WO2024183014A1 - Method for selectively recycling lithium and system device for selectively recycling lithium - Google Patents
Method for selectively recycling lithium and system device for selectively recycling lithium Download PDFInfo
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- WO2024183014A1 WO2024183014A1 PCT/CN2023/080220 CN2023080220W WO2024183014A1 WO 2024183014 A1 WO2024183014 A1 WO 2024183014A1 CN 2023080220 W CN2023080220 W CN 2023080220W WO 2024183014 A1 WO2024183014 A1 WO 2024183014A1
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- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B26/00—Obtaining alkali, alkaline earth metals or magnesium
- C22B26/10—Obtaining alkali metals
- C22B26/12—Obtaining lithium
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- Y—GENERAL 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
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- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P10/00—Technologies related to metal processing
- Y02P10/20—Recycling
Definitions
- the embodiments of the present application relate to the field of resource recovery technology, such as a method for selectively recovering lithium and a system device for selectively recovering lithium.
- the method of selectively recovering lithium at the front end is mainly to selectively leach lithium after pretreatment.
- water leaching or carbonization water leaching is used after pyrometallurgical pretreatment or mechanical pretreatment.
- conventional pyrometallurgical pretreatments include carbon reduction, hydrogen reduction, and sulfation roasting
- mechanical pretreatments include chloride ball milling, nitrate ball milling activation, etc.
- the selectivity of leaching after mechanical pretreatment is relatively poor, and the leaching rate of lithium is difficult to reach a high level, while the selectivity of leaching after pyrometallurgical pretreatment is better, and the leaching rate of lithium can reach a high level.
- water leaching usually has the problem of too high liquid-to-solid ratio, resulting in too low lithium liquid concentration and difficulty in recovering lithium.
- carbonization water leaching is more conducive to obtaining high-concentration lithium liquid, which is conducive to lithium recovery.
- the related technology uses carbon dioxide finished product to pass into water for carbonization water leaching, which will also increase the recovery cost.
- the embodiment of the present application provides a method for selectively recovering lithium and a system device for selectively recovering lithium, which uses a roasting method to treat the positive electrode active material so that the carbonization water leaching process has a high selectivity for lithium, so that the lithium content in the lithium-rich leachate is much higher than the content of other metal elements.
- the use of tail gas for carbonization water leaching can not only convert lithium carbonate into easily soluble lithium bicarbonate, improve the leaching rate of lithium, but also make full use of tail gas to save recovery costs.
- the present invention provides a method for selectively recovering lithium, the method comprising: follow these steps:
- the present application provides a method for selectively recovering lithium, wherein a carbon reducing agent is used to reduce and roast the positive electrode active material. After reduction, the lithium in the positive electrode active material is converted into lithium carbonate, and a lithium-rich leachate is obtained by carbonizing and leaching the lithium carbonate and other products, wherein the gas source of the carbonizing and leaching is the tail gas (including CO 2 and H 2 O) generated during the roasting process.
- the positive electrode active material is treated by roasting, so that the carbonizing and leaching process has a high selectivity for lithium, so that the lithium content in the lithium-rich leachate is much higher than the content of other metal elements.
- the use of tail gas for carbonizing and leaching can not only convert lithium carbonate into easily soluble lithium bicarbonate, thereby improving the leaching rate of lithium, but also make full use of tail gas and save recovery costs.
- the present application does not specifically limit the type of active substance in the positive electrode active material, including but not limited to any one of lithium cobalt oxide, lithium nickel oxide, lithium manganese oxide, lithium iron phosphate, lithium nickel cobalt oxide, lithium nickel manganese oxide, lithium cobalt manganese oxide, lithium nickel cobalt manganese oxide or lithium nickel cobalt aluminum oxide, or a combination of at least two thereof.
- the particle size of the positive electrode active material is 100-200 mesh, for example, it can be 100 mesh, 110 mesh, 120 mesh, 130 mesh, 140 mesh, 150 mesh, 160 mesh, 170 mesh, 180 mesh, 190 mesh or 200 mesh.
- the positive electrode active material is prepared by crushing a positive electrode sheet.
- the present application does not limit the method of crushing, for example, crushing can be performed in a crusher.
- the type of crusher is not specifically limited.
- the crusher can be a shearing crusher or a shredder.
- a screening step is also provided.
- the positive electrode sheet is crushed and then sieved to separate the positive electrode active material and the aluminum foil, and the positive electrode active material is used to recover lithium.
- the crushing time is 5 to 20 min, for example, 5 min, 7 min, 10 min, 12 min, 14 min, 16 min, 18 min or 20 min.
- the carbon reducing agent includes an organic carbon reducing agent and/or an inorganic carbon reducing agent.
- the carbon reducing agent and the positive electrode active material will undergo a "solid-solid” reduction reaction.
- the carbon reducing agent will be cracked during the reduction calcination process, and the reducing gas (such as CO, H2 and CH4 , etc.) can also participate in the reaction to carry out a "gas-solid" reduction reaction, greatly improving the efficiency of the reduction process.
- the reducing gas (such as CO, H2 and CH4 , etc.) produced by the decomposition of the carbon reducing agent is combustible and can be fully burned with air to provide heat for the reduction roasting process, and the tail gas produced by the combustion (i.e., the tail gas produced by the reduction roasting process) is used for water immersion treatment. It should be noted that the tail gas produced by the combustion does not contain combustible reducing gas.
- the carbon reducing agent is preferably an organic carbon reducing agent.
- the carbon dioxide content in the tail gas generated after the organic carbon reduction roasting is relatively high, and the tail gas can be directly introduced into water for carbonization immersion.
- the organic carbon reductant comprises sugars and/or biomass.
- the present application does not specifically limit the types of sugars, including but not limited to starch.
- the present application does not specifically limit the type of biomass, including but not limited to any one of wood chips, straw, rice straw or sawdust, or a combination of at least two of them.
- the inorganic carbon reducing agent comprises coal.
- the mass ratio of the carbon reducing agent to the positive electrode active material is 0.1 to 0.4, for example, it can be 0.1, 0.15, 0.2, 0.25, 0.3, 0.35 or 0.4.
- the mixing method includes ball milling.
- the rotation speed of the ball mill is 300-600 r/min, for example, it can be 300 r/min, 350 r/min, 400 r/min, 450 r/min, 500 r/min, 550 r/min or 600 r/min.
- the ball milling time is 15 to 60 min, for example, 15 min, 20 min, 25 min, 30 min, 35 min, 40 min, 45 min, 50 min, 55 min or 60 min.
- the heating method during the roasting process includes electric heating and/or self-heating.
- self-heating specifically means that during the reduction roasting process, the carbon reducing agent is cracked to produce combustible gas (such as CO, H2 and CH4 , etc.), and the discharged combustible gas can be burned with air to release heat for reduction roasting, and the tail gas generated after combustion is used for carbonization water immersion treatment.
- combustible gas such as CO, H2 and CH4 , etc.
- the use of self-heating can not only reduce energy consumption and improve heating efficiency, but also solve the problem of cracking gas treatment, avoiding the pollution and safety problems of cracking gas.
- Electric heating refers to the conversion of electrical energy into thermal energy. This process is usually achieved in heating equipment (such as atmosphere tube furnace or box furnace, etc.).
- an optional implementation method includes: the heating method during the roasting process adopts electric heating Combined with self-heating, when the heat provided by self-heating is not enough to support the heat required for the roasting process, electric heating can be started to supplement the required heat.
- the calcination process is carried out under a protective atmosphere.
- the gas in the protective atmosphere includes any one of nitrogen, argon or carbon dioxide, or a combination of at least two of them.
- the calcination heating rate is 3 to 10°C/min, for example, it can be 3°C/min, 4°C/min, 5°C/min, 6°C/min, 7°C/min, 8°C/min, 9°C/min or 10°C/min, etc.
- the calcination temperature is 500-750°C, for example, 500°C, 550°C, 600°C, 650°C, 700°C or 750°C.
- the lithium extraction efficiency will be reduced. This is because the low temperature causes the reduction reaction to be insufficient, and some positive electrode active materials still maintain their inherent form, resulting in insufficient lithium carbonate production; if the calcination temperature is too high, the lithium extraction efficiency will be reduced. This is because the reduction reaction is too sufficient, and more metal elements are generated, which wraps the lithium carbonate and increases the difficulty of leaching.
- the calcination time is 1 to 5 h, for example, 1 h, 1.5 h, 2 h, 2.5 h, 3 h, 3.5 h, 4 h, 4.5 h or 5 h.
- the liquid-to-solid ratio of water to the product is (5-15) mL:1g, for example, it can be 5 mL:1g, 7 mL:1g, 9 mL:1g, 11 mL:1g, 13 mL:1g or 15 mL:1g, etc.
- the ratio of the exhaust gas introduction rate to the volume of water is (0.5-2) mL/min:1 mL, for example, it can be 0.5 mL/min:1 mL, 0.7 mL/min:1 mL, 1 mL/min:1 mL, 1.2 mL/min:1 mL, 1.4 mL/min:1 mL, 1.6 mL/min:1 mL, 1.8 mL/min:1 mL or 2 mL/min:1 mL, etc.
- the lithium leaching efficiency will be reduced, because the low flow rate of CO2 will lead to a lower concentration of carbonate in the solution, affecting the dissolution rate and total amount of lithium carbonate dissolved; if the ratio of the tail gas introduction rate to the volume of water is too high, it will lead to excessive waste of CO2 , and in the case of insufficient lithium carbonate, it will increase the dissolution rate of other valuable metals and reduce the selectivity of leaching.
- the water immersion treatment is accompanied by stirring.
- the stirring speed is 300-500 r/min, for example, it can be 300 r/min, 320 r/min, 340 r/min, 360 r/min, 380 r/min, 400 r/min, 420 r/min, 440 r/min, 460 r/min, 480 r/min or 500 r/min.
- the method specifically comprises the following steps:
- the product is subjected to water leaching treatment, wherein the liquid-to-solid ratio of water to the product is (5-15) mL:1 g.
- the water leaching treatment tail gas generated during the roasting process is passed through, and the ratio of the introduction rate of the tail gas to the volume of water is (0.5-2) mL/min:1 mL. After 0.5-1.5 h of water leaching treatment, a lithium-rich leaching solution and leaching residue are obtained.
- the valuable metal elements such as nickel, cobalt or manganese, etc.
- the valuable metal elements such as nickel, cobalt or manganese, etc.
- the positive electrode active material also includes a binder and a conductive agent, among which the binder may participate in the reduction roasting, and is basically removed by cracking, and the unreacted conductive agent enters the leaching slag.
- an embodiment of the present application provides a system device for selectively recovering lithium, wherein the method described in the first aspect is performed in the system device;
- the system device comprises a roasting device and a water immersion container connected in sequence;
- the roasting equipment comprises a pyrolysis chamber and a combustion chamber arranged outside the pyrolysis chamber, the pyrolysis chamber is provided with a feed inlet and a combustible gas outlet, the combustion chamber is provided with a combustible gas inlet, an air inlet and an exhaust gas outlet, and the combustible gas outlet is connected to the combustible gas inlet;
- the tail gas outlet is connected to an exhaust pipeline, and the output end of the exhaust pipeline extends into the inner cavity of the water immersion container.
- the carbon reducing agent and the positive electrode active material can be reduced and calcined in a pyrolysis chamber.
- the combustible gas generated by the cracking of the carbon reducing agent is discharged through the combustible gas outlet and then enters the combustion chamber through the combustible gas inlet.
- the combustible gas burns with the air entering the combustion chamber, and the heat released by the combustion is transferred to the pyrolysis chamber; the exhaust gas generated after the combustion is transported to the water immersion container through the exhaust gas outlet for water immersion treatment.
- Self-heating can be achieved by using the above-mentioned system device.
- an interlayer is provided between the pyrolysis chamber and the combustion chamber, and a heating element is provided in the interlayer.
- an interlayer is provided between the pyrolysis chamber and the combustion chamber and a heating element is provided therein, and the heating element can convert electrical energy into thermal energy, thereby realizing combined heating of electric heating and self-heating.
- the heating element comprises a heating coil.
- an air intake valve is provided on the connecting pipeline between the combustible gas outlet and the combustible gas inlet.
- an exhaust valve is provided on the exhaust pipeline.
- the embodiment of the present application provides a method for selectively recovering lithium, wherein a carbon reducing agent is used to reduce and roast the positive electrode active material. After reduction, the lithium in the positive electrode active material is converted into lithium carbonate, and a lithium-rich leachate is obtained by carbonization water leaching of the lithium carbonate and other products, wherein the gas source of the carbonization water leaching is the tail gas (including CO 2 and H 2 O) generated during the roasting process.
- the positive electrode active material is treated by roasting, so that the carbonization water leaching process has a high selectivity for lithium, so that the lithium content in the lithium-rich leachate is much higher than the content of other metal elements.
- the use of tail gas for carbonization water leaching can not only convert lithium carbonate into easily soluble lithium bicarbonate, thereby improving the leaching rate of lithium, but also make full use of tail gas to save recovery costs.
- FIG1 is a schematic flow diagram of a method for selectively recovering lithium provided in one embodiment of the present application.
- FIG2 is a schematic diagram of a self-heating reduction roasting device provided in a specific embodiment of the present application.
- 1-pyrolysis chamber 2-combustion chamber; 3-feeding port; 4-combustible gas outlet; 5-combustible gas inlet; 6-air inlet; 7-exhaust gas outlet; 8-water immersion container.
- the present application provides a method for selectively recovering lithium, as shown in FIG1 , the method specifically comprises the following steps:
- the roasted product is subjected to a carbonization water leaching treatment, during which combustion tail gas generated during the autothermal reduction roasting process is passed through the carbonization water leaching treatment to obtain a lithium-rich leaching solution and nickel-cobalt-manganese slag.
- the present embodiment provides a system device for selectively recovering lithium, as shown in FIG2 , comprising a roasting device and a water immersion container 8 connected in sequence;
- the roasting device comprises a pyrolysis chamber 1 and a combustion chamber 2 arranged at the periphery of the pyrolysis chamber 1, the pyrolysis chamber 1 is provided with a feed port 3 and a combustible gas outlet 4, the combustion chamber 2 is provided with a combustible gas inlet 5, an air inlet 6 and an exhaust gas outlet 7, the combustible gas outlet 4 is connected to the combustible gas inlet 5;
- the exhaust gas outlet 7 is connected to an exhaust pipeline, and the output end of the exhaust pipeline extends into the inner cavity of the water immersion container 8;
- An interlayer is provided between the pyrolysis chamber 1 and the combustion chamber 2, a heating coil is provided in the interlayer, and the heating coil and the combustion chamber 2 are electrically connected via a controller, and the controller is used to adjust the temperature.
- the carbon reducing agent and the positive electrode active material can react in the pyrolysis chamber 1, and the combustible gas generated by the cracking of the carbon reducing agent is discharged through the combustible gas outlet 4, and then enters the combustion chamber 2 through the combustible gas inlet 5.
- the combustible gas is burned with the air introduced into the combustion chamber 2, and the heat released by the combustion is transferred to the pyrolysis chamber 1.
- the exhaust gas generated by the combustion can be introduced into the water immersion container 8.
- This embodiment provides a method for selectively recovering lithium, which is carried out in the system device provided in Example 1, and specifically comprises the following steps:
- the lithium-rich leaching solution was subjected to ICP element analysis to detect the concentration of each valuable metal ion therein.
- This embodiment provides a method for selectively recovering lithium, which is carried out in the system device provided in Example 1, and specifically comprises the following steps:
- the lithium-rich leaching solution was tested using the test method described in Example 2.
- This embodiment provides a method for selectively recovering lithium, which is carried out in the system device provided in Example 1, and specifically comprises the following steps:
- the lithium-rich leaching solution was tested using the test method described in Example 2.
- This embodiment provides a method for selectively recovering lithium, which is carried out in the system device provided in Example 1, and specifically comprises the following steps:
- the lithium-rich leaching solution was tested using the test method described in Example 2.
- This embodiment provides a method for selectively recovering lithium.
- the difference from Embodiment 2 is that the calcination temperature is adjusted to 450° C., and the other process parameters and operation steps are the same as those of Embodiment 2.
- the lithium-rich leaching solution was tested using the test method described in Example 2.
- This embodiment provides a method for selectively recovering lithium.
- the difference from Embodiment 2 is that the roasting temperature is adjusted to 800° C., and the other process parameters and operation steps are the same as those of Embodiment 2.
- the lithium-rich leaching solution was tested using the test method described in Example 2.
- This embodiment provides a method for selectively recovering lithium.
- the difference from Example 2 is that the ventilation rate of the tail gas is adjusted to 200 mL/min, so that the ratio of the ventilation rate of the tail gas to the water volume is adjusted to 0.2 mL/min:1 mL, and the remaining process parameters and operating steps are the same as those in Example 2.
- the lithium-rich leaching solution was tested using the test method described in Example 2.
- This embodiment provides a method for selectively recovering lithium.
- the difference from Example 2 is that the ventilation rate of the tail gas is adjusted to 2500 mL/min, so that the ratio of the ventilation rate of the tail gas to the water volume is adjusted to 2.5 mL/min:1 mL, and the remaining process parameters and operating steps are the same as those in Example 2.
- the lithium-rich leaching solution was tested using the test method described in Example 2.
- Example 2 From the results of Example 2, it can be seen that when the method of the present application is used for lithium extraction, the Li leaching rate is as high as 97%, while the leaching rates of Ni, Co and Mn are very low, which indicates that the method for selectively recovering lithium provided by the present application has a high Li selectivity and a high Li leaching rate.
- Example 6 and Example 7 affects the lithium extraction effect.
- the calcination temperature affects the lithium extraction effect.
- the lithium extraction efficiency will be reduced to only 45.7%. This is because the low temperature causes the reduction reaction to be insufficient, and some positive electrode active materials still maintain their inherent form, resulting in insufficient lithium carbonate production; when the calcination temperature is too high, the lithium extraction efficiency will be reduced to 88.7%. This is because the reduction reaction occurs too fully, more metal elements are generated, and the lithium carbonate is wrapped, increasing the difficulty of leaching.
- Example 8 and Example 9 the ratio of the tail gas introduction rate to the volume of water will also affect the lithium extraction effect.
- the ratio of the tail gas introduction rate to the volume of water is too low, the lithium leaching efficiency will be reduced to 85%. This is because the low flow rate of CO2 will lead to a lower concentration of carbonic acid in the solution, affecting the dissolution rate and total amount of lithium carbonate dissolved; when the ratio of the tail gas introduction rate to the volume of water is too high, it will lead to excessive waste of CO2 . In the case of insufficient lithium carbonate, the dissolution rate of other valuable metals will increase, reducing the selectivity of leaching.
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Abstract
Description
本申请实施例涉及资源回收技术领域,例如一种选择性回收锂的方法和选择性回收锂的系统装置。The embodiments of the present application relate to the field of resource recovery technology, such as a method for selectively recovering lithium and a system device for selectively recovering lithium.
近年来,随着新能源汽车的迅速发展,锂离子动力电池的市场需求也持续高速增长,锂作为锂离子动力电池的重要组成元素出现了供不应求的现象,同时在价格上持续走高。目前工业生产上回收三元锂电池中锂的主要手段是将锂放在后端回收,这造成了相当部分的锂损失,因此在前端高效选择性回收锂对于解决市场缺锂以及缓解我国锂资源相对贫乏的问题具有重要意义。In recent years, with the rapid development of new energy vehicles, the market demand for lithium-ion power batteries has continued to grow rapidly. As an important component of lithium-ion power batteries, lithium has been in short supply, and its price has continued to rise. At present, the main means of recycling lithium in ternary lithium batteries in industrial production is to recycle lithium at the back end, which causes a considerable amount of lithium loss. Therefore, efficient and selective recycling of lithium at the front end is of great significance to solve the problem of lithium shortage in the market and alleviate the problem of relatively scarce lithium resources in my country.
当前,在前端选择性回收锂的方法主要为预处理后选择性浸出锂。通常为火法预处理或机械预处理后使用水浸或碳化水浸。其中,常规的火法预处理有碳还原、氢还原和硫酸化焙烧等,机械预处理有氯盐球磨、硝酸盐球磨活化等。机械预处理后浸出的选择性相对较差,且锂的浸出率难以达到较高水平,而火法预处理后浸出的选择性较好,且锂的浸出率能达到较高水平。At present, the method of selectively recovering lithium at the front end is mainly to selectively leach lithium after pretreatment. Usually, water leaching or carbonization water leaching is used after pyrometallurgical pretreatment or mechanical pretreatment. Among them, conventional pyrometallurgical pretreatments include carbon reduction, hydrogen reduction, and sulfation roasting, and mechanical pretreatments include chloride ball milling, nitrate ball milling activation, etc. The selectivity of leaching after mechanical pretreatment is relatively poor, and the leaching rate of lithium is difficult to reach a high level, while the selectivity of leaching after pyrometallurgical pretreatment is better, and the leaching rate of lithium can reach a high level.
在浸出方式中,水浸通常存在液固比过高导致锂液浓度过低难以回收锂的问题。相比之下,碳化水浸更有利于获得高浓度的锂液,利于回收锂。但是相关技术采用二氧化碳成品通入水中进行碳化水浸,也会增加回收成本。Among the leaching methods, water leaching usually has the problem of too high liquid-to-solid ratio, resulting in too low lithium liquid concentration and difficulty in recovering lithium. In contrast, carbonization water leaching is more conducive to obtaining high-concentration lithium liquid, which is conducive to lithium recovery. However, the related technology uses carbon dioxide finished product to pass into water for carbonization water leaching, which will also increase the recovery cost.
因此,亟需一种成本低、选择性好和浸出率高的方法来选择性回收锂。Therefore, a method with low cost, good selectivity and high leaching rate is urgently needed to selectively recover lithium.
发明内容Summary of the invention
以下是对本文详细描述的主题的概述。本概述并非是为了限制权利要求的保护范围。The following is a summary of the subject matter described in detail herein. This summary is not intended to limit the scope of the claims.
本申请实施例提供一种选择性回收锂的方法和选择性回收锂的系统装置,采用焙烧的方式处理正极活性材料,使得碳化水浸的过程对锂具有较高的选择性,从而使得富锂浸出液中锂的含量远远高于其它金属元素的含量。此外,利用尾气进行碳化水浸,既能将碳酸锂转变为易溶碳酸氢锂,提高锂的浸出率,又能充分利用尾气,节约回收成本。The embodiment of the present application provides a method for selectively recovering lithium and a system device for selectively recovering lithium, which uses a roasting method to treat the positive electrode active material so that the carbonization water leaching process has a high selectivity for lithium, so that the lithium content in the lithium-rich leachate is much higher than the content of other metal elements. In addition, the use of tail gas for carbonization water leaching can not only convert lithium carbonate into easily soluble lithium bicarbonate, improve the leaching rate of lithium, but also make full use of tail gas to save recovery costs.
第一方面,本申请实施例提供了一种选择性回收锂的方法,所述方法包括 以下步骤:In a first aspect, the present invention provides a method for selectively recovering lithium, the method comprising: Follow these steps:
(1)将正极活性材料与碳还原剂混合,焙烧得到产物;(1) mixing a positive electrode active material with a carbon reducing agent and calcining to obtain a product;
(2)对产物进行水浸处理,水浸处理的过程中通有焙烧过程产生的尾气,得到富锂浸出液。(2) The product is subjected to water leaching treatment, during which tail gas generated during the roasting process is passed through the water leaching treatment to obtain a lithium-rich leaching solution.
本申请提供了一种选择性回收锂的方法,使用碳还原剂对正极活性材料进行还原焙烧,还原后,正极活性材料中的锂转变为碳酸锂,通过对碳酸锂等产物进行碳化水浸,获得富锂浸出液,其中,碳化水浸的气体来源为焙烧过程产生的尾气(包含CO2和H2O)。采用焙烧的方式处理正极活性材料,使得碳化水浸的过程对锂具有较高的选择性,从而使得富锂浸出液中锂的含量远远高于其它金属元素的含量。此外,利用尾气进行碳化水浸,既能将碳酸锂转变为易溶碳酸氢锂,提高锂的浸出率,又能充分利用尾气,节约回收成本。The present application provides a method for selectively recovering lithium, wherein a carbon reducing agent is used to reduce and roast the positive electrode active material. After reduction, the lithium in the positive electrode active material is converted into lithium carbonate, and a lithium-rich leachate is obtained by carbonizing and leaching the lithium carbonate and other products, wherein the gas source of the carbonizing and leaching is the tail gas (including CO 2 and H 2 O) generated during the roasting process. The positive electrode active material is treated by roasting, so that the carbonizing and leaching process has a high selectivity for lithium, so that the lithium content in the lithium-rich leachate is much higher than the content of other metal elements. In addition, the use of tail gas for carbonizing and leaching can not only convert lithium carbonate into easily soluble lithium bicarbonate, thereby improving the leaching rate of lithium, but also make full use of tail gas and save recovery costs.
本申请对正极活性材料中活性物质的种类不作具体限定,包括但不限于钴酸锂、镍酸锂、锰酸锂、磷酸铁锂、镍钴酸锂、镍锰酸锂、钴锰酸锂、镍钴锰酸锂或镍钴铝酸锂中的任意一种或至少两种的组合。The present application does not specifically limit the type of active substance in the positive electrode active material, including but not limited to any one of lithium cobalt oxide, lithium nickel oxide, lithium manganese oxide, lithium iron phosphate, lithium nickel cobalt oxide, lithium nickel manganese oxide, lithium cobalt manganese oxide, lithium nickel cobalt manganese oxide or lithium nickel cobalt aluminum oxide, or a combination of at least two thereof.
作为本申请优选的一种技术方案,所述正极活性材料的粒度为100~200目,例如可以是100目、110目、120目、130目、140目、150目、160目、170目、180目、190目或200目等。As a preferred technical solution of the present application, the particle size of the positive electrode active material is 100-200 mesh, for example, it can be 100 mesh, 110 mesh, 120 mesh, 130 mesh, 140 mesh, 150 mesh, 160 mesh, 170 mesh, 180 mesh, 190 mesh or 200 mesh.
优选地,所述正极活性材料通过对正极片进行破碎的方式制备得到。Preferably, the positive electrode active material is prepared by crushing a positive electrode sheet.
本申请对破碎的方式不作限定,例如可以在破碎机中进行破碎,同时,对破碎机的种类不作具体限定,示例性地,破碎机可以是剪切式破碎机,也可以是撕碎机。The present application does not limit the method of crushing, for example, crushing can be performed in a crusher. At the same time, the type of crusher is not specifically limited. For example, the crusher can be a shearing crusher or a shredder.
优选地,所述对正极片进行破碎之后,还设置有筛分的步骤。Preferably, after the positive electrode sheets are crushed, a screening step is also provided.
本申请中,对正极片进行破碎后,再进行筛分,即可分开正极活性材料和铝箔,正极活性材料用于回收锂。In the present application, the positive electrode sheet is crushed and then sieved to separate the positive electrode active material and the aluminum foil, and the positive electrode active material is used to recover lithium.
优选地,所述破碎的时间为5~20min,例如可以是5min、7min、10min、12min、14min、16min、18min或20min等。Preferably, the crushing time is 5 to 20 min, for example, 5 min, 7 min, 10 min, 12 min, 14 min, 16 min, 18 min or 20 min.
作为本申请优选的一种技术方案,所述碳还原剂包括有机碳还原剂和/或无机碳还原剂。As a preferred technical solution of the present application, the carbon reducing agent includes an organic carbon reducing agent and/or an inorganic carbon reducing agent.
本申请的焙烧过程中,碳还原剂与正极活性材料会发生“固-固”还原反应,此外,碳还原剂在还原焙烧过程中会发生裂解,其裂解产生的还原性气体(如 CO、H2和CH4等)也可以参与到反应中,进行“气-固”还原反应,大大提高还原过程的效率。During the calcination process of the present application, the carbon reducing agent and the positive electrode active material will undergo a "solid-solid" reduction reaction. In addition, the carbon reducing agent will be cracked during the reduction calcination process, and the reducing gas (such as CO, H2 and CH4 , etc.) can also participate in the reaction to carry out a "gas-solid" reduction reaction, greatly improving the efficiency of the reduction process.
本申请中,碳还原剂裂解产生的还原性气体(如CO、H2和CH4等)是可燃的,能够与空气充分燃烧为还原焙烧过程提供热量,燃烧产生的尾气(即还原焙烧过程产生的尾气)用于水浸处理。需要说明的是,燃烧产生的尾气中不含可燃还原性气体。In the present application, the reducing gas (such as CO, H2 and CH4 , etc.) produced by the decomposition of the carbon reducing agent is combustible and can be fully burned with air to provide heat for the reduction roasting process, and the tail gas produced by the combustion (i.e., the tail gas produced by the reduction roasting process) is used for water immersion treatment. It should be noted that the tail gas produced by the combustion does not contain combustible reducing gas.
本申请中,碳还原剂优选为有机碳还原剂,使用有机碳还原焙烧后产生的尾气中的二氧化碳含量较高,尾气可直接通入水中进行碳化水浸。In the present application, the carbon reducing agent is preferably an organic carbon reducing agent. The carbon dioxide content in the tail gas generated after the organic carbon reduction roasting is relatively high, and the tail gas can be directly introduced into water for carbonization immersion.
优选地,所述有机碳还原剂包括糖类和/或生物质。Preferably, the organic carbon reductant comprises sugars and/or biomass.
本申请对糖类的种类不作具体限定,包括但不限于淀粉。The present application does not specifically limit the types of sugars, including but not limited to starch.
本申请对生物质的种类不作具体限定,包括但不限于木屑、秸秆、稻草或锯末屑中的任意一种或至少两种的组合。The present application does not specifically limit the type of biomass, including but not limited to any one of wood chips, straw, rice straw or sawdust, or a combination of at least two of them.
优选地,所述无机碳还原剂包括煤。Preferably, the inorganic carbon reducing agent comprises coal.
作为本申请优选的一种技术方案,所述碳还原剂与正极活性材料的质量比为0.1~0.4,例如可以是0.1、0.15、0.2、0.25、0.3、0.35或0.4等。As a preferred technical solution of the present application, the mass ratio of the carbon reducing agent to the positive electrode active material is 0.1 to 0.4, for example, it can be 0.1, 0.15, 0.2, 0.25, 0.3, 0.35 or 0.4.
作为本申请优选的一种技术方案,所述混合的方式包括球磨。As a preferred technical solution of the present application, the mixing method includes ball milling.
优选地,所述球磨的转速为300~600r/min,例如可以是300r/min、350r/min、400r/min、450r/min、500r/min、550r/min或600r/min等。Preferably, the rotation speed of the ball mill is 300-600 r/min, for example, it can be 300 r/min, 350 r/min, 400 r/min, 450 r/min, 500 r/min, 550 r/min or 600 r/min.
优选地,所述球磨的时间为15~60min,例如可以是15min、20min、25min、30min、35min、40min、45min、50min、55min或60min等。Preferably, the ball milling time is 15 to 60 min, for example, 15 min, 20 min, 25 min, 30 min, 35 min, 40 min, 45 min, 50 min, 55 min or 60 min.
作为本申请优选的一种技术方案,所述焙烧的过程中的加热方式包括电加热和/或自加热。As a preferred technical solution of the present application, the heating method during the roasting process includes electric heating and/or self-heating.
本申请中,自加热具体是指,还原焙烧过程中,碳还原剂发生裂解产生可燃气(如CO、H2和CH4等),排出的可燃气可以与空气进行燃烧放出热量供还原焙烧使用,燃烧后产生的尾气用于碳化水浸处理。采用自加热,不仅能降低能耗,提高加热效率,还能解决裂解气体的处理问题,避免了裂解气的污染以及安全问题。In the present application, self-heating specifically means that during the reduction roasting process, the carbon reducing agent is cracked to produce combustible gas (such as CO, H2 and CH4 , etc.), and the discharged combustible gas can be burned with air to release heat for reduction roasting, and the tail gas generated after combustion is used for carbonization water immersion treatment. The use of self-heating can not only reduce energy consumption and improve heating efficiency, but also solve the problem of cracking gas treatment, avoiding the pollution and safety problems of cracking gas.
电加热是指,将电能转化为热能,通常此过程在加热设备(如气氛管式炉或箱式炉等)中实现。Electric heating refers to the conversion of electrical energy into thermal energy. This process is usually achieved in heating equipment (such as atmosphere tube furnace or box furnace, etc.).
本申请中,一种可选的实施方式包括:焙烧过程中的加热方式采用电加热 与自加热联合加热,当自加热提供的热量不足以支持焙烧过程所需的热量,可以启动电加热,补充所需热量。In the present application, an optional implementation method includes: the heating method during the roasting process adopts electric heating Combined with self-heating, when the heat provided by self-heating is not enough to support the heat required for the roasting process, electric heating can be started to supplement the required heat.
优选地,所述焙烧的过程在保护气氛下进行。Preferably, the calcination process is carried out under a protective atmosphere.
优选地,所述保护气氛中的气体包括氮气、氩气或二氧化碳中的任意一种或至少两种的组合。Preferably, the gas in the protective atmosphere includes any one of nitrogen, argon or carbon dioxide, or a combination of at least two of them.
作为本申请优选的一种技术方案,所述焙烧的升温速率为3~10℃/min,例如可以是3℃/min、4℃/min、5℃/min、6℃/min、7℃/min、8℃/min、9℃/min或10℃/min等。As a preferred technical solution of the present application, the calcination heating rate is 3 to 10°C/min, for example, it can be 3°C/min, 4°C/min, 5°C/min, 6°C/min, 7°C/min, 8°C/min, 9°C/min or 10°C/min, etc.
优选地,所述焙烧的温度为500~750℃,例如可以是500℃、550℃、600℃、650℃、700℃或750℃等。Preferably, the calcination temperature is 500-750°C, for example, 500°C, 550°C, 600°C, 650°C, 700°C or 750°C.
本申请中,若焙烧的温度过低,会导致提锂效率降低,是由于低温导致还原反应发生不够充分,部分正极活性材料仍维持固有形态,使得碳酸锂生产量不足;若焙烧的温度过高,会导致提锂效率降低,是由于还原反应发生过于充分,金属单质生成较多,对碳酸锂形成包裹增加浸出难度。In the present application, if the calcination temperature is too low, the lithium extraction efficiency will be reduced. This is because the low temperature causes the reduction reaction to be insufficient, and some positive electrode active materials still maintain their inherent form, resulting in insufficient lithium carbonate production; if the calcination temperature is too high, the lithium extraction efficiency will be reduced. This is because the reduction reaction is too sufficient, and more metal elements are generated, which wraps the lithium carbonate and increases the difficulty of leaching.
优选地,所述焙烧的时间为1~5h,例如可以是1h、1.5h、2h、2.5h、3h、3.5h、4h、4.5h或5h等。Preferably, the calcination time is 1 to 5 h, for example, 1 h, 1.5 h, 2 h, 2.5 h, 3 h, 3.5 h, 4 h, 4.5 h or 5 h.
作为本申请优选的一种技术方案,所述水浸处理的过程中,水与所述产物的液固比为(5~15)mL:1g,例如可以是5mL:1g、7mL:1g、9mL:1g、11mL:1g、13mL:1g或15mL:1g等。As a preferred technical solution of the present application, during the water immersion treatment, the liquid-to-solid ratio of water to the product is (5-15) mL:1g, for example, it can be 5 mL:1g, 7 mL:1g, 9 mL:1g, 11 mL:1g, 13 mL:1g or 15 mL:1g, etc.
优选地,所述水浸处理的过程中,所述尾气的通入速率与水的体积的比为(0.5~2)mL/min:1mL,例如可以是0.5mL/min:1mL、0.7mL/min:1mL、1mL/min:1mL、1.2mL/min:1mL、1.4mL/min:1mL、1.6mL/min:1mL、1.8mL/min:1mL或2mL/min:1mL等。Preferably, during the water immersion treatment, the ratio of the exhaust gas introduction rate to the volume of water is (0.5-2) mL/min:1 mL, for example, it can be 0.5 mL/min:1 mL, 0.7 mL/min:1 mL, 1 mL/min:1 mL, 1.2 mL/min:1 mL, 1.4 mL/min:1 mL, 1.6 mL/min:1 mL, 1.8 mL/min:1 mL or 2 mL/min:1 mL, etc.
本申请中,若尾气的通入速率与水的体积的比值过低,会导致锂的浸出效率降低,是由于低流速的CO2会导致溶液中碳酸浓度较低,影响碳酸锂的溶解速率和溶解总量;若尾气的通入速率与水的体积的比值过高,会导致CO2过度浪费,在碳酸锂不足的情况下,会增加其他有价金属的溶出率,降低浸出的选择性。In the present application, if the ratio of the tail gas introduction rate to the volume of water is too low, the lithium leaching efficiency will be reduced, because the low flow rate of CO2 will lead to a lower concentration of carbonate in the solution, affecting the dissolution rate and total amount of lithium carbonate dissolved; if the ratio of the tail gas introduction rate to the volume of water is too high, it will lead to excessive waste of CO2 , and in the case of insufficient lithium carbonate, it will increase the dissolution rate of other valuable metals and reduce the selectivity of leaching.
作为本申请优选的一种技术方案,所述水浸处理的时间为0.5~1.5h,例如可以是0.5h、0.7h、1h、1.2h或1.5h等。 As a preferred technical solution of the present application, the time of the water immersion treatment is 0.5 to 1.5 h, for example, it can be 0.5 h, 0.7 h, 1 h, 1.2 h or 1.5 h.
优选地,所述水浸处理伴有搅拌。Preferably, the water immersion treatment is accompanied by stirring.
优选地,所述搅拌的转速为300~500r/min,例如可以是300r/min、320r/min、340r/min、360r/min、380r/min、400r/min、420r/min、440r/min、460r/min、480r/min或500r/min等。Preferably, the stirring speed is 300-500 r/min, for example, it can be 300 r/min, 320 r/min, 340 r/min, 360 r/min, 380 r/min, 400 r/min, 420 r/min, 440 r/min, 460 r/min, 480 r/min or 500 r/min.
作为本申请优选的一种技术方案,所述方法具体包括以下步骤:As a preferred technical solution of the present application, the method specifically comprises the following steps:
(Ⅰ)将正极活性材料与碳还原剂以300~600r/min的转速混合15~60min,得到混合物,将混合物在500~750℃的温度下焙烧1~5h,得到产物;(I) mixing the positive electrode active material and the carbon reducing agent at a rotation speed of 300 to 600 r/min for 15 to 60 min to obtain a mixture, and calcining the mixture at a temperature of 500 to 750° C. for 1 to 5 h to obtain a product;
(Ⅱ)对产物进行水浸处理,水与产物的液固比为(5~15)mL:1g,水浸处理的过程中通有焙烧过程产生的尾气,所述尾气的通入速率与水的体积的比为(0.5~2)mL/min:1mL,水浸处理0.5~1.5h后,得到富锂浸出液和浸出渣。(II) The product is subjected to water leaching treatment, wherein the liquid-to-solid ratio of water to the product is (5-15) mL:1 g. During the water leaching treatment, tail gas generated during the roasting process is passed through, and the ratio of the introduction rate of the tail gas to the volume of water is (0.5-2) mL/min:1 mL. After 0.5-1.5 h of water leaching treatment, a lithium-rich leaching solution and leaching residue are obtained.
本申请中,正极活性材料与碳还原剂进行还原焙烧之后,正极活性材料活性物质中的有价金属元素(如镍、钴或锰等)转变为金属态或低价氧化物状态,碳化水浸后置于浸出渣中。In the present application, after the positive electrode active material and the carbon reducing agent are reduced and roasted, the valuable metal elements (such as nickel, cobalt or manganese, etc.) in the active substance of the positive electrode active material are converted into a metallic state or a low-valent oxide state, and are carbonized and then immersed in water and placed in the leached slag.
正极活性材料中还包括粘结剂和导电剂等,其中,粘结剂可能会参与还原焙烧,发生裂解基本被除去,未反应的导电剂进入浸出渣中。The positive electrode active material also includes a binder and a conductive agent, among which the binder may participate in the reduction roasting, and is basically removed by cracking, and the unreacted conductive agent enters the leaching slag.
第二方面,本申请实施例提供了一种选择性回收锂的系统装置,第一方面所述的方法在所述系统装置中进行;In a second aspect, an embodiment of the present application provides a system device for selectively recovering lithium, wherein the method described in the first aspect is performed in the system device;
所述系统装置包括依次连接的焙烧设备和水浸容器;The system device comprises a roasting device and a water immersion container connected in sequence;
所述焙烧设备包括热解室和设置在所述热解室外周的燃烧室,所述热解室设置有进料口和可燃气出口,所述燃烧室设置有可燃气入口、空气入口和尾气出口,所述可燃气出口连通所述可燃气入口;The roasting equipment comprises a pyrolysis chamber and a combustion chamber arranged outside the pyrolysis chamber, the pyrolysis chamber is provided with a feed inlet and a combustible gas outlet, the combustion chamber is provided with a combustible gas inlet, an air inlet and an exhaust gas outlet, and the combustible gas outlet is connected to the combustible gas inlet;
所述尾气出口连接有排气管路,所述排气管路的输出端伸入所述水浸容器的内腔中。The tail gas outlet is connected to an exhaust pipeline, and the output end of the exhaust pipeline extends into the inner cavity of the water immersion container.
本申请中,碳还原剂与正极活性材料可在热解室中进行还原焙烧,碳还原剂发生裂解产生的可燃性气体经可燃气出口排出,再经可燃气入口进入燃烧室,可燃性气体与通入燃烧室的空气进行燃烧,燃烧放出的热量传递至热解室;燃烧后产生的尾气经尾气出口输送至水浸容器中,进行水浸处理。In the present application, the carbon reducing agent and the positive electrode active material can be reduced and calcined in a pyrolysis chamber. The combustible gas generated by the cracking of the carbon reducing agent is discharged through the combustible gas outlet and then enters the combustion chamber through the combustible gas inlet. The combustible gas burns with the air entering the combustion chamber, and the heat released by the combustion is transferred to the pyrolysis chamber; the exhaust gas generated after the combustion is transported to the water immersion container through the exhaust gas outlet for water immersion treatment.
采用上述的系统装置可实现自加热。Self-heating can be achieved by using the above-mentioned system device.
优选地,所述热解室和所述燃烧室之间设置有夹层,所述夹层内设置有加热件。 Preferably, an interlayer is provided between the pyrolysis chamber and the combustion chamber, and a heating element is provided in the interlayer.
本申请中,在热解室和燃烧室之间设置夹层并在其中设置加热件,加热件可将电能转化为热能,从而能够实现电加热与自加热联合加热。In the present application, an interlayer is provided between the pyrolysis chamber and the combustion chamber and a heating element is provided therein, and the heating element can convert electrical energy into thermal energy, thereby realizing combined heating of electric heating and self-heating.
优选地,所述加热件包括加热线圈。Preferably, the heating element comprises a heating coil.
优选地,所述可燃气出口与所述可燃气入口的连通管路上设置有进气阀。Preferably, an air intake valve is provided on the connecting pipeline between the combustible gas outlet and the combustible gas inlet.
优选地,所述排气管路上设置有排气阀。Preferably, an exhaust valve is provided on the exhaust pipeline.
本申请所述的数值范围不仅包括上述列举的点值,还包括没有列举出的上述数值范围之间的任意的点值,限于篇幅及出于简明的考虑,本申请不再穷尽列举所述范围包括的具体点值。The numerical range described in this application includes not only the point values listed above, but also any point values between the above numerical ranges that are not listed. Due to limited space and for the sake of brevity, this application no longer exhaustively lists the specific point values included in the range.
与相关技术相比,本申请实施例的有益效果为:Compared with the related art, the beneficial effects of the embodiments of the present application are:
本申请实施例提供了一种选择性回收锂的方法,使用碳还原剂对正极活性材料进行还原焙烧,还原后,正极活性材料中的锂转变为碳酸锂,通过对碳酸锂等产物进行碳化水浸,获得富锂浸出液,其中,碳化水浸的气体来源为焙烧过程产生的尾气(包含CO2和H2O)。采用焙烧的方式处理正极活性材料,使得碳化水浸的过程对锂具有较高的选择性,从而使得富锂浸出液中锂的含量远远高于其它金属元素的含量。此外,利用尾气进行碳化水浸,既能将碳酸锂转变为易溶碳酸氢锂,提高锂的浸出率,又能充分利用尾气,节约回收成本。The embodiment of the present application provides a method for selectively recovering lithium, wherein a carbon reducing agent is used to reduce and roast the positive electrode active material. After reduction, the lithium in the positive electrode active material is converted into lithium carbonate, and a lithium-rich leachate is obtained by carbonization water leaching of the lithium carbonate and other products, wherein the gas source of the carbonization water leaching is the tail gas (including CO 2 and H 2 O) generated during the roasting process. The positive electrode active material is treated by roasting, so that the carbonization water leaching process has a high selectivity for lithium, so that the lithium content in the lithium-rich leachate is much higher than the content of other metal elements. In addition, the use of tail gas for carbonization water leaching can not only convert lithium carbonate into easily soluble lithium bicarbonate, thereby improving the leaching rate of lithium, but also make full use of tail gas to save recovery costs.
在阅读并理解了附图和详细描述后,可以明白其他方面。Other aspects will be apparent upon reading and understanding the drawings and detailed description.
附图用来提供对本文技术方案的进一步理解,并且构成说明书的一部分,与本申请的实施例一起用于解释本文的技术方案,并不构成对本文技术方案的限制。The accompanying drawings are used to provide further understanding of the technical solution of this article and constitute a part of the specification. Together with the embodiments of the present application, they are used to explain the technical solution of this article and do not constitute a limitation on the technical solution of this article.
图1为本申请一个具体实施方式提供的选择性回收锂的方法的流程示意图;FIG1 is a schematic flow diagram of a method for selectively recovering lithium provided in one embodiment of the present application;
图2为本申请一个具体实施方式提供的自热还原焙烧设备的简要示意图;FIG2 is a schematic diagram of a self-heating reduction roasting device provided in a specific embodiment of the present application;
其中,1-热解室;2-燃烧室;3-进料口;4-可燃气出口;5-可燃气入口;6-空气入口;7-尾气出口;8-水浸容器。Among them, 1-pyrolysis chamber; 2-combustion chamber; 3-feeding port; 4-combustible gas outlet; 5-combustible gas inlet; 6-air inlet; 7-exhaust gas outlet; 8-water immersion container.
下面通过具体实施方式来进一步说明本申请的技术方案。The technical solution of the present application is further illustrated below through specific implementation methods.
在一个具体实施方式中,本申请提供了一种选择性回收锂的方法,如图1所示,所述方法具体包括以下步骤: In a specific embodiment, the present application provides a method for selectively recovering lithium, as shown in FIG1 , the method specifically comprises the following steps:
(1)将镍钴锰三元正极片进行破碎筛分,得到铝箔和镍钴锰三元正极活性材料;(1) crushing and screening the nickel-cobalt-manganese ternary positive electrode sheet to obtain aluminum foil and nickel-cobalt-manganese ternary positive electrode active material;
(2)将镍钴锰三元正极活性材料与有机碳还原剂混合进行自热还原焙烧后,得到焙烧产物;其中,有机碳还原剂在还原焙烧过程中发生裂解产生裂解可燃气,裂解可燃气与空气进行燃烧用于向还原焙烧过程提供热量,裂解可燃气充分燃烧后产生燃烧尾气;(2) mixing the nickel-cobalt-manganese ternary positive electrode active material with an organic carbon reducing agent and performing autothermal reduction roasting to obtain a roasting product; wherein the organic carbon reducing agent is cracked during the reduction roasting process to produce a cracked combustible gas, the cracked combustible gas is burned with air to provide heat for the reduction roasting process, and the cracked combustible gas is fully burned to produce a combustion exhaust gas;
(3)对焙烧产物进行碳化水浸处理,碳化水浸处理过程中通有自热还原焙烧过程产生的燃烧尾气,得到富锂浸出液和镍钴锰渣。(3) The roasted product is subjected to a carbonization water leaching treatment, during which combustion tail gas generated during the autothermal reduction roasting process is passed through the carbonization water leaching treatment to obtain a lithium-rich leaching solution and nickel-cobalt-manganese slag.
实施例1Example 1
本实施例提供了一种选择性回收锂的系统装置,如图2所示,包括依次连接的焙烧设备和水浸容器8;所述焙烧设备包括热解室1和设置在所述热解室1外周的燃烧室2,所述热解室1设置有进料口3和可燃气出口4,所述燃烧室2设置有可燃气入口5、空气入口6和尾气出口7,所述可燃气出口4连通所述可燃气入口5;所述尾气出口7连接有排气管路,所述排气管路的输出端伸入所述水浸容器8的内腔中;The present embodiment provides a system device for selectively recovering lithium, as shown in FIG2 , comprising a roasting device and a water immersion container 8 connected in sequence; the roasting device comprises a pyrolysis chamber 1 and a combustion chamber 2 arranged at the periphery of the pyrolysis chamber 1, the pyrolysis chamber 1 is provided with a feed port 3 and a combustible gas outlet 4, the combustion chamber 2 is provided with a combustible gas inlet 5, an air inlet 6 and an exhaust gas outlet 7, the combustible gas outlet 4 is connected to the combustible gas inlet 5; the exhaust gas outlet 7 is connected to an exhaust pipeline, and the output end of the exhaust pipeline extends into the inner cavity of the water immersion container 8;
所述热解室1和所述燃烧室2之间设置有夹层,所述夹层内设置有加热线圈,所述加热线圈和所述燃烧室2电性连接有控制器,所述控制器用于调控温度。An interlayer is provided between the pyrolysis chamber 1 and the combustion chamber 2, a heating coil is provided in the interlayer, and the heating coil and the combustion chamber 2 are electrically connected via a controller, and the controller is used to adjust the temperature.
在本实施例的系统装置中,碳还原剂与正极活性材料可在热解室1中进行反应,碳还原剂发生裂解产生的可燃性气体经可燃气出口4排出,再经可燃气入口5进入燃烧室2,可燃性气体与通入燃烧室2的空气进行燃烧,燃烧放出的热量传递至热解室1,燃烧产生的尾气可通入水浸容器8中。In the system device of this embodiment, the carbon reducing agent and the positive electrode active material can react in the pyrolysis chamber 1, and the combustible gas generated by the cracking of the carbon reducing agent is discharged through the combustible gas outlet 4, and then enters the combustion chamber 2 through the combustible gas inlet 5. The combustible gas is burned with the air introduced into the combustion chamber 2, and the heat released by the combustion is transferred to the pyrolysis chamber 1. The exhaust gas generated by the combustion can be introduced into the water immersion container 8.
实施例2Example 2
本实施例提供了一种选择性回收锂的方法,所述方法在实施例1提供的系统装置中进行,所述方法具体包括以下步骤:This embodiment provides a method for selectively recovering lithium, which is carried out in the system device provided in Example 1, and specifically comprises the following steps:
(1)取1000g LiNi0.5Co0.2Mn0.3O2(NCM523)正极片使用剪切式破碎机破碎10min后得到破碎后三元极片粉,使用120目筛对破碎的三元极片粉进行筛分,得到903g三元正极活性材料和94g铝箔;(1) 1000 g of LiNi 0.5 Co 0.2 Mn 0.3 O 2 (NCM523) positive electrode sheet was crushed using a shear crusher for 10 min to obtain crushed ternary electrode sheet powder, and the crushed ternary electrode sheet powder was sieved using a 120-mesh sieve to obtain 903 g of ternary positive electrode active material and 94 g of aluminum foil;
(2)取900g NCM523三元正极活性材料,配入180g淀粉,使用球磨机以450r/min的转速球磨混料30min后,将1000g混合充分的待焙烧物料放置于刚 玉坩埚内,再放入氮气保护的热解室内,以5℃/min升温速率加热至650℃,升温过程中将裂解产生的可燃气体通入燃烧室内,混合空气燃烧补充热量,并通过控制器调控热解室温度,在650℃保温3h得到还原焙烧产物;(2) Take 900g of NCM523 ternary positive electrode active material, add 180g of starch, use a ball mill to mix at a speed of 450r/min for 30min, and then place 1000g of the fully mixed material to be calcined on a steel plate. The crucible was placed in a pyrolysis chamber protected by nitrogen and heated to 650°C at a heating rate of 5°C/min. During the heating process, the combustible gas produced by cracking was introduced into the combustion chamber and mixed with air to supplement the heat. The temperature of the pyrolysis chamber was regulated by a controller and kept at 650°C for 3 hours to obtain a reduction roasting product.
(3)取100g还原焙烧产物置于水浸容器中,使用燃烧尾气对其进行碳化水浸,水与还原焙烧产物的液固比为10mL:1g,尾气的通气速率为1000mL/min,碳化水浸伴有搅拌,搅拌速率为400r/min,浸出时间1.5h后分离得到富锂浸出液和浸出渣。(3) 100 g of the reduction roasting product was placed in a water immersion container and carbonized in water using combustion tail gas. The liquid-solid ratio of water to the reduction roasting product was 10 mL:1 g. The ventilation rate of the tail gas was 1000 mL/min. The carbonization water immersion was accompanied by stirring at a stirring rate of 400 r/min. After leaching for 1.5 h, lithium-rich leaching solution and leaching residue were separated.
测试方法:Test Method:
对富锂浸出液进行ICP元素分析,检测其中各有价金属离子浓度。The lithium-rich leaching solution was subjected to ICP element analysis to detect the concentration of each valuable metal ion therein.
对测试结果进行分析计算,可知Li浸出率为97%,Ni浸出率为0.1%,Co浸出率为0.001%,Mn浸出率为0.001%。Analysis and calculation of the test results show that the Li leaching rate is 97%, the Ni leaching rate is 0.1%, the Co leaching rate is 0.001%, and the Mn leaching rate is 0.001%.
实施例3Example 3
本实施例提供了一种选择性回收锂的方法,所述方法在实施例1提供的系统装置中进行,所述方法具体包括以下步骤:This embodiment provides a method for selectively recovering lithium, which is carried out in the system device provided in Example 1, and specifically comprises the following steps:
(1)取1000g LiNi0.6Co0.2Mn0.2O2(NCM622)正极片使用剪切式破碎机破碎10min后得到破碎后三元极片粉,使用200目筛对破碎的三元极片粉进行筛分,得到873g三元正极活性材料和125g铝箔;(1) 1000 g of LiNi 0.6 Co 0.2 Mn 0.2 O 2 (NCM622) positive electrode sheet was crushed using a shear crusher for 10 min to obtain crushed ternary electrode sheet powder, and the crushed ternary electrode sheet powder was sieved using a 200-mesh sieve to obtain 873 g of ternary positive electrode active material and 125 g of aluminum foil;
(2)取800g NCM622三元正极活性材料,配入240g木屑,使用球磨机以450r/min的转速球磨混料30min后,将1000g混合充分的待焙烧物料放置于刚玉坩埚内,再放入氮气保护的热解室内,以5℃/min升温速率加热至700℃,升温过程中将裂解产生的可燃气体通入燃烧室内,混合空气燃烧补充热量,并通过控制器调控热解室温度,在700℃保温4h得到还原焙烧产物;(2) 800 g of NCM622 ternary positive electrode active material was taken, 240 g of sawdust was added, and the mixture was ball milled at a speed of 450 r/min for 30 min. Then, 1000 g of the fully mixed material to be calcined was placed in a corundum crucible, and then placed in a nitrogen-protected pyrolysis chamber, and heated to 700 °C at a heating rate of 5 °C/min. During the heating process, the combustible gas generated by cracking was introduced into the combustion chamber, mixed with air to supplement heat, and the temperature of the pyrolysis chamber was regulated by a controller, and kept at 700 °C for 4 h to obtain a reduction calcination product;
(3)取200g还原焙烧产物置于水浸容器中,使用燃烧尾气对其进行碳化水浸,水与还原焙烧产物的液固比为15mL:1g,尾气的通气速率为1500mL/min,碳化水浸伴有搅拌,搅拌速率为500r/min,浸出时间1h后分离得到富锂浸出液和浸出渣。(3) 200 g of the reduction roasting product was placed in a water immersion container and carbonized in water using combustion tail gas. The liquid-solid ratio of water to the reduction roasting product was 15 mL:1 g. The ventilation rate of the tail gas was 1500 mL/min. The carbonization water immersion was accompanied by stirring at a stirring rate of 500 r/min. After leaching for 1 h, lithium-rich leaching solution and leaching residue were separated.
采用实施例2所述的测试方法对富锂浸出液进行测试。The lithium-rich leaching solution was tested using the test method described in Example 2.
对测试结果进行分析计算,可知Li浸出率为98%,Ni浸出率为0.03%,Co浸出率为0.001%,Mn浸出率为0.001%。Analysis and calculation of the test results show that the Li leaching rate is 98%, the Ni leaching rate is 0.03%, the Co leaching rate is 0.001%, and the Mn leaching rate is 0.001%.
实施例4 Example 4
本实施例提供了一种选择性回收锂的方法,所述方法在实施例1提供的系统装置中进行,所述方法具体包括以下步骤:This embodiment provides a method for selectively recovering lithium, which is carried out in the system device provided in Example 1, and specifically comprises the following steps:
(1)取1000g LiNi0.8Co0.1Mn0.1O2(NCM811)正极片使用剪切式破碎机破碎10min后得到破碎后三元极片粉,使用200目筛对破碎的三元极片粉进行筛分,得到863g三元正极活性材料和130g铝箔;(1) 1000 g of LiNi 0.8 Co 0.1 Mn 0.1 O 2 (NCM811) positive electrode sheet was crushed using a shear crusher for 10 min to obtain crushed ternary electrode sheet powder, and the crushed ternary electrode sheet powder was sieved using a 200-mesh sieve to obtain 863 g of ternary positive electrode active material and 130 g of aluminum foil;
(2)取700g NCM811三元正极活性材料,配入175g秸秆,使用球磨机以450r/min的转速球磨混料30min后,将800g混合充分的待焙烧物料放置于刚玉坩埚内,再放入氮气保护的热解室内,以5℃/min升温速率加热至600℃,升温过程中将裂解产生的可燃气体通入燃烧室内,混合空气燃烧补充热量,并通过控制器调控热解室温度,在600℃保温5h得到还原焙烧产物;(2) 700 g of NCM811 ternary positive electrode active material was taken, and 175 g of straw was added. The mixture was ball milled at a speed of 450 r/min for 30 min, and then 800 g of the fully mixed material to be calcined was placed in a corundum crucible, and then placed in a pyrolysis chamber protected by nitrogen, and heated to 600 °C at a heating rate of 5 °C/min. During the heating process, the combustible gas generated by cracking was introduced into the combustion chamber, mixed with air to supplement heat, and the temperature of the pyrolysis chamber was regulated by a controller, and the temperature was kept at 600 °C for 5 h to obtain a reduction calcination product;
(3)取500g还原焙烧产物置于水浸容器中,使用燃烧尾气对其进行碳化水浸,水与还原焙烧产物的液固比为5mL:1g,尾气的通气速率为5000mL/min,碳化水浸伴有搅拌,搅拌速率为300r/min,浸出时间1.5h后分离得到富锂浸出液和浸出渣。(3) 500 g of the reduction roasting product was placed in a water immersion container and carbonized in water using combustion tail gas. The liquid-solid ratio of water to the reduction roasting product was 5 mL:1 g. The ventilation rate of the tail gas was 5000 mL/min. The carbonization water immersion was accompanied by stirring at a stirring rate of 300 r/min. After leaching for 1.5 h, lithium-rich leaching solution and leaching residue were separated.
采用实施例2所述的测试方法对富锂浸出液进行测试。The lithium-rich leaching solution was tested using the test method described in Example 2.
对测试结果进行分析计算,可知Li浸出率为97.6%,Ni浸出率为0.001%,Co浸出率为0.001%,Mn浸出率为0.001%。Analysis and calculation of the test results show that the Li leaching rate is 97.6%, the Ni leaching rate is 0.001%, the Co leaching rate is 0.001%, and the Mn leaching rate is 0.001%.
实施例5Example 5
本实施例提供了一种选择性回收锂的方法,所述方法在实施例1提供的系统装置中进行,所述方法具体包括以下步骤:This embodiment provides a method for selectively recovering lithium, which is carried out in the system device provided in Example 1, and specifically comprises the following steps:
(1)取1000g LiCoO2正极片使用剪切式破碎机破碎15min后得到破碎的极片粉,使用150目筛对破碎的极片粉进行筛分,得到890g正极活性材料和105g铝箔;(1) 1000 g of LiCoO2 positive electrode sheet was crushed using a shear crusher for 15 min to obtain crushed electrode sheet powder, and the crushed electrode sheet powder was sieved using a 150-mesh sieve to obtain 890 g of positive electrode active material and 105 g of aluminum foil;
(2)取800g LiCoO2正极活性材料,配入80g谷壳,使用球磨机以450r/min的转速球磨混料30min后,将800g混合充分的待焙烧物料放置于刚玉坩埚内,再放入氮气保护的热解室内,以5℃/min升温速率加热至750℃,升温过程中将裂解产生的可燃气体通入燃烧室内,混合空气燃烧补充热量,并通过控制器调控热解室温度,在750℃保温2h得到还原焙烧产物;(2) 800 g of LiCoO2 positive electrode active material was added with 80 g of rice husk, and the mixture was ball milled at a speed of 450 r/min for 30 min. Then, 800 g of the fully mixed material to be calcined was placed in a corundum crucible, and then placed in a pyrolysis chamber protected by nitrogen, and heated to 750 °C at a heating rate of 5 °C/min. During the heating process, the combustible gas generated by cracking was introduced into the combustion chamber, mixed with air to supplement heat, and the temperature of the pyrolysis chamber was regulated by a controller, and kept at 750 °C for 2 h to obtain a reduction calcination product;
(3)取300g还原焙烧产物置于水浸容器中,使用燃烧尾气对其进行碳化水浸,水与还原焙烧产物的液固比为10mL:1g,尾气的通气速率为2000mL/min, 碳化水浸伴有搅拌,搅拌速率为400r/min,浸出时间1.5h后分离得到富锂浸出液和浸出渣。(3) 300 g of the reduced roasted product was placed in a water immersion container and carbonized by water immersion using combustion tail gas. The liquid-solid ratio of water to the reduced roasted product was 10 mL:1 g, and the ventilation rate of the tail gas was 2000 mL/min. The carbonization water leaching was accompanied by stirring at a stirring rate of 400 r/min. After leaching for 1.5 h, lithium-rich leaching solution and leaching residue were separated.
采用实施例2所述的测试方法对富锂浸出液进行测试。The lithium-rich leaching solution was tested using the test method described in Example 2.
对测试结果进行分析计算,可知Li浸出率为98.2%,Co浸出率为0.01%。Analysis and calculation of the test results show that the Li leaching rate is 98.2% and the Co leaching rate is 0.01%.
实施例6Example 6
本实施例提供了一种选择性回收锂的方法,与实施例2的区别在于,焙烧的温度调整为450℃,其余工艺参数与操作步骤与实施例2相同。This embodiment provides a method for selectively recovering lithium. The difference from Embodiment 2 is that the calcination temperature is adjusted to 450° C., and the other process parameters and operation steps are the same as those of Embodiment 2.
采用实施例2所述的测试方法对富锂浸出液进行测试。The lithium-rich leaching solution was tested using the test method described in Example 2.
对测试结果进行分析计算,可知Li浸出率为45.7%,Ni浸出率为0.86%,Co浸出率为0.23%,Mn浸出率为0.21%。Analysis and calculation of the test results show that the Li leaching rate is 45.7%, the Ni leaching rate is 0.86%, the Co leaching rate is 0.23%, and the Mn leaching rate is 0.21%.
实施例7Example 7
本实施例提供了一种选择性回收锂的方法,与实施例2的区别在于,焙烧的温度调整为800℃,其余工艺参数与操作步骤与实施例2相同。This embodiment provides a method for selectively recovering lithium. The difference from Embodiment 2 is that the roasting temperature is adjusted to 800° C., and the other process parameters and operation steps are the same as those of Embodiment 2.
采用实施例2所述的测试方法对富锂浸出液进行测试。The lithium-rich leaching solution was tested using the test method described in Example 2.
对测试结果进行分析计算,可知Li浸出率为88.7%,Ni浸出率为0.29%,Co浸出率为0.01%,Mn浸出率为0.01%。Analysis and calculation of the test results show that the Li leaching rate is 88.7%, the Ni leaching rate is 0.29%, the Co leaching rate is 0.01%, and the Mn leaching rate is 0.01%.
实施例8Example 8
本实施例提供了一种选择性回收锂的方法,与实施例2的区别在于,尾气的通气速率调整为200mL/min,使得尾气的通气速率与水体积的比调整为0.2mL/min:1mL,其余工艺参数与操作步骤与实施例2相同。This embodiment provides a method for selectively recovering lithium. The difference from Example 2 is that the ventilation rate of the tail gas is adjusted to 200 mL/min, so that the ratio of the ventilation rate of the tail gas to the water volume is adjusted to 0.2 mL/min:1 mL, and the remaining process parameters and operating steps are the same as those in Example 2.
采用实施例2所述的测试方法对富锂浸出液进行测试。The lithium-rich leaching solution was tested using the test method described in Example 2.
对测试结果进行分析计算,可知Li浸出率为85%,Ni浸出率为0.01%,Co浸出率为0.01%,Mn浸出率为0.01%。Analysis and calculation of the test results show that the Li leaching rate is 85%, the Ni leaching rate is 0.01%, the Co leaching rate is 0.01%, and the Mn leaching rate is 0.01%.
实施例9Example 9
本实施例提供了一种选择性回收锂的方法,与实施例2的区别在于,尾气的通气速率调整为2500mL/min,使得尾气的通气速率与水体积的比调整为2.5mL/min:1mL,其余工艺参数与操作步骤与实施例2相同。This embodiment provides a method for selectively recovering lithium. The difference from Example 2 is that the ventilation rate of the tail gas is adjusted to 2500 mL/min, so that the ratio of the ventilation rate of the tail gas to the water volume is adjusted to 2.5 mL/min:1 mL, and the remaining process parameters and operating steps are the same as those in Example 2.
采用实施例2所述的测试方法对富锂浸出液进行测试。The lithium-rich leaching solution was tested using the test method described in Example 2.
对测试结果进行分析计算,可知Li浸出率为95.3%,Ni浸出率为1.03%,Co浸出率为0.5%,Mn浸出率为0.6%。 Analysis and calculation of the test results show that the Li leaching rate is 95.3%, the Ni leaching rate is 1.03%, the Co leaching rate is 0.5%, and the Mn leaching rate is 0.6%.
分析:analyze:
由实施例2的结果可知,采用本申请的方法进行提锂,Li浸出率高达97%,而Ni、Co和Mn的浸出率很低,这表明本申请提供的选择性回收锂的方法具有较高的对Li选择性和较高的Li浸出率。From the results of Example 2, it can be seen that when the method of the present application is used for lithium extraction, the Li leaching rate is as high as 97%, while the leaching rates of Ni, Co and Mn are very low, which indicates that the method for selectively recovering lithium provided by the present application has a high Li selectivity and a high Li leaching rate.
由实施例2、实施例6和实施例7的结果可知,焙烧的温度影响着提锂效果,当焙烧的温度过低时,会导致提锂效率降低,仅为45.7%,这是由于低温导致还原反应发生不够充分,部分正极活性材料仍维持固有形态,使得碳酸锂生产量不足;当焙烧的温度过高时,会导致提锂效率降低,降至88.7%,这是由于还原反应发生过于充分,金属单质生成较多,对碳酸锂形成包裹增加浸出难度。It can be seen from the results of Example 2, Example 6 and Example 7 that the calcination temperature affects the lithium extraction effect. When the calcination temperature is too low, the lithium extraction efficiency will be reduced to only 45.7%. This is because the low temperature causes the reduction reaction to be insufficient, and some positive electrode active materials still maintain their inherent form, resulting in insufficient lithium carbonate production; when the calcination temperature is too high, the lithium extraction efficiency will be reduced to 88.7%. This is because the reduction reaction occurs too fully, more metal elements are generated, and the lithium carbonate is wrapped, increasing the difficulty of leaching.
由实施例2、实施例8和实施例9的结果可知,尾气的通入速率与水的体积的比值也会影响提锂效果,当尾气的通入速率与水的体积的比值过低时,会导致锂的浸出效率降低,降至85%,这是由于低流速的CO2会导致溶液中碳酸浓度较低,影响碳酸锂的溶解速率和溶解总量;当尾气的通入速率与水的体积的比值过高时,会导致CO2过度浪费,在碳酸锂不足的情况下,会增加其他有价金属的溶出率,降低浸出的选择性。It can be seen from the results of Example 2, Example 8 and Example 9 that the ratio of the tail gas introduction rate to the volume of water will also affect the lithium extraction effect. When the ratio of the tail gas introduction rate to the volume of water is too low, the lithium leaching efficiency will be reduced to 85%. This is because the low flow rate of CO2 will lead to a lower concentration of carbonic acid in the solution, affecting the dissolution rate and total amount of lithium carbonate dissolved; when the ratio of the tail gas introduction rate to the volume of water is too high, it will lead to excessive waste of CO2 . In the case of insufficient lithium carbonate, the dissolution rate of other valuable metals will increase, reducing the selectivity of leaching.
申请人声明,以上所述仅为本申请的具体实施方式,但本申请的保护范围并不局限于此,所属技术领域的技术人员应该明了,任何属于本技术领域的技术人员在本申请揭露的技术范围内,可轻易想到的变化或替换,均落在本申请的保护范围和公开范围之内。 The applicant declares that the above is only a specific implementation method of the present application, but the protection scope of the present application is not limited thereto. Technical personnel in the relevant technical field should understand that any changes or substitutions that can be easily thought of by technical personnel in the relevant technical field within the technical scope disclosed in the present application are within the protection scope and disclosure scope of the present application.
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Citations (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2004011010A (en) * | 2002-06-11 | 2004-01-15 | Sumitomo Metal Mining Co Ltd | Method for recovering lithium and cobalt from lithium cobaltate |
| WO2014042136A1 (en) * | 2012-09-11 | 2014-03-20 | 株式会社日立製作所 | Method for recycling lithium-ion batteries and device therefor |
| CN106129511A (en) * | 2016-06-27 | 2016-11-16 | 北京科技大学 | A kind of method of comprehensively recovering valuable metal from waste and old lithium ion battery material |
| CN108220607A (en) * | 2018-02-23 | 2018-06-29 | 中国科学院过程工程研究所 | A kind of method that lithium is recycled from waste material containing lithium electrode |
| CN111271711A (en) * | 2020-01-20 | 2020-06-12 | 上海智迭科技有限公司 | A kind of continuous carbonization pyrolysis disposal method of waste lithium battery |
| CN111463475A (en) * | 2020-03-11 | 2020-07-28 | 长沙有色冶金设计研究院有限公司 | Method for selectively recycling waste power lithium battery positive electrode material |
| CN112993428A (en) * | 2021-02-08 | 2021-06-18 | 中节能工程技术研究院有限公司 | Method for recycling waste ternary lithium battery positive electrode material |
| CN113120975A (en) * | 2021-04-14 | 2021-07-16 | 北京佰利格瑞资源科技有限公司 | Method for recycling waste ternary lithium battery positive electrode material |
| CN115417434A (en) * | 2022-09-02 | 2022-12-02 | 安徽格派锂电循环科技有限公司 | Method for recovering valuable metals in black powder of waste lithium ion battery and preparing lithium carbonate product in carbothermic reduction mode |
-
2023
- 2023-03-08 CN CN202380008503.0A patent/CN116568832A/en active Pending
- 2023-03-08 WO PCT/CN2023/080220 patent/WO2024183014A1/en active Pending
Patent Citations (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2004011010A (en) * | 2002-06-11 | 2004-01-15 | Sumitomo Metal Mining Co Ltd | Method for recovering lithium and cobalt from lithium cobaltate |
| WO2014042136A1 (en) * | 2012-09-11 | 2014-03-20 | 株式会社日立製作所 | Method for recycling lithium-ion batteries and device therefor |
| CN106129511A (en) * | 2016-06-27 | 2016-11-16 | 北京科技大学 | A kind of method of comprehensively recovering valuable metal from waste and old lithium ion battery material |
| CN108220607A (en) * | 2018-02-23 | 2018-06-29 | 中国科学院过程工程研究所 | A kind of method that lithium is recycled from waste material containing lithium electrode |
| CN111271711A (en) * | 2020-01-20 | 2020-06-12 | 上海智迭科技有限公司 | A kind of continuous carbonization pyrolysis disposal method of waste lithium battery |
| CN111463475A (en) * | 2020-03-11 | 2020-07-28 | 长沙有色冶金设计研究院有限公司 | Method for selectively recycling waste power lithium battery positive electrode material |
| CN112993428A (en) * | 2021-02-08 | 2021-06-18 | 中节能工程技术研究院有限公司 | Method for recycling waste ternary lithium battery positive electrode material |
| CN113120975A (en) * | 2021-04-14 | 2021-07-16 | 北京佰利格瑞资源科技有限公司 | Method for recycling waste ternary lithium battery positive electrode material |
| CN115417434A (en) * | 2022-09-02 | 2022-12-02 | 安徽格派锂电循环科技有限公司 | Method for recovering valuable metals in black powder of waste lithium ion battery and preparing lithium carbonate product in carbothermic reduction mode |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN119979908A (en) * | 2025-03-17 | 2025-05-13 | 哈尔滨工业大学 | A method for recovering valuable metals from waste lithium-ion batteries |
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