CN115584393A - Method for selectively recovering lithium from waste lithium batteries and simultaneously preparing cobalt ferrite catalyst - Google Patents

Method for selectively recovering lithium from waste lithium batteries and simultaneously preparing cobalt ferrite catalyst Download PDF

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CN115584393A
CN115584393A CN202211094584.4A CN202211094584A CN115584393A CN 115584393 A CN115584393 A CN 115584393A CN 202211094584 A CN202211094584 A CN 202211094584A CN 115584393 A CN115584393 A CN 115584393A
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lithium
waste
cobalt ferrite
leaching
copperas
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CN115584393B (en
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刘维燥
何民宇
金熙
滕柳梅
刘清才
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Chongqing University
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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
    • C22B7/009General processes for recovering metals or metallic compounds from spent catalysts
    • 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
    • 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
    • C22B7/00Working up raw materials other than ores, e.g. scrap, to produce non-ferrous metals and compounds thereof; Methods of a general interest or applied to the winning of more than two metals
    • C22B7/006Wet processes
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/84Recycling of batteries or fuel cells

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Abstract

The invention discloses a method for selectively recovering lithium from a waste lithium battery and preparing a cobalt ferrite catalyst, which comprises the following steps: (1) Discharging, disassembling and classifying the waste lithium cobaltate battery to obtain a positive electrode material, and then performing high-temperature treatment to remove the adhesive; (2) Drying and screening lithium cobaltate positive electrode powder, uniformly mixing the lithium cobaltate positive electrode powder with copperas according to a certain mass ratio, and roasting for a certain time at a certain temperature; (3) Leaching the roasted product obtained in the first step by using deionized water to obtain a lithium sulfate leaching solution and a solution rich in CoFe 2 O 4 Leaching residue of (2); (3) Adding ammonia water into the leachate obtained in the second step to adjust the pH value, and filtering iron impurities; (4) Adding an ammonium carbonate solution into the filtrate obtained in the third step for carbonization, and filtering and drying the precipitate to obtain lithium carbonate; (5) Loading activity to the leaching residue obtained in the third stepAnd modifying the substance to obtain the SCR catalyst. The mixed roasting leaching process of the waste lithium cobaltate batteries and the copperas is adopted, the operation is simple, the production cost is low, the separation is easy, the waste lithium cobaltate batteries and the copperas are recycled, and the method has the characteristics of remarkable economic benefit and environmental friendliness.

Description

Method for selectively recovering lithium from waste lithium batteries and simultaneously preparing cobalt ferrite catalyst
Technical Field
The invention belongs to the field of solid waste resource utilization, and mainly relates to a method for selectively recovering lithium and simultaneously preparing a cobalt ferrite catalyst by using waste lithium batteries.
Background
Since the industrial revolution, the burning of fossil mass fuels has promoted the development of global industrialization, but has posed serious energy and environmental problems. The new energy technology can be applied to the environmental problems and the energy shortage of the world, and has attracted extensive attention. As one of the most important new energy carriers, lithium ion batteries have been widely used in mobile electronic devices and electric vehicles due to their high energy density, good cycle performance, and low memory effect. However, the long-term charge and discharge processes of lithium ion batteries result in short cycle life, producing a large amount of spent lithium ion batteries each year. It is estimated that by 2030, the number of global spent lithium ion batteries is expected to reach 193 ten thousand tons and the global lithium ion battery recycling market is expected to reach 2000 yen. The waste lithium cobalt oxide battery is used as the earliest used anode material and accounts for more than 20 percent of the waste lithium batteries in the world. However, waste lithium ion batteries are classified as hazardous waste because toxic materials such as cobalt, nickel and organic solvents will result in heavy metal contamination, spontaneous combustion and explosion hazards. Meanwhile, the waste lithium ion battery is an important secondary resource, and contains more valuable elements than natural resources such as minerals and brine. Therefore, the method for recovering valuable metals from the waste lithium ion batteries can effectively solve the problems of environmental pollution and resource shortage.
Researchers have conducted extensive research aiming at resource utilization of valuable elements in waste lithium cobaltate batteries. CN106868317A is a method for precipitating Fe by mixing a cobalt acid lithium battery anode material with ferrous sulfate, placing the mixture in a reactor, adding inorganic acid solution into slurry after adding water and mixing the slurry, reacting, adding inorganic base to neutralize residual acid, adjusting the pH value of the slurry and precipitating Fe 3+ And completing liquid-solid separation, wherein solid slag is a mixture of carbon powder and ferric hydroxide, and the leaching solution is a high-concentration cobalt and lithium solution. CN113481368A is a method for reacting waste lithium cobaltate battery powder with a high-concentration first sodium hydroxide solution, performing solid-liquid separation to obtain a first filter residue and a first filtrate, and then performing first filtration on the first filter residue and the first filtrateAnd reacting the filter residue with a low-concentration second sodium hydroxide solution, and then carrying out solid-liquid separation to obtain a second filter residue and a second filtrate, wherein the first filtrate and the second filtrate are jointly used as a first leaching solution containing aluminum, the second filter residue is used as a first leaching residue, the first leaching residue is reacted with phosphoric acid, and the solid-liquid separation is carried out to obtain a second leaching residue and a second leaching solution containing lithium. And reacting the second leaching residue with a mixed solution of sulfuric acid and ascorbic acid, and performing solid-liquid separation to obtain a third leaching residue and a third leaching solution containing cobalt. The consumption of alkali for removing aluminum is reduced by adopting high and low alkali, and lithium cobaltate is prevented from being leached in the process of leaching aluminum, so that higher recovery rate of cobalt and lithium is obtained. In patent CN114317977a, polyvinyl chloride and waste lithium cobaltate are pyrolyzed in a circulating inert gas atmosphere to obtain a co-pyrolysis product containing lithium and cobalt; and then, leaching the co-pyrolysis product by using water, and filtering to obtain a leaching solution and a leaching product, wherein the leaching solution is a lithium salt-containing leaching solution, and the leaching product is a cobalt-containing leaching product. Patent CN113943867a is to put the positive electrode active material into vitamin C and dilute nitric acid to react to obtain a mixed solution, and then filter the mixed solution after reaction to obtain a leaching solution containing valuable metal ions and a residue. However, the above method has problems of expensive reducing agent or acid-base solution and complicated process, and limits the recycling of the waste lithium cobalt oxide battery to a certain extent. Therefore, it is necessary to find cheaper raw materials or simpler operation process to meet the resource utilization of the waste lithium cobalt oxide battery.
The copperas are solid wastes discharged in the process of producing titanium dioxide by a sulfuric acid method. For every ton of titanium dioxide produced, about 3.5 tons of copperas are produced. The titanium dioxide yield in 2021 years in china is about 426 ten thousand tons, of which 91% is produced by sulfuric acid process, producing nearly 1200 ten thousand tons of copperas. At present, the main purpose of copperas is to produce sulfuric acid by thermal decomposition, but the process needs a large amount of energy consumption and has higher production cost than the existing sulfur-based acid production. With the rapid development of the titanium dioxide industry, the problem of resource utilization of copperas needs to be solved urgently.
Based on the above, the invention utilizes the solid waste copperas of titanium dioxide as an auxiliary agent, mixes and roasts the solid waste copperas with the anode material of the waste lithium cobaltate battery, selectively extracts and separates lithium elements of the lithium cobaltate battery into a solution, and the leaching residue is cobalt ferrite, and the lithium carbonate and the iron-based SCR catalyst are respectively prepared. The process adopts the mixed roasting and leaching process of the lithium cobaltate and the copperas, has simple operation, low production cost and easy separation, realizes the recycling of the lithium cobaltate battery and the copperas, simultaneously has little iron leached from the solution and greatly simplifies the purification process. The process combines the characteristics of lithium cobaltate and copperas, so that solid waste is recycled, and the process has the characteristics of remarkable economic benefit and environmental friendliness.
Disclosure of Invention
The invention provides a method for selectively recycling lithium and preparing a cobalt ferrite catalyst from waste lithium batteries, aiming at the problems of resource utilization of the waste lithium cobalt oxide batteries and solid waste treatment of the titanium dioxide industry.
The invention discloses a method for preparing lithium carbonate and SCR catalyst by using waste lithium cobaltate and copperas, which takes the waste lithium cobaltate and the copperas as raw materials and sequentially comprises the following process steps:
1. carrying out pre-treatment processes such as discharging, disassembling, crushing and screening on the waste lithium cobalt oxide battery to obtain a lithium battery positive electrode material lithium cobalt oxide;
2. copperas decomposed positive electrode material lithium cobaltate
Uniformly mixing lithium cobaltate anode powder which is finely ground to less than 2000 mu m with copperas, and controlling the mass ratio of the lithium cobaltate to the copperas to be 1:1-10; roasting the mixture at 800-1000 ℃ for 60-240 min to obtain a solid product;
3. leaching of roasted product
Leaching the solid product obtained in the step 2 by using deionized water at 25-80 ℃, wherein the leaching time is 30-240 min, the liquid-solid mass ratio is 4-20;
3. preparation of SCR catalyst
Adding the filter residue obtained in the step (3) into a salt solution (cerium nitrate, niobium nitrate, ammonium metavanadate and samarium nitrate), stirring in a water bath at 80 ℃ until the mixture is completely evaporated to dryness, and placing the mixture in a forced air drying oven for vacuum drying at 100 ℃ for 12 hours to obtain an SCR catalyst;
4. preparation of lithium carbonate
And (3) adding ammonia water slowly into the filtrate obtained in the step (3), removing impurities, adding a proper amount of ammonium carbonate solution (the molar ratio of lithium sulfate to ammonium carbonate is 1:1-6) with the concentration of 1-5 mol/L into the filtrate, collecting a precipitate product, and drying to obtain a lithium carbonate product.
The method utilizes ferrous iron in copperas and SO generated by thermal decomposition 2 The lithium cobaltate positive electrode material continues to be reduced and sulfated, converting lithium and cobalt to the corresponding sulfates. The thermal stability of cobalt sulfate is inferior to that of lithium sulfate, and the cobalt sulfate can be decomposed into oxides at a temperature of more than 800 ℃, so that the selective extraction of lithium is realized, and cobalt oxide is further combined with iron oxide generated by the decomposition of copperas to generate cobalt ferrite.
8LiCoO 2 +12FeSO 4 ·7H 2 O+O 2 (g)=6Fe 2 O 3 +4Li 2 SO 4 +84H 2 O(g)+8CoSO 4 (1)
8CoSO 4 +8Fe 2 O 3 =8CoFe 2 O 4 +8SO 2 (g)+4O 2 (g) (2)
Compared with the prior art, the invention has the following advantages: (1) The process adopts industrial solid wastes as raw materials, thereby realizing the resource utilization of wastes; (2) the reaction conditions of the process are mild; (3) The process uses the solid waste copperas, has wide sources, reduces the environmental pollution and saves the production cost; (4) The method has the advantages of simple process, convenient operation, low production cost and industrial application prospect.
Drawings
FIG. 1 is a process flow diagram of the present invention
Detailed Description
The present invention will be described in detail with reference to examples, but the scope of the present invention is not limited to the examples.
The elemental composition (mass%) of the positive electrode material after pretreatment of the used lithium batteries in each of the following examples was 54.38% by weight of CO, 6.76% by weight of Li, 0.1% by weight of Al, 0.05% by weight of Ni, and the XRD analysis result showed that the main phase in the positive electrode powder was lithium cobaltate.
Example one
(1) Discharging, disassembling and classifying the waste lithium cobaltate battery to obtain a positive electrode material, and then performing high-temperature treatment to remove the adhesive;
(2) Uniformly mixing lithium cobaltate positive electrode powder which is finely ground to be less than 200 mu m with copperas, wherein the mass ratio of the lithium cobaltate to the copperas is 1:1; roasting the mixture at 800 ℃ for 60min to obtain a solid product;
(3) Magnetically stirring the solid product obtained in the step 2 with deionized water at 25 ℃, leaching for 180min, wherein the liquid-solid mass ratio is 4:1, and performing solid-liquid separation to obtain a leaching solution containing lithium sulfate and filter residue;
(4) Adding the filter residue obtained in the step 3 into a cerous nitrate solution, stirring in a water bath at 80 ℃ until the filter residue is completely evaporated to dryness, and placing the filter residue in an air-blast drying oven for vacuum drying at 100 ℃ for 12 hours to obtain an SCR catalyst;
(5) And (4) adding ammonia water slowly into the filtrate obtained in the step (3), filtering to remove aluminum and iron ions, adding a proper amount of ammonium carbonate solution (the molar ratio of manganese sulfate to ammonium carbonate is 1:1) with the concentration of 5mol/L into the filtrate, collecting a precipitate product, and drying to obtain a lithium carbonate product.
Example two
(1) Discharging, disassembling and classifying the waste lithium cobaltate battery to obtain a positive electrode material, and then performing high-temperature treatment to remove the adhesive;
(2) Uniformly mixing lithium cobaltate positive electrode powder which is finely ground to be less than 200 mu m with copperas, wherein the mass ratio of the lithium cobaltate to the copperas is 1:4; roasting the mixture at 900 ℃ for 120min to obtain a solid product;
(3) Magnetically stirring the solid product obtained in the step 2 with deionized water at 55 ℃, leaching for 60min, wherein the mass ratio of liquid to solid is 8:1, and performing solid-liquid separation to obtain leachate containing lithium sulfate and filter residue;
(4) Adding the filter residue obtained in the step 3 into a niobium nitrate solution, stirring in a water bath at 80 ℃ until the filter residue is completely evaporated to dryness, and placing the filter residue in an air-blast drying oven for vacuum drying at 100 ℃ for 12 hours to obtain an SCR catalyst;
(5) And (3) adding ammonia water slowly into the filtrate obtained in the step (3), filtering to remove aluminum and iron ions, adding a proper amount of ammonium carbonate solution (the molar ratio of manganese sulfate to ammonium carbonate is 1:2) with the concentration of 6mol/L into the filtrate, collecting a precipitate product, and drying to obtain a lithium carbonate product.
EXAMPLE III
(1) Discharging, disassembling and classifying the waste lithium cobaltate battery to obtain a positive electrode material, and then performing high-temperature treatment to remove the adhesive;
(2) Uniformly mixing lithium cobaltate positive electrode powder which is finely ground to be less than 200 mu m with copperas, wherein the mass ratio of the lithium cobaltate to the copperas is 1:1; roasting the mixture at 1000 ℃ for 120min to obtain a solid product;
(3) Magnetically stirring the solid product obtained in the step 2 with deionized water at 70 ℃, leaching for 240min, wherein the liquid-solid mass ratio is 10, and performing solid-liquid separation to obtain leachate containing lithium sulfate and filter residue;
(4) Adding the filter residue obtained in the step 3 into a vanadium nitrate solution, stirring in a water bath at 80 ℃ until the filter residue is completely evaporated to dryness, and placing the filter residue in an air-blast drying oven for vacuum drying at 100 ℃ for 12 hours to obtain an SCR catalyst;
(5) And (3) adding ammonia water slowly into the filtrate obtained in the step (3), filtering to remove aluminum and iron ions, adding a proper amount of ammonium carbonate solution (the molar ratio of manganese sulfate to ammonium carbonate is 1:4) with the concentration of 4mol/L into the filtrate, collecting a precipitate product, and drying to obtain a lithium carbonate product.
Example four
(1) Discharging, disassembling and classifying the waste lithium cobaltate battery to obtain a positive electrode material, and then performing high-temperature treatment to remove the adhesive;
(2) Uniformly mixing the lithium cobaltate which is finely ground to be a positive electrode material with the particle size of less than 200 mu m with the copperas, wherein the mass ratio of the lithium cobaltate to the copperas is 1:1; roasting the mixture at 1000 ℃ for 240min to obtain a solid product;
(3) Magnetically stirring the solid product obtained in the step 2 with deionized water at 80 ℃, leaching for 240min, wherein the liquid-solid mass ratio is 20;
(4) Adding the filter residue obtained in the step 3 into a cerous nitrate solution, stirring in a water bath at 80 ℃ until the filter residue is completely evaporated to dryness, and placing the filter residue in an air-blast drying oven for vacuum drying at 100 ℃ for 12 hours to obtain an SCR catalyst;
(5) And (3) adding ammonia water slowly into the filtrate obtained in the step (3), filtering to remove aluminum and iron ions, adding a proper amount of ammonium carbonate solution (the molar ratio of manganese sulfate to ammonium carbonate is 1:6) with the concentration of 1mol/L into the filtrate, collecting a precipitate product, and drying to obtain a lithium carbonate product.

Claims (6)

1. A method for selectively recovering lithium from waste lithium batteries and simultaneously preparing a cobalt ferrite catalyst is characterized by comprising the following steps:
step 1: discharging, disassembling and classifying the waste lithium cobaltate battery to obtain a positive electrode material, and then performing high-temperature treatment to remove the adhesive;
step 2: uniformly mixing lithium cobaltate positive electrode powder which is finely ground to be less than 200 mu m with copperas according to a certain mass ratio, and roasting for a certain time at 800-1000 ℃ to obtain a solid product;
and step 3: magnetically stirring the solid product obtained in the step 2 with deionized water at a certain temperature for a certain time, and performing suction filtration on the leachate to realize solid-liquid separation to obtain leachate containing lithium sulfate and filter residue containing cobalt ferrite;
and 4, step 4: modifying the cobalt ferrite filter residue obtained in the step 3 by adopting an impregnation method to load an active component to obtain an SCR catalyst;
and 5: and 3, adjusting the pH value of the leachate obtained in the step 3 by using ammonia water, filtering iron ions, adding ammonium carbonate into the filtrate, collecting a precipitate product and drying to obtain a lithium carbonate product.
2. The method for selectively recycling lithium and simultaneously preparing a cobalt ferrite catalyst by using waste lithium batteries as claimed in claim 1, wherein the mass ratio of the lithium cobaltate to the copperas in the step 2 is 1:1-10.
3. The method for selectively recovering lithium and simultaneously preparing a cobalt ferrite catalyst by using waste lithium batteries as claimed in claim 1, wherein the calcination time in step 2 is 60-240 min.
4. The method for selectively recovering lithium and simultaneously preparing the cobalt ferrite catalyst by using the waste lithium batteries as claimed in claim 1, wherein the solid product in the step 3 has a water leaching temperature of 25-80 ℃, a leaching time of 30-250 min and a liquid-solid mass ratio of 2-20.
5. The method for selectively recovering lithium and simultaneously preparing a cobalt ferrite catalyst by using the waste lithium batteries as claimed in claim 1, wherein the active components in the step 4 comprise one or more of Ce, nb, V and Sm.
6. The method for selectively recovering lithium from waste lithium batteries and simultaneously preparing a cobalt ferrite catalyst according to claim 1, wherein the pH value of the solution obtained in the step 5 after adding ammonia water is 4-8, the solution temperature is 25-100 ℃, the concentration of ammonium carbonate is 1-5 mol/L, the molar ratio of lithium cobaltate to ammonium carbonate is 1:1-6, and the reaction time is 30-180 min.
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