CN115287458A - Method for recovering valuable metals in lithium-containing power battery waste - Google Patents

Method for recovering valuable metals in lithium-containing power battery waste Download PDF

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Publication number
CN115287458A
CN115287458A CN202210911744.3A CN202210911744A CN115287458A CN 115287458 A CN115287458 A CN 115287458A CN 202210911744 A CN202210911744 A CN 202210911744A CN 115287458 A CN115287458 A CN 115287458A
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lithium
power battery
containing power
battery waste
leaching
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刘炼
彭亚光
胡意
许开华
李琴香
肖汀汀
李杨
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Jingmen GEM New Material Co Ltd
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Jingmen GEM New Material Co Ltd
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    • 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
    • C22B1/00Preliminary treatment of ores or scrap
    • C22B1/02Roasting 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
    • C22B23/02Obtaining 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
    • C22B23/0423Halogenated 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
    • C22B23/0407Leaching 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
    • C22B23/0407Leaching processes
    • C22B23/0415Leaching processes with acids or salt solutions except ammonium salts solutions
    • C22B23/0438Nitric 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
    • 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
    • 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
    • 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
    • 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
    • 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

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  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Manufacturing & Machinery (AREA)
  • Materials Engineering (AREA)
  • Mechanical Engineering (AREA)
  • Metallurgy (AREA)
  • Organic Chemistry (AREA)
  • Environmental & Geological Engineering (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Geology (AREA)
  • Geochemistry & Mineralogy (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Electrochemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

The invention discloses a method for recovering valuable metals in lithium-containing power battery waste, which comprises the following steps: adding a reagent and carbon powder into the lithium-containing power battery waste material, and then curing and uniformly mixing to obtain cured lithium-containing power battery waste material; the reagent is one of concentrated sulfuric acid, sodium bisulfate, sodium sulfate, ammonium sulfate and ammonium bisulfate; sequentially roasting, crushing, water leaching, filtering and washing the aged lithium-containing power battery waste to obtain lithium extraction slag; drying the lithium extraction slag to obtain dried lithium extraction slag; putting the dried lithium extraction slag into a reducing furnace, introducing reducing gas into the reducing furnace or adding a reducing agent into the reducing furnace, and reducing the dried lithium extraction slag to obtain reduced lithium extraction slag; adding acid and oxidant into the reduced lithium extraction slag for leaching to obtain leachate and leaching slag; and adding a reducing agent into the leached residues for washing. The method is efficient, safe and environment-friendly.

Description

Method for recovering valuable metals in lithium-containing power battery waste
Technical Field
The invention belongs to the field of metallurgy, and particularly relates to a method for recovering valuable metals in lithium-containing power battery waste.
Background
In the prior art, although the recovery rate of cobalt nickel manganese lithium is high in the one-time whole leaching process of cobalt nickel manganese lithium, nickel is not easy to separate from lithium, so that the content of lithium in the produced nickel salt is high, and the process flow for producing battery-grade lithium carbonate is long; the process for selectively extracting lithium by hydrogen reduction and then extracting cobalt, nickel and manganese has weak adaptability to raw materials, and only can treat battery waste with low aluminum content and fully pyrolyzed organic matters. Therefore, a lithium-containing power battery waste recovery method with strong raw material applicability and high cobalt-nickel-manganese-lithium recovery rate is needed.
Disclosure of Invention
Aiming at the problems in the prior art, the invention provides a method for efficiently, safely and environmentally recovering valuable metals in lithium-containing power battery waste.
The invention adopts the following technical scheme:
a method of recovering valuable metals from lithium-containing power cell waste, the method comprising the steps of:
(1) Adding a reagent and carbon powder into the lithium-containing power battery waste, and curing and uniformly mixing to obtain cured lithium-containing power battery waste; the reagent is one of concentrated sulfuric acid, sodium bisulfate, sodium sulfate, ammonium sulfate and ammonium bisulfate; the ratio of the molar weight of lithium in the lithium-containing power battery waste to the molar weight of the reagent is 1.1-1.8, and the mass ratio of the lithium-containing power battery waste to the carbon powder is 5-20;
(2) Sequentially roasting, crushing, water leaching, filtering and washing the aged lithium-containing power battery waste to obtain lithium extraction slag;
(3) Drying the lithium extraction slag to obtain dried lithium extraction slag;
(4) Putting the dried lithium extraction slag into a reducing furnace, introducing reducing gas into the reducing furnace or adding a reducing agent into the reducing furnace, and reducing the dried lithium extraction slag to obtain reduced lithium extraction slag; when reducing gas is introduced into the reducing furnace, controlling the pressure in the reducing furnace to be 0.15MPa-0.2MPa; when a reducing agent is added into the reducing furnace, the mass ratio of the reducing agent to the dried lithium extraction slag is 0.2-1;
(5) Adding acid and oxidant into the reduced lithium extraction slag for leaching to obtain leachate and leaching slag;
(6) And adding a reducing agent into the leached residues for washing.
The method for recovering valuable metals from the lithium-containing power battery waste is characterized in that the mesh number of the carbon powder in the step (1) is 100-325 meshes.
The method for recovering valuable metals from lithium-containing power battery waste is characterized in that in the step (2), the aged lithium-containing power battery waste is placed into a rotary kiln for roasting, the oxygen content in the rotary kiln is controlled to be 4% -6%, and roasting process conditions are as follows: the roasting temperature is 550-600 ℃, and the roasting time is 1-3 h.
According to the method for recovering valuable metals in lithium-containing power battery waste, the process conditions of water immersion in the step (2) are as follows: the water temperature is 80-85 ℃, and the leaching time is 1-2 h; the washing mode is countercurrent washing for 2-3 times.
The method for recovering valuable metals from lithium-containing power battery waste is characterized in that the process conditions for reducing the dried lithium extraction slag in the step (4) are as follows: the reduction temperature is 450-600 ℃, and the reduction time is 2-3 h.
The method for recovering valuable metals from the lithium-containing power battery waste is characterized in that the reducing gas introduced into the reducing furnace in the step (4) is one of hydrogen, ammonia, methane and sulfur dioxide; the reducing agent added into the reducing furnace is one of carbon powder, sodium sulfide, sulfur, fructose, glucose, oxalic acid and edible flour.
The method for recovering valuable metals from the lithium-containing power battery waste is characterized in that the acid in the step (5) is sulfuric acid or hydrochloric acid or nitric acid, and the oxidant is one of potassium peroxide, sodium peroxide, potassium dichromate, sodium dichromate, potassium chlorate, sodium chlorate, hydrogen peroxide, potassium permanganate, sodium permanganate, perchloric acid, potassium hypochlorite, sodium hypochlorite, potassium persulfate and sodium persulfate; the technological conditions for leaching the reduced lithium extraction slag by adding acid and oxidant are as follows: the leaching pH is 1.5-2.0, and the leaching temperature is 70-90 ℃.
According to the method for recovering valuable metals in the lithium-containing power battery waste, the method is characterized in that the reducing agent added into the leaching slag in the step (6) is sodium sulfite or sodium metabisulfite or hydrogen peroxide; the process conditions for adding the reducing agent into the leaching residue for washing are as follows: the pH value of washing is 1.0-1.5, and the washing temperature is 50-80 ℃.
The method for recovering valuable metals from the lithium-containing power battery waste is characterized in that the drying temperature for drying the lithium extraction slag in the step (3) is 80-105 ℃.
The invention has the beneficial technical effects that: the method can lead the recovery rate of lithium in the lithium-containing power battery waste to reach about 95 percent, lead the recovery rate of nickel, cobalt and manganese to reach more than 99 percent, lead the finally obtained leaching slag to meet the standard treatment requirement and lead the leaching liquid to meet the process index requirement of the next working procedure. When the method is used for treating the lithium-containing power battery waste, the valuable metals in the lithium-containing power battery waste can be efficiently recovered, and the treatment process is safe, environment-friendly and harmless.
Detailed Description
The invention relates to a method for recovering valuable metals in lithium-containing power battery waste, which comprises the following steps:
(1) Adding a reagent and carbon powder into the lithium-containing power battery waste material, and then curing and uniformly mixing to obtain cured lithium-containing power battery waste material; the reagent is one of concentrated sulfuric acid, sodium bisulfate, sodium sulfate, ammonium sulfate and ammonium bisulfate; the ratio of the molar weight of lithium in the lithium-containing power battery waste to the molar weight of the reagent is 1.1-1.8, and the mass ratio of the lithium-containing power battery waste to the carbon powder is 5-20; the mesh number of the carbon powder is 100-325 meshes.
(2) Sequentially roasting, crushing, water leaching, filtering and washing the aged lithium-containing power battery waste to obtain lithium extraction slag; placing the aged lithium-containing power battery waste into a rotary kiln for roasting, wherein the oxygen content in the rotary kiln is controlled to be 4-6%, and the roasting process conditions are as follows: the roasting temperature is 550-600 ℃, and the roasting time is 1-3 h. The crushing mode is ball milling. The process conditions of water leaching are as follows: the water temperature is 80-85 ℃, and the leaching time is 1-2 h; the washing mode is countercurrent washing for 2-3 times. Adding water during water leaching, controlling the temperature at 80-85 deg.C, leaching for 1-2h, filtering, and washing the leaching residue with counter current for 2-3 times.
(3) Putting the lithium extraction slag into an oven for drying to obtain dried lithium extraction slag; the drying temperature for drying the lithium extraction slag is 80-105 ℃.
(4) Putting the dried lithium extraction slag into a reduction furnace with good tightness, introducing reducing gas into the reduction furnace or adding a reducing agent into the reduction furnace, and reducing the dried lithium extraction slag to obtain reduced lithium extraction slag; when reducing gas is introduced into the reducing furnace, controlling the pressure in the reducing furnace to be 0.15-0.2 MPa, and controlling the micro-positive pressure in the reducing furnace; when a reducing agent is added into the reducing furnace, the mass ratio of the reducing agent to the dried lithium extraction slag is 0.2-1; the technological conditions for reducing the dried lithium extraction slag are as follows: the reduction temperature is 450-600 ℃, and the reduction time is 2-3 h. The reducing gas introduced into the reduction furnace is one of hydrogen, ammonia, methane and sulfur dioxide; the reducing agent added into the reducing furnace is one of carbon powder, sodium sulfide, sulfur, fructose, glucose, oxalic acid and edible flour.
(5) Adding acid and oxidant into the reduced lithium extraction slag for leaching to obtain leachate and leaching slag; the acid is sulfuric acid or hydrochloric acid or nitric acid, and the oxidant is one of potassium peroxide, sodium peroxide, potassium dichromate, sodium dichromate, potassium chlorate, sodium chlorate, hydrogen peroxide, potassium permanganate, sodium permanganate, perchloric acid, potassium hypochlorite, sodium hypochlorite, potassium persulfate and sodium persulfate; the technological conditions for leaching the reduced lithium extraction slag by adding acid and oxidant are as follows: the leaching pH is 1.5-2.0, and the leaching temperature is 70-90 ℃. Valuable metals of nickel, cobalt and manganese contained in the reduced lithium extraction slag are dissolved into the leaching solution by acid.
(6) And adding a reducing agent into the leaching residue for washing. Adding a reducing agent into the leaching residue, wherein the reducing agent is sodium sulfite or sodium pyrosulfite or hydrogen peroxide; the process conditions for adding the reducing agent into the leaching residue for washing are as follows: the pH value of washing is 1.0-1.5, and the washing temperature is 50-80 ℃.
In order to make the objects, technical solutions and advantages of the present invention more apparent, the technical solutions of the present invention will be described in detail with reference to the embodiments.
Example 1
And (3) adding 30mL of concentrated sulfuric acid into 100g of cracked lithium-containing power battery waste for curing for 30 minutes, continuously adding 20g of 200-mesh carbon powder, and uniformly stirring to obtain the cured lithium-containing power battery waste. And placing the obtained aged lithium-containing power battery waste into a rotary kiln to be roasted for 2 hours at the temperature of 600 ℃. And then grinding the sample, and leaching with water to recover lithium to obtain water leaching residue. And drying the water leaching residues, flattening the water leaching residues, putting the water leaching residues into an atmosphere furnace, vacuumizing the atmosphere furnace, introducing hydrogen, and roasting the water leaching residues at 500 ℃ for 2 hours in the atmosphere of the hydrogen to obtain a reduced material. Leaching the reduced materials step by step. In example 1, the recovery rate of lithium in the lithium-containing power battery waste material is 95.46%, and the recovery rate of nickel, cobalt and manganese is more than 98%.
Example 2
And (3) adding 35mL of concentrated sulfuric acid into 100g of cracked lithium-containing power battery waste for curing for 30 minutes, continuously adding 5g of 200-mesh carbon powder, and uniformly stirring to obtain the cured lithium-containing power battery waste. The obtained aged lithium-containing power battery waste is put into a rotary kiln to be roasted for 2 hours at 550 ℃. And grinding the sample, and leaching with water to recover lithium to obtain water leaching residue. Drying the water leaching slag, flattening the water leaching slag, putting the water leaching slag into an atmosphere furnace, vacuumizing the atmosphere furnace, introducing sulfur dioxide, and roasting the water leaching slag at 450 ℃ for 2 hours in an atmosphere with the sulfur dioxide to obtain a reduced material. Leaching the reduced materials step by step. In example 2, the recovery rate of lithium in lithium-containing power battery waste is 94.57%, and the recovery rate of nickel, cobalt and manganese reaches more than 98%.
Example 3
And (3) taking 100g of cracked lithium-containing power battery waste, adding 28mL of concentrated sulfuric acid, curing for 30 minutes, continuously adding 5g of 200-mesh carbon powder, and uniformly stirring to obtain the cured lithium-containing power battery waste. And (3) placing the aged lithium-containing power battery waste into a muffle furnace to be roasted for 2 hours at the temperature of 600 ℃. And grinding the sample, and leaching with water to recover lithium to obtain water leaching residue. And drying the water leaching residues, adding 20g of glucose, grinding uniformly to obtain a mixture, flattening the mixture, putting the mixture into an atmosphere furnace, vacuumizing the atmosphere furnace, introducing hydrogen, and roasting at 550 ℃ for 2 hours in the atmosphere with the hydrogen to obtain a reduced material. Leaching the reduced materials step by step. In example 3, the recovery rate of lithium in lithium-containing power battery waste is 96.01%, and the recovery rate of nickel, cobalt and manganese reaches more than 98%.
Example 4
And (3) adding 25mL of concentrated sulfuric acid into 100g of cracked lithium-containing power battery waste for curing for 30 minutes, continuously adding 20g of 200-mesh carbon powder, and uniformly stirring to obtain the cured lithium-containing power battery waste. And (3) putting the obtained aged lithium-containing power battery waste into a muffle furnace, and roasting for 2 hours at 600 ℃. And grinding the sample, and leaching with water to recover lithium to obtain water leaching residue. Drying the water-soaked slag, adding 20g of edible flour, grinding uniformly to obtain a mixture, flattening the mixture, putting the mixture into an atmosphere furnace, vacuumizing the atmosphere furnace firstly, then introducing carbon monoxide, and roasting for 2 hours at 600 ℃ in the atmosphere with the carbon monoxide to obtain a reduced material. Leaching the reduced materials step by step. In example 4, the recovery rate of lithium in the lithium-containing power battery waste material is 96.01%, and the recovery rate of nickel, cobalt and manganese is more than 98%.
Example 5
Taking 100g of the lithium-containing waste ternary material, adding 25mL of concentrated sulfuric acid, curing for 30 minutes, continuously adding 20g of 200-mesh carbon powder, and uniformly stirring to obtain a cured material. The cured material was calcined in a muffle furnace at 600 ℃ for 2 hours. And crushing and grinding the materials, and leaching in water to recover lithium to obtain water leaching residue. And (3) drying the water leaching slag, adding 30g of sulfur, flattening the material, putting the material into an atmosphere furnace, vacuumizing the atmosphere furnace, introducing nitrogen, and roasting at 1200 ℃ for 2 hours in the atmosphere with nitrogen to obtain the reduced material. Leaching the reduced materials step by step. In example 5, the recovery rate of lithium in the lithium-containing waste ternary material is 96.01 percent, and the recovery rate of nickel, cobalt and manganese reaches more than 98 percent.

Claims (9)

1. A method of recovering valuable metals from lithium-containing power cell waste, the method comprising the steps of:
(1) Adding a reagent and carbon powder into the lithium-containing power battery waste, and curing and uniformly mixing to obtain cured lithium-containing power battery waste; the reagent is one of concentrated sulfuric acid, sodium bisulfate, sodium sulfate, ammonium sulfate and ammonium bisulfate; the ratio of the molar weight of lithium in the lithium-containing power battery waste to the molar weight of the reagent is 1: 1.1-1.8, and the mass ratio of the lithium-containing power battery waste to the carbon powder is 5-20;
(2) Sequentially roasting, crushing, water leaching, filtering and washing the aged lithium-containing power battery waste to obtain lithium extraction slag;
(3) Drying the lithium extraction slag to obtain dried lithium extraction slag;
(4) Putting the dried lithium extraction slag into a reduction furnace, introducing reducing gas into the reduction furnace or adding a reducing agent into the reduction furnace, and reducing the dried lithium extraction slag to obtain reduced lithium extraction slag; when reducing gas is introduced into the reducing furnace, controlling the pressure in the reducing furnace to be 0.15MPa-0.2MPa; when a reducing agent is added into the reducing furnace, the mass ratio of the reducing agent to the dried lithium extraction slag is 0.2-1;
(5) Adding acid and oxidant into the reduced lithium extraction slag for leaching to obtain leachate and leaching slag;
(6) And adding a reducing agent into the leached residues for washing.
2. The method for recovering valuable metals from lithium-containing power battery wastes according to claim 1, wherein the mesh number of the carbon powder in the step (1) is 100-325 meshes.
3. The method for recovering valuable metals from lithium-containing power battery waste as claimed in claim 1, wherein in the step (2), the aged lithium-containing power battery waste is placed into a rotary kiln for roasting, the oxygen content in the rotary kiln is controlled to be 4% -6%, and the roasting process conditions are as follows: the roasting temperature is 550-600 ℃, and the roasting time is 1-3 h.
4. The method for recovering valuable metals from lithium-containing power battery waste materials according to claim 1, wherein the water leaching in the step (2) is carried out under the following process conditions: the water temperature is 80-85 ℃, and the leaching time is 1-2 h; the washing mode is countercurrent washing for 2-3 times.
5. The method for recovering valuable metals from lithium-containing power battery waste material according to claim 1, wherein the process conditions for reducing the dried lithium extraction slag in the step (4) are as follows: the reduction temperature is 450-600 ℃, and the reduction time is 2-3 h.
6. The method for recovering valuable metals from lithium-containing power battery waste materials as claimed in claim 5, wherein the reducing gas introduced into the reducing furnace in the step (4) is one of hydrogen, ammonia, methane and sulfur dioxide; the reducing agent added into the reducing furnace is one of carbon powder, sodium sulfide, sulfur, fructose, glucose, oxalic acid and edible flour.
7. The method for recycling valuable metals from lithium-containing power battery waste material according to claim 1, wherein the acid in step (5) is sulfuric acid or hydrochloric acid or nitric acid, and the oxidizing agent is one of potassium peroxide, sodium peroxide, potassium dichromate, sodium dichromate, potassium chlorate, sodium chlorate, hydrogen peroxide, potassium permanganate, sodium permanganate, perchloric acid, potassium hypochlorite, sodium hypochlorite, potassium persulfate and sodium persulfate; the technological conditions for leaching the reduced lithium extraction slag by adding acid and oxidant are as follows: the leaching pH is 1.5-2.0, and the leaching temperature is 70-90 ℃.
8. The method for recovering valuable metals from lithium-containing power battery wastes according to claim 1, characterized in that the reducing agent added to the leaching residue in the step (6) is sodium sulfite or sodium metabisulfite or hydrogen peroxide; the process conditions for adding the reducing agent into the leaching residue for washing are as follows: the pH value of washing is 1.0-1.5, and the washing temperature is 50-80 ℃.
9. The method for recycling valuable metals in lithium-containing power battery waste material according to claim 1, wherein the drying temperature for drying the lithium extraction slag in the step (3) is 80-105 ℃.
CN202210911744.3A 2022-07-28 2022-07-28 Method for recovering valuable metals in lithium-containing power battery waste Pending CN115287458A (en)

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