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CN116789150A - Method for removing organic fluorine in lithium ion positive electrode material - Google Patents

Method for removing organic fluorine in lithium ion positive electrode material Download PDF

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CN116789150A
CN116789150A CN202310759825.0A CN202310759825A CN116789150A CN 116789150 A CN116789150 A CN 116789150A CN 202310759825 A CN202310759825 A CN 202310759825A CN 116789150 A CN116789150 A CN 116789150A
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organic fluorine
lithium
lithium ion
removing organic
cathode material
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肖杰锋
林双杰
洪俊明
张倩
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Huaqiao University
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Abstract

本发明涉及废旧锂离子电池无害化处理技术领域,具体涉及一种去除锂离子正极材料中有机氟的方法;该去除锂离子正极材料中有机氟的方法,包括以下步骤:获得废旧锂离子电池的正极片;对正极片进行破碎、筛分,获得正极材料;将获得的正极材料与碱性金属氢氧化物混合后进行无氧焙烧;将无氧焙烧后的产物水洗过滤。本发明利用碱性金属氢氧化物同作催化剂和捕获剂,一步实现锂离子电池正极材料中有机氟的热催化脱除及其固化分离,既有效去除了有机氟粘结剂、利于正极材料的资源化利用,同时有效避免了有机氟潜在的二次环境污染风险。本方法依托于工业上应用广泛的热处理技术,操作简单、易规模化应用,具有广泛的工业应用潜力。

The invention relates to the technical field of harmless treatment of waste lithium-ion batteries, and specifically relates to a method for removing organic fluorine from lithium-ion cathode materials; the method for removing organic fluorine from lithium-ion cathode materials includes the following steps: Obtaining waste lithium-ion batteries The positive electrode sheet is crushed and screened to obtain positive electrode material; the obtained positive electrode material is mixed with alkaline metal hydroxide and then roasted anaerobically; the product after anaerobic roasting is washed and filtered. The present invention uses alkaline metal hydroxide as a catalyst and capture agent to realize the thermal catalytic removal and solidification separation of organic fluorine in the lithium ion battery cathode material in one step, which not only effectively removes the organic fluorine binder, but also facilitates the removal of the cathode material. Resource utilization, while effectively avoiding the potential secondary environmental pollution risks of organic fluorine. This method relies on heat treatment technology that is widely used in industry, is simple to operate, easy to apply on a large scale, and has broad industrial application potential.

Description

一种去除锂离子正极材料中有机氟的方法A method for removing organic fluorine from lithium ion cathode materials

技术领域Technical field

本发明涉及废旧锂离子电池无害化处理技术领域,特别涉及一种去除锂离子正极材料中有机氟的方法。The present invention relates to the technical field of harmless treatment of waste lithium-ion batteries, and in particular to a method for removing organic fluorine in lithium-ion positive electrode materials.

背景技术Background technique

随着新能源汽车产业的高速发展,2021年我国新能源汽车销量增至352.1万辆,连续7年位居世界第一,新能源汽车已成为我国绿色低碳的战略性产业。动力电池作为新能源汽车的核心组件,其成本占据整车造价的40%以上。目前,因三元动力锂离子电池大量消耗锂、钴、镍等稀贵资源,使得我国对该类资源的对外依存度超过了80%,严重影响我国新能源汽车产业的国家安全。因此,回收废动力电池中锂、钴、镍等战略性金属可有效缓解资源对外依存程度,补齐我国新能源汽车产业内循环的关键链条。目前,针对废旧锂离子电池正极材料的处理处置已成为资源化利用的前沿热点。With the rapid development of the new energy vehicle industry, my country's new energy vehicle sales increased to 3.521 million units in 2021, ranking first in the world for 7 consecutive years. New energy vehicles have become my country's green and low-carbon strategic industry. As the core component of new energy vehicles, power batteries account for more than 40% of the total vehicle cost. At present, because ternary power lithium-ion batteries consume a large amount of rare and precious resources such as lithium, cobalt, and nickel, my country's external dependence on such resources exceeds 80%, seriously affecting the national security of my country's new energy automobile industry. Therefore, recycling strategic metals such as lithium, cobalt, and nickel in used power batteries can effectively alleviate the dependence on external resources and complete the key chain of the internal cycle of my country's new energy automobile industry. At present, the treatment and disposal of used lithium-ion battery cathode materials has become a hot topic in resource utilization.

根据《中国废旧锂离子电池回收拆解与梯次利用行业发展白皮书(2022年)》,2021年中国理论废动力电池回收量为29.4万吨。针对废动力电池回收,工业上采用带电破碎、物理分离等组合方法快速解离电池组分,富集得到废正极材料,以备资源化利用。其中,所得废正极材料被聚偏氟乙烯(PVDF)等有机氟粘结剂紧密包裹。由于PVDF具有优良的机械强度、抗紫外线辐射、化学稳定性和抗老化性,难以被酸、碱、强氧化剂或卤素分解,严重不利于废正极材料的资源化利用。为实现废正极材料的高效利用,需先将PVDF粘结剂去除。同时,若处理不当可能造成严重的二次氟污染。因此,如何经济、高效且环境友好地去除PVDF对于废正极材料的资源化利用具有重要的先决影响。According to the "White Paper on the Development of China's Waste Li-ion Battery Recycling, Dismantling and Echelon Utilization Industry (2022)", China's theoretical waste power battery recycling volume in 2021 will be 294,000 tons. For the recycling of waste power batteries, the industry uses a combination of methods such as electrified crushing and physical separation to quickly dissociate battery components and enrich waste cathode materials for resource utilization. Among them, the obtained waste cathode material is tightly wrapped with an organic fluorine binder such as polyvinylidene fluoride (PVDF). Because PVDF has excellent mechanical strength, resistance to ultraviolet radiation, chemical stability and anti-aging properties, it is difficult to be decomposed by acids, alkalis, strong oxidants or halogens, which is seriously detrimental to the resource utilization of waste cathode materials. In order to achieve efficient utilization of waste cathode materials, the PVDF binder needs to be removed first. At the same time, improper handling may cause serious secondary fluorine pollution. Therefore, how to remove PVDF economically, efficiently and environmentally friendly has an important prerequisite impact on the resource utilization of waste cathode materials.

发明内容Contents of the invention

本发明的目的在于克服上述现有技术中的不足,提供一种去除锂离子正极材料中有机氟的方法。The object of the present invention is to overcome the above-mentioned shortcomings in the prior art and provide a method for removing organic fluorine in lithium ion cathode materials.

为了解决上述技术问题,本发明提供的技术方案如下:In order to solve the above technical problems, the technical solutions provided by the present invention are as follows:

一种去除锂离子正极材料中有机氟的方法,包括以下步骤:A method for removing organic fluorine from lithium ion cathode materials, including the following steps:

获得废旧锂离子电池的正极片;Obtain positive electrode sheets from used lithium-ion batteries;

对正极片进行破碎、筛分,获得正极材料;Crush and screen the positive electrode sheets to obtain positive electrode materials;

将获得的正极材料与碱性金属氢氧化物混合后进行无氧焙烧;Mix the obtained cathode material with alkaline metal hydroxide and then perform oxygen-free roasting;

将无氧焙烧后的产物水洗过滤,分离得到氟化盐和去除有机氟的正极材料。The product after anaerobic roasting is washed and filtered with water to separate the fluoride salt and the cathode material for removing organic fluorine.

本发明提供的方法具体涉及一种去除锂离子正极材料中有机氟的方法,尤其是涉及一种正极材料中含氟有机物催化热解为无机氟并原位固化为氟化盐的方法,其中,所述正极材料中有机氟指的是聚偏氟乙烯(PVDF)等含氟有机物,而所述正极材料是通过将废旧锂离子电池的正极片,经过破碎、筛分等物理处理,分离富集得到;The method provided by the invention specifically relates to a method for removing organic fluorine in lithium ion cathode materials, and in particular to a method for catalytically pyrolyzing fluorine-containing organic matter in the cathode material into inorganic fluorine and solidifying it in situ into fluoride salts, wherein, The organic fluorine in the cathode material refers to fluorine-containing organic matter such as polyvinylidene fluoride (PVDF), and the cathode material is separated and enriched by crushing and screening the cathode sheets of used lithium-ion batteries. get;

目前锂离子电池正极材料中有机氟的处理方法较多,如有机溶剂/熔盐法,利用有机氟的在有机相或熔盐相中的溶解性,将其溶解去除,但处理后的复杂有机相/熔盐相的处理又成了新难题;如直接热解法,在高温焙烧下,有机氟裂解为氟化氢、氟乙烯、三氟苯等逸散产物,会造成严重的二次污染。At present, there are many methods for treating organic fluorine in lithium-ion battery cathode materials, such as the organic solvent/molten salt method, which uses the solubility of organic fluorine in the organic phase or molten salt phase to dissolve and remove it. However, the complex organic fluorine after treatment The treatment of phase/molten salt phase has become a new problem; such as direct pyrolysis method, under high-temperature roasting, organic fluorine is cracked into fugitive products such as hydrogen fluoride, vinyl fluoride, trifluorobenzene, etc., which will cause serious secondary pollution.

在本发明中,将得到的正极材料与碱性金属氢氧化物混合后进行无氧焙烧处理,通过将正极材料中有机氟热催化转化为无机氟并原位固化为氟化盐,从而实现将正极材料中的有机氟予以去除;In the present invention, the obtained cathode material is mixed with an alkaline metal hydroxide and then subjected to an oxygen-free roasting treatment. The organic fluorine in the cathode material is thermally catalytically converted into inorganic fluorine and solidified in situ into a fluoride salt, thereby achieving the The organic fluorine in the cathode material is removed;

具体来说,碱性金属氢氧化物在高温条件下融化,与有机氟作用,可以起到催化作用,促进C-F键断裂生成HF等无机氟产物,而后,碱性金属氢氧化物将HF等无机氟产物捕获,最终发生中和反应。本发明利用碱性金属氢氧化物同作催化剂和捕获剂,一步实现锂离子电池正极材料中有机氟的热催化脱除及其固化分离,既有效去除了有机氟粘结剂、利于正极材料的资源化利用,同时有效避免了有机氟潜在的二次环境污染风险。本方法依托于工业上应用广泛的热处理技术,操作简单、易规模化应用,具有广泛的工业应用潜力。Specifically, alkaline metal hydroxide melts under high temperature conditions and reacts with organic fluorine to play a catalytic role, promoting the breakage of C-F bonds to generate inorganic fluorine products such as HF. Then, the alkaline metal hydroxide converts inorganic fluorine products such as HF into The fluorine product is captured and eventually a neutralization reaction occurs. The present invention uses alkaline metal hydroxide as a catalyst and capture agent to realize the thermal catalytic removal and solidification separation of organic fluorine in the lithium ion battery cathode material in one step, which not only effectively removes the organic fluorine binder, but also facilitates the removal of the cathode material. Resource utilization, while effectively avoiding the potential secondary environmental pollution risks of organic fluorine. This method relies on heat treatment technology that is widely used in industry, is simple to operate, easy to apply on a large scale, and has broad industrial application potential.

在一更佳的实施例中,所述破碎的转速为1000-2000rpm,破碎时间为5-30min。In a more preferred embodiment, the crushing speed is 1000-2000 rpm, and the crushing time is 5-30 minutes.

在一更佳的实施例中,所述筛分的目数大于100目。In a more preferred embodiment, the mesh size of the screening is greater than 100 mesh.

在一更佳的实施例中,所述锂离子电池的正极材料为钴酸锂、三元锂、锰酸锂、钛酸锂和磷酸铁锂中的一种或多种。In a more preferred embodiment, the cathode material of the lithium-ion battery is one or more of lithium cobalt oxide, ternary lithium, lithium manganate, lithium titanate and lithium iron phosphate.

在一更佳的实施例中,所述碱性金属氢氧化物为氢氧化钠、氢氧化钾中的一种或两种的混合物。In a more preferred embodiment, the alkaline metal hydroxide is one or a mixture of sodium hydroxide and potassium hydroxide.

在一更佳的实施例中,所述正极材料与碱性金属氢氧化物混合的质量比为100:20~5;由于添加的碱性金属氢氧化物是为了将有机氟热催化转化为无机氟、并原位固化为氟化盐,其用量应控制在5%-20%。如果碱性金属氢氧化物添加比例过低,则催化效果和固化效果不佳;过高,则会影响后续正极材料中金属元素的回收。In a more preferred embodiment, the mass ratio of the mixture of the positive electrode material and the alkaline metal hydroxide is 100:20-5; since the added alkaline metal hydroxide is to thermally catalytically convert organic fluorine into inorganic Fluorine is cured in situ into fluoride salt, and its dosage should be controlled at 5%-20%. If the addition ratio of alkaline metal hydroxide is too low, the catalytic and curing effects will be poor; if it is too high, it will affect the subsequent recovery of metal elements in the cathode material.

在一更佳的实施例中,所述无氧焙烧的反应温度为300-500℃,所述无氧焙烧的反应时间为0.5-2h。In a more preferred embodiment, the reaction temperature of the oxygen-free roasting is 300-500°C, and the reaction time of the oxygen-free roasting is 0.5-2h.

在一更佳的实施例中,所述无氧焙烧是在氮气/氩气流量为50-100ml/min的条件下进行的。In a more preferred embodiment, the anaerobic roasting is performed under the condition of a nitrogen/argon flow rate of 50-100 ml/min.

在一更佳的实施例中,所述无氧焙烧是在真空度小于1000Pa的条件下进行的。In a more preferred embodiment, the oxygen-free roasting is performed under a vacuum degree of less than 1000 Pa.

在一更佳的实施例中,所述水洗过滤所用固液比为100-200g/L,时间为30min。In a more preferred embodiment, the solid-to-liquid ratio used for the water washing and filtration is 100-200g/L, and the time is 30 minutes.

综上所述,本申请包括以下至少一种有益技术效果:To sum up, this application includes at least one of the following beneficial technical effects:

(1)采用的热催化处理技术可有效提高有机氟的脱除效率,降低反应能垒,定向引导有机氟热催化转化为无机氟,利于污染固化;(1) The thermal catalytic treatment technology used can effectively improve the removal efficiency of organic fluorine, reduce the reaction energy barrier, and guide the thermal catalytic conversion of organic fluorine into inorganic fluorine, which is beneficial to the solidification of pollution;

(2)采用碱性金属氢氧化物同做催化剂和捕获剂,可将定向转化的无机氟原位捕获,固化为氟化盐,避免含氟热解产物逸散,造成二次污染。(2) Using alkaline metal hydroxide as a catalyst and capture agent, the directional converted inorganic fluorine can be captured in situ and solidified into fluoride salt to avoid fluorine-containing pyrolysis products from escaping and causing secondary pollution.

本发明的其它特征和有益效果将在随后的说明书中阐述,并且,部分地从说明书中变得显而易见,或者通过实施本发明而了解。本发明的目的和其他有益效果可通过在说明书、权利要求书以及附图中所特别指出的结构来实现和获得。Additional features and advantages of the invention will be set forth in the description which follows, and in part will be apparent from the description, or may be learned by practice of the invention. The objectives and other beneficial effects of the present invention may be realized and obtained by the structure particularly pointed out in the specification, claims and drawings.

附图说明Description of the drawings

为了更清楚地说明本发明实施例或现有技术中的技术方案,下面将对实施例或现有技术描述中所需要使用的附图作一简单地介绍,显而易见地,下面描述中的附图是本发明的一些实施例,对于本领域普通技术人员来讲,在不付出创造性劳动的前提下,还可以根据这些附图获得其他的附图;在下面描述中附图所述的位置关系,若无特别指明,皆是图示中组件绘示的方向为基准。In order to more clearly illustrate the embodiments of the present invention or the technical solutions in the prior art, the following will briefly introduce the drawings that need to be used in the description of the embodiments or the prior art. Obviously, the drawings in the following description are some embodiments of the present invention. For those of ordinary skill in the art, other drawings can be obtained based on these drawings without exerting creative efforts; in the following description, the positional relationships described in the drawings, Unless otherwise specified, the directions of the components in the illustrations are used as the basis.

图1为本发明的去除锂离子正极材料中有机氟的方法的工艺路线图;Figure 1 is a process road map of the method for removing organic fluorine in lithium ion cathode materials according to the present invention;

图2为本发明所提热催化技术处理前后锂离子电池正极材料中C/F元素的XPS图;Figure 2 is an XPS image of the C/F elements in the lithium-ion battery cathode material before and after the thermal catalytic technology treatment proposed by the present invention;

图3为本发明分离得到的氟化盐(氟化盐)XRD图。Figure 3 is an XRD pattern of the fluoride salt (fluoride salt) separated by the present invention.

具体实施方式Detailed ways

为使本发明实施例的目的、技术方案和优点更加清楚,下面将结合本发明实施例中的附图,对本发明实施例中的技术方案进行清楚、完整地描述,显然,所描述的实施例是本发明一部分实施例,而不是全部的实施例;下面所描述的本发明不同实施方式中所设计的技术特征只要彼此之间未构成冲突就可以相互结合;基于本发明中的实施例,本领域普通技术人员在没有作出创造性劳动前提下所获得的所有其他实施例,都属于本发明保护的范围。In order to make the purpose, technical solutions and advantages of the embodiments of the present invention clearer, the technical solutions in the embodiments of the present invention will be clearly and completely described below in conjunction with the drawings in the embodiments of the present invention. Obviously, the described embodiments These are some embodiments of the present invention, not all of them; the technical features designed in different embodiments of the present invention described below can be combined with each other as long as they do not conflict with each other; based on the embodiments of the present invention, All other embodiments obtained by those of ordinary skill in the art without creative efforts fall within the scope of protection of the present invention.

在本发明的描述中,需要说明的是,本发明所使用的所有术语(包括技术术语和科学术语)具有与本发明所属领域的普通技术人员通常所理解的含义相同的含义,不能理解为对本发明的限制;应进一步理解,本发明所使用的术语应被理解为具有与这些术语在本说明书的上下文和相关领域中的含义一致的含义,并且不应以理想化或过于正式的意义来理解,除本发明中明确如此定义之外。In the description of the present invention, it should be noted that all terms (including technical terms and scientific terms) used in the present invention have the same meaning as commonly understood by those of ordinary skill in the field to which the present invention belongs, and cannot be understood as being a definition of the present invention. Limitations of the Invention; It should be further understood that the terms used in the present invention should be understood to have meanings consistent with the meanings of these terms in the context of this specification and in the relevant fields, and should not be understood in an idealized or overly formal sense. , unless explicitly so defined in the present invention.

以下通过具体实施例对本发明的技术方案进行进一步的说明和描述。但本发明的保护范围不限于此。The technical solutions of the present invention will be further illustrated and described below through specific examples. However, the protection scope of the present invention is not limited to this.

实施例1Example 1

本实施例提供一种去除锂离子正极材料中有机氟的方法,参考图1所示,包括如下步骤:This embodiment provides a method for removing organic fluorine from lithium ion cathode materials, as shown in Figure 1, including the following steps:

1.将废旧锂离子电池经过拆解获得正极片,而后将正极片于1500rpm转速下破碎10min,经多级筛分,获得正极材料粉末(>100目);1. Disassemble the used lithium-ion battery to obtain the positive electrode sheet, then crush the positive electrode sheet at 1500 rpm for 10 minutes, and then undergo multi-stage screening to obtain the positive electrode material powder (>100 mesh);

2.将获得的正极材料与氢氧化钠以100:10的质量比均匀混合,然后进行无氧焙烧。控制氮气流量50ml/min,升温速率10℃/min,反应温度为500℃,反应时间为0.5h。2. Evenly mix the obtained cathode material and sodium hydroxide at a mass ratio of 100:10, and then perform oxygen-free roasting. Control the nitrogen flow rate to 50 ml/min, the heating rate to 10°C/min, the reaction temperature to 500°C, and the reaction time to 0.5h.

3.将反应后的残渣,经水洗过滤处理分别获得正极材料和氟化钠溶液,最终固氟率为91.23%,水洗过滤所用的固液比为200g/L,时间为30min。3. The reaction residue was washed and filtered to obtain the cathode material and sodium fluoride solution respectively. The final fluorine fixation rate was 91.23%. The solid-liquid ratio used for water washing and filtration was 200g/L and the time was 30 minutes.

实施例2Example 2

本实施例提供一种去除锂离子正极材料中有机氟的方法,参考图1所示,包括如下步骤:This embodiment provides a method for removing organic fluorine from lithium ion cathode materials, as shown in Figure 1, including the following steps:

1.将废旧锂离子电池经过拆解获得正极片,而后将正极片于1500rpm转速下破碎10min,经多级筛分,获得正极材料粉末(>100目);1. Disassemble the used lithium-ion battery to obtain the positive electrode sheet, then crush the positive electrode sheet at 1500 rpm for 10 minutes, and then undergo multi-stage screening to obtain the positive electrode material powder (>100 mesh);

2.将获得的正极材料与氢氧化钠以100:10的质量比均匀混合,然后进行无氧焙烧。控制氮气流量50ml/min,升温速率10℃/min,反应温度为400℃,反应时间为1h。2. Evenly mix the obtained cathode material and sodium hydroxide at a mass ratio of 100:10, and then perform oxygen-free roasting. Control the nitrogen flow rate to 50 ml/min, the heating rate to 10°C/min, the reaction temperature to 400°C, and the reaction time to 1 hour.

3.将反应后的残渣,经水洗过滤处理分别获得正极材料和氟化钠溶液,最终固氟率为88.56%,水洗过滤所用的固液比为200g/L,时间为30min。3. The reaction residue was washed and filtered to obtain the cathode material and sodium fluoride solution respectively. The final fluorine fixation rate was 88.56%. The solid-liquid ratio used for water washing and filtration was 200g/L and the time was 30 minutes.

实施例3Example 3

本实施例提供一种去除锂离子正极材料中有机氟的方法,参考图1所示,包括如下步骤:This embodiment provides a method for removing organic fluorine from lithium ion cathode materials, as shown in Figure 1, including the following steps:

1.将废旧锂离子电池经过拆解获得正极片,而后将正极片于1500rpm转速下破碎10min,经多级筛分,获得正极材料粉末(>100目);1. Disassemble the used lithium-ion battery to obtain the positive electrode sheet, then crush the positive electrode sheet at 1500 rpm for 10 minutes, and then undergo multi-stage screening to obtain the positive electrode material powder (>100 mesh);

2.将获得的正极材料与氢氧化钠以100:10的质量比均匀混合,然后进行无氧焙烧。控制氮气流量50ml/min,升温速率10℃/min,反应温度为300℃,反应时间为2h。2. Evenly mix the obtained cathode material and sodium hydroxide at a mass ratio of 100:10, and then perform oxygen-free roasting. Control the nitrogen flow rate to 50 ml/min, the heating rate to 10°C/min, the reaction temperature to 300°C, and the reaction time to 2 hours.

3.将反应后的残渣,经水洗过滤处理分别获得正极材料和氟化钠溶液,最终固氟率为51.04%,水洗过滤所用的固液比为200g/L,时间为30min,相比其他实施例而言,本实施例由于反应温度较低,因此固氟率有所下降。3. The residue after the reaction was washed and filtered to obtain the positive electrode material and sodium fluoride solution respectively. The final fluorine fixation rate was 51.04%. The solid-liquid ratio used for water washing and filtration was 200g/L and the time was 30 minutes. Compared with other implementations, For example, in this embodiment, due to the lower reaction temperature, the fluorine fixation rate decreases.

实施例4Example 4

本实施例提供一种去除锂离子正极材料中有机氟的方法,参考图1所示,包括如下步骤:This embodiment provides a method for removing organic fluorine from lithium ion cathode materials, as shown in Figure 1, including the following steps:

1.将废旧锂离子电池经过拆解获得正极片,而后将正极片于1500rpm转速下破碎10min,经多级筛分,获得正极材料粉末(>100目);1. Disassemble the used lithium-ion battery to obtain the positive electrode sheet, then crush the positive electrode sheet at 1500 rpm for 10 minutes, and then undergo multi-stage screening to obtain the positive electrode material powder (>100 mesh);

2.将获得的正极材料与氢氧化钠以100:5的质量比均匀混合,然后进行无氧焙烧。控制氮气流量50ml/min,升温速率10℃/min,反应温度为500℃,反应时间为0.5h。2. Evenly mix the obtained cathode material and sodium hydroxide at a mass ratio of 100:5, and then perform oxygen-free roasting. Control the nitrogen flow rate to 50 ml/min, the heating rate to 10°C/min, the reaction temperature to 500°C, and the reaction time to 0.5h.

3.将反应后的残渣,经水洗过滤处理分别获得正极材料和氟化钠溶液,最终固氟率为67.81%,水洗过滤所用的固液比为200g/L,时间为30min,相比其他实施例而言,本实施例由于氢氧化钠的用量比例较低,因此固氟率有所下降。3. The reaction residue was washed and filtered to obtain the cathode material and sodium fluoride solution respectively. The final fluorine fixation rate was 67.81%. The solid-liquid ratio used in the water washing and filtration was 200g/L and the time was 30 minutes. Compared with other implementations, For example, in this embodiment, the dosage ratio of sodium hydroxide is relatively low, so the fluorine fixation rate decreases.

实施例5Example 5

本实施例提供一种去除锂离子正极材料中有机氟的方法,参考图1所示,包括如下步骤:This embodiment provides a method for removing organic fluorine from lithium ion cathode materials, as shown in Figure 1, including the following steps:

1.将废旧锂离子电池经过拆解获得正极片,而后将正极片于1500rpm转速下破碎10min,经多级筛分,获得正极材料粉末(>100目);1. Disassemble the used lithium-ion battery to obtain the positive electrode sheet, then crush the positive electrode sheet at 1500 rpm for 10 minutes, and then undergo multi-stage screening to obtain the positive electrode material powder (>100 mesh);

2.将获得的正极材料与氢氧化钠以100:20的质量比均匀混合,然后进行无氧焙烧。控制氮气流量50ml/min,升温速率10℃/min,反应温度为500℃,反应时间为0.5h。2. Evenly mix the obtained cathode material and sodium hydroxide at a mass ratio of 100:20, and then perform oxygen-free roasting. Control the nitrogen flow rate to 50 ml/min, the heating rate to 10°C/min, the reaction temperature to 500°C, and the reaction time to 0.5h.

3.将反应后的残渣,经水洗过滤处理分别获得正极材料和氟化钠溶液,最终固氟率为92.54%,水洗过滤所用的固液比为200g/L,时间为30min。3. The reaction residue was washed and filtered to obtain the cathode material and sodium fluoride solution respectively. The final fluorine fixation rate was 92.54%. The solid-liquid ratio used for water washing and filtration was 200g/L and the time was 30 minutes.

实施例6Example 6

本实施例提供一种去除锂离子正极材料中有机氟的方法,参考图1所示,包括如下步骤:This embodiment provides a method for removing organic fluorine from lithium ion cathode materials, as shown in Figure 1, including the following steps:

1.将废旧锂离子电池经过拆解获得正极片,而后将正极片于1500rpm转速下破碎10min,经多级筛分,获得正极材料粉末(>100目);1. Disassemble the used lithium-ion battery to obtain the positive electrode sheet, then crush the positive electrode sheet at 1500 rpm for 10 minutes, and then undergo multi-stage screening to obtain the positive electrode material powder (>100 mesh);

2.将获得的正极材料与氢氧化钾以100:20的质量比均匀混合,然后进行无氧焙烧。控制氮气流量50ml/min,升温速率10℃/min,反应温度为500℃,反应时间为0.5h。2. Evenly mix the obtained cathode material and potassium hydroxide at a mass ratio of 100:20, and then perform oxygen-free roasting. Control the nitrogen flow rate to 50 ml/min, the heating rate to 10°C/min, the reaction temperature to 500°C, and the reaction time to 0.5h.

3.将反应后的残渣,经水洗过滤处理分别获得正极材料和氟化钠溶液,最终固氟率为90.07%,水洗过滤所用的固液比为200g/L,时间为30min。3. The reaction residue was washed and filtered to obtain the cathode material and sodium fluoride solution respectively. The final fluorine fixation rate was 90.07%. The solid-liquid ratio used for water washing and filtration was 200g/L and the time was 30 minutes.

实施例7Example 7

本实施例提供一种去除锂离子正极材料中有机氟的方法,参考图1所示,包括如下步骤:This embodiment provides a method for removing organic fluorine from lithium ion cathode materials, as shown in Figure 1, including the following steps:

1.将废旧锂离子电池经过拆解获得正极片,而后将正极片于1500rpm转速下破碎10min,经多级筛分,获得正极材料粉末(>100目);1. Disassemble the used lithium-ion battery to obtain the positive electrode sheet, then crush the positive electrode sheet at 1500 rpm for 10 minutes, and then undergo multi-stage screening to obtain the positive electrode material powder (>100 mesh);

2.将获得的正极材料与氢氧化钠/氢氧化钾混合物(氢氧化钠和氢氧化钾质量比1:1)以100:10的质量比均匀混合,然后进行无氧焙烧。控制氮气流量50ml/min,升温速率10℃/min,反应温度为500℃,反应时间为0.5h。2. Evenly mix the obtained cathode material with the sodium hydroxide/potassium hydroxide mixture (mass ratio of sodium hydroxide and potassium hydroxide 1:1) at a mass ratio of 100:10, and then perform anaerobic roasting. Control the nitrogen flow rate to 50 ml/min, the heating rate to 10°C/min, the reaction temperature to 500°C, and the reaction time to 0.5h.

3.将反应后的残渣,经水洗过滤处理分别获得正极材料和氟化钠溶液,最终固氟率为93.11%,水洗过滤所用的固液比为200g/L,时间为30min。3. The reaction residue was washed and filtered to obtain the cathode material and sodium fluoride solution respectively. The final fluorine fixation rate was 93.11%. The solid-liquid ratio used for water washing and filtration was 200g/L and the time was 30 minutes.

需要说明的是,上述实施例中的具体参数或一些常用试剂,为本发明构思下的具体实施例或优选实施例,而非对其限制;本领域技术人员在本发明构思及保护范围内,可以进行适应性调整。此外,若无特殊说明,所采用的原料也可以为本领域常规市售产品、或者由本领域常规方法制备得到。It should be noted that the specific parameters or some commonly used reagents in the above embodiments are specific embodiments or preferred embodiments under the concept of the present invention, and are not limitations thereof; those skilled in the art, within the concept and protection scope of the present invention, Adaptable adjustments are possible. In addition, unless otherwise specified, the raw materials used may also be conventional commercially available products in the art, or may be prepared by conventional methods in the art.

对比例1Comparative example 1

本对比例提供一种去除锂离子正极材料中有机氟的方法,包括如下步骤:This comparative example provides a method for removing organic fluorine from lithium ion cathode materials, including the following steps:

1.将废旧锂离子电池经过拆解获得正极片,而后将正极片于1500rpm转速下破碎10min,经多级筛分,获得正极材料粉末(>100目);1. Disassemble the used lithium-ion battery to obtain the positive electrode sheet, then crush the positive electrode sheet at 1500 rpm for 10 minutes, and then undergo multi-stage screening to obtain the positive electrode material powder (>100 mesh);

2.将获得的正极材料与氢氧化钠以100:1的质量比均匀混合,然后进行无氧焙烧。控制氩气流量50ml/min,升温速率10℃/min,反应温度为500℃,反应时间为0.5h。2. Evenly mix the obtained cathode material and sodium hydroxide at a mass ratio of 100:1, and then perform oxygen-free roasting. Control the argon flow rate to 50 ml/min, the heating rate to 10°C/min, the reaction temperature to 500°C, and the reaction time to 0.5h.

3.将反应后的残渣,经水洗过滤处理分别获得正极材料和氟化钠溶液,最终固氟率为21.23%,水洗过滤所用的固液比为200g/L,时间为30min。3. The reaction residue was washed and filtered to obtain the cathode material and sodium fluoride solution respectively. The final fluorine fixation rate was 21.23%. The solid-liquid ratio used for water washing and filtration was 200g/L and the time was 30 minutes.

4.由于碱性金属氢氧化物使用量过低,有机氟的脱除及固化效果不佳,未有效得到氟化盐。4. Because the amount of alkaline metal hydroxide used is too low, the removal and solidification effect of organic fluorine is not good, and the fluoride salt is not effectively obtained.

若比例过高(即超过100:20),则固氟率趋于稳定,即达到93%后开始趋于平稳,继续增加氢氧化钠/氢氧化钾的用量对于固氟率的增加没有显著影响,因此,最佳的比例范围在100:5-20以下。If the ratio is too high (that is, more than 100:20), the fluoride fixation rate will become stable, that is, it will start to level off after reaching 93%. Continuing to increase the dosage of sodium hydroxide/potassium hydroxide will have no significant impact on the increase in the fluorine fixation rate. , therefore, the optimal ratio range is below 100:5-20.

对比例2Comparative example 2

本对比例提供一种去除锂离子正极材料中有机氟的方法,包括如下步骤:This comparative example provides a method for removing organic fluorine from lithium ion cathode materials, including the following steps:

1.将废旧锂离子电池经过拆解获得正极片,而后将正极片于1500rpm转速下破碎10min,经多级筛分,获得正极材料粉末(>100目);1. Disassemble the used lithium-ion battery to obtain the positive electrode sheet, then crush the positive electrode sheet at 1500 rpm for 10 minutes, and then undergo multi-stage screening to obtain the positive electrode material powder (>100 mesh);

2.将获得的正极材料与氢氧化钙以100:10的质量比均匀混合,然后进行无氧焙烧。控制氩气流量50ml/min,升温速率10℃/min,反应温度为300℃,反应时间为2h。2. Evenly mix the obtained cathode material and calcium hydroxide at a mass ratio of 100:10, and then perform oxygen-free roasting. Control the argon flow rate to 50 ml/min, the heating rate to 10°C/min, the reaction temperature to 300°C, and the reaction time to 2 hours.

3.将反应后的残渣,经水洗过滤处理分别获得正极材料和氟化钠溶液,最终固氟率为0%,水洗过滤条件为,固液比200g/L,时间30min。3. Wash and filter the residue after the reaction to obtain the positive electrode material and sodium fluoride solution respectively. The final fluorine fixation rate is 0%. The washing and filtration conditions are: solid-liquid ratio 200g/L, time 30 minutes.

4.由于采用的碱性金属氢氧化物是氢氧化钙,氢氧化钙因为其高熔沸点,影响催化与固氟效果。4. Since the alkaline metal hydroxide used is calcium hydroxide, calcium hydroxide affects the catalytic and fluorine fixation effects due to its high melting and boiling point.

图2为本发明所提去除方法处理锂离子电池正极材料的SEM图像及C/O/F/Na元素的EDS图,由图2可知,经过热催化处理后,正极材料中有机氟得到有效地去除并固化为氟化钠,具体对应实施例1中处理后的正极材料。Figure 2 is an SEM image of the cathode material of a lithium-ion battery treated by the removal method proposed by the present invention and an EDS image of the C/O/F/Na element. It can be seen from Figure 2 that after thermal catalytic treatment, the organic fluorine in the cathode material is effectively removed Removed and solidified into sodium fluoride, specifically corresponding to the treated cathode material in Example 1.

图3为本发明分离得到的氟化盐(氟化盐)XRD图,由图3可知,当使用碱性金属氢氧化物进行热催化处理后,正极材料中有机氟被定向转化为无机氟并固化为氟化盐,具体对应实施例1-4。Figure 3 is an XRD pattern of the fluoride salt (fluoride salt) separated by the present invention. It can be seen from Figure 3 that when an alkaline metal hydroxide is used for thermal catalytic treatment, the organic fluorine in the cathode material is directionally converted into inorganic fluoride. Solidify into fluoride salt, specifically corresponding to Examples 1-4.

综上所述,本发明利用碱性金属氢氧化物同作催化剂和捕获剂,一步实现锂离子电池正极材料中有机氟的热催化脱除及其固化分离,既有效去除了有机氟粘结剂、利于正极材料的资源化利用,同时又有效避免了有机氟潜在的二次环境污染风险。本方法依托于工业上应用广泛的热处理技术,操作简单、易规模化应用,具有广泛的工业应用潜力。In summary, the present invention uses alkaline metal hydroxide as both a catalyst and a capture agent to realize the thermal catalytic removal and solidification separation of organic fluorine in the lithium-ion battery cathode material in one step, effectively removing the organic fluorine binder. , conducive to resource utilization of cathode materials, and at the same time effectively avoids potential secondary environmental pollution risks of organic fluorine. This method relies on heat treatment technology that is widely used in industry, is simple to operate, easy to apply on a large scale, and has broad industrial application potential.

另外,本领域技术人员应当理解,尽管现有技术中存在许多问题,但是,本发明的每个实施例或技术方案可以仅在一个或几个方面进行改进,而不必同时解决现有技术中或者背景技术中列出的全部技术问题。本领域技术人员应当理解,对于一个权利要求中没有提到的内容不应当作为对于该权利要求的限制。In addition, those skilled in the art should understand that although there are many problems in the prior art, each embodiment or technical solution of the present invention can only be improved in one or several aspects, without having to simultaneously solve the problems in the prior art or All technical issues listed in the background art. Those skilled in the art will understand that content not mentioned in a claim shall not be used as a limitation on the claim.

尽管本文中较多的使用了诸如正极片、正极材料、碱性金属氢氧化物、无氧焙烧、水洗过滤等术语,但并不排除使用其它术语的可能性。使用这些术语仅仅是为了更方便地描述和解释本发明的本质;把它们解释成任何一种附加的限制都是与本发明精神相违背的;本发明实施例的说明书和权利要求书及上述附图中的术语“第一”、“第二”、等(如果存在)是用于区别类似的对象,而不必用于描述特定的顺序或先后次序。Although terms such as cathode sheet, cathode material, alkaline metal hydroxide, oxygen-free roasting, water washing and filtration are frequently used in this article, the possibility of using other terms is not excluded. The use of these terms is only to more conveniently describe and explain the essence of the present invention; interpreting them as any additional restrictions is contrary to the spirit of the present invention; the description and claims of the embodiments of the present invention and the above appendix The terms "first", "second", etc. (if present) in the figures are used to distinguish similar objects and are not necessarily used to describe a specific order or sequence.

最后应说明的是:以上各实施例仅用以说明本发明的技术方案,而非对其限制;尽管参照前述各实施例对本发明进行了详细的说明,本领域的普通技术人员应当理解:其依然可以对前述各实施例所记载的技术方案进行修改,或者对其中部分或者全部技术特征进行等同替换;而这些修改或者替换,并不使相应技术方案的本质脱离本发明各实施例技术方案的范围。Finally, it should be noted that the above embodiments are only used to illustrate the technical solution of the present invention, but not to limit it. Although the present invention has been described in detail with reference to the foregoing embodiments, those of ordinary skill in the art should understand that: The technical solutions described in the foregoing embodiments can still be modified, or some or all of the technical features can be equivalently replaced; and these modifications or substitutions do not deviate from the essence of the corresponding technical solutions from the technical solutions of the embodiments of the present invention. scope.

Claims (10)

1. A method for removing organic fluorine in a lithium ion positive electrode material, comprising the steps of:
obtaining a positive plate of the waste lithium ion battery;
crushing and screening the positive plate to obtain a positive material;
mixing the obtained anode material with alkaline metal hydroxide, and then performing anaerobic roasting;
and washing and filtering the product after anaerobic roasting.
2. The method for removing organic fluorine in a lithium ion cathode material according to claim 1, wherein: the rotational speed of the crushing is 1000-2000rpm, and the crushing time is 5-30min.
3. The method for removing organic fluorine in a lithium ion cathode material according to claim 1, wherein: the mesh number of the screening is more than 100 meshes.
4. The method for removing organic fluorine in a lithium ion cathode material according to claim 1, wherein: the positive electrode material of the lithium ion battery is one or more of lithium cobaltate, ternary lithium, lithium manganate, lithium titanate and lithium iron phosphate.
5. The method for removing organic fluorine in a lithium ion cathode material according to claim 1, wherein: the alkaline metal hydroxide is one or a mixture of two of sodium hydroxide and potassium hydroxide.
6. The method for removing organic fluorine in a lithium ion cathode material according to claim 1, wherein: the mass ratio of the positive electrode material to the alkaline metal hydroxide is 100:20-5.
7. The method for removing organic fluorine in a lithium ion cathode material according to claim 1, wherein: the reaction temperature of the anaerobic roasting is 300-500 ℃, and the reaction time of the anaerobic roasting is 0.5-2h.
8. The method for removing organic fluorine in a lithium ion cathode material according to claim 1, wherein: the anaerobic roasting is carried out under the condition of 50-100ml/min of nitrogen/argon flow.
9. The method for removing organic fluorine in a lithium ion cathode material according to claim 1, wherein: the anaerobic roasting is carried out under the condition that the vacuum degree is less than 1000 Pa.
10. The method for removing organic fluorine in a lithium ion cathode material according to claim 1, wherein: the solid-liquid ratio used for the water washing and filtering is 100-200g/L, and the time is 30min.
CN202310759825.0A 2023-06-26 2023-06-26 Method for removing organic fluorine in lithium ion positive electrode material Pending CN116789150A (en)

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Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110364748A (en) * 2019-07-29 2019-10-22 清远佳致新材料研究院有限公司 The regeneration method of waste lithium ion cell anode material
CN111392750A (en) * 2020-04-02 2020-07-10 天齐锂业股份有限公司 Method for removing impurities and recovering lithium from waste lithium ion batteries
US20220013815A1 (en) * 2020-07-08 2022-01-13 American Hyperform, Inc. Process for Recycling Cobalt and Nickel from Lithium Ion Batteries
CN115699405A (en) * 2020-09-11 2023-02-03 株式会社Lg新能源 Method for recovering positive electrode material
CN116024439A (en) * 2022-10-14 2023-04-28 中国矿业大学 A kind of selective extraction method of lithium element in waste lithium ion battery

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110364748A (en) * 2019-07-29 2019-10-22 清远佳致新材料研究院有限公司 The regeneration method of waste lithium ion cell anode material
CN111392750A (en) * 2020-04-02 2020-07-10 天齐锂业股份有限公司 Method for removing impurities and recovering lithium from waste lithium ion batteries
US20220013815A1 (en) * 2020-07-08 2022-01-13 American Hyperform, Inc. Process for Recycling Cobalt and Nickel from Lithium Ion Batteries
CN115699405A (en) * 2020-09-11 2023-02-03 株式会社Lg新能源 Method for recovering positive electrode material
CN116024439A (en) * 2022-10-14 2023-04-28 中国矿业大学 A kind of selective extraction method of lithium element in waste lithium ion battery

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