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CN1287481C - Method for recovering valuable metals from waste secondary batteries - Google Patents

Method for recovering valuable metals from waste secondary batteries Download PDF

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CN1287481C
CN1287481C CNB2003101035847A CN200310103584A CN1287481C CN 1287481 C CN1287481 C CN 1287481C CN B2003101035847 A CNB2003101035847 A CN B2003101035847A CN 200310103584 A CN200310103584 A CN 200310103584A CN 1287481 C CN1287481 C CN 1287481C
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nickel
cadmium
metal
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cobalt
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CN1617380A (en
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林俊仁
张怡隆
江玉琳
许哲源
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Industrial Technology Research Institute ITRI
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    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
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    • Y02W30/84Recycling of batteries or fuel cells

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Abstract

The invention relates to a new technology for recovering metal and valuable resources from waste lithium ion/nickel-hydrogen/nickel-cadmium batteries. The method of the invention is to roast the used waste lithium ion/nickel-hydrogen/nickel-cadmium battery in a high temperature furnace and sieve the battery to produce fine powder containing metal and metal oxide. The fine powder is dissolved and filtered in two stages, cadmium sulfate is crystallized and separated out from the filtrate obtained by the first stage dissolution and filtration, and iron, aluminum and rare earth metals are precipitated and recovered by hydroxide by adjusting the pH value of the filtrate obtained by the second stage dissolution and filtration. The remaining filtrate is subjected to extraction and back extraction procedures to obtain two aqueous solutions containing cobalt and nickel, which are then electrolyzed to separate out high-purity cobalt and nickel metals. The residual aqueous solution after nickel metal electrolysis is added with a water-soluble carbonate to precipitate lithium ions in the aqueous solution as carbonate.

Description

从废二次电池回收有价金属的方法Method for recovering valuable metals from waste secondary batteries

                          技术领域Technical field

本发明是有关一种从废锂离子/镍氢/镍镉电池中回收有价金属的方法。The invention relates to a method for recovering valuable metals from waste lithium-ion/nickel-hydrogen/nickel-cadmium batteries.

                          背景技术 Background technique

锂离子电池由于其所具有的高电能量密度、高工作电压、循环寿命长及无记忆效应等各项优点,已经被公认为是最具发展潜力的电池系统,目前除了已经大量被应用于各项3C产品上外,并且可望于未来也取代镍镉及镍氢二次电池成为电动车动力来源。虽然如此,在某些特定应用上镍镉及镍氢电池仍然被广泛使用。因此目前在实际回收的废二次电池仍然可发现为数不少的镍镉及镍氢电池掺混于废锂离子电池中。也因此有需要开发出一种对混合的废二次电池有效率的有价金属回收方法。Due to its high energy density, high working voltage, long cycle life and no memory effect, lithium-ion batteries have been recognized as the battery system with the most development potential. At present, in addition to being widely used in various The 3C products are on the market, and are expected to replace nickel-cadmium and nickel-metal hydride secondary batteries as the power source of electric vehicles in the future. Even so, NiCd and NiMH batteries are still widely used in some specific applications. Therefore, a large number of nickel-cadmium and nickel-metal hydride batteries can still be found mixed in the waste lithium-ion batteries in the actual recovered waste secondary batteries. Therefore, there is a need to develop an efficient recovery method for valuable metals from mixed spent secondary batteries.

本案申请人在发明专利申请号CN01130735.8(平行的美国专利第6514311号)揭示了一种从废锂离子电池回收有价金属的方法,包括将使用过的废弃锂离子电池于高温炉中焙烧,分解除去有机电解质,粉碎后筛分,筛上物再以磁选及涡电流分选处理,分离出碎解的铁壳、铜箔与铝箔等;而筛下物则径行溶蚀、过滤,并借助pH值及电解条件的控制,分别以隔膜电解法电解析出金属铜与钴,电解过程中于阴极侧所产生的酸可经由扩散透析处理被回收并再循环至溶蚀步骤使用,成一封闭流程。而经电解后富含锂离子的溶液,在调整酸碱值沉淀金属杂质后,则可以添加碳酸根形成锂的高纯度碳酸盐而将锂回收。该案的内容以参考方式被并入本案。The applicant of this case discloses a method for recovering valuable metals from waste lithium-ion batteries in the invention patent application number CN01130735.8 (parallel U.S. Patent No. 6514311), including roasting the used waste lithium-ion batteries in a high-temperature furnace , decompose and remove the organic electrolyte, sieve after crushing, and then use magnetic separation and eddy current sorting to separate the broken iron shell, copper foil and aluminum foil, etc. With the control of pH value and electrolysis conditions, metal copper and cobalt are electrolyzed by diaphragm electrolysis, and the acid generated on the cathode side during the electrolysis process can be recovered through diffusion dialysis and recycled to the dissolution step, forming a closed process . And the solution rich in lithium ions after electrolysis, after adjusting the pH value to precipitate metal impurities, can add carbonate to form high-purity carbonate of lithium to recover lithium. The content of that case is incorporated by reference into this case.

                          发明内容Contents of Invention

本发明的目的是揭示一种从包含锂离子电池、镍氢电池及镍镉电池的废二次电池中回收有价金属的方法,其中该废二次电池经由焙烧、粉碎及筛分而产生一含金属及金属氧化物的灰状物,该方法包含下列步骤:The object of the present invention is to disclose a method for recovering valuable metals from waste secondary batteries including lithium-ion batteries, nickel-hydrogen batteries and nickel-cadmium batteries, wherein the waste secondary batteries produce a Ashes containing metals and metal oxides, the method comprises the following steps:

a)以含有过氧化氢的2当量摩尔浓度至6当量摩尔浓度硫酸水溶液溶蚀该灰状物;a) Dissolving the ashes with a sulfuric acid aqueous solution of 2 to 6 molar concentrations containing hydrogen peroxide;

b)将一碱加入步骤a)所产生的溶蚀溶液,而使得其中的镉、稀土金属离子产生结晶;b) adding an alkali to the corrosion solution produced in step a), so that the cadmium and rare earth metal ions therein are crystallized;

c)固液分离步骤b)的混合物;c) the mixture of solid-liquid separation step b);

d)以第一有机萃取剂对步骤c)所得到的水溶液进行萃取,而产生富含镍及钴离子的水层及富含镉、铁及锌离子的有机层;d) extracting the aqueous solution obtained in step c) with the first organic extractant to produce an aqueous layer rich in nickel and cobalt ions and an organic layer rich in cadmium, iron and zinc ions;

e)以第二有机萃取剂对步骤d)所得到的水层进行萃取,而产生富含钴离子的有机层及富含镍离子的水层;e) extracting the aqueous layer obtained in step d) with a second organic extractant to produce an organic layer rich in cobalt ions and an aqueous layer rich in nickel ions;

f)以硫酸水溶液反萃该富含钴离子的有机层,而产生富含钴离子的水层;f) back-extracting the organic layer rich in cobalt ions with aqueous sulfuric acid to produce an aqueous layer rich in cobalt ions;

g)以步骤e)所得到的富含镍离子的水层作为电解液使用一介于1.5~4.0伏特的电压进行电解,于是在一阴极上还原出镍金属;g) using the nickel-ion-rich water layer obtained in step e) as an electrolytic solution to perform electrolysis at a voltage of 1.5-4.0 volts, so that nickel metal is reduced on a cathode;

h)以步骤f)所得到的富含钴离子的水层作为电解液使用一介于1.5~4.0伏特的电压进行电解,于是在一阴极上还原出钴金属;及h) using the water layer rich in cobalt ions obtained in step f) as an electrolyte to perform electrolysis at a voltage of 1.5-4.0 volts, so that cobalt metal is reduced on a cathode; and

i)将一水可溶的碳酸盐加入于步骤g)电解后的电解液,而形成碳酸锂的沉淀。i) adding a water-soluble carbonate to the electrolytic solution after electrolysis in step g) to form a lithium carbonate precipitate.

较佳的,步骤a)及b)合并包含:Preferably, steps a) and b) are combined to include:

a1)以2当量摩尔浓度至6当量摩尔浓度的硫酸水溶液溶蚀该灰状物;a1) Dissolving the ashes with an aqueous sulfuric acid solution of 2 to 6 molar concentrations;

a2)固液分离步骤a1)的混合物;a2) the mixture of the solid-liquid separation step a1);

a3)以含有过氧化氢的4当量摩尔浓度至12当量摩尔浓度硫酸水溶液溶蚀步骤a2)所产生的固体;a3) dissolving the solid produced in step a2) with an aqueous sulfuric acid solution of 4 to 12 NM containing hydrogen peroxide;

b1)将步骤a2)所产生的溶蚀溶液中的一部分水蒸发移除,而获得一具有硫酸镉结晶为其主要部份的沉淀物;b1) evaporating part of the water in the corrosion solution produced in step a2) to obtain a precipitate with cadmium sulfate crystals as its main part;

b2)将一碱加入步骤a3)所产生的溶蚀溶液,而获得一具有稀土金属氢氧化物、Fe(OH)3及Al(OH)3为主要部份的沉淀物,b2) adding a base to the corrosion solution produced in step a3) to obtain a precipitate with rare earth metal hydroxides, Fe(OH ) and Al(OH ) as the main parts,

其中步骤b2)所产生的混合物被作为步骤c)固液分离的混合物。Wherein the mixture produced in step b2) is taken as the mixture of solid-liquid separation in step c).

更佳的,步骤b1)所产生的混合物被固液分离,且將固液分离所获得的液体用作为步骤a3)的4当量摩尔浓度至12当量摩尔浓度硫酸水溶液的一部分,且该沉淀物的约85重量%为硫酸镉。More preferably, the mixture produced in step b1) is separated from the solid-liquid, and the liquid obtained by the solid-liquid separation is used as a part of the aqueous solution of sulfuric acid from 4 NM to 12 NM in step a3), and the precipitate About 85% by weight is cadmium sulfate.

更佳的,步骤b2)的碱为氢氧化钠,且氢氧化钠的用量使得溶液pH值为6左右。More preferably, the alkali in step b2) is sodium hydroxide, and the amount of sodium hydroxide is such that the pH value of the solution is about 6.

较佳的,本发明方法的步骤i)的水可溶碳酸盐为碳酸钠。Preferably, the water-soluble carbonate in step i) of the method of the present invention is sodium carbonate.

较佳的,本发明方法进一步包含以硫酸水溶液反萃步骤d)中的富含镉、铁及锌离子的有机层,而得到富含镉、铁及锌离子的水层;及以离子交换树脂除去该水层中的镉、铁及锌离子。Preferably, the method of the present invention further comprises back-extracting the organic layer rich in cadmium, iron and zinc ions in step d) with sulfuric acid aqueous solution to obtain an aqueous layer rich in cadmium, iron and zinc ions; Cadmium, iron and zinc ions in the water layer are removed.

较佳的,本发明方法进一步包含将该焙烧后的产物加予破碎,并且于破碎过程中以20~5网目的筛网收集破碎产物。更佳的,本发明方法进一步包含以网目介于10~5目的筛网分离该破碎产物,而获得一通过该筛网的含金属及金属氧化物的灰状物及一不能通过该筛网的筛上物。Preferably, the method of the present invention further comprises crushing the calcined product, and collecting the crushed product with a 20-5 mesh screen during the crushing process. More preferably, the method of the present invention further comprises separating the crushed product with a sieve whose mesh size is between 10 and 5 meshes, so as to obtain an ashes containing metal and metal oxides passing through the sieve and an ash that cannot pass through the sieve. of the sieve.

较佳的,本发明方法进一步包含以磁选方式从该筛上物分离出铁。更佳的,本发明方法进一步包含以涡电流分选方式分离前述磁选后所产生的残余物中的铜及铝。Preferably, the method of the present invention further comprises separating iron from the oversize by magnetic separation. More preferably, the method of the present invention further includes separating copper and aluminum in the residue produced after the aforementioned magnetic separation by means of eddy current separation.

本发明以完整的物理分选单元,并搭配各金属特性所设计的化学纯化系统,可针对锂离子/镍氢/镍镉电池中所有金属进行完善的处理与回收,并可大幅提高金属的回收率及回收金属的质量。The present invention uses a complete physical separation unit and a chemical purification system designed with the characteristics of each metal to perform perfect treatment and recovery of all metals in lithium-ion/nickel-metal hydride/nickel-cadmium batteries, and can greatly improve the recovery of metals rate and quality of recovered metal.

实施方式Implementation

目前商用锂离子电池、镍氢电池及镍镉电池,依照其应用特性主要可分为圆筒型与方型两类,但不论其外观型态为何,多是将正极活性物质涂布于镍合金或铝箔上当成正极板,而以金属合金或石墨涂布于铜箔上当成负极板,两板间置入隔离膜,并填充电解液后再卷曲压缩成所需的规格,再接上导电柄、泄压安全阀及端盖等零件后,封上铁质或铝质罐体再套上塑料外壳即成型。因而在处理废锂离子/镍氢/镍镉电池时,所面对的金属种类不外乎铁、钴、镍、镉、铝、铜、锂及稀土金属元素,及非金属部分则主要为塑料、碳材或石墨。At present, commercial lithium-ion batteries, nickel-hydrogen batteries and nickel-cadmium batteries can be mainly divided into two types according to their application characteristics: cylindrical and square. Or the aluminum foil is used as the positive plate, and the metal alloy or graphite is coated on the copper foil as the negative plate. The separator is placed between the two plates, and the electrolyte is filled and then crimped and compressed to the required specifications, and then connected to the conductive handle. , Pressure relief safety valve and end cover and other parts, seal the iron or aluminum tank body and put it on the plastic shell to form. Therefore, when dealing with waste lithium-ion/nickel-metal hydride/nickel-cadmium batteries, the types of metals faced are nothing more than iron, cobalt, nickel, cadmium, aluminum, copper, lithium and rare earth metal elements, and the non-metallic parts are mainly plastics , carbon or graphite.

综观现行所发表的技术可发现,各个技术均只针对一项二次电池的处理与回收进行研究与探讨,然而在工业生产操作上,欲将回收的废二次电池料源按照镍氢、镍镉……有效进行分类,实有相当的困难度存在。若只考虑一种电池的处理流程,一但其它电池混掺其中造成杂质的干扰,很可能就超出了原本制程的容许度。Looking at the currently published technologies, it can be found that each technology only studies and discusses the treatment and recycling of one secondary battery. Cadmium... There is considerable difficulty in effectively classifying it. If only one type of battery treatment process is considered, once other batteries are mixed in to cause interference from impurities, it is likely to exceed the tolerance of the original manufacturing process.

本发明是一种从废锂离子/镍氢/镍镉电池中回收金属与有价资源的新技术,目的是以清洁湿式回收技术搭配物理分选法、以使所回收的各金属品质及回收率大幅提高。而本发明的方法主要仍是将使用过的废弃锂离子/镍氢/镍镉电池于高温炉中焙烧,分解除去有机物质后粉碎,再利用筛分筛目的选择,获得不同粒度的粉碎体,针对粗粒度的粉碎体,可径行以磁选分离回收碎解的铁壳,以涡电流分选回收铜箔及铝箔。而含有极板金属及金属氧化物的细粉体部分则被施予两阶段溶蚀及过滤处理。从第一阶段溶蚀及过滤所得的滤液中结晶析出硫酸镉或电解析出金属镉,及调整第二阶段溶蚀及过滤所得的滤液的pH值将铁、铝及稀土金属以氢氧化物分别沉淀回收。留下的滤液再经过一系列萃取及反萃取,可分别得到富含钴及镍的两水溶液。它们接着分别被电解析出钴及镍金属。电解析出镍金属后残余的水溶液再被加入一水可溶碳酸盐而将其中的锂离子以碳酸盐型态沉淀出。The present invention is a new technology for recovering metals and valuable resources from waste lithium-ion/nickel-metal hydride/nickel-cadmium batteries. rate increased substantially. However, the method of the present invention is still mainly to roast the used waste lithium-ion/nickel-hydrogen/nickel-cadmium battery in a high-temperature furnace, decompose and remove the organic matter, and then pulverize it, and then use the purpose of sieving to obtain pulverized bodies of different particle sizes. For coarse-grained pulverized objects, the broken iron shell can be separated and recovered by magnetic separation, and copper foil and aluminum foil can be recovered by eddy current separation. The fine powder part containing plate metal and metal oxide is subjected to two-stage dissolution and filtration treatment. Crystallize cadmium sulfate or electrolytically separate cadmium metal from the filtrate obtained from the first stage of dissolution and filtration, and adjust the pH value of the filtrate obtained from the second stage of dissolution and filtration to separately precipitate and recover iron, aluminum and rare earth metals as hydroxides . The remaining filtrate is subjected to a series of extraction and back extraction to obtain two aqueous solutions rich in cobalt and nickel respectively. They are then electrolyzed to separate cobalt and nickel metals, respectively. After the electrolysis of nickel metal, the remaining aqueous solution is added with a water-soluble carbonate to precipitate lithium ions in the form of carbonate.

本发明与现行发表的技术相比较,除有相当高的金属回收率及金属品质外,更以一套系统即可处理市面上最为广泛使用的锂离子、镍氢、镍镉二次电池,除了大幅提升处理回收系统对料源的容许度外,更可大幅降低设备成本。Compared with the currently published technology, the present invention not only has a relatively high metal recovery rate and metal quality, but also can process the most widely used lithium-ion, nickel-metal hydride, and nickel-cadmium secondary batteries on the market with a set of systems. In addition to greatly improving the tolerance of the processing and recycling system for material sources, it can also greatly reduce equipment costs.

本发明的一较佳实施方式将配合图1的流程图说明如下。将废弃(或生产制造过程中的不良品)的锂离子、镍氢、镍镉电池(1)以破壳机进行破解与打孔(2),再置入高温炉中以250℃~350℃的温度焙烧60~240分钟(3),焙烧温度不宜超过350C,过高的焙烧温度将造成大量镉金属形成镉蒸气而挥发逸散。电池中的有机物质(4)将因高温而分解形成二氧化碳/一氧化碳逸失,部份会还原电池中的氧化物,或形成焦炭沉积于电池中。将焙烧完成的废二次电池原料送入粉碎系统(5),粉碎过程中网目的选择以5~20目(mesh)为佳。因铁、铜及铝的延展性较佳,于粉碎后通常其粉碎体颗粒较大。粉碎后物质经由5~200目的筛网筛分(6)后,得到主要为铁及少量铜箔与铝箔的粗粒度粉碎体部分(7)及细粉体部份(11)。镍氢/镍镉电池中的铁镍合金极板、正极涂布物质及锂离子电池的正极活性物质于粉碎后粒度较小,此部分属于细粉体(11)。A preferred embodiment of the present invention will be described as follows in conjunction with the flowchart of FIG. 1 . The discarded (or defective products in the manufacturing process) lithium-ion, nickel-metal hydride, and nickel-cadmium batteries (1) are cracked and punched with a shell breaker (2), and then placed in a high-temperature furnace at 250 ° C to 350 ° C (3) The roasting temperature should not exceed 350C. Excessively high roasting temperature will cause a large amount of cadmium metal to form cadmium vapor and volatilize and escape. The organic matter (4) in the battery will decompose due to high temperature to form carbon dioxide/carbon monoxide and escape, and part of the oxide in the battery will be reduced, or coke will be deposited in the battery. The roasted waste secondary battery raw materials are sent to the crushing system (5). During the crushing process, the mesh size is preferably 5-20 mesh. Because iron, copper, and aluminum have better ductility, they usually have larger particles after crushing. After the pulverized material is sieved through a 5-200 mesh screen (6), a coarse-grained pulverized body part (7) and a fine powder part (11) mainly consisting of iron and a small amount of copper foil and aluminum foil are obtained. The particle size of the iron-nickel alloy plate in the nickel-hydrogen/nickel-cadmium battery, the positive electrode coating material and the positive electrode active material of the lithium ion battery is small after pulverization, and this part belongs to the fine powder (11).

粗粒度粉碎体部分(7),可轻易的借助磁选单元(8)在500~1500G的磁场下,将铁壳屑(9)及非磁性物(10)分离,针对非磁性物质部份可依其中铜箔与铝箔的含量而选用涡电流分选设备分选之。The coarse-grained pulverized body part (7) can easily separate the iron shell scraps (9) and non-magnetic materials (10) with the help of the magnetic separation unit (8) under a magnetic field of 500-1500G, and the non-magnetic material part can be According to the content of copper foil and aluminum foil, eddy current sorting equipment is used for sorting.

经由筛分(6)所得的细粉体(11)可直接进入第一阶段溶蚀系统(13),溶蚀的条件为3~9N的硫酸(12),液固比值为20~5,此阶段主要是将镉金属溶出。过滤(14)后的镉离子溶液可经由离子交换树脂单元去除其中的碱金及碱土金属离子,再于80℃蒸发移除纯化后水溶液中的水分而获得硫酸镉(16)结晶(15)。通过过滤方式将硫酸镉(16)结晶与浓缩后的溶液分离,再将此浓缩的溶液用作为以下第二阶段溶蚀(20)所用的硫酸(19)的一部分。The fine powder (11) obtained through sieving (6) can directly enter the first-stage corrosion system (13), the corrosion condition is 3-9N sulfuric acid (12), and the liquid-solid ratio is 20-5. It is the dissolution of cadmium metal. The filtered cadmium ion solution (14) can be used to remove the alkali gold and alkaline earth metal ions in the ion exchange resin unit, and then evaporate the water in the purified aqueous solution at 80° C. to obtain cadmium sulfate (16) crystals (15). The cadmium (16) sulphate crystals are separated from the concentrated solution by filtration, and the concentrated solution is used as part of the sulfuric acid (19) used in the second stage of erosion (20) below.

经由第一阶段溶蚀(13)后的残渣(17)再进入第二阶段溶蚀(20),将镍、钴等金属子溶出,溶蚀的条件以4~12N的硫酸(19),液固比值为20~5较佳。此阶段溶蚀时可加入过氧化氢(18)以提高其氧化还原电位值,增进系统的溶蚀能力。以过滤方式(21)移除碳等不溶物(22)。在双氧水存在的情况下,可确保铁、铝离子在滤液中是以三价状态存在,因而在未进入电解系统前,可借助调整酸碱度值(23)至3以上,将铁、铝分别以氢氧化铁(24)及氢氧化铝(25)的形态沉淀分离至相当低的浓度。本发明以氢氧化钠及硫酸来作为酸碱值的调整剂,可使其同时产生后续钴/镍电析所需添加的硫酸钠成分。于此调整pH值沉淀过程中,稀土金属元素于相当低的酸碱值下即会先形成沉淀而有效回收,与氢氧化铁(24)及氢氧化铝(25)有相当明显的区隔。The residue (17) after the first-stage corrosion (13) enters the second-stage corrosion (20) to dissolve metals such as nickel and cobalt. The conditions for dissolution are 4-12N sulfuric acid (19), and the liquid-solid ratio is 20-5 is better. Hydrogen peroxide (18) can be added during corrosion at this stage to increase its redox potential value and improve the corrosion capacity of the system. Insoluble matter (22) such as carbon is removed by filtration (21). In the presence of hydrogen peroxide, it can be ensured that iron and aluminum ions exist in the trivalent state in the filtrate. Therefore, before entering the electrolysis system, the iron and aluminum can be separated into hydrogen by adjusting the pH value (23) to more than 3 Species of iron oxide (24) and aluminum hydroxide (25) were precipitated and isolated to fairly low concentrations. In the present invention, sodium hydroxide and sulfuric acid are used as regulators of the pH value, so that the sodium sulfate component required for the subsequent cobalt/nickel electrolysis can be produced at the same time. In the precipitation process of adjusting the pH value, the rare earth metal elements will first form a precipitate and be effectively recovered at a relatively low pH value, which is quite distinct from iron hydroxide (24) and aluminum hydroxide (25).

除去大部分铁、铝杂质后富含镍、钴的金属离子溶液,可以以20~40%(于煤油中)的烷基或芳香基取代的磷酸萃取剂(例如二(-2-乙基己基)磷酸(di-2-ethylhexylphosphoric acid简称D2EHPA),可从日本的DAIHACHI公司购得)于0~4的酸碱度范围内进行第一阶段萃取(27),先行除去掺杂其中的镉、铁、锌及锰的金属离子离质(28)。萃取后含有镍及钴的水相,再以20~40%(于煤油中)的烷基或芳香基取代的磷酸、膦酸、次膦酸或焦磷酸的萃取剂(例如二(-2-乙基己基)磷酸(D2EHPA)、二(-2-乙基己基)磷酸(bis-2-ethylhexyl phosphonic acid)(PC88ATM,可从日本的DAIHACHI公司购得)或二(2,4,4-三甲基苯基)磷酸(bis(2,4,4-trimethylphenyl)phosphinic acid)(Cyanex272TM,可从CYANAMID公司购得)在3~9的酸碱度环境下,进行第二阶段萃取(29)将钴/镍分离。存在于有机相的钴在进行电析之前先进行反萃。上述反萃所用的反萃剂为0.4~2.0N的硫酸。After removing most of the iron and aluminum impurities, the metal ion solution rich in nickel and cobalt can be extracted with 20-40% (in kerosene) alkyl or aromatic substituted phosphoric acid extractant (such as bis(-2-ethylhexyl) ) Phosphoric acid (di-2-ethylhexylphosphoric acid referred to as D2EHPA), which can be purchased from Japan's DAIHACHI company) carries out the first-stage extraction (27) in the pH range of 0 to 4, and removes cadmium, iron, and zinc doped therein in advance And manganese metal ion ion (28). After extraction, the aqueous phase containing nickel and cobalt is then replaced with 20-40% (in kerosene) alkyl or aryl-based extractant of phosphoric acid, phosphonic acid, phosphinic acid or pyrophosphoric acid (such as bis(-2- Ethylhexyl) phosphate (D2EHPA), bis-2-ethylhexyl phosphonic acid (bis-2-ethylhexyl phosphonic acid) (PC88A TM , available from Japan's DAIHACHI company) or bis (2,4,4- Trimethylphenyl) phosphate (bis (2,4,4-trimethylphenyl) phosphinic acid) (Cyanex272 TM , available from CYANAMID company) in the pH environment of 3 ~ 9, the second stage of extraction (29) will Cobalt/nickel separation. The cobalt present in the organic phase is stripped before electrolysis. The stripping agent used for the stripping is 0.4-2.0N sulfuric acid.

将纯化后的钴/镍硫酸水溶液调整酸碱值至2~7后,分别以电析单元(30、32),将高单价的钴/镍以金属型态(31、33)回收之。电析单元的较佳操作条件如下表所示。   金属   电解质组成(g/L)   电流密度mA/cm2   槽电压Volt   操作温度℃   电流效率(%)   钴   硫酸钴(150~200)硫酸钠(100~150)氯化钠(15~20)硼酸(10~30)   15~20   1.5~4.0   60   ~80   镍   硫酸镍(150~200)氯化钠(15~20)硼酸(10~30)   15~20   1.5~4.0   60   ~98 After adjusting the pH value of the purified cobalt/nickel sulfuric acid aqueous solution to 2-7, electrolytic units (30, 32) are used to recover high monovalent cobalt/nickel in metal form (31, 33). The optimal operating conditions of the electrolysis unit are shown in the table below. Metal Electrolyte composition (g/L) Current density mA/cm 2 Tank voltage Volt Operating temperature °C Current efficiency (%) cobalt Cobalt sulfate (150~200) Sodium sulfate (100~150) Sodium chloride (15~20) Boric acid (10~30) 15~20 1.5~4.0 60 ~80 nickel Nickel sulfate (150~200) sodium chloride (15~20) boric acid (10~30) 15~20 1.5~4.0 60 ~98

镍电解析出后的电解液为富含锂离子的水溶液,可径行添加碳酸根形成锂的碳酸盐而将锂有效回收。在第一阶段萃取(27)所产生的含有镉、铁、锌及锰的金属离子的有机相以0.2~1.0N的硫酸或盐酸水溶液进行反萃,反萃后的酸水溶液经由离子交换树脂或沉淀方式(38)处理除去其中的金属离子即可排放(39)。The electrolyte solution after electrolysis of nickel is an aqueous solution rich in lithium ions, and carbonate can be directly added to form lithium carbonate to effectively recover lithium. The organic phase containing metal ions of cadmium, iron, zinc and manganese produced in the first stage extraction (27) is back-extracted with 0.2-1.0N sulfuric acid or hydrochloric acid aqueous solution, and the acid aqueous solution after the back-extraction is passed through ion exchange resin or Precipitation (38) can be used to remove the metal ions and discharge (39).

                         附图说明Description of drawings

图1.为本发明方法的一较佳实施例的流程方块图。FIG. 1 is a flow block diagram of a preferred embodiment of the method of the present invention.

                        具体实施方式 Detailed ways

实施例Example

各取锂离子电池、镍氢电池及镍镉电池1公斤,各种电池的金属成分如表一所示。非金属物质部分包含碳质、塑料包装、金属化合物中的阴离子部分、有机物及水分等。Take 1 kg of lithium-ion battery, nickel-metal hydride battery and nickel-cadmium battery each, and the metal composition of each battery is shown in Table 1. Non-metallic substances include carbon, plastic packaging, anion parts in metal compounds, organic matter, and water.

表一各式电池金属成分含量(克)   金属成分   锂离子电池   镍氢电池   镍镉电池   镉   0   0   200.1   钴   199.3   23.6   17.4   锂   22.6   0   0   铜   65.4   0   0   铝   52.2   4.4   0   铁   214.4   205.2   304.4   锰   0.7   25.2   0   镍   7.0   244.3   152.4   锌   0   2.8   0   稀土   0   87.8   0   非金属   438.4   406.7   325.7 Table 1 Metal component content of various batteries (g) metal composition Lithium Ion Battery NiMH batteries Nickel-cadmium batteries cadmium 0 0 200.1 cobalt 199.3 23.6 17.4 lithium 22.6 0 0 copper 65.4 0 0 aluminum 52.2 4.4 0 iron 214.4 205.2 304.4 manganese 0.7 25.2 0 nickel 7.0 244.3 152.4 zinc 0 2.8 0 rare earth 0 87.8 0 non-metal 438.4 406.7 325.7

将此些电池混合后打孔避免焙烧时内压过大而爆炸,以350℃(4Hr)焙烧分解混合电池中的有机物质,共逸失426克有机物质与水分。再以5网目粉碎机碎解电池并以20网目筛网筛分粉碎体,粉碎与筛分过程中混合电池共损失58克粉体。筛分后可得1096克的筛上物(粗粒度粉碎体)与1420克的筛下物(细粉体)。经由分析可得各部分其主要成分如下表(表二):After these batteries were mixed, holes were drilled to avoid explosion due to excessive internal pressure during firing. The organic substances in the mixed batteries were decomposed by roasting at 350°C (4Hr), and a total of 426 grams of organic substances and water were lost. The battery was crushed with a 5-mesh pulverizer and the pulverized body was sieved with a 20-mesh sieve. During the pulverization and sieving process, the mixed battery lost a total of 58 grams of powder. After sieving, 1096 grams of oversize (coarse-grained pulverized body) and 1420 grams of undersize (fine powder) can be obtained. After analysis, the main components of each part can be obtained as follows (Table 2):

表二筛分后各部分粉碎体成分   金属成分   粗粒度粉碎体   细粉体   镉   12.76   161.55   钴   20.23   193.15   锂   7.17   14.98   铜   58.67   4.43   铝   49.02   5.49   铁   652.16   26.69   锰   3.39   23.45   镍   73.14   272.61   锌   0.14   2.32   Nd   0   40.80   镧   0   45.15   非金属   219.25   629.40 Table 2 Composition of each part of crushed body after sieving metal composition Coarse-grained pulverized body fine powder cadmium 12.76 161.55 cobalt 20.23 193.15 lithium 7.17 14.98 copper 58.67 4.43 aluminum 49.02 5.49 iron 652.16 26.69 manganese 3.39 23.45 nickel 73.14 272.61 zinc 0.14 2.32 Nd 0 40.80 lanthanum 0 45.15 non-metal 219.25 629.40

将粗粒度粉碎体在1100G的磁力强度下,以磁选机分选之,可回收得到780克品质达80%以上主要为铁壳的铁质。而经磁选后296克非磁性物质的组成主要则为54%的碳质、18.7%的铜箔及15.5的铝箔。铜/铝金属可进一步借助重力分选法与碳质部分分离,所获得的铜铝箔混合体再利用涡电流分选机可分离回收获得高品味的铜箔与铝箔。The coarse-grained pulverized body is sorted by a magnetic separator under a magnetic force of 1100G, and 780 grams of iron with a quality of more than 80% mainly composed of iron shells can be recovered. The composition of 296 grams of non-magnetic material after magnetic separation is mainly 54% carbon, 18.7% copper foil and 15.5% aluminum foil. The copper/aluminum metal can be further separated from the carbonaceous part by gravity separation, and the obtained copper-aluminum foil mixture can be separated and recycled by an eddy current separator to obtain high-grade copper foil and aluminum foil.

至于细粉体部分则以1M 9L的硫酸进行第一阶段选择性溶蚀,在溶蚀时间达10分钟左右进行过滤,此阶段的各金属溶出率如表三所示。所获得富含硫酸镉的滤液在经由离子交换树脂单元去除其中的碱金及碱土金属离子后于80℃蒸发移除水分,可获得纯度达95%以上的硫酸镉结晶及浓缩的硫酸水溶液(体积为水分蒸发前的滤液的40%左右)。As for the fine powder part, 1M 9L sulfuric acid is used for the first stage of selective dissolution, and the dissolution time is about 10 minutes for filtration. The dissolution rate of each metal in this stage is shown in Table 3. The obtained filtrate rich in cadmium sulfate is evaporated to remove water at 80° C. after removing alkali gold and alkaline earth metal ions therein through an ion exchange resin unit, and can obtain cadmium sulfate crystals and concentrated sulfuric acid aqueous solution (volume It is about 40% of the filtrate before water evaporation).

经过第一阶段选择性溶蚀溶出金属镉后的粉体再以4M 6L的硫酸及3%的过氧化氢(0.5L)将粉体中的主要金属溶出(时间约1小时),各金属的溶出效果如表三所示。在过滤后,将溶蚀液以氢氧化钠调整溶蚀液的酸碱值至2,可彻底(98%)将溶液中稀土金属形成氢氧化物沉淀而回收。持续调升溶蚀液酸碱质至6,一来有利于后续萃取纯化,二来溶蚀液中部分铁离子(20%)及大部分(99%)铝离子可形成氢氧化物沉淀而被分离,达到纯化的效果。After the first stage of selective dissolution and dissolution of metal cadmium, the main metals in the powder are dissolved with 4M 6L sulfuric acid and 3% hydrogen peroxide (0.5L) (the time is about 1 hour), and the dissolution of each metal The effect is shown in Table 3. After filtering, the pH value of the solution is adjusted to 2 with sodium hydroxide, and the rare earth metals in the solution can be completely (98%) recovered by forming hydroxide precipitates. Continue to increase the acidity and alkalinity of the solution to 6, which is beneficial to the subsequent extraction and purification, and secondly, some iron ions (20%) and most (99%) aluminum ions in the solution can form hydroxide precipitates and be separated. achieve the effect of purification.

表三主要金属溶出效果   金属成分   第一阶段溶蚀溶出率   第二阶段溶蚀溶出率   镉   93.36%   100.00%   钴   8.11%   93.16%   锂   27.84%   100.00%   铜   7.45%   2.03%   铝   44.37%   81.25%   铁   14.40%   72.09%   锰   46.24%   74.00%   镍   5.56%   88.82%   锌   49.30%   20.93%   镧   10.19%   93.56%   Nd   10.06%   100.00% Table 3 Dissolution effect of main metals metal composition The dissolution rate of the first stage The second stage dissolution rate cadmium 93.36% 100.00% cobalt 8.11% 93.16% lithium 27.84% 100.00% copper 7.45% 2.03% aluminum 44.37% 81.25% iron 14.40% 72.09% manganese 46.24% 74.00% nickel 5.56% 88.82% zinc 49.30% 20.93% lanthanum 10.19% 93.56% Nd 10.06% 100.00%

接着以萃取的方式将富含钴、镍及少量镉的硫酸溶液以萃取法进行分离纯化。先以煤油將D2EHPA萃取剂配成浓度为25%的萃取液,在O/A比为1的状况下,将溶液的酸碱度调整至3,可将镉、铁、锌及锰萃取至有机相而与富含钴及镍离子的水相分离。接着将富钴及镍离子的水相以Cyanex272萃取剂在煤油中浓度为0.5M的萃取液,O/A比为1的情况下,将水溶液的酸碱度以NaOH调整至6.7进行萃取,可将钴(有机相)/镍(水相)分离。以0.5M的硫酸反萃含有钴的有机相,即可获得含有钴离子的硫酸水溶液。钴/镍分离后所得的钴与镍水溶液组成如表四所示。Then, the sulfuric acid solution rich in cobalt, nickel and a small amount of cadmium is separated and purified by extraction. First use kerosene to make D2EHPA extractant into an extract with a concentration of 25%, and adjust the pH of the solution to 3 under the condition of O/A ratio of 1, so that cadmium, iron, zinc and manganese can be extracted into the organic phase and Separated from the aqueous phase rich in cobalt and nickel ions. Then, the aqueous phase rich in cobalt and nickel ions is extracted with Cyanex272 extractant in kerosene at a concentration of 0.5M, and the O/A ratio is 1, and the pH of the aqueous solution is adjusted to 6.7 with NaOH for extraction. Cobalt (organic phase)/nickel (aqueous phase) separation. The organic phase containing cobalt is back-extracted with 0.5M sulfuric acid to obtain an aqueous solution of sulfuric acid containing cobalt ions. The composition of the cobalt and nickel aqueous solution obtained after cobalt/nickel separation is shown in Table 4.

表四萃取分离后钴与镍水溶液组成   金属成分   钴水溶液(%)   镍水溶液(%)   镉   1.3   0.3   钴   94.4   1.3   铁   1.3   0   锰   0.9   0   镍   2.1   98.4 Table 4 Composition of cobalt and nickel aqueous solution after extraction and separation metal composition Cobalt aqueous solution (%) Nickel aqueous solution (%) cadmium 1.3 0.3 cobalt 94.4 1.3 iron 1.3 0 manganese 0.9 0 nickel 2.1 98.4

将所得的钴、镍水溶液分别添加2%硼酸并控制酸碱值在4以上,及在电解电压3.5伏特进行平版电解。当水溶液的金属浓度降低至500ppm以下,为提高电解的电流效率将水溶液导入流体化电解槽继续进行电解,可将钴/镍完全回收。在本例中可回收获得金属镍约204克及钴约154克。Add 2% boric acid to the obtained cobalt and nickel aqueous solutions respectively, control the pH value above 4, and carry out lithographic electrolysis at an electrolysis voltage of 3.5 volts. When the metal concentration of the aqueous solution is reduced to below 500ppm, in order to improve the current efficiency of electrolysis, the aqueous solution is introduced into a fluidized electrolytic cell to continue electrolysis, and the cobalt/nickel can be completely recovered. In this example, about 204 grams of metallic nickel and about 154 grams of cobalt can be recovered.

Claims (6)

1. method that reclaims valuable metal from useless secondary cell, should comprise lithium ion battery, Ni-MH battery and nickel-cadmium cell by useless secondary cell, wherein should useless secondary cell produce the grey shape thing of a containing metal and metal oxide via roasting and screening, this method comprises the following step:
A) should ash shape thing with 2 equivalent molar concentration to the 6 equivalent molar concentration aqueous sulfuric acid corrosions that contain hydrogen peroxide;
B) alkali is added the corrosion solution that step a) produced, and make wherein cadmium, rare earth ion produce crystallization;
C) mixture solid-liquid separation step b);
D) with first organic extractant resulting aqueous solution of step c) is extracted, and produce the organic layer that is rich in the water layer of nickel and cobalt ions and is rich in cadmium, iron and zinc ion;
E) with second organic extractant resulting water layer of step d) is extracted, and produce the water layer that is rich in the organic layer of cobalt ions and is rich in nickel ion;
F) this is rich in the organic layer of cobalt ions with the aqueous sulfuric acid back extraction, and produces the water layer that is rich in cobalt ions;
G) use one to carry out electrolysis with the resulting water layer that is rich in nickel ion of step e) as electrolyte, so on a negative electrode, restore the nickel metal between 1.5~4.0 volts voltage;
H) use one to carry out electrolysis with the resulting water layer that is rich in cobalt ions of step f) as electrolyte, so on a negative electrode, restore the cobalt metal between 1.5~4.0 volts voltage; And
I) carbonate of a water soluble is incorporated in electrolyte after the step g) electrolysis, and forms the precipitation of lithium carbonate;
Wherein:
First organic extractant is the phosphoric acid extraction agent that alkyl or aromatic radical replace; Second organic extractant is the extractant of phosphoric acid, phosphonic acids, phosphinic acids or the pyrophosphoric acid of alkyl or aromatic radical replacement.
2. the method for claim 1, wherein step a) and b) merge and comprise:
A1) should ash shape thing with the aqueous sulfuric acid corrosion of 2 equivalent molar concentration to 6 equivalent molar concentrations;
A2) mixture solid-liquid separation step a1);
A3) to contain 4 equivalent molar concentration to 12 equivalent molar concentration aqueous sulfuric acid corrosion step a2 of hydrogen peroxide) solid that produced;
B1) with step a2) a part of water evaporation in the corrosion solution that produced removes, has the cadmium sulfate crystallization and is its main sediment partly and obtain one;
B2) alkali is added step a3) the corrosion solution that produced, have rare earth metal hydroxide, Fe (OH) and obtain one 3And Al (OH) 3Be main sediment partly,
Step b2 wherein) mixture that is produced is used as the mixture of step c) Separation of Solid and Liquid.
3. method as claimed in claim 2, wherein step b2) alkali be NaOH, and the consumption of this NaOH makes that the pH value of solution value is 6.
4. method as claimed in claim 2, wherein step b1) mixture that produced is by Separation of Solid and Liquid, and the liquid that Separation of Solid and Liquid obtained is used as step a3) the part of 4 equivalent molar concentration to 12 equivalent molar concentration aqueous sulfuric acids.
5. the method for claim 1, wherein step I) water soluble carbonate be sodium carbonate.
6. the method for claim 1, it further comprises with the organic layer that is rich in cadmium, iron and zinc ion in the aqueous sulfuric acid back extraction step d), and obtains being rich in the water layer of cadmium, iron and zinc ion; And remove cadmium, iron and zinc ion in this water layer with ion exchange resin.
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