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CN105331819A - Method for recycling Co3O4 from positive electrode material of waste lithium cobalt oxide battery - Google Patents

Method for recycling Co3O4 from positive electrode material of waste lithium cobalt oxide battery Download PDF

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CN105331819A
CN105331819A CN201510754980.9A CN201510754980A CN105331819A CN 105331819 A CN105331819 A CN 105331819A CN 201510754980 A CN201510754980 A CN 201510754980A CN 105331819 A CN105331819 A CN 105331819A
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waste lithium
positive electrode
acid
cobalt oxide
waste
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刘建文
郑莹
李敏平
张阳阳
宋鑫
周来
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Hubei University
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Hubei University
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    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
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    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

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Abstract

The invention discloses a method for recycling Co3O4 from a positive electrode material of a waste lithium cobalt oxide battery. By means of an organic acid leaching method, the positive electrode material of the waste lithium cobalt oxide battery is obtained through separation, operation is simple, and the separation rate reaches more than 98%. Meanwhile, in the leaching process, the pollution to the environment is reduced by selecting organic acid. Zero pollution to the environment is achieved in the process of obtaining Co3O4 through spraying sintering, and operation is simple and feasible. An obtained product is stable in chemical property, the material performance is superior, and the product can serve as an electronic material and can also be widely applied to catalysts and oxidizing agents and applied to manufacturing cobalt salt, enamel pigment and the like.

Description

从废旧钴酸锂电池正极材料中回收Co3O4的方法Method for recovering Co3O4 from waste lithium cobalt oxide battery cathode material

技术领域technical field

本发明属于废旧钴酸锂电池正极材料回收领域,尤其涉及一种从废旧钴酸锂电池正极材料中回收Co3O4的方法。The invention belongs to the field of recycling positive electrode materials of waste lithium cobalt oxide batteries, and in particular relates to a method for recovering Co3O4 from the positive electrode materials of waste lithium cobalt oxide batteries .

背景技术Background technique

如今,随着锂离子电池的不断发展,其应用变得越来越广泛。锂离子电池由于充电电压高、比能量大、循环寿命长、安全性能好、无公害、无记忆效应、自放电小等优点,已广泛应用于便携式电子产品领域,包括移动电话、笔记本电脑、摄像机、数码相机、医疗器械等。锂离子电池的广泛使用势必带来大量废旧电池,废旧锂离子电池含有多种无机、有机化合物,暴露于环境中对环境造成严重污染。因此,废旧锂离子电池进行资源回收,对降低环境污染,资源再利用,具有积极的现实意义。Today, with the continuous development of lithium-ion batteries, their applications are becoming more and more extensive. Due to the advantages of high charging voltage, large specific energy, long cycle life, good safety performance, no pollution, no memory effect, and small self-discharge, lithium-ion batteries have been widely used in the field of portable electronic products, including mobile phones, notebook computers, cameras , digital cameras, medical equipment, etc. The widespread use of lithium-ion batteries will inevitably bring a large number of waste batteries. Waste lithium-ion batteries contain a variety of inorganic and organic compounds, which will cause serious pollution to the environment when exposed to the environment. Therefore, recycling waste lithium-ion batteries has positive practical significance for reducing environmental pollution and reusing resources.

而废旧锂离子电池中含有大量价格昂贵的金属钴,而我国钴资源短缺,生产过程中金属回收率低,工艺复杂,生产成本高。如果能将废旧锂离子电池中的钴资源加以回收利用,无论是从环保方面,还是资源的循环利用方面来讲,都具有重大意义的,其中氧化物Co3O4应用广泛,可用于催化剂、氧化剂,制造钴盐、搪瓷颜料等,其回收制备的价值的很大。However, waste lithium-ion batteries contain a large amount of expensive metal cobalt, and my country has a shortage of cobalt resources. The metal recovery rate in the production process is low, the process is complicated, and the production cost is high. If the cobalt resources in the waste lithium-ion batteries can be recycled, it is of great significance both in terms of environmental protection and resource recycling. Among them, the oxide Co 3 O 4 is widely used and can be used for catalysts, Oxidants, cobalt salts, enamel pigments, etc., are of great value for their recovery and preparation.

目前关于废旧锂离子电池正极材料回收技术主要分为两大过程:一是分离浸出过程。CN101280357B公开了一种废旧锂电池回收的酸浸萃取工艺,主要采用硫酸、双氧水等浸出。CN1688065A则指出得到的废旧电池材料在酸性条件下用双氧水或硫代硫酸钠作为还原剂浸出,再以氢氧化钠为沉淀剂沉淀钴。CN103757399A公开了采用硫酸和硝酸联合浸出的方法来处理废旧锂电池的方法。二是煅烧制备过程。CN101673859A公开了一种从废旧锂离子电池中回收钴酸锂的方法,一次煅烧形成干凝胶,二次煅烧形成钴酸锂电极材料。CN104103870A经过分离浸出球磨之后,分离锂和钴分别得到草酸钴和碳酸锂。CN102751549A则公开了采用镍钴锰碳酸盐三元前驱体与分离的废旧材料调控,最终得到三元系复合正极材料的方法。At present, the recovery technology of waste lithium-ion battery cathode materials is mainly divided into two processes: one is the separation and leaching process. CN101280357B discloses an acid leaching extraction process for recycling waste lithium batteries, mainly using sulfuric acid, hydrogen peroxide and the like for leaching. CN1688065A points out that the obtained waste battery material is leached with hydrogen peroxide or sodium thiosulfate as a reducing agent under acidic conditions, and then cobalt is precipitated with sodium hydroxide as a precipitating agent. CN103757399A discloses a method for treating waste lithium batteries using a combined leaching method of sulfuric acid and nitric acid. The second is the calcination preparation process. CN101673859A discloses a method for recovering lithium cobaltate from waste lithium-ion batteries. The first calcination forms a xerogel, and the second calcination forms a lithium cobaltate electrode material. After CN104103870A undergoes separation, leaching and ball milling, lithium and cobalt are separated to obtain cobalt oxalate and lithium carbonate respectively. CN102751549A discloses a method for finally obtaining a ternary composite positive electrode material by using nickel-cobalt-manganese carbonate ternary precursor and separated waste materials to regulate.

从已公开的现有技术来看,废旧锂离子电池回收领域还主要存在以下问题:一是浸出部分,大部分采用无机强酸如:硫酸、盐酸、硝酸等,会对周围环境造成二次污染、且能耗大;二是煅烧制备过程,煅烧过程中产生有毒有害气体,造成粉尘和重金属污染。Judging from the disclosed prior art, the following problems still exist in the field of waste lithium-ion battery recycling: one is the leaching part, most of which use inorganic strong acids such as sulfuric acid, hydrochloric acid, nitric acid, etc., which will cause secondary pollution to the surrounding environment, And the energy consumption is large; the second is the calcination preparation process, which produces toxic and harmful gases during the calcination process, causing dust and heavy metal pollution.

发明内容Contents of the invention

为了达到上述目的,本发明提供了一种分离率高、对环境的污染程度低、回收的材料性能优良的从废旧钴酸锂电池正极材料中回收Co3O4的方法。In order to achieve the above purpose, the present invention provides a method for recovering Co 3 O 4 from waste lithium cobaltate battery cathode materials with high separation rate, low environmental pollution and excellent performance of recovered materials.

本发明提供了一种从废旧钴酸锂电池正极材料中回收Co3O4的方法,其包括以下步骤:The present invention provides a kind of method that reclaims Co 3 O 4 from waste and old lithium cobalt oxide battery anode material, and it comprises the following steps:

步骤A,将废旧LiCoO2电池拆解开,取出正极片,加有机溶剂浸泡10~60min,固液比为1:5~1:15,过滤分离集电体,干燥得到黑色固体;Step A , disassemble the waste LiCoO2 battery, take out the positive electrode sheet, soak in an organic solvent for 10-60 minutes, the solid-liquid ratio is 1:5-1:15, filter and separate the current collector, and dry to obtain a black solid;

步骤B,将步骤A分离得到的黑色固体,加入有机酸和H2O2溶液,固液比控制在5~20g/l,在30~90℃下搅拌浸出1~5h,过滤得到含钴的滤液;Step B, adding organic acid and H 2 O 2 solution to the black solid obtained in Step A, controlling the solid-liquid ratio at 5-20 g/l, stirring and leaching at 30-90°C for 1-5 hours, and filtering to obtain cobalt-containing filtrate;

步骤C,往步骤B得到的滤液中加入相应的钴离子萃取剂,萃取得到钴离子络合物;Step C, adding the corresponding cobalt ion extractant to the filtrate obtained in step B, and extracting to obtain a cobalt ion complex;

步骤D,向步骤C得到钴离子络合物中鼓入氧气,在600~1300℃,180~300MPa条件下焙烧,得到Co3O4经过脱酸处理后以粉末的形式回收。Step D, bubbling oxygen into the cobalt ion complex obtained in step C, roasting at 600-1300° C., 180-300 MPa to obtain Co 3 O 4 which is deacidified and recovered in the form of powder.

本发明提供的从废旧钴酸锂电池正极材料中回收Co3O4的方法的有益效果是:The beneficial effects of the method for reclaiming Co from waste lithium cobalt oxide battery positive electrode materials provided by the present invention O The method is:

(1)本发明采用有机酸浸出方法分离得到废旧钴酸锂电池正极材料,操作简单,分离率高达到98%以上;同时,浸出过程选用有机酸降低了对环境的污染。(1) The present invention uses an organic acid leaching method to separate and obtain the positive electrode material of the waste lithium cobalt oxide battery, which is simple to operate and has a separation rate as high as 98% or more; meanwhile, the organic acid used in the leaching process reduces environmental pollution.

(2)本发明利用喷雾焙烧得到Co3O4的过程对环境零污染,且操作简单易行,得到的产品化学性质稳定,材料性能优良,不仅可作为电子材料使用,还可广泛应用于催化剂、氧化剂,制造钴盐、搪瓷颜料等。(2) The process of obtaining Co 3 O 4 by spray roasting in the present invention has zero pollution to the environment, and the operation is simple and easy. The obtained product has stable chemical properties and excellent material performance. It can not only be used as electronic materials, but also widely used in catalysts , oxidant, manufacture cobalt salt, enamel pigment, etc.

附图说明Description of drawings

图1为本发明从废旧钴酸锂电池正极材料中回收Co3O4的方法的流程图。Fig. 1 is a flow chart of the method for recovering Co 3 O 4 from waste lithium cobalt oxide battery cathode materials according to the present invention.

图2为通过本发明方法回收的Co3O4的形貌特征图。Fig. 2 is a characteristic diagram of the morphology of Co 3 O 4 recovered by the method of the present invention.

具体实施方式detailed description

如图1所示,本发明提供了一种从废旧钴酸锂电池正极材料中回收Co3O4的方法,其包括以下步骤:As shown in Figure 1 , the present invention provides a kind of method that reclaims Co3O4 from waste lithium cobalt oxide battery cathode material, and it comprises the following steps:

步骤A,将废旧LiCoO2电池拆解开,取出正极片,加有机溶剂浸泡10~60min,固液比为1:5~1:15,过滤分离集电体,干燥得到黑色固体;Step A , disassemble the waste LiCoO2 battery, take out the positive electrode sheet, soak in an organic solvent for 10-60 minutes, the solid-liquid ratio is 1:5-1:15, filter and separate the current collector, and dry to obtain a black solid;

步骤B,将步骤A分离得到的黑色固体,加入有机酸和H2O2溶液,固液比控制在5~20g/l,在30~90℃下搅拌浸出1~5h,过滤得到含钴的滤液;Step B, adding organic acid and H 2 O 2 solution to the black solid obtained in Step A, controlling the solid-liquid ratio at 5-20 g/l, stirring and leaching at 30-90°C for 1-5 hours, and filtering to obtain cobalt-containing filtrate;

步骤C,往步骤B得到的滤液中加入相应的钴离子萃取剂,萃取得到钴离子络合物;Step C, adding the corresponding cobalt ion extractant to the filtrate obtained in step B, and extracting to obtain a cobalt ion complex;

步骤D,向步骤C得到钴离子络合物中鼓入氧气,在600~1300℃,180~300MPa条件下焙烧,得到Co3O4经过脱酸处理后以粉末的形式回收。Step D, bubbling oxygen into the cobalt ion complex obtained in step C, roasting at 600-1300° C., 180-300 MPa to obtain Co 3 O 4 which is deacidified and recovered in the form of powder.

优选的,所述步骤A中浸泡过程配合超声和机械搅拌10~60min。Preferably, the soaking process in step A is combined with ultrasonic and mechanical stirring for 10-60 minutes.

优选的,所述步骤A中有机溶剂包括二甲基甲酰胺、N-甲基吡咯烷酮、二甲基乙酰胺或二甲基亚砜。Preferably, the organic solvent in step A includes dimethylformamide, N-methylpyrrolidone, dimethylacetamide or dimethylsulfoxide.

优选的,所述步骤B中有机酸包括柠檬酸、乙酸、草酸、甲酸、马来酸或抗坏血酸,用量为30~50g/l。Preferably, the organic acid in step B includes citric acid, acetic acid, oxalic acid, formic acid, maleic acid or ascorbic acid, and the dosage is 30-50 g/l.

优选的,步骤B中H2O2溶液体积分数为0.1~2%,用量为LiCoO2的1.2~2摩尔倍数。Preferably, in step B, the volume fraction of the H 2 O 2 solution is 0.1-2%, and the amount used is 1.2-2 mole multiples of LiCoO 2 .

优选的,步骤C中所述钴离子萃取剂包括叔碳羧酸Versatic911、二(2-羟基-5-辛基)苯甲胺、2-乙基己基三(辛-癸)烷基叔胺、二(2-乙基己基)磷酸酯或乙基己基磷酸单-2-乙基己酯。Preferably, the cobalt ion extractant described in step C includes tertiary carbon carboxylic acid Versatic911, two (2-hydroxy-5-octyl) benzylamine, 2-ethylhexyl tri (octyl-decyl) alkyl tertiary amine, Di(2-ethylhexyl)phosphate or mono-2-ethylhexyl ethylhexylphosphate.

优选的,步骤D在焙烧炉中进行,通过并鼓入空气的形式鼓入氧气。Preferably, step D is carried out in a roasting furnace, and oxygen gas is blown through and blown in air.

下面结合具体实施例,进一步对本发明进行详细描述。当然所描述的实施例仅是本发明的一部分实施例,而不是全部实施例,基于本发明中的实施例,本领域技术人员在没有做出创造性劳动前提下所获得的所有其他实施例,都属于本发明的保护范围。The present invention will be further described in detail below in conjunction with specific embodiments. Of course, the described embodiments are only some of the embodiments of the present invention, rather than all embodiments. Based on the embodiments of the present invention, all other embodiments obtained by those skilled in the art without creative work are all Belong to the protection scope of the present invention.

实施例1Example 1

将废旧的LiCoO2电池手工破碎拆解,取出其中的正极片。将上述正极片浸泡于NMP溶液中,以1:5的固液比(g/ml)在室温条件下,配合机械搅拌10min,过滤干燥收集其中的黑色粉末。The waste LiCoO 2 battery was manually broken and disassembled, and the positive electrode sheet was taken out. Soak the above-mentioned positive electrode sheet in NMP solution, stir it mechanically for 10 min at room temperature with a solid-to-liquid ratio (g/ml) of 1:5, filter and dry to collect the black powder therein.

取分离阶段中得到的黑色粉末,加入柠檬酸浸出,酸的用量为30g/l,按摩尔比1:1.5加入体积分数为1%的H2O2,固液比控制在10g/l,在30℃下搅拌浸出5h,过滤得到含钴的滤液。Take the black powder obtained in the separation stage, add citric acid for leaching, the acid consumption is 30g/l, add H 2 O 2 with a volume fraction of 1% according to the molar ratio 1:1.5, and the solid-liquid ratio is controlled at 10g/l. Stir and leach at 30°C for 5 hours, and filter to obtain a cobalt-containing filtrate.

往滤液中加入叔碳羧酸Versatic911,萃取1h,得到较为纯净的Co离子络合物。Add tertiary carbon carboxylic acid Versatic911 to the filtrate and extract for 1 hour to obtain relatively pure Co ion complex.

经过萃取得到钴酸盐浸出液通过气动给料装置送入焙烧炉中,并鼓入空气,将焙烧炉加热区域的温度控制在600℃,炉顶负压控制在280MPa,焙烧得到的Co3O4经过脱酸处理后以粉末的形式回收。After extraction, the cobaltate leaching liquid is sent into the roasting furnace through a pneumatic feeding device, and air is blown in. The temperature of the heating area of the roasting furnace is controlled at 600 ° C, and the negative pressure on the top of the furnace is controlled at 280 MPa. The Co 3 O 4 obtained by roasting It is recovered in the form of powder after deacidification treatment.

实施例2Example 2

将废旧的LiCoO2电池手工破碎拆解,取出其中的正极片。将上述正极片浸泡于DMF溶液中,以1:15的固液比(g/ml)在室温条件下,配合机械搅拌30min,过滤干燥收集其中的黑色粉末。The waste LiCoO 2 battery was manually broken and disassembled, and the positive electrode sheet was taken out. Soak the above-mentioned positive electrode sheet in DMF solution, with a solid-to-liquid ratio (g/ml) of 1:15 at room temperature, with mechanical stirring for 30 minutes, filter and dry to collect the black powder therein.

取分离阶段中得到的黑色粉末,加入乙酸浸出,酸的用量为50g/l,按摩尔比1:2加入体积分数为1%的H2O2,固液比控制在20g/l,在60℃下搅拌浸出3h,过滤得到含钴的滤液。Take the black powder obtained in the separation stage, add acetic acid for leaching, the amount of acid is 50g/l, add H 2 O 2 with a volume fraction of 1% in a molar ratio of 1:2, and control the solid-liquid ratio at 20g/l, at 60 Stir and leach for 3 hours at °C, and filter to obtain a cobalt-containing filtrate.

往滤液中加入二(2-羟基-5-辛基)苯甲胺,萃取1h,得到较为纯净的Co离子络合物。Add bis(2-hydroxy-5-octyl)benzylamine to the filtrate and extract for 1 hour to obtain relatively pure Co ion complex.

经过萃取得到钴酸盐浸出液通过气动给料装置送入焙烧炉中,并鼓入空气,将焙烧炉加热区域的温度控制在1000℃,炉顶负压控制在280MPa,焙烧得到的Co3O4经过脱酸处理后以粉末的形式回收。After extraction, the cobaltate leaching liquid is sent to the roasting furnace through a pneumatic feeding device, and air is blown in. The temperature of the heating area of the roasting furnace is controlled at 1000 ° C, and the negative pressure on the top of the furnace is controlled at 280 MPa. The Co 3 O 4 obtained by roasting It is recovered in the form of powder after deacidification treatment.

图2为通过本发明方法回收的Co3O4的形貌特征图。由图2可知,所述Co3O4粉末颗粒尺寸均匀,杂质相少,颗粒团聚较少,性能稳定。Fig. 2 is a characteristic diagram of the morphology of Co 3 O 4 recovered by the method of the present invention. It can be seen from Fig. 2 that the Co 3 O 4 powder has uniform particle size, less impurity phase, less particle agglomeration, and stable performance.

Claims (7)

1.一种从废旧钴酸锂电池正极材料中回收Co3O4的方法,其包括以下步骤:1. a kind of reclaiming Co from waste and old lithium cobalt oxide battery anode material 3 O 4 method, it may further comprise the steps: 步骤A,将废旧LiCoO2电池拆解开,取出正极片,加有机溶剂浸泡10~60min,固液比为1:5~1:15,过滤分离集电体,干燥得到黑色固体;Step A , disassemble the waste LiCoO2 battery, take out the positive electrode sheet, soak in an organic solvent for 10-60 minutes, the solid-liquid ratio is 1:5-1:15, filter and separate the current collector, and dry to obtain a black solid; 步骤B,将步骤A分离得到的黑色固体,加入有机酸和H2O2溶液,固液比控制在5~20g/l,在30~90℃下搅拌浸出1~5h,过滤得到含钴的滤液;Step B, adding organic acid and H 2 O 2 solution to the black solid obtained in Step A, controlling the solid-liquid ratio at 5-20 g/l, stirring and leaching at 30-90°C for 1-5 hours, and filtering to obtain cobalt-containing filtrate; 步骤C,往步骤B得到的滤液中加入相应的钴离子萃取剂,萃取得到钴离子络合物;Step C, adding the corresponding cobalt ion extractant to the filtrate obtained in step B, and extracting to obtain a cobalt ion complex; 步骤D,向步骤C得到钴离子络合物中鼓入氧气,在600~1300℃,180~300MPa条件下焙烧,得到Co3O4经过脱酸处理后以粉末的形式回收。Step D, bubbling oxygen into the cobalt ion complex obtained in step C, roasting at 600-1300° C., 180-300 MPa to obtain Co 3 O 4 which is deacidified and recovered in the form of powder. 2.如权利要求1所述的从废旧钴酸锂电池正极材料中回收Co3O4的方法,其特征在于:所述步骤A中浸泡过程配合超声和机械搅拌10~60min。2. The method for recovering Co 3 O 4 from waste lithium cobaltate battery positive electrode materials according to claim 1, characterized in that: in the step A, the soaking process is combined with ultrasonic and mechanical stirring for 10-60 minutes. 3.如权利要求1所述的从废旧钴酸锂电池正极材料中回收Co3O4的方法,其特征在于:所述步骤A中有机溶剂包括二甲基甲酰胺、N-甲基吡咯烷酮、二甲基乙酰胺或二甲基亚砜。3. as claimed in claim 1 from waste lithium cobaltate battery cathode material recovery Co 3 O The method is characterized in that: in the described step A, the organic solvent comprises dimethylformamide, N-methylpyrrolidone, Dimethylacetamide or dimethylsulfoxide. 4.如权利要求1所述的从废旧钴酸锂电池正极材料中回收Co3O4的方法,其特征在于:所述步骤B中有机酸包括柠檬酸、乙酸、草酸、甲酸、马来酸或抗坏血酸,用量为30~50g/l。4. The method for reclaiming Co from waste lithium cobalt oxide battery cathode materials as claimed in claim 1 3 O The method is characterized in that: in the step B, the organic acid comprises citric acid, acetic acid, oxalic acid, formic acid, maleic acid Or ascorbic acid, the dosage is 30-50g/l. 5.如权利要求1所述的从废旧钴酸锂电池正极材料中回收Co3O4的方法,其特征在于:步骤B中H2O2溶液体积分数为0.1~2%,用量为LiCoO2的1.2~2摩尔倍数。5. The method for recovering Co 3 O 4 from the positive electrode material of waste lithium cobalt oxide battery as claimed in claim 1, characterized in that: in step B, the volume fraction of H 2 O 2 solution is 0.1-2%, and the dosage is LiCoO 2 1.2 to 2 molar multiples of . 6.如权利要求1所述的从废旧钴酸锂电池正极材料中回收Co3O4的方法,其特征在于:步骤C中所述钴离子萃取剂包括叔碳羧酸Versatic911、二(2-羟基-5-辛基)苯甲胺、2-乙基己基三(辛-癸)烷基叔胺、二(2-乙基己基)磷酸酯或乙基己基磷酸单-2-乙基己酯。6. as claimed in claim 1 from waste lithium cobaltate battery cathode material recovery Co 3 O The method is characterized in that: the cobalt ion extraction agent described in the step C comprises tertiary carbon carboxylic acid Versatic911, two (2- Hydroxy-5-octyl)benzylamine, 2-ethylhexyltris(oct-decyl)alkyl tertiary amine, di(2-ethylhexyl)phosphate or mono-2-ethylhexyl ethylhexylphosphate . 7.如权利要求1所述的从废旧钴酸锂电池正极材料中回收Co3O4的方法,其特征在于:步骤D在焙烧炉中进行,通过并鼓入空气的形式鼓入氧气。7. The method for recovering Co 3 O 4 from waste lithium cobalt oxide battery positive electrode materials as claimed in claim 1, characterized in that: step D is carried out in a roasting furnace, and oxygen is blown through and blown in the form of air.
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