[go: up one dir, main page]

CN116179858A - Method for homogeneous modified complementary leaching of cobalt-containing waste lithium battery - Google Patents

Method for homogeneous modified complementary leaching of cobalt-containing waste lithium battery Download PDF

Info

Publication number
CN116179858A
CN116179858A CN202310216255.0A CN202310216255A CN116179858A CN 116179858 A CN116179858 A CN 116179858A CN 202310216255 A CN202310216255 A CN 202310216255A CN 116179858 A CN116179858 A CN 116179858A
Authority
CN
China
Prior art keywords
cobalt
leaching
lithium battery
waste lithium
containing waste
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN202310216255.0A
Other languages
Chinese (zh)
Inventor
熊以俊
许用华
钟轩
刘东辉
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Ganzhou Yihao Umicore Ind Co ltd
Original Assignee
Ganzhou Yihao Umicore Ind Co ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Ganzhou Yihao Umicore Ind Co ltd filed Critical Ganzhou Yihao Umicore Ind Co ltd
Priority to CN202310216255.0A priority Critical patent/CN116179858A/en
Publication of CN116179858A publication Critical patent/CN116179858A/en
Pending legal-status Critical Current

Links

Classifications

    • 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
    • C22B7/007Wet processes by acid leaching
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B22CASTING; POWDER METALLURGY
    • B22FWORKING METALLIC POWDER; MANUFACTURE OF ARTICLES FROM METALLIC POWDER; MAKING METALLIC POWDER; APPARATUS OR DEVICES SPECIALLY ADAPTED FOR METALLIC POWDER
    • B22F9/00Making metallic powder or suspensions thereof
    • B22F9/02Making metallic powder or suspensions thereof using physical processes
    • B22F9/04Making metallic powder or suspensions thereof using physical processes starting from solid material, e.g. by crushing, grinding or milling
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B1/00Preliminary treatment of ores or scrap
    • C22B1/005Preliminary treatment of scrap
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B15/00Obtaining copper
    • C22B15/0002Preliminary treatment
    • C22B15/0004Preliminary treatment without modification of the copper constituent
    • C22B15/0006Preliminary treatment without modification of the copper constituent by dry processes
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B21/00Obtaining aluminium
    • C22B21/0007Preliminary treatment of ores or scrap or any other metal source
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B21/00Obtaining aluminium
    • C22B21/0038Obtaining aluminium by other processes
    • C22B21/0069Obtaining aluminium by other processes from scrap, skimmings or any secondary source aluminium, e.g. recovery of alloy constituents
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B23/00Obtaining nickel or cobalt
    • C22B23/02Obtaining nickel or cobalt by dry processes
    • C22B23/021Obtaining nickel or cobalt by dry processes by reduction in solid state, e.g. by segregation processes
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B23/00Obtaining nickel or cobalt
    • C22B23/04Obtaining nickel or cobalt by wet processes
    • C22B23/0407Leaching processes
    • C22B23/0415Leaching processes with acids or salt solutions except ammonium salts solutions
    • C22B23/043Sulfurated acids or salts thereof
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B23/00Obtaining nickel or cobalt
    • C22B23/04Obtaining nickel or cobalt by wet processes
    • C22B23/0453Treatment or purification of solutions, e.g. obtained by leaching
    • C22B23/0461Treatment or purification of solutions, e.g. obtained by leaching by chemical methods
    • 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
    • C22B47/00Obtaining manganese
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B5/00General methods of reducing to metals
    • C22B5/02Dry methods smelting of sulfides or formation of mattes
    • C22B5/10Dry methods smelting of sulfides or formation of mattes by solid carbonaceous reducing agents
    • 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
    • C22B7/001Dry processes
    • 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
    • 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

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Materials Engineering (AREA)
  • Manufacturing & Machinery (AREA)
  • Mechanical Engineering (AREA)
  • Metallurgy (AREA)
  • Organic Chemistry (AREA)
  • Geology (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Geochemistry & Mineralogy (AREA)
  • Electrochemistry (AREA)
  • Manufacture And Refinement Of Metals (AREA)
  • Battery Electrode And Active Subsutance (AREA)

Abstract

The invention discloses a method for carrying out homogeneous modification and complementary leaching on a cobalt-containing waste lithium battery, which comprises the steps of discharging, preparing positive black powder and alloy powder, carrying out complementary leaching, removing copper, iron and aluminum, preparing ternary hydroxide, evaporating ammonia, precipitating lithium and the like. The method comprises the steps of respectively preparing anode black powder and alloy powder from cobalt-containing waste lithium batteries; the oxidizing property of the positive black powder and the reducing property of the alloy powder are utilized, and the acid is directly added for complementary leaching, SO that no reducing agent or oxidant is required to be additionally added, and SO generated by adding sulfite when the positive black powder is subjected to independent acid leaching is avoided 2 The gas hazard also avoids the potential safety hazard of generating a large amount of hydrogen in direct acid leaching after the alloy powder is obtained by the traditional pyrogenic process. The process has high leaching speed, and the leaching rates of valuable elements cobalt, nickel, manganese, copper and lithium are all up to more than 99.5 percent. The process has the advantages of good production safety, economy, environmental protection and easy industrial application.

Description

Method for homogeneous modified complementary leaching of cobalt-containing waste lithium battery
Technical Field
The invention relates to a recycling method of waste lithium batteries in the metallurgical field, in particular to a method for carrying out homogeneous modification and complementary leaching on waste lithium batteries (lithium cobaltate batteries and ternary lithium batteries) containing cobalt.
Background
The waste lithium batteries are treated and recycled in a plurality of methods, which generally comprise a fire method, a wet method and a bioleaching method. The pyrogenic process is simpler but has high energy consumption and produces a large amount of waste gas. Wet processing primarily leaches metals through mineral or organic acids. Using mineral acids (HCl, H) 2 SO 4 、HNO 3 Etc.) as leaching agent, has high leaching rate and large treatment capacity, but can generate toxic and harmful gas (Cl) 2 、SO 2 、NO 2 ) And the like, the residual acid waste liquid is difficult to treat, and secondary pollution is caused. Organic acid (citric acid, oxalic acid, ascorbic acid, grape acid and the like) is used as a leaching agent, so that the ternary lithium ion power battery has good treatment effect, and the acidity of the acidic waste liquid is low, so that the subsequent treatment and recovery are easy; however, the cost of the organic acid raw material is higher than that of the inorganic acid, and the subsequent nickel-cobalt-manganese separation process is more complex, so that the recovery cost is further increased. The bioleaching method has low cost and environmental protection, but bacteria are difficult to culture, the leaching period is long, and the leaching rate is low, so that the industrial application of the bioleaching method is limited. Accordingly, the prior art is still in need of improvement and development. The optimal combination of various leaching methods can be an ideal treatment method, and a large number of scientific researchers are continuously researching and optimizing.
Disclosure of Invention
In view of the drawbacks and deficiencies of the prior art, the present invention is directed to a method for homogeneous modified complementary leaching of spent lithium batteries containing cobalt.
In order to achieve the above purpose, the technical scheme adopted by the invention is as follows:
a method of homogeneity-modified complementary leaching of waste lithium batteries containing cobalt, the method comprising the steps of:
s1, discharging: the cobalt-containing waste lithium battery is put into the battery containing NaCl and/or Na 2 SO 4 In the discharge cell of the sodium salt solution, discharging for 24-48 hours, draining, and feeding the drained water into the discharge cell for recycling;
s2, preparing positive electrode black powder and alloy powder: dividing the discharged cobalt-containing waste lithium battery into two parts according to the size, wherein the large-size cobalt-containing waste lithium battery is used for preparing positive black powder, and the small-size cobalt-containing waste lithium battery is used for preparing alloy powder;
s3, complementary leaching: mixing the obtained anode black powder and alloy powder according to an electron gain-loss balance principle, mixing the materials according to the weight ratio of 1:1-3:1, and leaching in dilute acid;
s4, copper, iron and aluminum removal: after leaching, ammonium bicarbonate or ammonia water is added to adjust the pH value to 2.5-3, ammonia sulfide is added to precipitate Cu, solid-liquid separation is carried out, and copper sulfide slag is recovered; adding ammonium bicarbonate or ammonia water into the filtrate to raise the pH to 5-6, precipitating Fe and Al, and carrying out solid-liquid separation to obtain impurity-removed filtrate and iron-aluminum slag;
s5, preparing a ternary hydroxide: the filtrate containing Mn, co, ni, li obtained in the step S4 is supplemented with one or two of Mn salt, co salt and Ni salt in proper amount according to the requirement; adding NaOH solution and ammonia water for coprecipitation in an inert atmosphere at the temperature of 45-55 ℃, and obtaining nickel cobalt manganese ternary hydroxide and coprecipitation solution after solid-liquid separation;
s6, ammonia distillation: heating and distilling ammonia from the coprecipitated liquid obtained in the step S5 by utilizing steam to obtain ammonia distilled liquid and ammonia gas;
s7, lithium precipitation: and (3) adding a carbonate solution into the ammonia distillation liquid obtained in the step (S6) to precipitate lithium, thereby obtaining lithium carbonate.
It should be noted that, the step S2 further includes:
s2.1, preparing positive electrode black powder: disassembling the drained large-size cobalt-containing waste lithium battery, removing the battery shell, performing low-temperature pyrolysis at 500-700 ℃, preserving heat for 1-2 h, and removing substances without recycling value; removing graphite powder and scrap iron by using the differences of powder density, magnetism and granularity after physical crushing through flotation, magnetic separation and screening, and separating to obtain copper scraps, aluminum scraps and positive black powder with higher purity;
s2.2, preparing alloy powder: putting the drained small-size cobalt-containing waste lithium battery into a high-temperature furnace for roasting, under the conditions of isolating air, protective atmosphere or negative pressure, keeping the roasting temperature at 1000-1200 ℃, preserving heat for 1-4 hours, modifying nickel, cobalt and manganese compounds by utilizing graphite contained in the cobalt-containing waste lithium battery, reducing the compounds into alloy, and crushing the alloy into alloy powder below 10 meshes by adopting a physical crushing mode;
the ammonia gas obtained in step S5 may be absorbed by water to obtain ammonia water, and the ammonia water obtained may be reused in step S4.
The waste lithium battery containing cobalt is a lithium cobalt oxide battery or a ternary lithium battery.
The large-size cobalt-containing waste lithium battery is a power lithium battery, and the small-size cobalt-containing waste lithium battery is a 3C lithium battery.
In the step S3, the dilute acid is dilute sulfuric acid.
The leaching in the step S3 has the technological parameters of pH 1.5-2.0, temperature 60-90 ℃ and stirring speed 50-200 r/min for 2-5 h;
the temperature is 70-80 ℃, the time is 3-4 hours, and the stirring speed is 60-120 r/min.
The impurity removal filtrate obtained in the step S4 has the content of Fe, al and Cu less than 1mg/L.
The invention has the beneficial effects that:
1. the alloy powder in the 0 valence state mainly reacts with the positive electrode black powder (mainly metal oxide) in the high valence state by adopting low acid leaching, only a small amount of alloy powder reacts with acid, the hydrogen generation amount is small, and the potential safety hazard that a large amount of hydrogen is generated when acid is added to leach the alloy powder after the alloy powder is obtained when waste lithium batteries are recovered by a pyrogenic process is avoided.
2. The alloy powder and the positive black powder are respectively used as the reducing agent and the oxidizing agent in the self-leaching process, so that the oxidizing agent and the reducing agent are not required to be added, auxiliary materials are saved, and the leaching cost is reduced.
3. Only sulfuric acid is added in the self-leaching process, SO that SO generated by adding a reducing agent in the leaching process of wet-process recovered waste lithium batteries is avoided 2 And the harm of the gas.
4. The leaching rate of nickel, cobalt, manganese, copper and lithium exceeds 99%, the purity of copper scraps and aluminum scraps obtained in the step (b) is higher, the copper scraps and aluminum scraps can be directly sold, and the recovery rate is more than 92%.
Detailed Description
The present invention will be further described below, and it should be noted that, while the present embodiment provides a detailed implementation manner and a specific operation process on the premise of the present technical solution, the protection scope of the present invention is not limited to the present embodiment.
Example 1
The invention relates to a method for leaching cobalt-containing waste lithium batteries in a homogeneous modified complementary manner, which comprises the following steps:
s1, discharging: the cobalt-containing waste lithium battery is put into the battery containing NaCl and/or Na 2 SO 4 In the discharge cell of the sodium salt solution, discharging for 24-48 hours, draining, and feeding the drained water into the discharge cell for recycling;
s2, preparing positive electrode black powder and alloy powder: dividing the discharged cobalt-containing waste lithium battery into two parts according to the size, wherein the large-size cobalt-containing waste lithium battery is used for preparing positive black powder, and the small-size cobalt-containing waste lithium battery is used for preparing alloy powder;
s3, complementary leaching: mixing the obtained anode black powder and alloy powder according to an electron gain-loss balance principle, mixing the materials according to the weight ratio of 1:1-3:1, and leaching in dilute acid;
s4, copper, iron and aluminum removal: after leaching, ammonium bicarbonate or ammonia water is added to adjust the pH value to 2.5-3, ammonia sulfide is added to precipitate Cu, solid-liquid separation is carried out, and copper sulfide slag is recovered; adding ammonium bicarbonate or ammonia water into the filtrate to raise the pH to 5-6, precipitating Fe and Al, and carrying out solid-liquid separation to obtain impurity-removed filtrate and iron-aluminum slag;
s5, preparing a ternary hydroxide: the filtrate containing Mn, co, ni, li obtained in the step S4 is supplemented with one or two of Mn salt, co salt and Ni salt in proper amount according to the requirement; adding NaOH solution and ammonia water for coprecipitation in an inert atmosphere at the temperature of 45-55 ℃, and obtaining nickel cobalt manganese ternary hydroxide and coprecipitation solution after solid-liquid separation;
s6, ammonia distillation: heating and distilling ammonia from the coprecipitated liquid obtained in the step S5 by utilizing steam to obtain ammonia distilled liquid and ammonia gas;
s7, lithium precipitation: and (3) adding a carbonate solution into the ammonia distillation liquid obtained in the step (S6) to precipitate lithium, thereby obtaining lithium carbonate.
Further, the step S2 of the present invention further includes:
s2.1, preparing positive electrode black powder: disassembling the drained large-size cobalt-containing waste lithium battery, removing the battery shell, performing low-temperature pyrolysis at 500-700 ℃, preserving heat for 1-2 h, and removing substances without recycling value; removing graphite powder and scrap iron by using the differences of powder density, magnetism and granularity after physical crushing through flotation, magnetic separation and screening, and separating to obtain copper scraps, aluminum scraps and positive black powder with higher purity;
s2.2, preparing alloy powder: putting the drained small-size cobalt-containing waste lithium battery into a high-temperature furnace for roasting, under the conditions of isolating air, protective atmosphere or negative pressure, keeping the roasting temperature at 1000-1200 ℃, preserving heat for 1-4 hours, modifying nickel, cobalt and manganese compounds by utilizing graphite contained in the cobalt-containing waste lithium battery, reducing the compounds into alloy, and crushing the alloy into alloy powder below 10 meshes by adopting a physical crushing mode;
it is noted that in the implementation step of the present invention, the alloy powder preparation process in step S2.2 can decompose and volatilize substances without recycling value, such as binder, separator, electrolyte, etc., in the battery cell, and also generate a reaction of reducing metal compounds by carbon, 2meo+c=me+co 2 Either ∈, or meo+c=me+co +..
On the other hand, in step S3, the reducibility of the alloy and the positive electrode black are mainly utilizedThe oxidability of the powder, which reacts directly under acidic conditions to form soluble low valence metal ions, e.g. Co 2+ 、Ni 2+ 、Mn 2+ 、Cu 2+ Etc. Because part of the battery shell is made of iron material, the complementary leaching system contains a small amount of iron element, and the iron is prepared by Fe under the acidic condition 2+ 、Fe 3+ The state exists in the solution, and the solid-solid oxidation-reduction reaction between the positive black powder and the alloy powder is accelerated by the transfer medium serving as electrons, so that the leaching rate is improved
Further, the ammonia gas obtained in the step S5 can be absorbed by water to obtain ammonia water, and the obtained ammonia water is reused in the step S4.
Further, the waste lithium battery containing cobalt is a lithium cobalt oxide battery or a ternary lithium battery.
Furthermore, the large-size cobalt-containing waste lithium battery is a power lithium battery, and the small-size cobalt-containing waste lithium battery is a 3C lithium battery.
Further, in the step S3 of the present invention, the dilute acid is dilute sulfuric acid.
Further, the leaching in the step S3 has the technological parameters of pH 1.5-2.0, temperature 60-90 ℃ and time 1-4 h, and stirring speed 50-200 r/min;
further, the temperature is 70-80 ℃, the time is 3-4 hours, and the stirring speed is 60-120 r/min.
Furthermore, the impurity removal filtrate obtained in the step S4 has the content of Fe, al and Cu less than 1mg/L.
Examples 2 to 5:
the process flow is the same as in example 1, the process parameters are adjusted, and the process parameters and implementation effects of examples 1 to 5 are shown in the following table.
Figure SMS_1
As can be seen from the process parameters and results of examples 1 to 5, the technology of the invention obtains the waste lithium batteries containing cobalt respectively with oxidability and oxidation by different methodsThe two materials with reducibility are mixed and then added with acid for complementary leaching, SO that the addition of a reducing agent and an oxidant and the generation of SO are avoided 2 、NO x The harm of gas saves the leaching cost and greatly reduces the generation of H in the pyrogenic recovery process 2 Has the advantages of high recovery rate of valuable metals.
Various other corresponding changes and modifications will occur to those skilled in the art from the foregoing description and the accompanying drawings, and all such changes and modifications are intended to be included within the scope of the present invention as defined in the appended claims.

Claims (9)

1. A method for the homogeneity-modified complementary leaching of waste lithium batteries containing cobalt, the method comprising the steps of:
s1, discharging: the cobalt-containing waste lithium battery is put into the battery containing NaCl and/or Na 2 SO 4 In the discharge cell of the sodium salt solution, discharging for 24-48 hours, draining, and feeding the drained water into the discharge cell for recycling;
s2, preparing positive electrode black powder and alloy powder: dividing the discharged cobalt-containing waste lithium battery into two parts according to the size, wherein the large-size cobalt-containing waste lithium battery is used for preparing positive black powder, and the small-size cobalt-containing waste lithium battery is used for preparing alloy powder;
s3, complementary leaching: mixing the obtained anode black powder and alloy powder according to an electron gain-loss balance principle, mixing the materials according to the weight ratio of 1:1-3:1, and leaching in dilute acid;
s4, copper, iron and aluminum removal: after leaching, ammonium bicarbonate or ammonia water is added to adjust the pH value to 2.5-3, ammonia sulfide is added to precipitate Cu, solid-liquid separation is carried out, and copper sulfide slag is recovered; adding ammonium bicarbonate or ammonia water into the filtrate to raise the pH to 5-6, precipitating Fe and Al, and carrying out solid-liquid separation to obtain impurity-removed filtrate and iron-aluminum slag;
s5, preparing a ternary hydroxide: the filtrate containing Mn, co, ni, li obtained in the step S4 is supplemented with one or two of Mn salt, co salt and Ni salt in proper amount according to the requirement; adding NaOH solution and ammonia water for coprecipitation in an inert atmosphere at the temperature of 45-55 ℃, and obtaining nickel cobalt manganese ternary hydroxide and coprecipitation solution after solid-liquid separation;
s6, ammonia distillation: heating and distilling ammonia from the coprecipitated liquid obtained in the step S5 by utilizing steam to obtain ammonia distilled liquid and ammonia gas;
s7, lithium precipitation: and (3) adding a carbonate solution into the ammonia distillation liquid obtained in the step (S6) to precipitate lithium, thereby obtaining lithium carbonate.
2. The method of homogeneous modified complementary leaching of lithium waste batteries containing cobalt according to claim 1, wherein said step S2 further comprises:
s2.1, preparing positive electrode black powder: disassembling the drained large-size cobalt-containing waste lithium battery, removing the battery shell, performing low-temperature pyrolysis at 500-700 ℃, preserving heat for 1-2 h, and removing substances without recycling value; removing graphite powder and scrap iron by using the differences of powder density, magnetism and granularity after physical crushing through flotation, magnetic separation and screening, and separating to obtain copper scraps, aluminum scraps and positive black powder with higher purity;
s2.2, preparing alloy powder: putting the drained small-size cobalt-containing waste lithium battery into a high-temperature furnace for roasting, under the conditions of air isolation, protective atmosphere or negative pressure, the roasting temperature is 1000-1200 ℃, the heat preservation is carried out for 1-4 hours, the nickel, cobalt and manganese compounds are modified by utilizing graphite contained in the cobalt-containing waste lithium battery, the compounds are reduced into alloy, and the alloy is crushed into alloy powder below 10 meshes by adopting a physical crushing mode.
3. The method for the homogeneous modified complementary leaching of waste lithium batteries containing cobalt according to claim 1, wherein the ammonia gas obtained in the step S5 can be absorbed by water to obtain ammonia water, and the ammonia water obtained is recycled in the step S4.
4. The method for the homogeneous modified complementary leaching of a waste lithium battery containing cobalt according to claim 1, wherein the waste lithium battery containing cobalt is a lithium cobaltate battery or a ternary lithium battery.
5. The method of claim 1, wherein the large size waste lithium battery is a power lithium battery and the small size waste lithium battery is a 3C lithium battery.
6. The method for homogeneous modified complementary leaching of lithium waste batteries containing cobalt according to claim 1, wherein the dilute acid in step S3 is dilute sulfuric acid.
7. The method for the homogeneous modified complementary leaching of the cobalt-containing waste lithium battery according to claim 1, wherein the leaching in the step S3 is characterized in that the technological parameters are that the pH is 1.5-2.0, the temperature is 60-90 ℃, the time is 2-5 h, and the stirring speed is 50 r/min-200 r/min;
8. the method for the homogeneous modified complementary leaching of the cobalt-containing waste lithium battery according to claim 7, wherein the temperature is 70-80 ℃, the time is 3-4 hours, and the stirring speed is 60-120 r/min.
9. The method for the homogeneous modified complementary leaching of the cobalt-containing waste lithium battery as claimed in claim 1, wherein the impurity removal filtrate obtained in the step S4 has the contents of Fe, al and Cu of less than 1mg/L.
CN202310216255.0A 2023-03-08 2023-03-08 Method for homogeneous modified complementary leaching of cobalt-containing waste lithium battery Pending CN116179858A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202310216255.0A CN116179858A (en) 2023-03-08 2023-03-08 Method for homogeneous modified complementary leaching of cobalt-containing waste lithium battery

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202310216255.0A CN116179858A (en) 2023-03-08 2023-03-08 Method for homogeneous modified complementary leaching of cobalt-containing waste lithium battery

Publications (1)

Publication Number Publication Date
CN116179858A true CN116179858A (en) 2023-05-30

Family

ID=86438353

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202310216255.0A Pending CN116179858A (en) 2023-03-08 2023-03-08 Method for homogeneous modified complementary leaching of cobalt-containing waste lithium battery

Country Status (1)

Country Link
CN (1) CN116179858A (en)

Similar Documents

Publication Publication Date Title
CN108878866B (en) Method for preparing ternary material precursor and recovering lithium by using ternary cathode material of waste lithium ion battery
CN113957252B (en) A method for selectively recovering valuable metals in waste lithium batteries
CN107017443B (en) A method for comprehensive recovery of valuable metals from waste lithium-ion batteries
CN108075203B (en) A method for recovering valuable metal components in waste lithium-ion battery materials
CN111118294A (en) Method for recycling valuable metals from waste lithium ion battery materials step by step
CN112374511A (en) Method for preparing lithium carbonate and ternary precursor by recycling waste ternary lithium battery
CN112207119B (en) Method for treating battery black powder
CN112680598A (en) Method for low-cost clean treatment of waste lithium ion battery anode material
CN106450542A (en) Recycling method of waste lithium manganate lithium-ion battery
EP3269832B1 (en) Method of recycling and processing waste battery
CN109022793B (en) Method for selectively leaching lithium from waste powder of cathode material containing at least one of cobalt, nickel and manganese
CN112111650B (en) Method for recovering valuable metals of waste lithium ion batteries by selective reduction
CN113415813A (en) Method for recovering lithium nickel cobalt manganese from waste ternary battery material
CN107046154B (en) Method for enhanced reduction leaching of waste ternary lithium battery
CN109179359A (en) A method of extracting lithium and ferric phosphate from LiFePO4 waste material
CN115321502A (en) Comprehensive recovery process for waste lithium iron phosphate battery and nickel-cobalt-manganese ternary battery
CN113801990A (en) Recycling method of waste lithium ion battery
CN112779421A (en) Method for recycling anode material of waste lithium ion battery
CN115141933B (en) Method for purifying ternary lithium battery recovery leaching liquid
CN113122725A (en) Method for improving metal recovery rate and purity of waste lithium battery
CN110498434B (en) Recovery method and application of lithium ion battery positive electrode active material
CN102358919A (en) Method for extracting valuable metal from submarine metallic ore
CN115304059A (en) Recycling treatment method for retired battery carbon slag
CN110747340A (en) Method for extracting lithium from lithium-containing secondary battery waste
CN115595456B (en) Method for extracting lithium from waste lithium cobalt oxide battery anode material through low-temperature vulcanization roasting

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination