CN110760682A - Process for selective recovery of lithium from spent lithium iron phosphate batteries by means of mechanochemical activation - Google Patents

Process for selective recovery of lithium from spent lithium iron phosphate batteries by means of mechanochemical activation Download PDF

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CN110760682A
CN110760682A CN201911072005.4A CN201911072005A CN110760682A CN 110760682 A CN110760682 A CN 110760682A CN 201911072005 A CN201911072005 A CN 201911072005A CN 110760682 A CN110760682 A CN 110760682A
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张付申
阿来拉姑
张聪聪
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Research Center for Eco Environmental Sciences of CAS
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    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B7/00Working up raw materials other than ores, e.g. scrap, to produce non-ferrous metals and compounds thereof; Methods of a general interest or applied to the winning of more than two metals
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    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
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    • H01MPROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
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Abstract

本发明提供一种选择性回收废旧磷酸铁锂电池正极材料的工艺,属于环境保护和资源综合利用领域的固体废弃物资源化新技术,其核心是首先进行机械活化,通过添加共磨剂达到优异的活化效果;随后利用复合浸出剂,将磷酸铁锂电池正极材料中的锂选择性浸出到溶液中,此时锂和铁完全分离,铁和磷以磷酸铁沉淀的形式与碳粉进入浸出残渣中,实现铁和磷的原位回收。本发明提供的工艺具有流程短、操作简单、能耗低、对环境友好、不产生二次污染的特点,应用前景广阔。

Figure 201911072005

The invention provides a process for selectively recovering positive electrode materials of waste lithium iron phosphate batteries, which belongs to the new technology of solid waste recycling in the field of environmental protection and comprehensive utilization of resources. Then, the lithium in the cathode material of the lithium iron phosphate battery is selectively leached into the solution by using the composite leaching agent. At this time, the lithium and iron are completely separated, and the iron and phosphorus enter the leaching residue with the carbon powder in the form of iron phosphate precipitation. In situ recovery of iron and phosphorus is achieved. The process provided by the invention has the characteristics of short process flow, simple operation, low energy consumption, environmental friendliness and no secondary pollution, and has broad application prospects.

Figure 201911072005

Description

借助机械化学活化法选择性回收废旧磷酸铁锂电池中锂的 工艺Selective recovery of lithium from spent lithium iron phosphate batteries by means of a mechanochemical activation method craft

技术领域technical field

本发明涉及一种废旧磷酸铁锂动力电池无害化处理与有价元素回收方法,属于环境保护和资源综合利用领域的固体废弃物资源化新技术,尤其适合于各类含锂废旧电池中锂的选择性回收。The invention relates to a method for the harmless treatment and recovery of valuable elements of waste lithium iron phosphate power batteries, belonging to a new technology of solid waste recycling in the fields of environmental protection and comprehensive utilization of resources, and is especially suitable for lithium in various types of waste lithium-containing batteries. selective recycling.

背景技术Background technique

磷酸铁锂电池具有比能量密度大、循环性能好等优点,广泛应用于电动汽车、混合动力电动车等车辆作为动力源。随着新能源汽车产业迅猛发展,动力电池有限的使用年限导致大量废旧磷酸铁锂电池退役,清洁回收有价金属尤其是战略金属锂具有重要的资源和经济效益。Lithium iron phosphate batteries have the advantages of high specific energy density and good cycle performance, and are widely used in electric vehicles, hybrid electric vehicles and other vehicles as power sources. With the rapid development of the new energy vehicle industry, the limited service life of power batteries has led to the retirement of a large number of waste lithium iron phosphate batteries. Clean recovery of valuable metals, especially strategic metal lithium, has important resources and economic benefits.

目前对废旧磷酸铁锂电池处理的主要关注点是提取正极材料中的有价金属,如锂、铁。正极片中分离回收有价金属的方法一般是先将废旧锂离子电池放电后进行拆解预处理得到含活性物质的正极片,再对正极片进行剥离后得到含锂正极材料。正极材料中有价元素的回收方法主要是通过采用无机酸或有机酸将正极材料浸出后,再将各元素分步沉淀,最终将有价元素作为单独的化合物进行回收,但是浸出时通常会使用过量的酸,残余的酸液排入水体中会对环境造成严重的污染,对人居环境造成破。另外,传统的酸浸技术存在回收成本高、处理流程长、浸出选择性差、浸出速度慢等问题,因此,寻找回收成本低、回收率高、浸出速度快的一种废磷酸铁锂正极材料的回收方法具有重要意义。At present, the main focus of the treatment of waste lithium iron phosphate batteries is to extract valuable metals such as lithium and iron from the cathode material. The method for separating and recovering valuable metals from the positive electrode sheet is generally to first discharge the waste lithium ion battery, disassemble and pretreat to obtain a positive electrode sheet containing an active material, and then peel off the positive electrode sheet to obtain a lithium-containing positive electrode material. The recovery method of the valuable elements in the positive electrode material is mainly by leaching the positive electrode material with inorganic acid or organic acid, and then precipitating each element step by step, and finally recovering the valuable element as a separate compound, but it is usually used in leaching. Excessive acid and residual acid discharged into the water body will cause serious pollution to the environment and damage to the living environment. In addition, the traditional acid leaching technology has problems such as high recovery cost, long treatment process, poor leaching selectivity, and slow leaching speed. Therefore, it is necessary to find a waste lithium iron phosphate cathode material with low recovery cost, high recovery rate and fast leaching speed. Recycling methods are important.

由于机械化学活化过程中产生的能量可以影响物质的物理和化学性能,如原位增强或操纵离子扩散,减小颗粒尺寸、增加比表面积、造成晶体结构中的点缺陷和位错、降低反应活化能、增强反应活性等,近年来在金属回收利用领域引起了研究人员的广泛关注,用这种方法替代传统的湿法冶金工艺来回收铁和锂,可有效地减少试剂、能源损耗及二次污染的排放,提高金属的回收率及回收选择性。Since the energy generated during mechanochemical activation can affect the physical and chemical properties of substances, such as in situ enhancement or manipulation of ion diffusion, reducing particle size, increasing specific surface area, causing point defects and dislocations in the crystal structure, reducing reaction activation In recent years, researchers have attracted extensive attention in the field of metal recycling. Using this method to replace the traditional hydrometallurgical process to recover iron and lithium can effectively reduce reagent, energy consumption and secondary Pollution emissions, improve metal recovery rate and recovery selectivity.

发明内容SUMMARY OF THE INVENTION

本发明的目的在于克服传统湿法冶金过程缓慢,浸出率低、流程繁琐、成本高、二次污染等不足,开发一种能够以简单快速、浸出率高、无二次污染、环保的方式,实现锂的高选择性浸出,同时原位回收磷和铁,实现废旧磷酸铁锂电池附加值的资源化回收利用。其特征在于:通过加入共磨剂,依靠机械化学活化产生的高能量破坏物质原有的晶相,改变物质的物理和化学性能从而诱导后续浸出剂的化学反应,高选择性的浸出锂,避免传统的湿法冶金存在的问题。The purpose of the present invention is to overcome the shortcomings of traditional hydrometallurgy process such as slow process, low leaching rate, cumbersome process, high cost, secondary pollution, etc. It realizes the highly selective leaching of lithium, and at the same time recovers phosphorus and iron in situ, and realizes the resource recovery and utilization of the added value of waste lithium iron phosphate batteries. It is characterized in that: by adding a co-grinding agent, relying on the high energy generated by mechanochemical activation to destroy the original crystal phase of the material, changing the physical and chemical properties of the material to induce the chemical reaction of the subsequent leaching agent, leaching lithium with high selectivity, avoiding Problems with traditional hydrometallurgy.

本发明按以下步骤完成:The present invention is completed according to the following steps:

前处理工序:首先将废旧磷酸铁锂电池置于氯化钠溶液中浸泡24h进行放电,然后进行人工拆解分类回收利用,负极片进行剥离后回收铜箔和碳粉,正极片在管式炉中氮气氛围下360℃焙烧2h后实现铝箔和正极材料的分离;Pre-treatment process: First, the waste lithium iron phosphate battery is soaked in sodium chloride solution for 24 hours for discharge, and then manually disassembled, classified and recycled. The negative electrode sheet is peeled off and then the copper foil and carbon powder are recovered. The separation of aluminum foil and cathode material was achieved after calcination at 360 °C for 2 h in a medium nitrogen atmosphere;

机械化学活化工序:取上述剥离后的正极材料,置于已加入3-10ml水的氧化锆球磨罐中,加入共磨剂,共磨剂与正极材料的摩尔比为1:1,密封后在600rpm的转速下,顺逆时针各研磨15min,设置2min的球磨间隙散去球磨时产生的热量;Mechanochemical activation process: take the above-mentioned peeled positive electrode material, place it in a zirconia ball mill jar with 3-10ml of water added, add a co-grinding agent, and the molar ratio of the co-grinding agent and the positive electrode material is 1:1, and after sealing, At a speed of 600rpm, grind clockwise and counterclockwise for 15 minutes each, and set a ball milling gap of 2 minutes to dissipate the heat generated during ball milling;

浸出工序:将球磨后的材料用去离子水清洗三次后转移到锥形瓶中,加入1vol.%-6vol.%的双氧水,开启磁力搅拌器,在设定的温度下进行搅拌浸出,温度设定范围为25℃-80℃,浸出时间设定为10min-60min,浸出转速固定在400rpm;Leaching process: The ball-milled material was washed three times with deionized water and then transferred to a conical flask, adding 1vol.%-6vol.% hydrogen peroxide, turning on the magnetic stirrer, stirring and leaching at the set temperature, and the temperature was set. The fixed range is 25℃-80℃, the leaching time is set at 10min-60min, and the leaching speed is fixed at 400rpm;

沉淀工序:上述浸出反应结束后,进行真空抽滤分离浸出残渣和浸出液,烘干浸出残渣,测定浸出液的pH值后加入氢氧化钠溶液调节pH值介于11-13,随后加入化学计量比为摩尔比1.05:1的磷酸钠进行锂的沉淀回收。Precipitation process: after the above-mentioned leaching reaction finishes, carry out vacuum filtration to separate leaching residue and leaching solution, dry leaching residue, measure the pH value of leaching solution, add sodium hydroxide solution to adjust pH value between 11-13, then add stoichiometric ratio as Lithium was recovered by precipitation with sodium phosphate in a molar ratio of 1.05:1.

本工艺具有以下特点:This process has the following characteristics:

本工艺使用的正极材料经过焙烧剥离后不引入铝、铜等杂质,避免锂的损失,焙烧过程中产生的气体用碱液进行处理,不造成大气污染;The cathode material used in this process does not introduce impurities such as aluminum and copper after roasting and stripping, so as to avoid the loss of lithium, and the gas generated in the roasting process is treated with alkaline solution, which does not cause atmospheric pollution;

传统的湿法冶金浸出废旧磷酸铁锂电池中的有价金属过程中产生大量的酸性废液,造成二次污染,本工艺具备反应温度低、操作简便、产品附加值高的特点,可以有效的避免二次污染的产生;The traditional hydrometallurgical leaching of valuable metals in waste lithium iron phosphate batteries produces a large amount of acidic waste liquid, causing secondary pollution. This process has the characteristics of low reaction temperature, simple operation and high added value of products, which can effectively Avoid secondary pollution;

本发明采用的机械化学活化法可以有效减少试剂的用量,锂可以完全浸出,锂和铁分离完全,锂以磷酸锂的形式回收,铁以磷酸铁的形式回收,两者都可以用于磷酸铁锂正极材料的再制备;The mechanochemical activation method adopted in the present invention can effectively reduce the dosage of reagents, lithium can be completely leached, lithium and iron are completely separated, lithium is recovered in the form of lithium phosphate, and iron is recovered in the form of iron phosphate, both of which can be used for iron phosphate Re-preparation of lithium cathode materials;

本发明实现了废旧磷酸铁锂电池的无害化处理以及绿色环保地回收有价金属,实现了二次资源的再利用。The invention realizes the harmless treatment of waste and old lithium iron phosphate batteries and the recovery of valuable metals in a green and environment-friendly manner, thereby realizing the reuse of secondary resources.

附图说明Description of drawings

为进一步了解本发明,下面用附图描述本发明工艺流程、浸出渣的物相、锂的沉淀物物相。In order to further understand the present invention, the following describes the process flow of the present invention, the phase of the leaching residue, and the phase of the lithium precipitate with the accompanying drawings.

图1是废旧磷酸铁锂电池无害化处理及回收有价金属的工艺流程图。Fig. 1 is the process flow chart of the harmless treatment of waste lithium iron phosphate batteries and the recovery of valuable metals.

图2是废旧磷酸铁锂电池正极材料机械化学活化浸出残渣的物相图。Fig. 2 is the phase diagram of the leaching residue of mechanochemical activation of the cathode material of waste lithium iron phosphate battery.

图3是废旧磷酸铁锂电池正极材料机械化学活化浸出液沉淀物的物相图。FIG. 3 is a phase diagram of the mechanochemically activated leachate precipitate of the cathode material of waste lithium iron phosphate battery.

具体实施方式Detailed ways

下面将通过具体的实施例对本发明的制备方法作进一步说明,但本发明并不限于这些实施例。The preparation method of the present invention will be further described below through specific examples, but the present invention is not limited to these examples.

实施例1Example 1

根据图1流程图,废旧磷酸铁锂电池放电后收集正极片,用剪刀将正极片剪成4*2cm的小长条置于管式炉中氮气氛围下360℃焙烧2h后取出,得到铝箔和正极材料;以正极材料LiFePO4为原料,加入适量的水和化学计量比的共磨剂进行机械化学活化处理,在600rpm转速下研磨30min后转入圆底锥形瓶,加入 4vol.%的浸出剂溶液,浸出60min后进行固液分离收集浸出液及浸出残渣(图2);浸出液在105℃蒸发水分数小时,剩余适量的含锂溶液移至水温为85℃的水浴锅中进行磁力搅拌,测定锂含量后加入适量的磷酸钠,搅拌两小时后分离固液体,回收沉淀物(图3);分析结果表明,浸出过程中锂浸出率高于99.80%,回收率铁100%、锂89.50%左右。According to the flow chart in Figure 1, the positive electrode sheet is collected after the waste lithium iron phosphate battery is discharged, and the positive electrode sheet is cut into small strips of 4*2cm with scissors and placed in a tube furnace under nitrogen atmosphere at 360 °C for 2 hours. Positive electrode material: Take positive electrode material LiFePO 4 as raw material, add an appropriate amount of water and a stoichiometric ratio of co-grinding agent for mechanochemical activation treatment, grind at 600 rpm for 30 min, transfer to a round-bottomed conical flask, add 4 vol.% leaching agent After leaching for 60 min, solid-liquid separation was performed to collect the leaching solution and leaching residue (Fig. 2); the leaching solution was evaporated at 105 °C for an hour, and the remaining appropriate amount of lithium-containing solution was moved to a water bath with a water temperature of 85 °C for magnetic stirring. After the lithium content, an appropriate amount of sodium phosphate was added, and the solid and liquid were separated after stirring for two hours, and the precipitate was recovered (Figure 3). .

实施例2Example 2

根据图1流程图,废旧磷酸铁锂电池放电后收集正极片,用剪刀将正极片剪成4*2cm的小长条置于管式炉中氮气氛围下360℃焙烧2h后取出,得到铝箔和正极材料;以正极材料LiFePO4为原料,加入适量的水和化学计量比的复配共磨剂进行机械化学活化处理,其中磷酸铁锂与共磨剂的摩尔比为1:0.5:0.5,在 600rpm转速下研磨30min后转入圆底锥形瓶,加入4vol.%的浸出剂溶液,浸出60min后进行固液分离收集浸出液及浸出残渣;浸出液在105℃蒸发水分数小时,剩余适量的含锂溶液移至水温为85℃的水浴锅中进行磁力搅拌,测定锂含量后加入适量的磷酸钠,搅拌两小时后分离固液体,回收沉淀物;分析结果表明,浸出过程中锂浸出率高于99.80%,回收率铁为100%、锂为89.50%左右。According to the flow chart in Figure 1, the positive electrode sheet is collected after the waste lithium iron phosphate battery is discharged, and the positive electrode sheet is cut into small strips of 4*2cm with scissors and placed in a tube furnace under nitrogen atmosphere at 360 °C for 2 hours. Positive electrode material; take positive electrode material LiFePO 4 as raw material, add an appropriate amount of water and a stoichiometric ratio of compound co-grinding agent for mechanochemical activation treatment, wherein the molar ratio of lithium iron phosphate and co-grinding agent is 1:0.5:0.5, at 600rpm After grinding for 30 minutes at the rotating speed, transfer it to a round-bottomed conical flask, add 4 vol.% leaching agent solution, and carry out solid-liquid separation after leaching for 60 minutes to collect the leaching solution and the leaching residue; the leaching solution is evaporated at 105 ° C for a few hours, and an appropriate amount of lithium-containing solution remains. Move to a water bath with a water temperature of 85°C for magnetic stirring, add an appropriate amount of sodium phosphate after measuring the lithium content, separate the solid and liquid after stirring for two hours, and recover the precipitate; the analysis results show that the lithium leaching rate during the leaching process is higher than 99.80% , the recovery rate of iron is 100% and lithium is about 89.50%.

上述实例仅仅是为了说明本发明的应用性,并非对实施方式的限制。废旧锂离子电池可选用锰酸锂、钴酸锂等锂电池。本发明不限于上述所举实施案例,所述内容均可实施,并有良好的效果。The above examples are only for illustrating the applicability of the present invention, and are not intended to limit the implementation. Waste lithium-ion batteries can be selected from lithium manganate, lithium cobaltate and other lithium batteries. The present invention is not limited to the above-mentioned implementation cases, and the content can be implemented with good effects.

Claims (5)

1. The process for selectively recovering lithium in the waste lithium iron phosphate batteries by means of a mechanochemical activation method is characterized by comprising the following steps:
(1) soaking the waste lithium iron phosphate battery in saturated saline water for 24 hours for discharging, then disassembling and separating to obtain a shell, a diaphragm, a negative plate and a positive plate, wherein the positive plate of the battery is a required experimental raw material, and the negative plate and the diaphragm are uniformly recovered for resource treatment;
(2) baking the obtained positive plateBurning and separating the anode material and the aluminum foil to obtain the anode material LiFePO4
(3) And (3) mixing the positive electrode material and the grinding aid in a weight ratio of 1:1, adding the mixture into a ball milling tank, then adding water, wherein the weight of the water is equal to the sum of the weights of the grinding aid and the anode material, and grinding for 15min clockwise and anticlockwise respectively at the rotating speed of 600 rpm;
(4) washing the sample subjected to mechanochemical activation for 2 times by using deionized water, adding a leaching agent, leaching for 1h to obtain a lithium-containing solution and leaching residues containing iron, phosphorus and carbon powder, and combining the phosphorus and the iron into an iron phosphate precipitate;
(5) adjusting the pH value of the lithium-containing solution to 11-13 by using 1.5M sodium hydroxide, then adding sodium phosphate into the solution, wherein the adding amount of the sodium phosphate is 1/3 which is equivalent to the mole number of lithium ions in the solution, then heating and stirring the solution at 90 ℃ for about 2 hours, and filtering the solution to obtain a precipitate, namely the product lithium phosphate.
2. The process as set forth in claim 1, characterized in that: in the step (2), the roasting atmosphere is nitrogen, the temperature is 360 ℃, and the time is 2 h.
3. The process as set forth in claim 1, characterized in that: the grinding aid in the step (2) is a mixture of two or more of ferrous sulfide, sodium sulfate, ammonium chloride, ferrous chloride, sodium phosphate, ammonium ferric phosphate and ammonium phosphate.
4. The process as set forth in claim 1, characterized in that: in the step (4), the leaching agent is a mixture of two or more of sodium thiosulfate, sodium bicarbonate, hydrogen peroxide, sodium hypochlorite, sodium pyrophosphate and ferric chloride.
5. The process as set forth in claim 1, characterized in that: the adding amount of the leaching agent in the step (4) is calculated according to the mole number of lithium ions in the solution, the leaching temperature is 80 ℃, and the leaching solid-liquid ratio is 50 g: 1000mL, leaching time 50 min.
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