CN111600089A - Recycling process of waste ternary lithium battery positive electrode material - Google Patents

Recycling process of waste ternary lithium battery positive electrode material Download PDF

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CN111600089A
CN111600089A CN202010485265.0A CN202010485265A CN111600089A CN 111600089 A CN111600089 A CN 111600089A CN 202010485265 A CN202010485265 A CN 202010485265A CN 111600089 A CN111600089 A CN 111600089A
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lithium battery
battery
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ternary lithium
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周明炯
刘博宇
庞宝成
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Ningbo University
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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
    • C22B26/00Obtaining alkali, alkaline earth metals or magnesium
    • C22B26/10Obtaining alkali metals
    • C22B26/12Obtaining lithium
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B3/00Extraction of metal compounds from ores or concentrates by wet processes
    • C22B3/04Extraction of metal compounds from ores or concentrates by wet processes by leaching
    • C22B3/06Extraction of metal compounds from ores or concentrates by wet processes by leaching in inorganic acid solutions, e.g. with acids generated in situ; in inorganic salt solutions other than ammonium salt solutions
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B3/00Extraction of metal compounds from ores or concentrates by wet processes
    • C22B3/20Treatment or purification of solutions, e.g. obtained by leaching
    • C22B3/44Treatment or purification of solutions, e.g. obtained by leaching by chemical processes
    • HELECTRICITY
    • H01ELECTRIC ELEMENTS
    • H01MPROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
    • H01M4/00Electrodes
    • H01M4/02Electrodes composed of, or comprising, active material
    • H01M4/13Electrodes for accumulators with non-aqueous electrolyte, e.g. for lithium-accumulators; Processes of manufacture thereof
    • HELECTRICITY
    • H01ELECTRIC ELEMENTS
    • H01MPROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
    • H01M4/00Electrodes
    • H01M4/02Electrodes composed of, or comprising, active material
    • H01M2004/026Electrodes composed of, or comprising, active material characterised by the polarity
    • H01M2004/028Positive electrodes
    • 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
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E60/00Enabling technologies; Technologies with a potential or indirect contribution to GHG emissions mitigation
    • Y02E60/10Energy storage using batteries
    • 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

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Abstract

The invention provides a recycling process of a waste ternary lithium battery anode material. The anode plate treating fluid used in the invention has extremely low toxicity on material components, can effectively dissolve the binder in the separation process, enables active substances to be separated out, has extremely high efficiency, is easy to degrade, and is very environment-friendly. In addition, in the subsequent recovery process, at present, organic extractant is used for extracting and recovering valuable metals, the used extractant has serious pollution to the environment, and the extraction process is very complex.

Description

Recycling process of waste ternary lithium battery positive electrode material
Technical Field
The invention belongs to the technical field of new energy batteries, and particularly relates to a process for recycling a waste ternary lithium battery positive electrode material.
Background
Lithium ion batteries have many advantages of small size, light weight, high specific energy, long service life, etc., and are widely used in many fields such as electric vehicles, mobile phones, notebook computers, cameras, etc. After the lithium batteries are popularized and used, a large amount of waste lithium batteries are generated. In addition, valuable metals contained in the waste lithium batteries can be recycled, so that the problem of resource shortage of metals such as nickel, cobalt, manganese and the like can be effectively solved, the metals are recycled, the waste is changed into valuable materials, and the environmental pollution is greatly reduced while the metals are well recycled. At present, in the recovery of lithium batteries, hydrometallurgy is mainly used, valuable metals exist in a solution in an ion form through acid leaching and dissolution, and then the valuable metals are gradually extracted by using an extracting agent, so that the cost consumption of the process is high, and the use of the extracting agent can affect the environment.
Disclosure of Invention
In view of the above, the technical problem to be solved by the invention is to provide a process for recycling a waste ternary lithium battery positive electrode material, wherein the process provided by the invention is energy-saving and environment-friendly, and can effectively separate an active substance from a current collector and circularly regenerate the active substance.
The invention provides a process for recycling a waste ternary lithium battery positive electrode material, which comprises the following steps:
A) placing a positive plate of a waste ternary lithium battery in a treatment solution, heating and stirring, and then filtering to obtain a filtered product, wherein the treatment solution comprises a solvent and a solute, the solvent is selected from one or more of ethylene glycol, glycerol and butanediol, and the solute is selected from one or more of xylitol, glucose, urea and choline chloride;
B) screening and acid leaching the filtered product in sequence to obtain acid leaching solution;
C) adjusting the ion concentration of the pickle liquor, adding a complexing agent and a precipitator to adjust the pH value, carrying out coprecipitation reaction to separate a precursor, and then recovering the metal lithium.
Preferably, the positive plate of the waste ternary lithium battery is obtained by the following method:
soaking the waste ternary lithium battery in saturated salt water for discharging treatment;
cleaning and drying the discharged waste ternary lithium battery with clear water;
cutting and crushing the dried battery into battery slices;
and separating the positive plate, the negative plate, the shell and the diaphragm of the battery by a flotation method.
Preferably, the size of the battery slice is 1-2 cm.
Preferably, the molar ratio of the solute to the solvent in the treatment solution is (1.5-2.5): 1, and the solid-liquid mass-volume ratio of the positive electrode sheet to the treatment solution is 1 g: (20-25) ml.
Preferably, the heating and stirring temperature is 150-200 ℃, and the time is 3-5 h.
Preferably, the mass-to-volume ratio of the positive electrode active material obtained after screening to the acid solution used for acid leaching is 1 g: (5-20) ml; the acid liquor used for acid leaching is a mixed solution of inorganic acid and a reducing agent, and the inorganic acid is H2SO4、HCl、HNO3The reducing agent is H2O2、Na2SO3、Na2S2O3The concentration of the inorganic acid in the acid solution is 2-4 mol/L, 1-2 mL of liquid reducing agent is added into each gram of active substance, or 0.2-0.5 g of solid reducing agent is added into each gram of positive active substance, the acid leaching temperature is 60-80 ℃, and the time is 4-5 hours.
Preferably, the ion concentration of the acid leaching solution is adjusted by adopting nickel salt, cobalt salt and manganese salt to adjust the ion concentration of nickel, cobalt and manganese in the acid leaching solution until the concentration of nickel ions is 0.5-2 mol/L, the concentration of cobalt ions is 0.2-1 mol/L and the concentration of manganese ions is 0.2-1 mol/L.
Preferably, the complexing agent is NH3·H2O, NaF and ammonium salt, wherein the precipitant is one or more of sodium hydroxide, potassium hydroxide, sodium bicarbonate, sodium carbonate and potassium carbonate, and the pH of the pickle liquor is adjusted to 11-12.
Preferably, in the step C), the reaction temperature is 50-60 ℃, the stirring speed during the reaction is 500-700 r/min, and the reaction time is 5-10 h.
Preferably, the method for recovering the metallic lithium comprises the following steps:
and adding water-soluble carbonate into the reaction solution after the reaction, so that lithium ions are precipitated as lithium carbonate.
Compared with the prior art, the invention provides a process for recycling a waste ternary lithium battery anode material, which comprises the following steps: A) placing a positive plate of a waste ternary lithium battery in a treatment solution, heating and stirring, and then filtering to obtain a filtered product, wherein the treatment solution comprises a solvent and a solute, the solvent is selected from one or more of ethylene glycol, glycerol and butanediol, and the solute is selected from one or more of xylitol, glucose, urea and choline chloride; B) screening and acid leaching the filtered product in sequence to obtain acid leaching solution; C) and after the pH value and the ion concentration of the pickle liquor are adjusted, adding a complexing agent and a precipitator for reaction, and recovering the lithium metal. The anode plate treating fluid used in the invention has extremely low toxicity on material components, can effectively dissolve the binder in the separation process, enables active substances to be separated out, has extremely high efficiency, is easy to degrade, and is very environment-friendly. In addition, in the subsequent recovery process, at present, organic extractant is used for extracting and recovering valuable metals, the used extractant has serious pollution to the environment, and the extraction process is very complex.
Drawings
FIG. 1 is a process flow chart of the recycling process of the anode material of the waste ternary lithium battery provided by the invention.
Detailed Description
The invention provides a process for recycling a waste ternary lithium battery positive electrode material, which comprises the following steps:
A) placing the positive plate of the waste ternary lithium battery in a treatment solution, heating and stirring, and then filtering to obtain a filtered product; the processing liquid comprises a solvent and a solute, wherein the solvent is selected from one or more of ethylene glycol, glycerol and butanediol, and the solute is selected from one or more of xylitol, glucose, urea and choline chloride;
B) screening and acid leaching the filtered product in sequence to obtain acid leaching solution;
C) and after the pH value and the ion concentration of the pickle liquor are adjusted, adding a complexing agent and a precipitator for reaction, and recovering the lithium metal.
The invention firstly separates the positive plate from the waste ternary lithium battery, and the specific method comprises the following steps:
soaking the waste ternary lithium battery in saturated salt water for discharging treatment;
cleaning and drying the discharged waste ternary lithium battery with clear water;
cutting and crushing the dried battery into battery slices, wherein the size of each battery slice is 1-2 cm;
the positive plate, the negative plate, the shell and the diaphragm of the battery are separated by a flotation method, and the specific method of the flotation method is not particularly limited, and can be a method known by a person skilled in the art.
And after obtaining the positive plate, placing the positive plate in a treatment solution for heating and stirring treatment.
The processing liquid comprises a solvent and a solute, wherein the solvent is selected from one or more of ethylene glycol, glycerol and butanediol, and the solute is selected from one or more of xylitol, glucose, urea and choline chloride. In some embodiments of the invention, the treatment fluid is a mixture of choline chloride and butylene glycol. The molar ratio of the solute to the solvent in the treatment liquid is (1.5-2.5): 1.
In the invention, the solid-liquid mass volume ratio of the positive plate to the treatment solution is 1 g: (20-25) ml.
In the invention, the solid-liquid mass-volume ratio is as follows: and ml is taken as a unit.
The heating and stirring temperature is 150-200 ℃, preferably 160-190 ℃, and the time is 3-5 h, preferably 3.5-4.5 h.
And after the heating and stirring treatment is finished, filtering, screening filter residues, and separating a larger aluminum foil from the positive active material.
And performing acid leaching on the positive electrode active substance to obtain acid leaching solution.
Wherein the mass-to-volume ratio of the anode active material obtained after screening to the acid solution used for acid leaching is 1 g: (5-20) ml; preferably 1 g: 10 ml; the acid liquor used for acid leaching is a mixed solution of inorganic acid and a reducing agent, and the inorganic acid is H2SO4、HCl、HNO3The reducing agent is H2O2、Na2SO3、Na2S2O3The concentration of the inorganic acid in the acid solution is 2-4 mol/L, preferably 2.5-3.5 mol/L, 1-2 mL of liquid reducing agent is added into each gram of positive electrode active substance, or 0.2-0.5 g of solid reducing agent is added into each gram of positive electrode active substance,
the acid leaching temperature is 60-80 ℃, preferably 65-75 ℃, and the time is 4-5 h.
After the acid leaching solution is obtained, adjusting the ion concentration of the acid leaching solution, namely adjusting the ion concentration of nickel, cobalt and manganese in the acid leaching solution by adopting nickel salt, cobalt salt and manganese salt until the nickel ion concentration is 0.5-2 mol/L, preferably 1mol/L, the cobalt ion concentration is 0.2-1 mol/L, preferably 0.6mol/L, and the manganese ion concentration is 0.2-1 mol/L, preferably 0.4 mol/L.
And then, adding a complexing agent and a precipitator to adjust the pH value for coprecipitation reaction. Wherein the complexing agent is NH3·H2O, NaF and ammonium salt, wherein the precipitant is one or more of sodium hydroxide, potassium hydroxide, sodium bicarbonate, sodium carbonate and potassium carbonate, and the pH of the solution is adjusted to 11-12.
And (3) carrying out coprecipitation reaction to generate a precursor, and washing and drying the precursor. Recovering metallic lithium from reaction liquid obtained after coprecipitation reaction, and the specific method comprises the following steps:
a water-soluble carbonate, preferably sodium carbonate or potassium carbonate, is added to the reaction solution after the reaction, so that lithium ions are precipitated as lithium carbonate.
Referring to fig. 1, fig. 1 is a flow chart of a process for recycling the anode material of the waste ternary lithium battery provided by the invention.
In the separation of active substances, high-temperature ignition and NMP and DMF solvent dissolution are commonly used at present, the former has high energy consumption and high risk, and the latter has high solvent toxicity. In the subsequent recovery process, at present, organic extractant is used for extracting and recovering valuable metals, the used extractant has serious pollution to the environment, and the extraction process is very complicated.
For further understanding of the present invention, the following describes a recycling process of the waste ternary lithium battery positive electrode material provided by the present invention with reference to the following examples, and the scope of the present invention is not limited by the following examples.
Example 1
1. Soaking the waste ternary lithium battery NCM532 in saturated salt water for discharge treatment for 12 hours;
2. repeatedly washing the discharged waste ternary lithium battery NCM532 with clear water for many times and drying;
3. cutting and crushing the dried battery into battery slices with the diameter of 1 cm;
4. separating the pole piece, the shell and the diaphragm by a flotation method;
5. soaking the positive plate in a solvent uniformly mixed by choline chloride and butanediol, wherein the mol ratio of the choline chloride to the butanediol is 2: 1, heating at 160 ℃, soaking and stirring for 5 hours, wherein the solid-liquid mass-volume ratio (g: ml) is 1: 20;
6. after soaking and filtering, screening filter residues, and separating larger aluminum foils from active substances;
7. mixing the active substance with H2SO4Soaking is carried out H2SO4The concentration is 2.5mol/L, the reducing agent is H2O22ml of H per gram of active substance2O2The soaking temperature is 60 ℃, the soaking time is 4 hours, and the solid-liquid mass-volume ratio (g: ml) is 1: 10;
8. adding nickel sulfate, cobalt sulfate and manganese sulfate into the solution to enable the ion concentration of nickel, cobalt and manganese in the solution to be close to 1mol/L, 0.6mol/L and 0.4mol/L, and adding NH3·H2Adjusting the pH value of O and NaOH solution to 11.5, the reaction temperature to 50 ℃, the stirring speed to 600r/min, coprecipitating to generate a precursor, repeatedly washing the precursor, and putting the precursor into a vacuum drying oven at 110 ℃ for 12 hours;
9. sodium carbonate was added to the solution to precipitate lithium as lithium carbonate, which was repeatedly washed with clean water and dried.
Example 2
1. Soaking the waste ternary lithium battery NCM532 in saturated salt water for discharge treatment for 12 hours;
2. repeatedly washing the discharged waste ternary lithium battery NCM532 with clear water for many times and drying;
3. cutting and crushing the dried battery into battery slices with the diameter of 1 cm;
4. separating the pole piece, the shell and the diaphragm by a flotation method;
5. soaking the positive plate in a solvent uniformly mixed by choline chloride and butanediol, wherein the mol ratio of the choline chloride to the butanediol is 2: 1, heating to 170 ℃, soaking and stirring for 5 hours, wherein the solid-liquid mass-volume ratio (g: ml) is 1: 20;
6. after soaking and filtering, screening filter residues, and separating larger aluminum foils from active substances;
7. mixing the active substance with H2SO4Soaking is carried out H2SO4The concentration is 2.5mol/L, the reducing agent is H2O22ml of H per gram of active substance2O2The soaking temperature is 60 ℃, the soaking time is 4 hours, and the solid-liquid mass-volume ratio (g: ml) is 1: 10;
8. adding nickel sulfate, cobalt sulfate and manganese sulfate into the solution to enable the ion concentration of nickel, cobalt and manganese in the solution to be close to 1mol/L, 0.6mol/L and 0.4mol/L, and adding NH3·H2Adjusting the pH value of O and NaOH solution to 11.5, the reaction temperature to 50 ℃, the stirring speed to 600r/min, generating a precursor for coprecipitation, repeatedly washing the precursor, and putting the precursor into a vacuum drying oven at 110 ℃ for 12 hours;
9. sodium carbonate was added to the solution to precipitate lithium as lithium carbonate, which was repeatedly washed with clean water and dried.
Example 3
1. Soaking the waste ternary lithium battery NCM532 in saturated salt water for discharge treatment for 12 hours;
2. repeatedly washing the discharged waste ternary lithium battery NCM532 with clear water for many times and drying;
3. cutting and crushing the dried battery into battery slices with the diameter of 1 cm;
4. separating the pole piece, the shell and the diaphragm by a flotation method;
5. soaking the positive plate in a solvent uniformly mixed by choline chloride and butanediol, wherein the mol ratio of the choline chloride to the butanediol is 2: 1, heating to 180 ℃, soaking and stirring for 5 hours, wherein the solid-liquid mass-volume ratio (g: ml) is 1: 20;
6. after soaking and filtering, screening filter residues, and separating larger aluminum foils from active substances;
7. mixing the active substance with H2SO4Soaking is carried out H2SO4The concentration is 2.5mol/L, the reducing agent is H2O22ml of H per gram of active substance2O2The soaking temperature is 60 ℃, the soaking time is 4 hours, and the solid-liquid mass-volume ratio (g: ml) is 1: 10;
8. adding nickel sulfate, cobalt sulfate and manganese sulfate into the solution to enable the ion concentration of nickel, cobalt and manganese in the solution to be close to 1mol/L, 0.6mol/L and 0.4mol/L, and adding NH3·H2Adjusting the pH value of O and NaOH solution to 11.5, the reaction temperature to 50 ℃, the stirring speed to 600r/min, coprecipitating to generate a precursor, repeatedly washing the precursor with clear water and placing the precursor into a vacuum drying oven at 110 ℃ for 12 hours;
9. sodium carbonate was added to the solution to precipitate lithium as lithium carbonate, which was repeatedly washed with clean water and dried.
Example 4
1. Soaking the waste ternary lithium battery NCM532 in saturated salt water for discharge treatment for 12 hours;
2. repeatedly washing the discharged waste ternary lithium battery NCM532 with clear water for many times and drying;
3. cutting and crushing the dried battery into battery slices with the diameter of 1 cm;
4. separating the pole piece, the shell and the diaphragm by a flotation method;
5. soaking the positive plate in a solvent uniformly mixed by choline chloride and butanediol, wherein the mol ratio of the choline chloride to the butanediol is 2: 1, heating to 180 ℃, soaking and stirring for 5 hours, wherein the solid-liquid mass-volume ratio (g: ml) is 1: 20;
6. after soaking and filtering, screening filter residues, and separating larger aluminum foils from active substances;
7. mixing the active substance with H2SO4Soaking is carried out H2SO4The concentration is 2.5mol/L, the reducing agent is H2O22ml of H per gram of active substance2O2The soaking temperature is 60 ℃, the soaking time is 4 hours, and the solid-liquid mass-volume ratio (g: ml) is 1: 10;
8. adding nickel sulfate, cobalt sulfate and manganese sulfate into the solution to enable the ion concentration of nickel, cobalt and manganese in the solution to be close to 1mol/L, 0.6mol/L and 0.4mol/L, and adding NH3·H2O and NaOH solution, regulating the pH value to 12, controlling the reaction temperature to 50 ℃, controlling the stirring speed to 600r/min, carrying out coprecipitation to generate a precursor, repeatedly washing the precursor with clear water, and placing the precursor into a vacuum drying oven at 110 ℃ for 12 hours;
9. sodium carbonate was added to the solution to precipitate lithium as lithium carbonate, which was repeatedly washed with clean water and dried.
Example 5
1. Soaking the waste ternary lithium battery NCM532 in saturated salt water for discharge treatment for 12 hours;
2. repeatedly washing the discharged waste ternary lithium battery NCM532 with clear water for many times and drying;
3. cutting and crushing the dried battery into battery slices with the diameter of 1 cm;
4. separating the pole piece, the shell and the diaphragm by a flotation method;
5. soaking the positive plate in a solvent uniformly mixed by choline chloride and butanediol, wherein the mol ratio of the choline chloride to the butanediol is 2: 1, heating to 180 ℃, soaking and stirring for 5 hours, wherein the solid-liquid mass-volume ratio (g: ml) is 1: 20;
6. after soaking and filtering, screening filter residues, and separating larger aluminum foils from active substances;
7. mixing the active substance with H2SO4Soaking is carried out H2SO4The concentration is 2.5mol/L, the reducing agent is H2O22ml of H per gram of active substance2O2The soaking temperature is 60 ℃, the soaking time is 4 hours, and the solid-liquid mass-volume ratio (g: ml) is 1: 10;
8. adding nickel sulfate, cobalt sulfate and manganese sulfate into the solution to enable the ion concentration of nickel, cobalt and manganese in the solution to be close to 1mol/L, 0.6mol/L and 0.4mol/L, and adding NH3·H2Adjusting the pH value of O and NaOH solution to 11.5, the reaction temperature to 60 ℃, the stirring speed to 600r/min, coprecipitating to generate a precursor, repeatedly washing the precursor with clear water and placing the precursor into a vacuum drying oven at 110 ℃ for 12 hours;
9. sodium carbonate was added to the solution to precipitate lithium as lithium carbonate, which was repeatedly washed with clean water and dried.
Example 6
1. Soaking the waste ternary lithium battery NCM111 in saturated salt water for discharge treatment for 12 hours;
2. repeatedly washing the discharged waste ternary lithium battery NCM111 with clear water for many times and drying;
3. cutting and crushing the dried battery into battery slices with the diameter of 1 cm;
4. separating the pole piece, the shell and the diaphragm by a flotation method;
5. soaking the positive plate in a solvent uniformly mixed by choline chloride and butanediol, wherein the mol ratio of the choline chloride to the butanediol is 2: 1, heating to 180 ℃, soaking and stirring for 5 hours, wherein the solid-liquid mass-volume ratio (g: ml) is 1: 20;
6. after soaking and filtering, screening filter residues, and separating larger aluminum foils from active substances;
7. mixing the active substance with H2SO4Soaking is carried out H2SO4The concentration is 2.5mol/L, the reducing agent is H2O22ml of H per gram of active substance2O2The soaking temperature is 60 ℃, the soaking time is 4 hours, and the solid-liquid mass-volume ratio (g: ml) is 1: 10;
8. adding nickel sulfate, cobalt sulfate and manganese sulfate into the solution to enable the ion concentration of nickel, cobalt and manganese in the solution to be close to 1mol/L, 1mol/L and 1mol/L, and adding NH3·H2Adjusting the pH value of O and NaOH solution to 11.5, the reaction temperature to 60 ℃, the stirring speed to 600r/min, coprecipitating to generate a precursor, repeatedly washing the precursor with clear water and placing the precursor into a vacuum drying oven at 110 ℃ for 12 hours;
9. sodium carbonate was added to the solution to precipitate lithium as lithium carbonate, which was repeatedly washed with clean water and dried.
Example 7
1. Soaking the waste ternary lithium battery NCM532 in saturated salt water for discharge treatment for 12 hours;
2. repeatedly washing the discharged waste ternary lithium battery NCM532 with clear water for many times and drying;
3. cutting and crushing the dried battery into battery slices with the diameter of 1 cm;
4. separating the pole piece, the shell and the diaphragm by a flotation method;
5. soaking the positive plate in a solvent uniformly mixed by choline chloride and glycerol, wherein the molar ratio of the choline chloride to the glycerol is 2: 1, heating to 180 ℃, soaking and stirring for 5 hours, wherein the solid-liquid mass-volume ratio (g: ml) is 1: 20;
6. after soaking and filtering, screening filter residues, and separating larger aluminum foils from active substances;
7. mixing the active substance with H2SO4Soaking is carried out H2SO4The concentration is 2.5mol/L, the reducing agent is H2O22ml of H per gram of active substance2O2The soaking temperature is 60 ℃, the soaking time is 4 hours, and the solid-liquid mass-volume ratio (g: ml) is 1: 10;
8. adding nickel sulfate, cobalt sulfate and manganese sulfate into the solution to enable the ion concentration of nickel, cobalt and manganese in the solution to be close to 1mol/L, 0.6mol/L and 0.4mol/L, and adding NH3·H2Adjusting the pH value of O and NaOH solution to 11.5, the reaction temperature to 60 ℃, the stirring speed to 600r/min, coprecipitating to generate a precursor, repeatedly washing the precursor with clear water and placing the precursor into a vacuum drying oven at 110 ℃ for 12 hours;
9. sodium carbonate was added to the solution to precipitate lithium as lithium carbonate, which was repeatedly washed with clean water and dried.
Comparative example 1.
(1) Soaking the waste ternary lithium battery NCM532 in saturated salt water for discharge treatment for 12 hours;
(2) repeatedly washing the discharged waste ternary lithium battery NCM532 with clear water for many times and drying;
(3) cutting and crushing the dried battery into battery slices with the diameter of 1 cm;
(4) separating the pole piece, the shell and the diaphragm by a flotation method;
(5) soaking the positive plate in a solvent uniformly mixed by choline chloride and water, wherein the mol ratio of the choline chloride to the water is 2: 1, heating at 70 ℃, soaking and stirring for 5 hours, wherein the solid-liquid mass-volume ratio is 1: 20;
(6) filtering the binder solution to obtain a filtered product;
through observation of the filtered product, the binder dissolving solution does not effectively dissolve the binder, and the experimental scheme has poor effect.
Comparative example 2.
(1) Soaking the waste ternary lithium battery NCM532 in saturated salt water for discharge treatment for 12 hours;
(2) repeatedly washing the discharged waste ternary lithium battery NCM532 with clear water for many times and drying;
(3) cutting and crushing the dried battery into battery slices with the diameter of 1 cm;
(4) separating the pole piece, the shell and the diaphragm by a flotation method;
(5) soaking the positive plate in NaOH solution;
(6) hydrolyzing, screening and washing the mixed solution
The observation shows that the effect of removing the active substances is not very good, and the dosage needs to be strictly controlled in the operation process, otherwise, hydrogen is generated, explosion is easily caused under the high-temperature condition, and the scheme has poor effect.
The recycling effects of the above examples and comparative examples were measured, and the results are shown in Table 1
TABLE 1 measurement results of recovery Effect
Figure BDA0002518823900000101
The foregoing is only a preferred embodiment of the present invention, and it should be noted that, for those skilled in the art, various modifications and decorations can be made without departing from the principle of the present invention, and these modifications and decorations should also be regarded as the protection scope of the present invention.

Claims (10)

1. A recycling process for a waste ternary lithium battery positive electrode material is characterized by comprising the following steps:
A) placing a positive plate of a waste ternary lithium battery in a treatment solution, heating and stirring, and then filtering to obtain a filtered product, wherein the treatment solution comprises a solvent and a solute, the solvent is selected from one or more of ethylene glycol, glycerol and butanediol, and the solute is selected from one or more of xylitol, glucose, urea and choline chloride;
B) screening and acid leaching the filtered product in sequence to obtain acid leaching solution;
C) adjusting the ion concentration of the pickle liquor, adding a complexing agent and a precipitator to adjust the pH value, carrying out coprecipitation reaction to separate a precursor, and then recovering the metal lithium.
2. The process as claimed in claim 1, wherein the positive plate of the waste ternary lithium battery is obtained by the following method:
soaking the waste ternary lithium battery in saturated salt water for discharging treatment;
cleaning and drying the discharged waste ternary lithium battery with clear water;
cutting and crushing the dried battery into battery slices;
and separating the positive plate, the negative plate, the shell and the diaphragm of the battery by a flotation method.
3. The process according to claim 1, wherein the battery slices have a size of 1-2 cm.
4. The process according to claim 1, wherein the molar ratio of the solute to the solvent in the treatment solution is (1.5-2.5): 1, and the solid-liquid mass-volume ratio of the positive electrode sheet to the treatment solution is 1 g: (20-25) ml.
5. The process according to claim 1, wherein the heating and stirring temperature is 150-200 ℃ and the time is 3-5 h.
6. The process according to claim 1, wherein the mass-to-volume ratio of the positive electrode active material obtained after screening to the acid solution used for acid leaching is 1 g: (5-20) ml; the acid liquor used for acid leaching is a mixed solution of inorganic acid and a reducing agent, and the inorganic acid is H2SO4、HCl、HNO3The reducing agent is H2O2、Na2SO3、Na2S2O3The concentration of the inorganic acid in the acid solution is 2-4 mol/L, 1-2 mL of liquid reducing agent is added into each gram of active substance, or 0.2-0.5 g of solid reducing agent is added into each gram of positive electrode active substance,
the acid leaching temperature is 60-80 ℃, and the time is 4-5 h.
7. The process of claim 1, wherein the ion concentration of the acid leaching solution is adjusted by using nickel salt, cobalt salt and manganese salt to adjust the ion concentration of nickel, cobalt and manganese in the acid leaching solution to 0.5-2 mol/L of nickel ion, 0.2-1 mol/L of cobalt ion and 0.2-1 mol/L of manganese ion.
8. The process of claim 1, wherein the complexing agent is NH3·H2O, NaF and ammonium salt, wherein the precipitant is one or more of sodium hydroxide, potassium hydroxide, sodium bicarbonate, sodium carbonate and potassium carbonate, and the pH of the pickle liquor is adjusted to 11-12.
9. The process according to claim 1, wherein in the step C), the reaction temperature is 50-60 ℃, the stirring speed during the reaction is 500-700 r/min, and the reaction time is 5-10 h.
10. The process of claim 1, wherein the method for recovering lithium metal is:
and adding water-soluble carbonate into the reaction solution after the reaction, so that lithium ions are precipitated as lithium carbonate.
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Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112143897A (en) * 2020-09-11 2020-12-29 威海广泰空港设备股份有限公司 Method for extracting noble metal from waste lithium battery in airport service vehicle
CN113117455A (en) * 2021-04-12 2021-07-16 江西师范大学 Application of choline chloride-glycerol eutectic solvent in absorbing HCl gas
WO2022119262A1 (en) * 2020-12-02 2022-06-09 에스케이이노베이션 주식회사 Method for recovering lithium precursor from waste lithium secondary battery positive electrode material
CN115466842A (en) * 2021-11-12 2022-12-13 金为环保科技(常州)有限公司 Treatment method and application of waste lithium battery waste liquid
CN115505757A (en) * 2022-10-21 2022-12-23 中国地质科学院郑州矿产综合利用研究所 Method for recycling lithium and manganese of anode materials of waste lithium manganate lithium batteries through eutectic solvent
CN116116867A (en) * 2022-09-07 2023-05-16 北京科技大学 Cooperative treatment system and method for waste dry batteries and kitchen waste

Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105789726A (en) * 2016-04-21 2016-07-20 苏州聚智同创环保科技有限公司 Method for preparing nickel-cobalt-manganese ternary material precursor from waste lithium ion battery
CN108878866A (en) * 2018-06-28 2018-11-23 山东理工大学 The method for preparing ternary material precursor using waste and old lithium ion battery tertiary cathode material and recycling lithium
CN108899604A (en) * 2018-06-28 2018-11-27 郑州中科新兴产业技术研究院 Utilize the method for waste lithium cell anode pole piece preparation ternary anode material precursor
CN110120560A (en) * 2019-04-16 2019-08-13 福建常青新能源科技有限公司 A kind of waste and old ternary lithium battery recycling sorting process
CN110331290A (en) * 2019-07-08 2019-10-15 中南大学 The method that liquid phase method recycles lithium and transition elements in waste lithium cell positive electrode
CN110422891A (en) * 2019-08-08 2019-11-08 中国科学院青海盐湖研究所 A kind of method preparing nickel-cobalt-manganese ternary presoma, system and application
CN110862110A (en) * 2019-11-26 2020-03-06 宁夏百川新材料有限公司 Method for preparing ternary positive electrode material precursor by using waste lithium ion battery
CN111041216A (en) * 2019-12-27 2020-04-21 中国矿业大学 Method for extracting and recycling waste ternary lithium battery positive electrode metal material by using glycerol eutectic solvent

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105789726A (en) * 2016-04-21 2016-07-20 苏州聚智同创环保科技有限公司 Method for preparing nickel-cobalt-manganese ternary material precursor from waste lithium ion battery
CN108878866A (en) * 2018-06-28 2018-11-23 山东理工大学 The method for preparing ternary material precursor using waste and old lithium ion battery tertiary cathode material and recycling lithium
CN108899604A (en) * 2018-06-28 2018-11-27 郑州中科新兴产业技术研究院 Utilize the method for waste lithium cell anode pole piece preparation ternary anode material precursor
CN110120560A (en) * 2019-04-16 2019-08-13 福建常青新能源科技有限公司 A kind of waste and old ternary lithium battery recycling sorting process
CN110331290A (en) * 2019-07-08 2019-10-15 中南大学 The method that liquid phase method recycles lithium and transition elements in waste lithium cell positive electrode
CN110422891A (en) * 2019-08-08 2019-11-08 中国科学院青海盐湖研究所 A kind of method preparing nickel-cobalt-manganese ternary presoma, system and application
CN110862110A (en) * 2019-11-26 2020-03-06 宁夏百川新材料有限公司 Method for preparing ternary positive electrode material precursor by using waste lithium ion battery
CN111041216A (en) * 2019-12-27 2020-04-21 中国矿业大学 Method for extracting and recycling waste ternary lithium battery positive electrode metal material by using glycerol eutectic solvent

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
MENGMENG WANG, QUANYIN TAN, LILI LIU, JINHUI LI: "A low-toxicity and high-efficiency deep eutectic solvent for the separation of aluminum foil and cathode materials from spent lithium-ion batteries" *

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112143897A (en) * 2020-09-11 2020-12-29 威海广泰空港设备股份有限公司 Method for extracting noble metal from waste lithium battery in airport service vehicle
CN112143897B (en) * 2020-09-11 2021-06-08 威海广泰空港设备股份有限公司 Method for extracting noble metal from waste lithium battery in airport service vehicle
WO2022119262A1 (en) * 2020-12-02 2022-06-09 에스케이이노베이션 주식회사 Method for recovering lithium precursor from waste lithium secondary battery positive electrode material
CN113117455A (en) * 2021-04-12 2021-07-16 江西师范大学 Application of choline chloride-glycerol eutectic solvent in absorbing HCl gas
CN115466842A (en) * 2021-11-12 2022-12-13 金为环保科技(常州)有限公司 Treatment method and application of waste lithium battery waste liquid
CN116116867A (en) * 2022-09-07 2023-05-16 北京科技大学 Cooperative treatment system and method for waste dry batteries and kitchen waste
CN116116867B (en) * 2022-09-07 2023-10-13 北京科技大学 Cooperative treatment system and method for waste dry batteries and kitchen waste
CN115505757A (en) * 2022-10-21 2022-12-23 中国地质科学院郑州矿产综合利用研究所 Method for recycling lithium and manganese of anode materials of waste lithium manganate lithium batteries through eutectic solvent

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