WO2018192121A1 - Method for efficiently recovering positive electrode material precursor and lithium carbonate from positive electrode waste material of lithium ion battery - Google Patents

Method for efficiently recovering positive electrode material precursor and lithium carbonate from positive electrode waste material of lithium ion battery Download PDF

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Publication number
WO2018192121A1
WO2018192121A1 PCT/CN2017/092709 CN2017092709W WO2018192121A1 WO 2018192121 A1 WO2018192121 A1 WO 2018192121A1 CN 2017092709 W CN2017092709 W CN 2017092709W WO 2018192121 A1 WO2018192121 A1 WO 2018192121A1
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leaching
lithium
solution
positive electrode
acid
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PCT/CN2017/092709
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French (fr)
Chinese (zh)
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王雪
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中科过程(北京)科技有限公司
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    • HELECTRICITY
    • H01ELECTRIC ELEMENTS
    • H01MPROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
    • H01M10/00Secondary cells; Manufacture thereof
    • H01M10/54Reclaiming serviceable parts of waste accumulators
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B7/00Working up raw materials other than ores, e.g. scrap, to produce non-ferrous metals and compounds thereof; Methods of a general interest or applied to the winning of more than two metals
    • C22B7/006Wet processes
    • 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/84Recycling of batteries or fuel cells

Definitions

  • the invention belongs to the technical field of secondary resource recycling and recycling economy, and particularly relates to a method for efficiently recovering a positive electrode material precursor and lithium carbonate from a lithium ion battery positive electrode waste.
  • Lithium-ion batteries have many advantages such as high energy density, small self-discharge, excellent cycle performance, high charging efficiency, no memory effect, etc., and are widely used in various consumer electronic products, military, pure electric vehicles and aerospace applications. With the development of electric vehicles, the future power lithium-ion batteries will usher in a huge market, and there will be a problem of recycling and recycling of a large number of power lithium-ion batteries. With the upcoming peak of power battery scrapping, the recycling scale of used lithium-ion batteries will grow rapidly, and the market value of used battery recycling will be even greater.
  • the hydrometallurgical treatment method has the advantages of high recovery efficiency, simple process, easy process control, etc. attention.
  • the mainstream recycling process can be divided into two types: step-by-step recycling and collaborative recycling.
  • the first type is based on a step-by-step recovery method to obtain elements such as lithium, cobalt, nickel, manganese, and the like, respectively.
  • CN105331819A discloses a method for recovering Co 3 O 4 from a cathode material of a waste lithium cobalt oxide battery, and the separation and recovery of cobalt elements are achieved by organic acid leaching and organic extraction.
  • CN101280357A reports multi-stage acid leaching extraction using a sulfuric acid/hydrogen peroxide mixed solution, and finally recovers cobalt oxalate and lithium carbonate separately.
  • CN104241724A discloses a method for recovering lithium carbonate from a spent lithium ion battery, in which other valuable elements are converted into impurities as impurities.
  • CN104124487A discloses a method for fractionally recovering cobalt, copper, aluminum and lithium in a waste lithium ion battery by using a liquid phase reaction. The method integrates alkali leaching, acid leaching, and agent extraction to achieve full component recovery of valuable elements in the battery.
  • the second type is a process for preparing a precursor of a positive electrode material in one step, such as nickel, cobalt, and manganese.
  • CN102676827A discloses a method for recovering valuable metals from a nickel-cobalt-manganese lithium battery, separating the positive electrode material and the battery powder by solvent sonication and filtration, and then using acid leaching oxidation, adjusting the pH of the alkali solution, etc. to obtain nickel-cobalt-manganese composite carbonic acid. salt.
  • CN105048020A discloses a method for preparing a lithium-doped cobalt ferrite material from a waste lithium battery, and finally obtains a cobalt ferrite material by acid leaching and high temperature baking in a microwave oven.
  • CN103199230A discloses a process for reversely recovering lithium nickel manganese oxide from a waste lithium battery as a raw material, obtaining nickel manganese oxide by using an acetate complexing agent and electrolysis, and calcining it with a lithium source to obtain lithium nickel manganese oxide.
  • CN103400965A uses a process similar to the patent CN103199230A to prepare lithium nickel cobaltate by reverse recovery from a waste lithium ion battery.
  • CN102751549A utilizes a method of leaching of a fluorine-containing organic acid to realize preparation of a ternary precursor of nickel, cobalt and manganese and recovery of lithium carbonate.
  • the prior art mainly relies on acid-base leaching, organic acid leaching/extraction, etc. to recover valuable elements in the used batteries by the above-mentioned step-by-step acquisition or synergistic recovery.
  • the selective leaching effect of the leaching agent is not obvious.
  • the leaching solution often contains a large amount of impurity elements, resulting in a large consumption of the leaching agent.
  • the purity of the obtained product is poor, especially the recovery and purification of lithium is relatively difficult, the impurity removal step is complicated, and the cost is complicated.
  • the recycling of the leaching agent has not been reported.
  • the present invention aims to provide a simple and efficient method.
  • a method for recovering and preparing a Co, Ni, Mn precursor and lithium carbonate wherein the method adopts a strong leaching ability of a leaching agent, a high leaching rate (greater than 90%), and a leaching agent is recycled by a concentrated distillation cycle .
  • the invention has simple process, no complicated impurity removal step and extraction enrichment, strong operability, low equipment requirement and low processing cost, and can obtain high purity Co, Ni, Mn precursor and lithium carbonate (purity >99.9%). Has a good application prospects.
  • Material including the following steps:
  • the leaching solution obtained in the step (1) is subjected to concentrated rectification, and the leaching agent is regenerated to obtain a volatile leaching agent and a residual liquid containing Co, Ni, Mn and Li;
  • Step (3) After the coprecipitation is completed, solid-liquid separation is performed to obtain a lithium-rich solution and a mixture for preparing a Co, Ni, Mn precursor;
  • the Co, Ni, Mn mixture obtained in the step (4) is prepared by a high temperature solid phase reaction to prepare a positive electrode material active material.
  • the obtained lithium-rich solution was added to a saturated sodium carbonate solution to obtain a white precipitate. After suction filtration, washing and drying, a high-purity lithium carbonate solid was obtained.
  • the leaching agent according to the step (1) is a solution in which one or more kinds of volatile organic and/or inorganic acids are mixed and mixed with one or more reducing agents;
  • the acid concentration is 0.1-15 mol/L
  • the mass percentage of the reducing agent is 0.1-20%
  • the leaching S/L ratio is 5-500 g/L
  • the leaching temperature is 5-100 ° C
  • the leaching time is 5-480 min.
  • the stirring speed is 0 to 2000 rpm.
  • the acid concentration is optimized to be 2 to 4 mol/L;
  • the volatile acid is optimized to be one or a mixture of sulfuric acid, hydrochloric acid, nitric acid, trichloroacetic acid, trifluoroacetic acid, citric acid, formic acid, acetic acid;
  • the reducing agent has a mass percentage of 2 to 8%;
  • the reducing agent is one or a combination of sodium sulfite, sulfurous acid, sodium thiosulfate or hydrogen peroxide;
  • the leaching S/L is 80-150 g/L
  • the leaching temperature is 20 to 80 ° C;
  • the stirring speed is 100 to 500 rpm.
  • the residual liquid obtained in the step (3) is subjected to co-precipitation of the Co, Ni, and Mn components by the component control, and the lithium-rich solution and the mixture for preparing the Co, Ni, and Mn precursors are obtained by solid-liquid separation.
  • the molar ratio of nickel, cobalt and manganese in the solution containing nickel and cobalt is adjusted to conform to the molar ratio of Ni, Co and Mn in the molecular formula LiNi x Co y Mn 1-xy O 2 , wherein x >0, y>0, and x+y ⁇ 1.
  • the molar ratio of nickel, cobalt and manganese in the solution containing nickel and cobalt is specifically: adding one or at least two of a water-soluble nickel salt, a cobalt salt or a manganese salt to a solution containing nickel, cobalt and manganese. combination.
  • the pH of the solution during the coprecipitation is 7-12
  • the solution for adjusting the pH is an alkaline solution
  • the concentration of the alkali solution is 0.1-10 mol/L
  • the stirring speed is 0-2000 rpm
  • the stirring adjustment time is 0.5-72 h
  • the pH is adjusted.
  • the temperature is 5 to 95 ° C;
  • the alkaline solution is a mixture of one or both of sodium hydroxide and aqueous ammonia.
  • the pH of the coprecipitation solution is optimized to be 10 to 11; the alkali concentration is optimized to be 2 to 4 mol/L; the stirring speed is optimized to be 100 to 500 rpm; the stirring adjustment time is optimized to be 2 to 4 hours; Temperature Optimized to 20 to 50 ° C.
  • the solid-liquid separation is achieved by suction filtration or filtration.
  • the Co, Ni, Mn precursor mixture obtained in the step (5) is prepared by a high temperature solid phase reaction to prepare a cathode active material;
  • the obtained lithium-rich solution is subjected to high-temperature concentration/rectification treatment, and a saturated sodium carbonate solution is added to obtain a white precipitate. After suction filtration, washing and drying, a high-purity lithium carbonate solid is obtained;
  • the precipitation temperature of lithium carbonate is 20-100 ° C
  • the stirring speed of lithium carbonate precipitation is 0-2000 rpm
  • the adjustment time of precipitation stirring is 0.5-72 h
  • the temperature of washing water is 10-100 ° C
  • the high temperature solid phase reaction temperature is 600 to 850 ° C, and the reaction time is 3 to 20 h;
  • the lithium carbonate precipitation temperature is 60 to 100 ° C;
  • the lithium carbonate precipitation stirring speed is 100 to 500 rpm;
  • the lithium carbonate precipitation stirring adjustment time is 1 to 16 h;
  • the molar ratio of the carbonate ion added to the lithium carbonate to the lithium ion in the solution is from 1 to 3:2; preferably, the temperature of the washing water is from 90 to 100 °C.
  • the present invention has the following significant advantages:
  • the volatile leaching agent of the invention has a wide source range, low raw material price, and can selectively extract valuable elements such as Co, Ni, Mn and Li element, thereby avoiding complicated impurity removal steps and extraction processes, and separating the obtained
  • the leachate can directly obtain the Co, Ni, Mn precursor mixture by coprecipitation, and the process is simple;
  • the leaching agent of the present invention does not leaching impurity elements such as Fe and Al, the leaching agent consumption is small in the production process, and the leaching agent is regenerated rapidly by concentrated rectification in a short-range, thereby further reducing the raw material cost and avoiding secondary pollution;
  • the precursor product and the lithium carbonate product obtained by the present invention have a small impurity content, and can prepare high-purity lithium carbonate (purity >99.9%).
  • FIG. 1 is a flow chart of a process for efficiently recovering a precursor of a positive electrode material and lithium carbonate from a positive electrode waste of a lithium ion battery according to the present invention.
  • a method for efficiently recovering a positive electrode material precursor and lithium carbonate from a lithium ion battery positive electrode waste includes the following steps:
  • the lithium ion battery positive electrode waste is leached with a volatile leaching agent containing a reducing agent, and the leaching liquid and the leaching slag are separated.
  • the leaching agent is one or more of a volatile organic and/or inorganic acid, such as an organic and/or inorganic acid such as sulfuric acid, hydrochloric acid, nitric acid, trichloroacetic acid, trifluoroacetic acid, citric acid, formic acid or acetic acid.
  • the acid concentration is 2 to 4 mol/L
  • the mixed mass percentage is 2 to 8% of sodium sulfite, sulfurous acid, sodium thiosulfate or hydrogen peroxide as a reducing agent.
  • the leaching S/L is 8 to 150 g/L, the leaching temperature is 20 to 80 ° C, the leaching time is 5 to 480 min, and the stirring speed is 100 to 500 rpm;
  • the obtained leachate is subjected to high-temperature concentration/rectification treatment to recover the volatile leaching agent to obtain a residual liquid containing Co, Ni, Mn and Li;
  • Co-precipitation of Co, Ni, and Mn components is carried out after the composition of Co, Ni, Mn, and Li is controlled by components.
  • the molar ratio of nickel, cobalt and manganese in the solution containing nickel and cobalt should be adjusted to match the molar ratio of Ni, Co and Mn in the formula LiNi x Co y Mn 1-xy O 2 , where x>0 , y>0, and x+y ⁇ 1.
  • the obtained Co, Ni, Mn precursor mixture was prepared by a high temperature solid phase reaction method to prepare a positive electrode active material.
  • the pH of the solution during coprecipitation is 10-11, and the solution for adjusting the pH is an alkaline solution, such as one or a mixture of sodium hydroxide and ammonia water, the concentration of the alkali solution is 2 to 4 mol/L, and the precipitation stirring speed is 100 ⁇ 500rpm, time is 2 ⁇ 4h, and the precipitation temperature is 20 ⁇ 50°C;
  • alkaline solution such as one or a mixture of sodium hydroxide and ammonia water
  • the concentration of the alkali solution is 2 to 4 mol/L
  • the precipitation stirring speed is 100 ⁇ 500rpm
  • time is 2 ⁇ 4h
  • the precipitation temperature is 20 ⁇ 50°C;
  • the positive electrode active material is prepared by high temperature solid phase reaction of Co, Ni, Mn mixture.
  • the solid temperature reaction temperature is 800-850 ° C and the reaction time is 15-20 h.
  • the lithium-rich solution is added to a saturated sodium carbonate solution to obtain a white precipitate. After suction filtration, washing, and drying, a high-purity lithium carbonate solid is obtained.
  • the precipitation temperature of lithium carbonate is 20-90 ° C
  • the stirring speed of precipitation is 100-500 rpm
  • the adjustment time of precipitation stirring is 1-16 h
  • the molar ratio of carbonate ion added by lithium carbonate precipitation to lithium ion in solution is 1-3:2.
  • the temperature of the water used for washing is 90 to 100 °C.
  • the lithium ion battery positive electrode waste was leached with a mixed acid of nitric acid and citric acid containing a hydrogen peroxide reducing agent (acid concentration of 2 mol/L, and a mass percentage of the reducing agent of 3%).
  • the leaching S/L was 50 g/L
  • the leaching temperature was 40 ° C
  • the leaching time was 200 min
  • the stirring speed was 150 rpm.
  • a leachate containing Li, Ni, Co, and Mn and a leach residue were obtained.
  • the leaching rates of the metals Li, Ni, Co and Mn were 92.21%, 90.60% and 91.20% and 92.5%, respectively, while the leaching rates of metal Al and Fe were only 1.32% and 2.76%.
  • the leachate is subjected to high-temperature concentration/rectification treatment to recover the volatile leaching agent to obtain a residual liquid containing Co, Ni, Mn and Li.
  • the distillation/concentration temperature was 200 ° C, the time was 30 min, and the stirring speed was 150 rpm.
  • the molar ratio of nickel, cobalt and manganese in the solution containing Co, Ni, Mn and Li is adjusted according to the molar ratio of Ni, Co and Mn in the formula LiNi x Co y Mn 1-xy O 2 , where x> 0, y>0, and x+y ⁇ 1.
  • the pH was adjusted to 11 by adding sodium hydroxide, and the precipitates of Ni, Co and Mn (purity: 99.3%) and the lithium-containing residual liquid were obtained after precipitation.
  • the alkali concentration was 2.5 mol/L
  • the stirring speed was 150 rpm
  • the stirring adjustment time was 4 h.
  • solid-liquid separation is carried out to obtain a lithium-rich solution and a mixture for preparing a Co, Ni, and Mn precursor.
  • the obtained Co, Ni, Mn precursor mixture was subjected to a solid phase reaction at 800 ° C for 15 h to prepare a positive electrode active material.
  • the lithium-rich solution is added with saturated sodium carbonate to obtain a white precipitate.
  • the precipitation temperature of lithium carbonate is 90 ° C
  • the stirring speed of precipitation is 150 rpm
  • the stirring adjustment time is 5 h
  • the molar ratio of carbonate ions added to the lithium carbonate precipitation to the lithium ion in the solution is 2:1
  • the temperature of the washing water is 90 ° C.
  • the purity of the obtained lithium carbonate was 99.92%.
  • Table 1 Composition of the metal elements of the cathode material of the used lithium ion battery
  • the lithium ion battery positive electrode waste was leached with a mixed acid of trichloroacetic acid and sulfuric acid containing a sodium sulfite reducing agent (acid concentration of 3 mol/L, and a mass percentage of the reducing agent of 4%).
  • the leaching S/L was 50 g/L
  • the leaching temperature was 40 ° C
  • the leaching time was 50 min
  • the stirring speed was 150 rpm.
  • a leachate containing Li, Ni, Co, and Mn and a leach residue were obtained.
  • the leaching rates of the metals Li, Ni, Co and Mn were 94.60%, 92.80% and 93.20% and 93.80%, respectively, while the leaching rates of metal Al and Fe were only 2.12% and 3.46%.
  • the leachate is subjected to high temperature concentration/rectification treatment to recover the leaching agent to obtain a residual liquid containing Co, Ni, Mn and Li.
  • the molar ratio of nickel, cobalt and manganese in the solution containing Co, Ni, Mn and Li is adjusted according to the molar ratio of Ni, Co and Mn in the formula LiNi x Co y Mn 1-xy O 2 , where x> 0, y>0, and x+y ⁇ 1.
  • the pH was adjusted to 10.4 by adding sodium hydroxide, and the precursors of Ni, Co and Mn (purity of 99.3%) and the lithium-containing residual liquid were obtained after precipitation.
  • the alkali concentration was 2.5 mol/L, the stirring speed was 150 rpm, and the stirring adjustment time was 4 h.
  • a lithium-rich solution and a mixture for preparing a Co, Ni, Mn precursor were obtained.
  • the obtained Co, Ni, Mn precursor mixture was subjected to a solid phase reaction at 800 ° C for 15 h to prepare a positive electrode active material.
  • the lithium-rich solution is added with saturated sodium carbonate to obtain a white precipitate. After suction filtration, washing and drying, a high-purity lithium carbonate solid is obtained.
  • the precipitation temperature of lithium carbonate is 85 ° C
  • the stirring speed of precipitation is 150 rpm
  • the stirring adjustment time is 5 h
  • the molar ratio of carbonate ions added to the lithium carbonate precipitation to the lithium ion in the solution is 2:1
  • the temperature of the washing water is 90 ° C.
  • the purity of the obtained lithium carbonate was 99.95%.
  • the present invention illustrates the process of the present invention by the above-described embodiments, but the present invention is not limited to the above process steps, that is, it does not mean that the present invention must rely on the above process steps to be implemented. It will be apparent to those skilled in the art that any modifications of the present invention, equivalent substitutions of the materials selected for the present invention, and the addition of the auxiliary ingredients, the selection of the specific means, etc., are all within the scope of the present invention.

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Abstract

A method for recovering a positive electrode material precursor and lithium carbonate from a positive electrode waste material of a lithium ion battery. The waste material is a positive electrode powder material containing impurities which is generated during battery production or obtained from waste batteries by means of mechanical crushing and sorting. The method comprises: carrying out leaching by using a volatile leaching agent containing a reducing agent to obtain a leachate; carrying out concentration rectification, and regenerating the volatile leaching agent; adjusting ingredients of the raffinate containing Co, Ni, Mn and Li, and carrying out coprecipitation on Co, Ni and Mn components; carrying out solid-liquid separation; and further treating the Li-rich solution to obtain high-purity lithium carbonate, and carrying out a high-temperature solid-phase reaction on the mixed material used for preparing Co, Ni and Mn precursors to obtain a positive electrode active material. The method has a simple flow and does not need a complicated impurity removal step and an extraction and enrichment process. In addition, the leaching agent may come from a wide range of sources, has high leaching selectivity and high leaching rate, and can be recycled after a leaching reaction by means of concentration rectification. Thus, the cost is reduced, and high-quality Co, Ni and Mn precursors and high-purity lithium carbonate can be obtained. The method has a good application prospect.

Description

一种从锂离子电池正极废料中高效回收正极材料前驱体和碳酸锂的方法Method for efficiently recovering positive electrode material precursor and lithium carbonate from cathode waste material of lithium ion battery 技术领域Technical field
本发明属于二次资源回收利用和循环经济技术领域,尤其涉及一种从锂离子电池正极废料中高效回收正极材料前驱体和碳酸锂的方法。The invention belongs to the technical field of secondary resource recycling and recycling economy, and particularly relates to a method for efficiently recovering a positive electrode material precursor and lithium carbonate from a lithium ion battery positive electrode waste.
背景技术Background technique
锂离子电池具有能量密度高、自放电小、循环性能优越、充电效率高、无记忆效应等诸多优点,被广泛应用于各类消费类电子产品、军事、纯电动汽车和航空航天应用。随着电动汽车的发展,未来动力型锂离子电池将迎来巨大的市场,并出现大量动力锂离子电池退役的回收再利用问题。随着即将到来的动力电池报废高峰,废旧锂离子电池的回收规模将迅速增长,废旧电池回收市场价值将更加巨大。Lithium-ion batteries have many advantages such as high energy density, small self-discharge, excellent cycle performance, high charging efficiency, no memory effect, etc., and are widely used in various consumer electronic products, military, pure electric vehicles and aerospace applications. With the development of electric vehicles, the future power lithium-ion batteries will usher in a huge market, and there will be a problem of recycling and recycling of a large number of power lithium-ion batteries. With the upcoming peak of power battery scrapping, the recycling scale of used lithium-ion batteries will grow rapidly, and the market value of used battery recycling will be even greater.
目前,国内外研究人员对废旧锂离子电池的处理和回收进行了大量的研究和探讨,其中基于湿法冶金的处理方法具有回收效率高、流程简单、工艺易控等优点,获得了较高的关注。目前主流的回收工艺按回收产品的方式可分为分步回收和协同回收两类。第一类基于分步回收的方法,分别得到元素如锂、钴、镍、锰等。如CN105331819A公布了从废旧钴酸锂电池正极材料回收Co3O4的方法,通过有机酸浸和有机萃取实现了钴元素的分离和回收。CN101280357A报道了采用硫酸/双氧水混合溶液进行多段酸浸萃取,最后分别沉淀回收得到草酸钴和碳酸锂。CN104241724A公布了从废旧锂离子电池回收碳酸锂的方法,其他有价元素被当作杂质转变为残渣。CN104124487A公布了一种利用液相反应分步回收废旧锂离子电池中钴、铜、铝、锂的方法。该方法整合了碱浸、酸浸、有剂萃取的方法实现了电池中有价元素的全组分回收。第二类是镍、钴、锰等一步制备正极材料前驱体的工艺。如CN102676827A公布了从镍钴锰酸锂电池回收有价金属的方法,通过溶剂超声处理和过滤分离正极材料和电池粉末,然后使用酸浸氧化,碱液调整pH值等获得镍钴锰复合碳酸盐。相似的,CN105048020A公布了一种废旧锂电池为原料制备锂掺杂钴铁氧体材料的方法,通过酸浸和和微波炉中高温焙烧的方法最终获得钴铁氧体材料。CN103199230A公布了一种从废旧锂电池为 原料逆向回收镍锰酸锂的工艺,通过使用醋酸盐络合剂和电解的方法获得镍锰氧化物,并配入锂源煅烧得到镍锰酸锂。CN103400965A采用与专利CN103199230A相似工艺,从废旧锂离子电池中逆向回收制备得到了镍钴酸锂。CN102751549A利用含氟有机酸浸出的方法,实现了镍、钴、锰三元前驱体的制备和碳酸锂的回收。At present, researchers at home and abroad have conducted a lot of research and discussion on the treatment and recycling of waste lithium-ion batteries. The hydrometallurgical treatment method has the advantages of high recovery efficiency, simple process, easy process control, etc. attention. At present, the mainstream recycling process can be divided into two types: step-by-step recycling and collaborative recycling. The first type is based on a step-by-step recovery method to obtain elements such as lithium, cobalt, nickel, manganese, and the like, respectively. For example, CN105331819A discloses a method for recovering Co 3 O 4 from a cathode material of a waste lithium cobalt oxide battery, and the separation and recovery of cobalt elements are achieved by organic acid leaching and organic extraction. CN101280357A reports multi-stage acid leaching extraction using a sulfuric acid/hydrogen peroxide mixed solution, and finally recovers cobalt oxalate and lithium carbonate separately. CN104241724A discloses a method for recovering lithium carbonate from a spent lithium ion battery, in which other valuable elements are converted into impurities as impurities. CN104124487A discloses a method for fractionally recovering cobalt, copper, aluminum and lithium in a waste lithium ion battery by using a liquid phase reaction. The method integrates alkali leaching, acid leaching, and agent extraction to achieve full component recovery of valuable elements in the battery. The second type is a process for preparing a precursor of a positive electrode material in one step, such as nickel, cobalt, and manganese. For example, CN102676827A discloses a method for recovering valuable metals from a nickel-cobalt-manganese lithium battery, separating the positive electrode material and the battery powder by solvent sonication and filtration, and then using acid leaching oxidation, adjusting the pH of the alkali solution, etc. to obtain nickel-cobalt-manganese composite carbonic acid. salt. Similarly, CN105048020A discloses a method for preparing a lithium-doped cobalt ferrite material from a waste lithium battery, and finally obtains a cobalt ferrite material by acid leaching and high temperature baking in a microwave oven. CN103199230A discloses a process for reversely recovering lithium nickel manganese oxide from a waste lithium battery as a raw material, obtaining nickel manganese oxide by using an acetate complexing agent and electrolysis, and calcining it with a lithium source to obtain lithium nickel manganese oxide. CN103400965A uses a process similar to the patent CN103199230A to prepare lithium nickel cobaltate by reverse recovery from a waste lithium ion battery. CN102751549A utilizes a method of leaching of a fluorine-containing organic acid to realize preparation of a ternary precursor of nickel, cobalt and manganese and recovery of lithium carbonate.
现有的技术主要依靠酸碱浸出、有机酸浸出/萃取等方式通过上述分步获取或协同回收的方法回收废旧电池中的有价元素。然而浸出剂选择性浸出效果不明显,浸出液往往含有大量的杂质元素,造成浸出剂大量消耗的同时,所获得的产品纯度差,特别是锂的回收和纯化相对比较困难、除杂步骤复杂、成本高;与此同时,浸出剂的循环回收利用也未见报道。The prior art mainly relies on acid-base leaching, organic acid leaching/extraction, etc. to recover valuable elements in the used batteries by the above-mentioned step-by-step acquisition or synergistic recovery. However, the selective leaching effect of the leaching agent is not obvious. The leaching solution often contains a large amount of impurity elements, resulting in a large consumption of the leaching agent. At the same time, the purity of the obtained product is poor, especially the recovery and purification of lithium is relatively difficult, the impurity removal step is complicated, and the cost is complicated. At the same time, the recycling of the leaching agent has not been reported.
发明内容Summary of the invention
针对现有废旧锂离子电池回收技术存在的不足,如回收工艺复杂、回收效率低、成本高、难以将有价金属综合回收、浸出剂无循环利用等问题,本发明旨在提供一种简单高效的回收并制备Co、Ni、Mn前驱体和碳酸锂的方法,所述方法所采用浸取剂选择性浸出能力强,浸出率高(大于90%),浸取剂经浓缩精馏循环回收利用。本发明流程简单,无需复杂的除杂步骤和萃取富集,操作性强,设备要求低,处理成本低,可获得高纯度的Co、Ni、Mn前驱体和碳酸锂(纯度>99.9%),具有良好的应用前景。In view of the deficiencies of the existing waste lithium ion battery recycling technology, such as complicated recycling process, low recovery efficiency, high cost, difficulty in comprehensive recovery of valuable metals, and non-recycling of leaching agent, the present invention aims to provide a simple and efficient method. A method for recovering and preparing a Co, Ni, Mn precursor and lithium carbonate, wherein the method adopts a strong leaching ability of a leaching agent, a high leaching rate (greater than 90%), and a leaching agent is recycled by a concentrated distillation cycle . The invention has simple process, no complicated impurity removal step and extraction enrichment, strong operability, low equipment requirement and low processing cost, and can obtain high purity Co, Ni, Mn precursor and lithium carbonate (purity >99.9%). Has a good application prospects.
为达此目的,本发明采用以下技术方案:To this end, the present invention employs the following technical solutions:
一种从锂离子电池正极废料中回收正极材料前驱体和碳酸锂的方法,所述废料为生产废料中去除正极片所得的粉料或废旧电池经过机械破碎、分选后得到的含杂质正极粉料,同时包含以下步骤:A method for recovering a positive electrode material precursor and lithium carbonate from a positive electrode waste of a lithium ion battery, wherein the waste material is an impurity-containing positive electrode powder obtained by mechanically crushing and sorting the powder or waste battery obtained by removing the positive electrode sheet in the production waste. Material, including the following steps:
(1)用含有还原剂的可挥发性浸取剂对锂离子电池正极废料进行浸出,分离得到浸取液和浸取渣;(1) leaching the lithium ion battery positive waste material with a volatile leaching agent containing a reducing agent, and separating the leaching liquid and the leaching slag;
(2)步骤(1)所得浸取液进行浓缩精馏,再生浸取剂,得到可挥发性浸取剂和含Co、Ni、Mn、Li余液;(2) The leaching solution obtained in the step (1) is subjected to concentrated rectification, and the leaching agent is regenerated to obtain a volatile leaching agent and a residual liquid containing Co, Ni, Mn and Li;
(3)步骤(2)所得余液经组分调控后进行Co、Ni、Mn组分的共沉淀;(3) The residual liquid obtained in the step (2) is subjected to co-precipitation of Co, Ni, and Mn components after being controlled by components;
(4)步骤(3)共沉淀完毕后进行固液分离,得到富锂溶液和用于制备Co、Ni、Mn前驱体的混料; (4) Step (3) After the coprecipitation is completed, solid-liquid separation is performed to obtain a lithium-rich solution and a mixture for preparing a Co, Ni, Mn precursor;
(5)步骤(4)所得Co、Ni、Mn混料通过高温固相反应制备正极材料活性材料。所得富锂溶液加入饱和碳酸钠溶液,得到白色沉淀,在抽滤、洗涤、干燥后,得到高纯碳酸锂固体。(5) The Co, Ni, Mn mixture obtained in the step (4) is prepared by a high temperature solid phase reaction to prepare a positive electrode material active material. The obtained lithium-rich solution was added to a saturated sodium carbonate solution to obtain a white precipitate. After suction filtration, washing and drying, a high-purity lithium carbonate solid was obtained.
步骤(1)所述的浸取剂为可挥发性有机和/或无机酸的一种或多种混合并混有一种或多种还原剂的溶液;The leaching agent according to the step (1) is a solution in which one or more kinds of volatile organic and/or inorganic acids are mixed and mixed with one or more reducing agents;
所述酸浓度为0.1~15mol/L,还原剂的质量百分含量为0.1~20%,浸出S/L比为5~500g/L,浸出温度为5~100℃,浸出时间为5~480min,搅拌速度为0~2000rpm。The acid concentration is 0.1-15 mol/L, the mass percentage of the reducing agent is 0.1-20%, the leaching S/L ratio is 5-500 g/L, the leaching temperature is 5-100 ° C, and the leaching time is 5-480 min. The stirring speed is 0 to 2000 rpm.
所述酸浓度优化为2~4mol/L;The acid concentration is optimized to be 2 to 4 mol/L;
所述挥发性酸优化为硫酸、盐酸、硝酸、三氯乙酸、三氟乙酸、柠檬酸、甲酸、乙酸中的一种或几种混合;The volatile acid is optimized to be one or a mixture of sulfuric acid, hydrochloric acid, nitric acid, trichloroacetic acid, trifluoroacetic acid, citric acid, formic acid, acetic acid;
优选的,所述还原剂的质量百分比含量为2~8%;Preferably, the reducing agent has a mass percentage of 2 to 8%;
优选的,所述还原剂为亚硫酸钠、亚硫酸、硫代硫酸钠或过氧化氢中的一种或者几种的组合;Preferably, the reducing agent is one or a combination of sodium sulfite, sulfurous acid, sodium thiosulfate or hydrogen peroxide;
优选的,所述浸出S/L为80~150g/L;Preferably, the leaching S/L is 80-150 g/L;
优选的,所述浸出温度为20~80℃;Preferably, the leaching temperature is 20 to 80 ° C;
优选的,所述搅拌速度为100~500rpm。Preferably, the stirring speed is 100 to 500 rpm.
步骤(3)所得余液经组分调控后执行Co、Ni、Mn组分的共沉淀,通过固液分离,得到富锂溶液和用于制备Co、Ni、Mn前驱体的混料。The residual liquid obtained in the step (3) is subjected to co-precipitation of the Co, Ni, and Mn components by the component control, and the lithium-rich solution and the mixture for preparing the Co, Ni, and Mn precursors are obtained by solid-liquid separation.
所述组分调控时需调节含镍和钴的溶液中镍、钴和锰的摩尔比,使其符合分子式LiNixCoyMn1-x-yO2中Ni、Co和Mn的摩尔比,其中x>0,y>0,且x+y<1。When the composition is adjusted, the molar ratio of nickel, cobalt and manganese in the solution containing nickel and cobalt is adjusted to conform to the molar ratio of Ni, Co and Mn in the molecular formula LiNi x Co y Mn 1-xy O 2 , wherein x >0, y>0, and x+y<1.
所述调节含镍和钴的溶液中镍、钴和锰的摩尔比具体为:向含镍、钴和锰的溶液中添加水溶性镍盐、钴盐或者锰盐中一种或至少两种的组合。The molar ratio of nickel, cobalt and manganese in the solution containing nickel and cobalt is specifically: adding one or at least two of a water-soluble nickel salt, a cobalt salt or a manganese salt to a solution containing nickel, cobalt and manganese. combination.
所述共沉淀时溶液的pH为7~12,调整pH的溶液为碱性溶液,碱液浓度为0.1~10mol/L,搅拌速度为0~2000rpm,搅拌调节时间为0.5~72h,调节pH的温度为5~95℃;The pH of the solution during the coprecipitation is 7-12, the solution for adjusting the pH is an alkaline solution, the concentration of the alkali solution is 0.1-10 mol/L, the stirring speed is 0-2000 rpm, the stirring adjustment time is 0.5-72 h, and the pH is adjusted. The temperature is 5 to 95 ° C;
优选的,所述碱性溶液为氢氧化钠、氨水中的一种或两种的混合。Preferably, the alkaline solution is a mixture of one or both of sodium hydroxide and aqueous ammonia.
所述共沉淀溶液pH优化为10~11;所述碱浓度优化为2~4mol/L;所述搅拌速度优化为100~500rpm;所述搅拌调节时间优化为2~4h;所述调节pH的温度 优化为20~50℃。The pH of the coprecipitation solution is optimized to be 10 to 11; the alkali concentration is optimized to be 2 to 4 mol/L; the stirring speed is optimized to be 100 to 500 rpm; the stirring adjustment time is optimized to be 2 to 4 hours; Temperature Optimized to 20 to 50 ° C.
步骤(4)共沉淀完毕后实行固液分离,得到富锂溶液和用于制备Co、Ni、Mn前驱体的混料;Step (4) after the completion of the coprecipitation, solid-liquid separation is performed to obtain a lithium-rich solution and a mixture for preparing a Co, Ni, and Mn precursor;
优选的,所述固液分离以抽滤或过滤方式实现。Preferably, the solid-liquid separation is achieved by suction filtration or filtration.
步骤(5)所得Co、Ni、Mn前驱体混料通过高温固相反应制备正极活性材料;The Co, Ni, Mn precursor mixture obtained in the step (5) is prepared by a high temperature solid phase reaction to prepare a cathode active material;
所得富锂溶液高温浓缩/精馏处理,加入饱和碳酸钠溶液,得到白色沉淀,在抽滤、洗涤、干燥后,得到高纯碳酸锂固体;The obtained lithium-rich solution is subjected to high-temperature concentration/rectification treatment, and a saturated sodium carbonate solution is added to obtain a white precipitate. After suction filtration, washing and drying, a high-purity lithium carbonate solid is obtained;
其中,碳酸锂沉淀温度为20~100℃,碳酸锂沉淀搅拌速度为0~2000rpm,沉淀搅拌调节时间为0.5~72h,洗涤所用水的温度为10~100℃;Wherein, the precipitation temperature of lithium carbonate is 20-100 ° C, the stirring speed of lithium carbonate precipitation is 0-2000 rpm, the adjustment time of precipitation stirring is 0.5-72 h, and the temperature of washing water is 10-100 ° C;
优选的,高温固相反应温度为600~850℃,反应时间为3~20h;Preferably, the high temperature solid phase reaction temperature is 600 to 850 ° C, and the reaction time is 3 to 20 h;
优选的,所述碳酸锂沉淀温度为60~100℃;Preferably, the lithium carbonate precipitation temperature is 60 to 100 ° C;
优选的,所述碳酸锂沉淀搅拌速度为100~500rpm;Preferably, the lithium carbonate precipitation stirring speed is 100 to 500 rpm;
优选的,所述碳酸锂沉淀搅拌调节时间为1~16h;Preferably, the lithium carbonate precipitation stirring adjustment time is 1 to 16 h;
优选的,所述碳酸锂沉淀加入的碳酸根离子与溶液中锂离子的摩尔比例为1~3:2;优选的,所述洗涤所用水的温度为90~100℃。Preferably, the molar ratio of the carbonate ion added to the lithium carbonate to the lithium ion in the solution is from 1 to 3:2; preferably, the temperature of the washing water is from 90 to 100 °C.
与现有技术相比,本发明具有以下显著优势:Compared with the prior art, the present invention has the following significant advantages:
(1)本发明挥发性浸出剂来源范围广,原料价格便宜,可选择性的提取Co、Ni、Mn等有价元素及Li元素,因此避免了复杂的除杂步骤和萃取流程,分离得到的浸取液可通过共沉淀直接得到Co、Ni、Mn前驱体混料,流程简单;(1) The volatile leaching agent of the invention has a wide source range, low raw material price, and can selectively extract valuable elements such as Co, Ni, Mn and Li element, thereby avoiding complicated impurity removal steps and extraction processes, and separating the obtained The leachate can directly obtain the Co, Ni, Mn precursor mixture by coprecipitation, and the process is simple;
(2)由于本发明浸出剂不浸出Fe、Al等杂质元素,因此生产过程中浸出剂消耗量小,同时浸出剂经浓缩精馏短程高效再生,进一步降低了原料成本,避免了二次污染;(2) Since the leaching agent of the present invention does not leaching impurity elements such as Fe and Al, the leaching agent consumption is small in the production process, and the leaching agent is regenerated rapidly by concentrated rectification in a short-range, thereby further reducing the raw material cost and avoiding secondary pollution;
(3)本发明所得前驱体产品和碳酸锂产品杂质含量少,能够制备高纯碳酸锂(纯度>99.9%)。(3) The precursor product and the lithium carbonate product obtained by the present invention have a small impurity content, and can prepare high-purity lithium carbonate (purity >99.9%).
附图说明DRAWINGS
图1为本发明一种从锂离子电池正极废料中高效回收正极材料前驱体和碳酸锂的工艺流程图。1 is a flow chart of a process for efficiently recovering a precursor of a positive electrode material and lithium carbonate from a positive electrode waste of a lithium ion battery according to the present invention.
具体实施方式 detailed description
下面结合附图并通过具体实施方式来进一步说明本发明的技术方案。领域的技术人员应该明了,所述的实施例仅仅是帮助理解本发明,不应视为对本发明的具体限制。The technical solution of the present invention will be further described below with reference to the accompanying drawings and specific embodiments. It should be understood by those skilled in the art that the described embodiments are only to be construed as illustrative and not restrictive.
一种从锂离子电池正极废料中高效回收正极材料前驱体和碳酸锂的方法,如图1所示,所述优选的工艺包括如下步骤:A method for efficiently recovering a positive electrode material precursor and lithium carbonate from a lithium ion battery positive electrode waste, as shown in FIG. 1, the preferred process includes the following steps:
(1)用含有还原剂的可挥发性浸取剂对锂离子电池正极废料进行浸出,分离得到浸取液和浸取渣。浸取剂为可挥发性有机和/或无机酸的一种或多种,如硫酸、盐酸、硝酸、三氯乙酸、三氟乙酸、柠檬酸、甲酸、乙酸等有机和/或无机酸中的一种或几种混合。所述酸浓度为2~4mol/L,混合质量百分比为2~8%的亚硫酸钠、亚硫酸、硫代硫酸钠或过氧化氢作为还原剂。浸出S/L为8~150g/L,浸出温度为20~80℃,浸出时间为5~480min,搅拌速度为100~500rpm;(1) The lithium ion battery positive electrode waste is leached with a volatile leaching agent containing a reducing agent, and the leaching liquid and the leaching slag are separated. The leaching agent is one or more of a volatile organic and/or inorganic acid, such as an organic and/or inorganic acid such as sulfuric acid, hydrochloric acid, nitric acid, trichloroacetic acid, trifluoroacetic acid, citric acid, formic acid or acetic acid. One or several blends. The acid concentration is 2 to 4 mol/L, and the mixed mass percentage is 2 to 8% of sodium sulfite, sulfurous acid, sodium thiosulfate or hydrogen peroxide as a reducing agent. The leaching S/L is 8 to 150 g/L, the leaching temperature is 20 to 80 ° C, the leaching time is 5 to 480 min, and the stirring speed is 100 to 500 rpm;
(2)所得浸取液高温浓缩/精馏处理回收挥发性浸出剂,得到含Co、Ni、Mn、Li余液;(2) The obtained leachate is subjected to high-temperature concentration/rectification treatment to recover the volatile leaching agent to obtain a residual liquid containing Co, Ni, Mn and Li;
(3)含Co、Ni、Mn、Li余液经组分调控后执行Co、Ni、Mn组分的共沉淀。组分调控时需调节含镍和钴的溶液中镍、钴和锰的摩尔比,使其符合分子式LiNixCoyMn1-x-yO2中Ni、Co和Mn的摩尔比,其中x>0,y>0,且x+y<1。所得Co、Ni、Mn前驱体混料通过高温固相反应法制备正极活性材料。共沉淀时溶液的pH为10~11,调整pH的溶液为碱性溶液,如氢氧化钠、氨水中的一种或两种的混合,碱液浓度为2~4mol/L,沉淀搅拌速度为100~500rpm,时间为2~4h,沉淀温度为20~50℃;(3) Co-precipitation of Co, Ni, and Mn components is carried out after the composition of Co, Ni, Mn, and Li is controlled by components. When adjusting the composition, the molar ratio of nickel, cobalt and manganese in the solution containing nickel and cobalt should be adjusted to match the molar ratio of Ni, Co and Mn in the formula LiNi x Co y Mn 1-xy O 2 , where x>0 , y>0, and x+y<1. The obtained Co, Ni, Mn precursor mixture was prepared by a high temperature solid phase reaction method to prepare a positive electrode active material. The pH of the solution during coprecipitation is 10-11, and the solution for adjusting the pH is an alkaline solution, such as one or a mixture of sodium hydroxide and ammonia water, the concentration of the alkali solution is 2 to 4 mol/L, and the precipitation stirring speed is 100~500rpm, time is 2~4h, and the precipitation temperature is 20~50°C;
(4)共沉淀完毕后以抽滤或过滤方式实行固液分离,得到富锂溶液和用于制备Co、Ni、Mn前驱体的混料;(4) After co-precipitation, solid-liquid separation is carried out by suction filtration or filtration to obtain a lithium-rich solution and a mixture for preparing a Co, Ni, Mn precursor;
(5)Co、Ni、Mn混料通过高温固相反应制备正极活性材料,高温固相反应温度为800~850℃,反应时间为15~20h。富锂溶液加入饱和碳酸钠溶液,得到白色沉淀,在抽滤、洗涤、干燥后,得到高纯碳酸锂固体。碳酸锂沉淀温度为20~90℃,沉淀搅拌速度为100~500rpm,沉淀搅拌调节时间为1~16h,碳酸锂沉淀加入的碳酸根离子与溶液中锂离子的摩尔比例为1~3:2,洗涤所用水的温度为90~100℃。(5) The positive electrode active material is prepared by high temperature solid phase reaction of Co, Ni, Mn mixture. The solid temperature reaction temperature is 800-850 ° C and the reaction time is 15-20 h. The lithium-rich solution is added to a saturated sodium carbonate solution to obtain a white precipitate. After suction filtration, washing, and drying, a high-purity lithium carbonate solid is obtained. The precipitation temperature of lithium carbonate is 20-90 ° C, the stirring speed of precipitation is 100-500 rpm, the adjustment time of precipitation stirring is 1-16 h, and the molar ratio of carbonate ion added by lithium carbonate precipitation to lithium ion in solution is 1-3:2. The temperature of the water used for washing is 90 to 100 °C.
实施例Example
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新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。Part of the embodiments of the present invention, but not all of the embodiments, based on the embodiments of the present invention, the skill All other embodiments obtained by a person skilled in the art without innovating labor are within the scope of the invention.
实施例1Example 1
用含有过氧化氢还原剂的硝酸和柠檬酸混合酸(酸浓度为2mol/L,还原剂的质量百分含量为3%)对锂离子电池正极废料进行浸出。浸出S/L为50g/L,浸出温度为40℃,浸出时间为200min,搅拌速度为150rpm。得到含Li、Ni、Co和Mn的浸取液和浸取渣。得到金属Li、Ni、Co和Mn的浸出率分别为92.21%、90.60%和91.20%和92.5%,而金属Al和Fe的浸出率仅为1.32%、2.76%。浸取液经高温浓缩/精馏处理回收挥发浸出剂,得到含Co、Ni、Mn、Li余液。精馏/浓缩温度为200℃,时间为30min,搅拌速度为150rpm。含Co、Ni、Mn、Li余液经组分调控使溶液中镍、钴和锰的摩尔比符合分子式LiNixCoyMn1-x-yO2中Ni、Co和Mn的摩尔比,其中x>0,y>0,且x+y<1。加氢氧化钠调整pH为11,沉淀后得Ni、Co和Mn前驱体(纯度99.3%)和含锂余液。所述碱浓度为2.5mol/L,搅拌速度为150rpm,搅拌调节时间为4h。抽滤后进行行固液分离,得到富锂溶液和用于制备Co、Ni、Mn前驱体的混料。所得Co、Ni、Mn前驱体混料在800℃下高温固相反应15h制备正极活性材料。富锂溶液加入饱和碳酸钠,得到白色沉淀,在抽滤、洗涤、干燥后,得到高纯碳酸锂固体。碳酸锂沉淀温度为90℃,沉淀搅拌速度为150rpm,沉淀搅拌调节时间为5h,碳酸锂沉淀加入的碳酸根离子与溶液中锂离子的摩尔比例为2:1,洗涤所用水的温度为90℃,所得碳酸锂纯度为99.92%。The lithium ion battery positive electrode waste was leached with a mixed acid of nitric acid and citric acid containing a hydrogen peroxide reducing agent (acid concentration of 2 mol/L, and a mass percentage of the reducing agent of 3%). The leaching S/L was 50 g/L, the leaching temperature was 40 ° C, the leaching time was 200 min, and the stirring speed was 150 rpm. A leachate containing Li, Ni, Co, and Mn and a leach residue were obtained. The leaching rates of the metals Li, Ni, Co and Mn were 92.21%, 90.60% and 91.20% and 92.5%, respectively, while the leaching rates of metal Al and Fe were only 1.32% and 2.76%. The leachate is subjected to high-temperature concentration/rectification treatment to recover the volatile leaching agent to obtain a residual liquid containing Co, Ni, Mn and Li. The distillation/concentration temperature was 200 ° C, the time was 30 min, and the stirring speed was 150 rpm. The molar ratio of nickel, cobalt and manganese in the solution containing Co, Ni, Mn and Li is adjusted according to the molar ratio of Ni, Co and Mn in the formula LiNi x Co y Mn 1-xy O 2 , where x> 0, y>0, and x+y<1. The pH was adjusted to 11 by adding sodium hydroxide, and the precipitates of Ni, Co and Mn (purity: 99.3%) and the lithium-containing residual liquid were obtained after precipitation. The alkali concentration was 2.5 mol/L, the stirring speed was 150 rpm, and the stirring adjustment time was 4 h. After suction filtration, solid-liquid separation is carried out to obtain a lithium-rich solution and a mixture for preparing a Co, Ni, and Mn precursor. The obtained Co, Ni, Mn precursor mixture was subjected to a solid phase reaction at 800 ° C for 15 h to prepare a positive electrode active material. The lithium-rich solution is added with saturated sodium carbonate to obtain a white precipitate. After suction filtration, washing and drying, a high-purity lithium carbonate solid is obtained. The precipitation temperature of lithium carbonate is 90 ° C, the stirring speed of precipitation is 150 rpm, the stirring adjustment time is 5 h, the molar ratio of carbonate ions added to the lithium carbonate precipitation to the lithium ion in the solution is 2:1, and the temperature of the washing water is 90 ° C. The purity of the obtained lithium carbonate was 99.92%.
表1废旧锂离子电池正极材料金属元素组成Table 1 Composition of the metal elements of the cathode material of the used lithium ion battery
金属metal AlAl FeFe LiLi NiNi CoCo MnMn
含量(%)content(%) 4.504.50 6.216.21 5.165.16 12.3112.31 10.7110.71 7.707.70
实施例2Example 2
用含有亚硫酸钠还原剂的三氯乙酸和硫酸混合酸(酸浓度为3mol/L,还原剂的质量百分含量为4%)对锂离子电池正极废料进行浸出。浸出S/L为50g/L,浸出温度为40℃,浸出时间为50min,搅拌速度为150rpm。得到含Li、Ni、Co和Mn的浸取液和浸取渣。得到金属Li、Ni、Co和Mn的浸出率分别为94.60%、92.80%和93.20%和93.80%,而金属Al和Fe的浸出率仅为2.12%、3.46%。浸取液经高 温浓缩/精馏处理回收浸出剂,得到含Co、Ni、Mn、Li余液。含Co、Ni、Mn、Li余液经组分调控使溶液中镍、钴和锰的摩尔比符合分子式LiNixCoyMn1-x-yO2中Ni、Co和Mn的摩尔比,其中x>0,y>0,且x+y<1。加氢氧化钠调整pH为10.4,沉淀后得Ni、Co和Mn前驱体(纯度99.3%)和含锂余液。所述碱浓度为2.5mol/L,搅拌速度为150rpm,搅拌调节时间为4h。过滤后,得到富锂溶液和用于制备Co、Ni、Mn前驱体的混料。所得Co、Ni、Mn前驱体混料在800℃下高温固相反应15h制备正极活性材料。富锂溶液加入饱和碳酸钠,得到白色沉淀,在抽滤、洗涤、干燥后,得到高纯碳酸锂固体。碳酸锂沉淀温度为85℃,沉淀搅拌速度为150rpm,沉淀搅拌调节时间为5h,碳酸锂沉淀加入的碳酸根离子与溶液中锂离子的摩尔比例为2:1,洗涤所用水的温度为90℃,所得碳酸锂纯度为99.95%。The lithium ion battery positive electrode waste was leached with a mixed acid of trichloroacetic acid and sulfuric acid containing a sodium sulfite reducing agent (acid concentration of 3 mol/L, and a mass percentage of the reducing agent of 4%). The leaching S/L was 50 g/L, the leaching temperature was 40 ° C, the leaching time was 50 min, and the stirring speed was 150 rpm. A leachate containing Li, Ni, Co, and Mn and a leach residue were obtained. The leaching rates of the metals Li, Ni, Co and Mn were 94.60%, 92.80% and 93.20% and 93.80%, respectively, while the leaching rates of metal Al and Fe were only 2.12% and 3.46%. The leachate is subjected to high temperature concentration/rectification treatment to recover the leaching agent to obtain a residual liquid containing Co, Ni, Mn and Li. The molar ratio of nickel, cobalt and manganese in the solution containing Co, Ni, Mn and Li is adjusted according to the molar ratio of Ni, Co and Mn in the formula LiNi x Co y Mn 1-xy O 2 , where x> 0, y>0, and x+y<1. The pH was adjusted to 10.4 by adding sodium hydroxide, and the precursors of Ni, Co and Mn (purity of 99.3%) and the lithium-containing residual liquid were obtained after precipitation. The alkali concentration was 2.5 mol/L, the stirring speed was 150 rpm, and the stirring adjustment time was 4 h. After filtration, a lithium-rich solution and a mixture for preparing a Co, Ni, Mn precursor were obtained. The obtained Co, Ni, Mn precursor mixture was subjected to a solid phase reaction at 800 ° C for 15 h to prepare a positive electrode active material. The lithium-rich solution is added with saturated sodium carbonate to obtain a white precipitate. After suction filtration, washing and drying, a high-purity lithium carbonate solid is obtained. The precipitation temperature of lithium carbonate is 85 ° C, the stirring speed of precipitation is 150 rpm, the stirring adjustment time is 5 h, the molar ratio of carbonate ions added to the lithium carbonate precipitation to the lithium ion in the solution is 2:1, and the temperature of the washing water is 90 ° C. The purity of the obtained lithium carbonate was 99.95%.
表2废旧锂离子电池正极材料金属元素组成Table 2 Composition of metal elements of cathode material of waste lithium ion battery
金属metal AlAl FeFe LiLi NiNi CoCo MnMn
含量(wt.%)Content (wt.%) 4.354.35 7.458.717.458.71 3.463.46 8.718.71 10.7110.71 7.017.01
申请人声明,本发明通过上述实施例来说明本发明的工艺方法,但本发明并不局限于上述工艺步骤,即不意味着本发明必须依赖上述工艺步骤才能实施。所属技术领域的技术人员应该明了,对本发明的任何改进,对本发明所选用原料的等效替换及辅助成分的添加、具体方式的选择等,均落在本发明的保护范围和公开范围之内。 The Applicant declares that the present invention illustrates the process of the present invention by the above-described embodiments, but the present invention is not limited to the above process steps, that is, it does not mean that the present invention must rely on the above process steps to be implemented. It will be apparent to those skilled in the art that any modifications of the present invention, equivalent substitutions of the materials selected for the present invention, and the addition of the auxiliary ingredients, the selection of the specific means, etc., are all within the scope of the present invention.

Claims (10)

  1. 一种从锂离子电池正极废料中回收正极材料前驱体和碳酸锂的方法,其特征在于,所述废料为生产废料中去除正极片所得的粉料或废旧电池经过机械破碎、分选后得到的含杂质正极粉料,同时包含以下步骤:A method for recovering a positive electrode material precursor and lithium carbonate from a lithium ion battery positive electrode waste, characterized in that the waste material is obtained by mechanically breaking and sorting the powder or waste battery obtained by removing the positive electrode sheet in the production waste. Impurity positive powder, including the following steps:
    (1)用含有还原剂的可挥发性浸取剂对锂离子电池正极废料进行浸出,分离得到浸取液和浸取渣;(1) leaching the lithium ion battery positive waste material with a volatile leaching agent containing a reducing agent, and separating the leaching liquid and the leaching slag;
    (2)步骤(1)所得浸取液进行浓缩精馏,再生浸取剂,得到可挥发性浸取剂和含Co、Ni、Mn、Li余液;(2) The leaching solution obtained in the step (1) is subjected to concentrated rectification, and the leaching agent is regenerated to obtain a volatile leaching agent and a residual liquid containing Co, Ni, Mn and Li;
    (3)步骤(2)所得余液经组分调控后进行Co、Ni、Mn组分的共沉淀;(3) The residual liquid obtained in the step (2) is subjected to co-precipitation of Co, Ni, and Mn components after being controlled by components;
    (4)步骤(3)共沉淀完毕后进行固液分离,得到富锂溶液和用于制备Co、Ni、Mn前驱体的混料;(4) Step (3) After the coprecipitation is completed, solid-liquid separation is performed to obtain a lithium-rich solution and a mixture for preparing a Co, Ni, Mn precursor;
    (5)步骤(4)所得Co、Ni、Mn混料通过高温固相反应制备正极材料活性材料;所得富锂溶液加入饱和碳酸钠溶液,得到白色沉淀,在抽滤、洗涤、干燥后,得到高纯碳酸锂固体。(5) The Co, Ni, Mn mixture obtained in the step (4) is prepared by a high-temperature solid phase reaction to prepare a positive electrode material active material; the obtained lithium-rich solution is added to a saturated sodium carbonate solution to obtain a white precipitate, which is obtained after suction filtration, washing and drying. High purity lithium carbonate solid.
  2. 根据权利要求1所述的方法,其特征在于,步骤(1)所述的浸取剂为可挥发性有机和/或无机酸的一种或多种混合并混有一种或多种还原剂的溶液;The method according to claim 1, wherein the leaching agent of step (1) is one or more of a volatile organic and/or inorganic acid mixed with one or more reducing agents. Solution
    所述酸浓度为0.1~15mol/L,还原剂的质量百分含量为0.1~20%,浸出S/L比为5~500g/L,浸出温度为5~100℃,浸出时间为5~480min,搅拌速度为0~2000rpm。The acid concentration is 0.1-15 mol/L, the mass percentage of the reducing agent is 0.1-20%, the leaching S/L ratio is 5-500 g/L, the leaching temperature is 5-100 ° C, and the leaching time is 5-480 min. The stirring speed is 0 to 2000 rpm.
  3. 根据权利要求2所述的方法,其特征在于,所述酸浓度优选为2~4mol/L;The method according to claim 2, wherein the acid concentration is preferably 2 to 4 mol/L;
    所述挥发性酸优选为硫酸、盐酸、硝酸、三氯乙酸、三氟乙酸、柠檬酸、甲酸、乙酸中的一种或几种混合;The volatile acid is preferably one or a mixture of sulfuric acid, hydrochloric acid, nitric acid, trichloroacetic acid, trifluoroacetic acid, citric acid, formic acid, acetic acid;
    优选的,所述还原剂的质量百分比含量为2~8%;Preferably, the reducing agent has a mass percentage of 2 to 8%;
    优选的,所述还原剂为亚硫酸钠、亚硫酸、硫代硫酸钠或过氧化氢中的一种或者几种的组合;Preferably, the reducing agent is one or a combination of sodium sulfite, sulfurous acid, sodium thiosulfate or hydrogen peroxide;
    优选的,所述浸出S/L为80~150g/L;Preferably, the leaching S/L is 80-150 g/L;
    优选的,所述浸出温度为20~80℃;Preferably, the leaching temperature is 20 to 80 ° C;
    优选的,所述搅拌速度为100~500rpm。Preferably, the stirring speed is 100 to 500 rpm.
  4. 根据权利要求1所述的方法,其特征在于,步骤(3)所得余液经组分调控后执行Co、Ni、Mn组分的共沉淀,通过固液分离,得到富锂溶液和用于制备Co、Ni、Mn前驱体的混料。 The method according to claim 1, wherein the residual liquid obtained in the step (3) is subjected to co-precipitation of Co, Ni, and Mn components after being controlled by components, and is obtained by solid-liquid separation to obtain a lithium-rich solution and used for preparation. Mixing of Co, Ni, Mn precursors.
  5. 根据权利要求4所述的方法,其特征在于,所述组分调控时需调节含镍和钴的溶液中镍、钴和锰的摩尔比,使其符合分子式LiNixCoyMn1-x-yO2中Ni、Co和Mn的摩尔比,其中x>0,y>0,且x+y<1。The method according to claim 4, wherein the composition is adjusted to adjust the molar ratio of nickel, cobalt and manganese in the solution containing nickel and cobalt to conform to the molecular formula LiNi x Co y Mn 1-xy O The molar ratio of Ni, Co and Mn in 2 , where x>0, y>0, and x+y<1.
  6. 根据权利要求5所述的方法,其特征在于,所述调节含镍和钴的溶液中镍、钴和锰的摩尔比具体为:向含镍、钴和锰的溶液中添加水溶性镍盐、钴盐或者锰盐中一种或至少两种的组合。The method according to claim 5, wherein the adjusting the molar ratio of nickel, cobalt and manganese in the solution containing nickel and cobalt is specifically: adding a water-soluble nickel salt to the solution containing nickel, cobalt and manganese, One or a combination of at least two of a cobalt salt or a manganese salt.
  7. 根据权利要求4所述的方法,其特征在于,所述共沉淀时溶液的pH为7~12,调整pH的溶液为碱性溶液,碱液浓度为0.1~10mol/L,搅拌速度为0~2000rpm,搅拌调节时间为0.5~72h,调节pH的温度为5~95℃;The method according to claim 4, wherein the pH of the solution during the coprecipitation is 7 to 12, the solution for adjusting the pH is an alkaline solution, the concentration of the alkali solution is 0.1 to 10 mol/L, and the stirring speed is 0 to 2000rpm, stirring adjustment time is 0.5 ~ 72h, the pH adjustment temperature is 5 ~ 95 ° C;
    优选的,所述碱性溶液为氢氧化钠、氨水中的一种或两种的混合。Preferably, the alkaline solution is a mixture of one or both of sodium hydroxide and aqueous ammonia.
  8. 根据权利要求7所述的方法,其特征在于,所述共沉淀溶液pH值优选为10~11;所述碱浓度优选为2~4mol/L;所述搅拌速度优选为100~500rpm;所述搅拌调节时间优选为2~4h;所述调节pH的温度优选为20~50℃。The method according to claim 7, wherein the pH of the coprecipitation solution is preferably 10 to 11; the alkali concentration is preferably 2 to 4 mol/L; and the stirring speed is preferably 100 to 500 rpm; The stirring adjustment time is preferably 2 to 4 hours; and the temperature for adjusting the pH is preferably 20 to 50 °C.
  9. 根据权利要求1所述的方法,其特征在于,步骤(4)共沉淀完毕后实行固液分离,得到富锂溶液和用于制备Co、Ni、Mn前驱体的混料;The method according to claim 1, wherein after the coprecipitation in step (4), solid-liquid separation is performed to obtain a lithium-rich solution and a mixture for preparing a Co, Ni, Mn precursor;
    优选的,所述固液分离以抽滤或过滤方式实现。Preferably, the solid-liquid separation is achieved by suction filtration or filtration.
  10. 根据权利要求1所述的方法,其特征在于,步骤(5)所得Co、Ni、Mn前驱体混料通过高温固相反应制备正极活性材料;The method according to claim 1, wherein the Co, Ni, Mn precursor mixture obtained in the step (5) is prepared by a high temperature solid phase reaction to prepare a positive electrode active material;
    所得富锂溶液高温浓缩/精馏处理,加入饱和碳酸钠溶液,得到白色沉淀,在抽滤、洗涤、干燥后,得到高纯碳酸锂固体;The obtained lithium-rich solution is subjected to high-temperature concentration/rectification treatment, and a saturated sodium carbonate solution is added to obtain a white precipitate. After suction filtration, washing and drying, a high-purity lithium carbonate solid is obtained;
    其中,碳酸锂沉淀温度为20~100℃,碳酸锂沉淀搅拌速度为0~2000rpm,沉淀搅拌调节时间为0.5~72h,洗涤所用水的温度为10~100℃;Wherein, the precipitation temperature of lithium carbonate is 20-100 ° C, the stirring speed of lithium carbonate precipitation is 0-2000 rpm, the adjustment time of precipitation stirring is 0.5-72 h, and the temperature of washing water is 10-100 ° C;
    优选的,高温固相反应温度为600~850℃,反应时间为3~20h;Preferably, the high temperature solid phase reaction temperature is 600 to 850 ° C, and the reaction time is 3 to 20 h;
    优选的,所述碳酸锂沉淀温度为60~100℃;Preferably, the lithium carbonate precipitation temperature is 60 to 100 ° C;
    优选的,所述碳酸锂沉淀搅拌速度为100~500rpm;Preferably, the lithium carbonate precipitation stirring speed is 100 to 500 rpm;
    优选的,所述碳酸锂沉淀搅拌调节时间为1~16h;Preferably, the lithium carbonate precipitation stirring adjustment time is 1 to 16 h;
    优选的,所述碳酸锂沉淀加入的碳酸根离子与溶液中锂离子的摩尔比例为1~3:2;Preferably, the molar ratio of carbonate ions added to the lithium carbonate precipitation to lithium ions in the solution is 1 to 3:2;
    优选的,所述洗涤所用水的温度为90~100℃ Preferably, the temperature of the washing water is 90-100 ° C
PCT/CN2017/092709 2017-04-18 2017-07-13 Method for efficiently recovering positive electrode material precursor and lithium carbonate from positive electrode waste material of lithium ion battery WO2018192121A1 (en)

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