluorine circulation flow can achieve The current recycling of HF does not require further collection and treatment of harmful gases, which is beneficial to reducing environmental pollution.
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