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CN116814984A - A method for extracting lithium from waste lithium iron phosphate batteries - Google Patents

A method for extracting lithium from waste lithium iron phosphate batteries Download PDF

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CN116814984A
CN116814984A CN202310824402.2A CN202310824402A CN116814984A CN 116814984 A CN116814984 A CN 116814984A CN 202310824402 A CN202310824402 A CN 202310824402A CN 116814984 A CN116814984 A CN 116814984A
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lithium
iron phosphate
waste
lithium iron
leaching
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南东东
张明
张颖
舒启溢
童声
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Jiangxi Jinhui Lithium Industry Co ltd
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Jiangxi Jinhui Lithium Industry Co ltd
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    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B26/00Obtaining alkali, alkaline earth metals or magnesium
    • C22B26/10Obtaining alkali metals
    • C22B26/12Obtaining lithium
    • HELECTRICITY
    • H01ELECTRIC ELEMENTS
    • H01MPROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
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    • H01M10/54Reclaiming serviceable parts of waste accumulators

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  • Electrochemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Processing Of Solid Wastes (AREA)
  • Manufacture And Refinement Of Metals (AREA)

Abstract

本发明公开了一种从废旧磷酸铁锂电池中提锂的方法,具体步骤如下:1)破碎:将废旧磷酸铁锂电池拆解回收的正极材料进行破碎后过筛,得到磷酸铁锂废料细粉料;2)焙烧:将磷酸铁锂废料细粉料经回转窑高温焙烧,焙烧后进行机械破碎球磨,得到焙烧破碎细粉料;3)浸出回调除杂:将焙烧破碎细粉熟料与酸溶液充分搅拌进行浸出、回调pH后固液分离后得到含锂溶液和浸出渣;4)净化溶液:将含锂溶液加入氢氧化钠、碳酸钠除杂,再用碳酸钠沉锂制备电池级碳酸锂。本发明方法过程中不需要使用氧化剂试剂,具有焙烧温度低、成本低、工艺操作简单等优点,用回转窑能够大规模的处理铁锂粉,适合工业化回收废旧磷酸铁锂电池提锂,浸出和除杂同时进行,简化了工艺流程、操作步骤及节省了设备投资。The invention discloses a method for extracting lithium from waste lithium iron phosphate batteries. The specific steps are as follows: 1) Crushing: the positive electrode materials recovered from the waste lithium iron phosphate batteries are crushed and screened to obtain fine lithium iron phosphate waste materials. Powder; 2) Roasting: Roast the lithium iron phosphate waste fine powder at high temperature in a rotary kiln, and then perform mechanical crushing and ball milling after roasting to obtain roasted and crushed fine powder; 3) Leaching back to remove impurities: Combine the roasted and crushed fine powder clinker with The acid solution is fully stirred for leaching, and the pH is adjusted back to solid-liquid separation to obtain a lithium-containing solution and leaching residue; 4) Purification solution: Add sodium hydroxide and sodium carbonate to the lithium-containing solution to remove impurities, and then use sodium carbonate to precipitate lithium to prepare battery grade Lithium carbonate. The method of the invention does not require the use of oxidant reagents, and has the advantages of low roasting temperature, low cost, simple process operation, etc. The rotary kiln can be used to process iron lithium powder on a large scale, and is suitable for industrial recycling of waste lithium iron phosphate batteries for lithium extraction, leaching and Impurities are removed at the same time, which simplifies the process flow, operating steps and saves equipment investment.

Description

一种从废旧磷酸铁锂电池中提锂的方法A method for extracting lithium from waste lithium iron phosphate batteries

技术领域Technical field

本发明属于锂离子回收技术领域,具体是涉及一种从废旧磷酸铁锂电池中提锂的方法。The invention belongs to the technical field of lithium ion recovery, and specifically relates to a method for extracting lithium from waste lithium iron phosphate batteries.

背景技术Background technique

随着经济的高速发展,新能源汽车产业得到了迅猛发展,磷酸铁锂电池作为新能源汽车的主要动力源,得到了大量生产和应用。因其安全系数高、循环寿命长等优异性能被广泛应用于启动电源、储能市场、军工、航标等领域。磷酸铁锂电池广泛应用已导致其报废量逐年递增,引发了浪费资源、污染环境、危害人体健康等严重问题。废旧磷酸铁锂电池有价金属锂含量低,回收经济性差,对其低成本回收已成为研究热点,虽取得了一些成果和应用,但仍存在有价元素回收率低、成本高等问题。因此,废旧磷酸铁锂电池的高值化全元素回收再利用成为解决上述问题的关键和难点。With the rapid development of the economy, the new energy vehicle industry has developed rapidly. As the main power source of new energy vehicles, lithium iron phosphate batteries have been produced and applied in large quantities. Because of its high safety factor, long cycle life and other excellent properties, it is widely used in starting power supply, energy storage market, military industry, navigation beacon and other fields. The widespread use of lithium iron phosphate batteries has led to an increase in scrapping year by year, causing serious problems such as wasting resources, polluting the environment, and endangering human health. Waste lithium iron phosphate batteries have low content of valuable metal lithium and poor recycling economics. Low-cost recycling has become a research hotspot. Although some results and applications have been achieved, there are still problems such as low recovery rate of valuable elements and high cost. Therefore, high-value all-element recycling of used lithium iron phosphate batteries has become the key and difficulty to solve the above problems.

现有技术中,CN106505225A公开了一种从锂废旧电池中回收锂制备电池级碳酸锂的方法,该方法主要步骤包括电池拆解、酸化浸出、除铁、铝、氟化沉锂、镁盐转型、碱化除杂、纯碱沉锂等,其核心点为往浆料中加入无机酸和双氧水,控制H+与Li+的摩尔比为3:1~4:1,双氧水与Li+的摩尔比为1:2~1:1,然后在常温下浸出30-60min回收锂;CN109534372A公开了一种利用磷酸铁锂废料制备碳酸锂的方法,常温条件下,取一定质量的磷酸铁锂废料放入反应容器中,边搅拌边加入一定质量的次氯酸钠溶液,控制Li与ClO-摩尔比值为2:1.05-2:1.20,得到混合溶液;得到的混合溶液中边搅拌边缓慢加入纯度为31-35%的盐酸,盐酸的加入速度控制在5-10ml/min,调节溶液pH至1-2,得到酸性溶液后,在80-90℃条件下搅拌反应0.5-2h;然后在过滤淋洗、浓缩除杂、碱化除杂、纯碱沉锂回收磷酸铁锂废料中的锂。可以看出现有湿法回收废旧磷酸铁锂电池中锂的方法过程中都存在利用氧化剂将 Fe2+氧化成 Fe3+,再通过调节 pH,与磷酸根或氢氧根共沉淀;然后在滤液中加入沉淀剂沉淀 Li+,实现 Li+的回收。此方法稳定性好,回收率较高,但在浸出过程中需要消耗大量的氧化剂,造成生产成本高、工艺复杂。In the prior art, CN106505225A discloses a method for recovering lithium from used lithium batteries to prepare battery-grade lithium carbonate. The main steps of the method include battery disassembly, acidification leaching, iron removal, aluminum, lithium fluoride precipitation, and magnesium salt transformation. , alkalization and impurity removal, soda ash lithium precipitation, etc. The core point is to add inorganic acid and hydrogen peroxide to the slurry, control the molar ratio of H + to Li + to 3:1~4:1, and control the molar ratio of hydrogen peroxide to Li + The ratio is 1:2~1:1, and then leached for 30-60 minutes at normal temperature to recover lithium; CN109534372A discloses a method for preparing lithium carbonate from lithium iron phosphate waste. Under normal temperature conditions, a certain mass of lithium iron phosphate waste is put into In the reaction vessel, a certain mass of sodium hypochlorite solution is added while stirring, and the molar ratio of Li and ClO is controlled to be 2:1.05-2:1.20 to obtain a mixed solution; the resulting mixed solution is slowly added while stirring, and the purity is 31-35%. Hydrochloric acid, the addition speed of hydrochloric acid is controlled at 5-10ml/min, adjust the pH of the solution to 1-2, after obtaining the acidic solution, stir the reaction at 80-90°C for 0.5-2h; then filter, rinse, concentrate and remove impurities , alkalization and impurity removal, soda ash lithium precipitation to recover lithium from lithium iron phosphate waste. It can be seen that the existing wet recovery method of lithium in waste lithium iron phosphate batteries uses an oxidant to oxidize Fe 2+ into Fe 3+ , and then adjusts the pH to co-precipitate with phosphate or hydroxide; and then in the filtrate A precipitant is added to precipitate Li + to achieve recovery of Li + . This method has good stability and high recovery rate, but it requires a large amount of oxidant to be consumed during the leaching process, resulting in high production costs and complicated processes.

发明内容Contents of the invention

针对现有技术的不足,本发明提供了一种从废旧磷酸铁锂电池中提锂的方法,浸出过程中不需要额外加入氧化剂,锂的回收率≥96.5%,具有处理规模大、工艺操作简单、成本低、易实现工业化生产等优点。In view of the shortcomings of the existing technology, the present invention provides a method for extracting lithium from waste lithium iron phosphate batteries. No additional oxidant is required during the leaching process. The recovery rate of lithium is ≥96.5%. It has large processing scale and simple process operation. , low cost, easy to achieve industrial production and other advantages.

一种从废旧磷酸铁锂电池中提锂的方法,具体步骤如下:A method for extracting lithium from waste lithium iron phosphate batteries. The specific steps are as follows:

1)破碎:将废旧磷酸铁锂电池拆解回收的正极材料进行破碎后过筛,得到磷酸铁锂废料细粉料;1) Crushing: The cathode materials recovered by dismantling and recycling waste lithium iron phosphate batteries are crushed and then sieved to obtain fine powder of lithium iron phosphate scrap;

2)焙烧:将磷酸铁锂废料细粉料经回转窑高温焙烧,焙烧后进行机械破碎球磨,得到焙烧破碎细粉料;2) Roasting: Roast the lithium iron phosphate scrap fine powder at high temperature in a rotary kiln, and then perform mechanical crushing and ball milling after roasting to obtain roasted and crushed fine powder;

3)浸出回调除杂:将焙烧破碎细粉熟料与酸溶液充分搅拌进行浸出、回调pH后固液分离后得到含锂溶液和浸出渣;3) Leaching callback and impurity removal: fully stir the roasted and crushed fine clinker and the acid solution for leaching, call back the pH and separate the solid and liquid to obtain the lithium-containing solution and leaching residue;

4)净化溶液:将含锂溶液加入氢氧化钠、碳酸钠除杂,再用碳酸钠沉锂制备电池级碳酸锂。4) Purify the solution: Add sodium hydroxide and sodium carbonate to the lithium-containing solution to remove impurities, and then use sodium carbonate to precipitate lithium to prepare battery-grade lithium carbonate.

优选的,所述步骤1)中磷酸铁锂废料细粉料锂含量2.5-4.4%,细度≤60目:Preferably, the lithium content of the lithium iron phosphate waste fine powder in step 1) is 2.5-4.4%, and the fineness is ≤60 mesh:

优选的,所述步骤2)中回转窑焙烧温度为400-800℃,焙烧时间为0.5-4h。Preferably, in step 2), the roasting temperature of the rotary kiln is 400-800°C, and the roasting time is 0.5-4h.

优选的,所述步骤2)中焙烧破碎细粉料细度为60-200目。Preferably, the fineness of the roasted and crushed fine powder in step 2) is 60-200 mesh.

优选的,所述步骤3)中酸溶液为硫酸、盐酸、乙酸中的至少一种。Preferably, the acid solution in step 3) is at least one of sulfuric acid, hydrochloric acid, and acetic acid.

优选的,所述步骤3)中浸出温度为30-80℃,浸出时间为0.5-6.0h,搅拌强度为100-600rpm,浸出完成后溶液pH为2-3。Preferably, the leaching temperature in step 3) is 30-80°C, the leaching time is 0.5-6.0h, the stirring intensity is 100-600rpm, and the pH of the solution after leaching is completed is 2-3.

优选的,所述步骤3)中回调pH使用片碱、熟石灰中的至少一种进行回调,回调后pH为4-5.5。Preferably, at least one of caustic soda and hydrated lime is used to adjust the pH in step 3), and the pH after the adjustment is 4-5.5.

优选的,所述步骤4)中除杂方法为通过用氢氧化钠调节pH至11-13后再根据溶液中钙镁含量并过量5%加入碳酸钠除杂。Preferably, the impurity removal method in step 4) is to adjust the pH to 11-13 with sodium hydroxide and then add sodium carbonate to remove impurities according to the calcium and magnesium content in the solution and an excess of 5%.

优选的,所述步骤4)中沉锂过程中温度≥85℃,碳酸钠浓度为180-300g/L。Preferably, the temperature during the lithium precipitation process in step 4) is ≥85°C, and the sodium carbonate concentration is 180-300g/L.

与现有技术相比,本发明具有以下优点:Compared with the prior art, the present invention has the following advantages:

本发明提供了一种从废旧磷酸铁锂电池中提锂的方法,通过在回转窑中中温焙烧将磷酸亚铁锂中的二价铁氧化成三价铁破坏其稳定的结构,然后再浸出,过程中不需要使用氧化剂试剂,具有焙烧温度低、成本低、工艺操作简单等优点,用回转窑能够大规模的处理铁锂粉适合工业化回收废旧磷酸铁锂电池提锂,本发明方法浸出和除杂同时进行,简化了工艺流程、操作步骤及节省了设备投资,通过本发明方法锂的回收率≥96.5%。The invention provides a method for extracting lithium from waste lithium iron phosphate batteries. By roasting at medium temperature in a rotary kiln, the divalent iron in the lithium iron phosphate is oxidized into trivalent iron to destroy its stable structure, and then leached. The process does not require the use of oxidant reagents, and has the advantages of low roasting temperature, low cost, and simple process operation. The rotary kiln can process lithium iron powder on a large scale and is suitable for industrial recycling of waste lithium iron phosphate batteries to extract lithium. The method of the present invention leaches and removes lithium. The process is carried out simultaneously, which simplifies the process flow, operating steps and saves equipment investment. The recovery rate of lithium through the method of the present invention is ≥96.5%.

实施方式Implementation

下面结合具体实施例对本发明做进一步详细说明The present invention will be further described in detail below in conjunction with specific embodiments.

实施例1Example 1

将废旧磷酸铁锂电池拆解回收的正极材料进行破碎后过60目筛网,取筛下物料得到≤60目磷酸铁锂废料细粉料,再将磷酸铁锂废料细粉料在回转窑中600℃焙烧1.0h,冷却至60℃以下后进行机械破碎球磨至80目,再将焙烧破碎细粉熟料和稀硫酸在60℃条件下搅拌浸出1.0h、搅拌强度为400rpm,液固比为3:1,浸出后液pH控制在2-3之间,pH偏高时补酸继续反应直到pH稳定在2-3且半小时内无变化浸出反应才完成,浸出反应完成后用片碱回调pH在4-5.5之间后用板框压滤机固液分离后得到含锂溶液和浸出渣;浸出渣经过洗涤后渣中锂离子浓度为0.03wt%,锂的回收率97.2%;含锂溶液用氢氧化钠调节pH至12后再根据溶液中钙镁含量并过量5%加入碳酸钠除钙镁离子得到含锂净化液,再在95℃条件下用260g/L的碳酸钠溶液沉锂得到电池级碳酸锂。The cathode material recovered from the disassembly and recycling of waste lithium iron phosphate batteries is crushed and passed through a 60-mesh screen. The material under the screen is taken to obtain ≤60-mesh lithium iron phosphate waste fine powder, and then the lithium iron phosphate waste fine powder is processed in a rotary kiln. Roast at 600°C for 1.0h, cool to below 60°C and perform mechanical crushing and ball milling to 80 mesh. Then roast and crush the fine powder clinker and dilute sulfuric acid and stir and leach at 60°C for 1.0h. The stirring intensity is 400rpm, and the liquid-to-solid ratio is 3:1, the pH of the post-leaching liquid is controlled between 2-3. When the pH is high, add acid and continue the reaction until the pH stabilizes at 2-3 and there is no change within half an hour. The leaching reaction is completed. After the leaching reaction is completed, use caustic soda to adjust the reaction. After the pH is between 4 and 5.5, a plate and frame filter press is used to separate solid and liquid to obtain a lithium-containing solution and leaching residue; after washing the leaching residue, the lithium ion concentration in the residue is 0.03wt%, and the recovery rate of lithium is 97.2%; lithium-containing solution After adjusting the pH of the solution to 12 with sodium hydroxide, add sodium carbonate to remove calcium and magnesium ions according to the calcium and magnesium content in the solution and an excess of 5% to obtain a lithium-containing purification solution, and then use 260g/L sodium carbonate solution to precipitate lithium at 95°C. Obtain battery grade lithium carbonate.

实施例Example

将废旧磷酸铁锂电池拆解回收的正极材料进行破碎后过60目筛网,取筛下物料得到≤60目磷酸铁锂废料细粉料,再将磷酸铁锂废料细粉料在回转窑中400℃焙烧4.0h,冷却至60℃以下后进行机械破碎球磨至100目,再将焙烧破碎细粉熟料和盐酸在60℃条件下搅拌浸出2.0h、搅拌强度为600rpm,液固比为4:1,浸出后液pH控制在2-3之间,pH偏高时补酸继续反应直到pH稳定在2-3且半小时内无变化浸出反应才完成,浸出反应完成后用片碱回调pH在4-5.5之间后用板框压滤机固液分离后得到含锂溶液和浸出渣;浸出渣经过洗涤后渣中锂离子浓度为0.05wt%,锂的回收率96.5%;含锂溶液用氢氧化钠调节pH至13后再根据溶液中钙镁含量并过量5%加入碳酸钠除钙镁离子得到含锂净化液,再在90℃条件下用280g/L的碳酸钠溶液沉锂得到电池级碳酸锂。The cathode material recovered from the disassembly and recycling of waste lithium iron phosphate batteries is crushed and passed through a 60-mesh screen. The material under the screen is taken to obtain ≤60-mesh lithium iron phosphate waste fine powder, and then the lithium iron phosphate waste fine powder is processed in a rotary kiln. Roast at 400°C for 4.0h, cool to below 60°C and then perform mechanical crushing and ball milling to 100 mesh, then roast and crush the fine powder clinker and hydrochloric acid, stir and leaching at 60°C for 2.0h, the stirring intensity is 600rpm, and the liquid-to-solid ratio is 4 :1. The pH of the liquid after leaching is controlled between 2-3. When the pH is high, add acid and continue the reaction until the pH stabilizes at 2-3 and there is no change within half an hour. The leaching reaction is completed. After the leaching reaction is completed, use caustic soda to adjust the pH. After solid-liquid separation using a plate and frame filter press between 4 and 5.5, the lithium-containing solution and leaching residue are obtained; the lithium ion concentration in the leaching residue after washing is 0.05wt%, and the lithium recovery rate is 96.5%; the lithium-containing solution Use sodium hydroxide to adjust the pH to 13, then add sodium carbonate to remove calcium and magnesium ions according to the calcium and magnesium content in the solution and an excess of 5% to obtain a lithium-containing purification solution, and then use 280g/L sodium carbonate solution to precipitate lithium at 90°C to obtain Battery grade lithium carbonate.

实施例Example

将废旧磷酸铁锂电池拆解回收的正极材料进行破碎后过60目筛网,取筛下物料得到≤60目磷酸铁锂废料细粉料,再将磷酸铁锂废料细粉料在回转窑中700℃焙烧1.5h,冷却至60℃以下后进行机械破碎球磨至150目,再将焙烧破碎细粉熟料和稀硫酸在60℃条件下搅拌浸出2.0h、搅拌强度为600rpm,液固比为5:1,浸出后液pH控制在2-3之间,pH偏高时补酸继续反应直到pH稳定在2-3且半小时内无变化浸出反应才完成,浸出反应完成后用片碱回调pH在4-5.5之间后用板框压滤机固液分离后得到含锂溶液和浸出渣;浸出渣经过洗涤后渣中锂离子浓度为0.02wt%,锂的回收率98.6%;含锂溶液用氢氧化钠调节pH至13后再根据溶液中钙镁含量并过量5%加入碳酸钠除钙镁离子得到含锂净化液,再在95℃条件下用275g/L的碳酸钠溶液沉锂得到电池级碳酸锂。The cathode material recovered from the disassembly and recycling of waste lithium iron phosphate batteries is crushed and passed through a 60-mesh screen. The material under the screen is taken to obtain ≤60-mesh lithium iron phosphate waste fine powder, and then the lithium iron phosphate waste fine powder is processed in a rotary kiln. Roast at 700°C for 1.5h, cool to below 60°C and then perform mechanical crushing and ball milling to 150 mesh. Then roast and crush the fine powder clinker and dilute sulfuric acid and stir and leaching at 60°C for 2.0h. The stirring intensity is 600rpm, and the liquid-to-solid ratio is 5:1, the pH of the post-leaching liquid is controlled between 2-3. When the pH is high, add acid and continue the reaction until the pH stabilizes at 2-3 and there is no change within half an hour. The leaching reaction is completed. After the leaching reaction is completed, use caustic soda to adjust the reaction. After the pH is between 4 and 5.5, use a plate and frame filter press to separate the solid and liquid to obtain a lithium-containing solution and leaching residue; after washing the leaching residue, the lithium ion concentration in the residue is 0.02wt%, and the recovery rate of lithium is 98.6%; lithium-containing solution After adjusting the pH of the solution to 13 with sodium hydroxide, add sodium carbonate to remove calcium and magnesium ions according to the calcium and magnesium content in the solution and an excess of 5% to obtain a lithium-containing purification solution, and then use 275g/L sodium carbonate solution to precipitate lithium at 95°C. Obtain battery grade lithium carbonate.

将废旧磷酸铁锂电池拆解回收的正极材料进行破碎后过100目筛网,取筛下物料得到≤100目磷酸铁锂废料细粉料,再将磷酸铁锂废料细粉料和稀硫酸、双氧水在80℃条件下搅拌浸出10h、35%双氧水的用量为1吨磷酸铁锂废料细粉料加0.45吨双氧水,搅拌强度为600rpm,液固比为4:1,浸出后液pH控制在2-3之间,pH偏高时补酸继续反应直到pH稳定在2-3且半小时内无变化浸出反应才完成,浸出反应完成后用片碱回调pH在4-5.5之间后用板框压滤机固液分离后得到含锂溶液和浸出渣;浸出渣经过洗涤后渣中锂离子浓度为0.08wt%,锂的回收率91.4%;含锂溶液用氢氧化钠调节pH至13后再根据溶液中钙镁含量并过量5%加入碳酸钠除钙镁离子得到含锂净化液,再在90℃条件下用280g/L的碳酸钠溶液沉锂得到电池级碳酸锂。The cathode material recovered from the disassembly and recycling of waste lithium iron phosphate batteries is crushed and passed through a 100-mesh screen. The material under the screen is taken to obtain ≤100-mesh lithium iron phosphate waste fine powder, and then the lithium iron phosphate waste fine powder and dilute sulfuric acid, The hydrogen peroxide is stirred and leached at 80°C for 10 hours. The dosage of 35% hydrogen peroxide is 1 ton of lithium iron phosphate waste fine powder plus 0.45 ton of hydrogen peroxide. The stirring intensity is 600 rpm, the liquid-to-solid ratio is 4:1, and the pH of the liquid after leaching is controlled at 2 -3. When the pH is high, add acid and continue the reaction until the pH stabilizes at 2-3 and there is no change within half an hour. The leaching reaction is completed. After the leaching reaction is completed, use caustic soda to adjust the pH to 4-5.5 and then use a plate and frame. After solid-liquid separation in the filter press, the lithium-containing solution and leaching residue are obtained; after washing, the lithium ion concentration in the leaching residue is 0.08wt%, and the lithium recovery rate is 91.4%; the lithium-containing solution is adjusted to pH 13 with sodium hydroxide. According to the calcium and magnesium content in the solution and an excess of 5%, sodium carbonate is added to remove calcium and magnesium ions to obtain a lithium-containing purification solution, and then lithium is precipitated with 280g/L sodium carbonate solution at 90°C to obtain battery-grade lithium carbonate.

将废旧磷酸铁锂电池拆解回收的正极材料进行破碎后过100目筛网,取筛下物料得到≤100目磷酸铁锂废料细粉料,再将磷酸铁锂废料细粉料和稀硫酸、氯酸钠在60℃条件下搅拌浸出4h、氯酸钠的用量为1吨磷酸铁锂废料细粉料加0.12吨氯酸钠,搅拌强度为600rpm,液固比为4:1,浸出后液pH控制在2-3之间,pH偏高时补酸继续反应直到pH稳定在2-3且半小时内无变化浸出反应才完成,浸出反应完成后用片碱回调pH在4-5.5之间后用板框压滤机固液分离后得到含锂溶液和浸出渣;浸出渣经过洗涤后渣中锂离子浓度为0.07wt%,锂的回收率95.6%;含锂溶液用氢氧化钠调节pH至13后再根据溶液中钙镁含量并过量5%加入碳酸钠除钙镁离子得到含锂净化液,再在90℃条件下用280g/L的碳酸钠溶液沉锂得到电池级碳酸锂。The cathode material recovered from the disassembly and recycling of waste lithium iron phosphate batteries is crushed and passed through a 100-mesh screen. The material under the screen is taken to obtain ≤100-mesh lithium iron phosphate waste fine powder, and then the lithium iron phosphate waste fine powder and dilute sulfuric acid, Sodium chlorate is stirred and leached at 60°C for 4 hours. The dosage of sodium chlorate is 1 ton of lithium iron phosphate waste fine powder plus 0.12 ton of sodium chlorate. The stirring intensity is 600rpm, and the liquid-to-solid ratio is 4:1. After leaching, the liquid The pH is controlled between 2-3. When the pH is high, acid supplementation continues to react until the pH stabilizes at 2-3 and there is no change within half an hour before the leaching reaction is completed. After the leaching reaction is completed, use caustic soda to adjust the pH to between 4-5.5. After solid-liquid separation using a plate and frame filter press, the lithium-containing solution and leaching residue are obtained; the lithium ion concentration in the leaching residue after washing is 0.07wt%, and the lithium recovery rate is 95.6%; the pH of the lithium-containing solution is adjusted with sodium hydroxide. After 13 days, sodium carbonate is added to remove calcium and magnesium ions according to the calcium and magnesium content in the solution and an excess of 5% to obtain a lithium-containing purification solution, and then lithium is precipitated with 280g/L sodium carbonate solution at 90°C to obtain battery-grade lithium carbonate.

以上所述仅为本发明的实施例,应当指出,对于本技术领域的普通技术人员来说,在不脱离本发明技术原理的前提下,可以对这些实施例进行多种变化、修改、替换和变型,这些变化、修改、替换和变型,也应视为本发明的保护范围。The above are only embodiments of the present invention. It should be noted that those of ordinary skill in the art can make various changes, modifications, replacements and modifications to these embodiments without departing from the technical principles of the present invention. Variations, these changes, modifications, replacements and modifications should also be regarded as the protection scope of the present invention.

Claims (9)

1. The method for extracting lithium from the waste lithium iron phosphate battery is characterized by comprising the following specific steps:
1) Crushing: crushing and sieving the positive electrode material recovered by disassembling the waste lithium iron phosphate battery to obtain lithium iron phosphate waste fine powder;
2) Roasting: roasting the lithium iron phosphate waste fine powder at a high temperature by a rotary kiln, and mechanically crushing and ball milling after roasting to obtain roasting and crushing fine powder;
3) Leaching callback impurity removal: fully stirring the roasting and crushing fine powder clinker and an acid solution to leach, adjusting the pH value, and then carrying out solid-liquid separation to obtain a lithium-containing solution and leaching residues;
4) Purifying solution: adding sodium hydroxide and sodium carbonate into the lithium-containing solution to remove impurities, and then precipitating lithium with sodium carbonate to prepare the battery grade lithium carbonate.
2. The method for extracting lithium from waste lithium iron phosphate batteries according to claim 1, wherein the lithium content of the lithium iron phosphate waste fine powder in the step 1) is 2.5-4.4%, and the fineness is less than or equal to 60 meshes.
3. The method for extracting lithium from waste lithium iron phosphate batteries according to claim 1, wherein the roasting temperature of the rotary kiln in the step 2) is 400-800 ℃ and the roasting time is 0.5-4h.
4. The method for extracting lithium from waste lithium iron phosphate batteries according to claim 1, wherein the fineness of the roasting and crushing fine powder in the step 2) is 60-200 meshes.
5. The method for extracting lithium from waste lithium iron phosphate batteries according to claim 1, wherein the acid solution in the step 3) is at least one of sulfuric acid, hydrochloric acid and acetic acid.
6. The method for extracting lithium from waste lithium iron phosphate battery according to claim 1, wherein the leaching temperature in the step 3) is 30-80 ℃, the leaching time is 0.5-6.0h, the stirring intensity is 100-600rpm, and the pH of the solution after leaching is 2-3.
7. The method for extracting lithium from the waste lithium iron phosphate battery according to claim 1, wherein the step 3) is performed with at least one of caustic soda and slaked lime, and the pH after the callback is 4-5.5.
8. The method for extracting lithium from waste lithium iron phosphate batteries according to claim 1, wherein the impurity removal method in the step 4) is to remove impurities by adjusting the pH to 11-13 with sodium hydroxide and adding sodium carbonate according to the content of calcium and magnesium in the solution and 5% excess.
9. The method for extracting lithium from waste lithium iron phosphate batteries according to claim 1, wherein the temperature in the lithium precipitation process in the step 4) is not less than 85 ℃, and the concentration of sodium carbonate is 180-300g/L.
CN202310824402.2A 2023-07-06 2023-07-06 A method for extracting lithium from waste lithium iron phosphate batteries Pending CN116814984A (en)

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CN106450547A (en) * 2016-10-19 2017-02-22 荆门市格林美新材料有限公司 Method for recycling iron phosphate and lithium carbonate from lithium iron phosphate waste
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