WO2024262506A1 - Method for producing leach solution from hydroxide including nickel and cobalt - Google Patents
Method for producing leach solution from hydroxide including nickel and cobalt Download PDFInfo
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- WO2024262506A1 WO2024262506A1 PCT/JP2024/022137 JP2024022137W WO2024262506A1 WO 2024262506 A1 WO2024262506 A1 WO 2024262506A1 JP 2024022137 W JP2024022137 W JP 2024022137W WO 2024262506 A1 WO2024262506 A1 WO 2024262506A1
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- the present invention relates to a method for producing a leachate containing nickel ions and cobalt ions from a hydroxide containing nickel and cobalt.
- Lithium-ion secondary batteries which charge and discharge by the movement of lithium ions between the positive and negative electrodes, have a high energy density and do not deteriorate easily even when repeatedly charged and discharged, so in recent years demand has been increasing for them as power sources for electric vehicles and smart grid storage batteries, as well as for electronic devices such as mobile phones and laptops.
- Lithium-ion secondary batteries have a structure in which an electrolyte is filled between the positive and negative electrodes that face each other with a separator in between, and lithium nickel oxide is used as the active material for the positive electrode, which is the main component.
- Lithium nickel oxide can be manufactured by mixing lithium hydroxide with nickel hydroxide as a precursor and firing the mixture.
- the above-mentioned nickel hydroxide as a precursor can be produced by a neutralization reaction caused by adding an aqueous sodium hydroxide solution to an aqueous nickel sulfate solution as a raw material.
- sodium sulfate (mirabilite) produced as a by-product in an equimolar amount with nickel hydroxide as shown in the following formula 1 can be problematic. That is, since total wastewater volume regulations are set for sodium sulfate in some regions, there have been cases where it has been necessary to install costly treatment facilities to meet the wastewater standards, or to limit the production volume of nickel hydroxide in order to suppress the discharge of sodium sulfate.
- Patent Document 1 proposes a technology in which oxygen is introduced into an aqueous ammonia solution containing powder of metallic nickel to leach the metallic nickel into the aqueous ammonia solution, and then seed crystals are added as necessary to the aqueous ammonia solution containing nickel and hydroxyl ions, and the aqueous ammonia solution is evaporated under atmospheric pressure or reduced pressure to precipitate and recover nickel hydroxide.
- nickel hydroxide can be produced without producing sodium sulfate as a by-product, but this technology uses metallic nickel as the precursor raw material, and therefore is not economically advantageous.
- metallic nickel is generally produced by leaching nickel from intermediate raw materials such as matte, sulfide, or hydroxide obtained by processing nickel ore using acid or chlorine, and then separating the impurities leached together with the nickel through a refining process before electrolytic winning, so that the metallic nickel finally obtained is in the form of a plate or lump. Therefore, a process is required to process metallic nickel into powder so that it can be efficiently leached with an aqueous ammonia solution.
- cobalt may be added to the precursor during the manufacturing stage of the lithium nickel oxide.
- the nickel used as the raw material for the precursor contains cobalt, and it is preferable that it contains a certain amount of cobalt.
- a process is carried out to separate and remove cobalt from nickel by a refining process such as a solvent extraction process prior to electrowinning, which results in unnecessary separation costs.
- the method of manufacturing nickel hydroxide using metallic nickel as a raw material requires many processes that increase costs, so there is a demand for an alternative method of manufacturing nickel hydroxide using unrefined intermediate raw materials containing a wide variety of impurities obtained, for example, by processing nickel oxide ore or scrap.
- the present invention was made in consideration of the above circumstances, and aims to provide a method for producing a leachate containing nickel ions and cobalt ions using raw materials containing nickel and cobalt, which are cheaper than metallic nickel.
- the method for producing a leachate according to the present invention is characterized in that a slurry is obtained by mixing hydroxide particles containing nickel and cobalt with ammonia water containing ammonium sulfate, and the slurry is subjected to a leaching treatment under a specified temperature condition to obtain a leachate containing nickel ions and cobalt ions leached from the hydroxide particles.
- FIG. 1 is a block flow diagram of a method for producing nickel hydroxide containing cobalt, which preferably includes the method for producing a leachate of the present invention.
- the method for producing a leachate according to this embodiment of the present invention is included in the method for producing nickel hydroxide containing cobalt as a precursor by subjecting a raw material nickel-cobalt mixed hydroxide to a series of treatments, as shown in Figure 1.
- This raw material nickel-cobalt mixed hydroxide contains impurities such as calcium, magnesium, zinc, sulfur, silicon, manganese, iron, and aluminum.
- Nickel-cobalt mixed hydroxide containing such various impurities is sometimes called a mixed hydroxide precipitate (MHP).
- the method for producing nickel hydroxide containing cobalt in FIG. 1 includes a water washing step in which nickel-cobalt mixed hydroxide particles (MHP) are washed, preferably with water at room temperature, to mainly remove calcium and magnesium, an alkaline washing reduction step in which the nickel-cobalt mixed hydroxide particles washed in the water washing step are washed and reduced with an alkaline washing solution consisting of an aqueous caustic soda solution at room temperature and preferably with a concentration of about 8 mol/L, which contains a reducing agent such as sodium sulfite, to mainly remove zinc, sulfur, and silicon, and a process for reducing the nickel-cobalt mixed hydroxide particles washed in the water washing step.
- MHP nickel-cobalt mixed hydroxide particles
- the process includes a leaching process in which the reduced nickel-cobalt mixed hydroxide particles are leached with an ammonia-containing aqueous solution containing ammonium sulfate, a thermal decomposition precipitation process in which the leaching solution obtained by the leaching process is heated to thermally decompose the ammonium sulfate into ammonia and sulfur trioxide and precipitate the precursors nickel hydroxide and cobalt hydroxide, and an alkaline washing process in which the precipitated nickel hydroxide and cobalt hydroxide are washed with an alkaline washing solution, preferably an aqueous caustic soda solution at room temperature with a concentration of about 4 mol/L, to mainly remove the carbon content.
- an alkaline washing solution preferably an aqueous caustic soda solution at room temperature with a concentration of about 4 mol/L
- the water washing step is a step of removing mainly calcium and magnesium as impurities contained in the raw material nickel-cobalt mixed hydroxide using washing water preferably at a liquid temperature of 10 to 90°C, more preferably at room temperature.
- this water washing step although there is no limitation, it is preferable to adopt a method in which the nickel-cobalt mixed hydroxide is introduced into washing water previously charged in a container equipped with a stirrer, and washed for 0.50 to 1.0 hours while stirring with the stirrer.
- the slurry containing the nickel-cobalt mixed hydroxide particles is introduced into a solid-liquid separation device such as a centrifuge or a filter for solid-liquid separation, whereby the washed wet nickel-cobalt mixed hydroxide can be recovered.
- a solid-liquid separation device such as a centrifuge or a filter for solid-liquid separation
- the alkaline washing reduction step is a step for removing impurities that are difficult to remove in the previous water washing step, mainly zinc, sulfur, and silicon, by washing with an alkaline washing solution such as a caustic soda solution with a concentration of 1.0 to 8.0 mol/L.
- the washing wastewater discharged after this washing contains impurities such as zinc, sulfur, and silicon, and is then repeatedly used as an alkaline washing solution after removing these impurities by a precipitation method or the like.
- the precipitation method refers to a method for extracting solutes dissolved in a solution as precipitate particles, and for example, the above-mentioned precipitate particles can be obtained by changing the above-mentioned solution from an unsaturated state to a supersaturated state and promoting the generation and growth of crystal nuclei.
- manganese, iron, and aluminum that are not leached in the above-mentioned leaching step remain as leaching residue, and are separated and removed from the leaching solution by solid-liquid separation means such as filtration.
- the ammonia and sulfur trioxide generated by the thermal decomposition in the thermal decomposition precipitation means are recovered and reused as the ammonia water containing ammonium sulfate in the previous leaching step, and the carbon content in the cleaning solution discharged after cleaning in the alkaline cleaning step is reduced in solubility as the temperature of the cleaning wastewater drops, so in this case too, it is possible to precipitate the carbon content as sodium carbonate by using the precipitation method in the same manner as above. After removing the sodium carbonate in this way, the cleaning wastewater is repeatedly used as the alkaline cleaning solution.
- the leaching process is a process in which the nickel-cobalt mixed hydroxide washed in the previous alkaline washing and reduction process is leached with an ammonium sulfate aqueous solution.
- water is first charged into a container equipped with a stirrer, and ammonia (NH 3 ) water and ammonium sulfate ((NH 4 ) 2 SO 4 ) are added thereto to prepare an ammonium sulfate aqueous solution.
- nickel-cobalt mixed hydroxide particles are charged into the container containing the prepared ammonium sulfate solution, and a slurry having a homogeneous concentration is prepared by stirring and mixing with the stirrer.
- the temperature of the slurry is preferably maintained under a temperature condition of 20°C or higher and 60°C or lower to perform the leaching process. This allows nickel ions and cobalt ions to be leached from the nickel-cobalt mixed hydroxide particles. If the slurry temperature is lower than 20°C, the reaction rate is too slow and the production efficiency is reduced, and conversely, if it exceeds 60°C, ammonium sulfate is easily thermally decomposed, making it difficult to leach it well. If the slurry temperature is below 0° C., the water will freeze, making it difficult to prepare the ammonium sulfate solution.
- the ammonium sulfate concentration in the ammonium sulfate aqueous solution is preferably adjusted to a range of 0.50 mol/L to 4.1 mol/L, more preferably 1.5 mol/L to 3.5 mol/L, and most preferably 2.0 mol/L to 3.0 mol/L. If the ammonium sulfate concentration is less than 1.5 mol/L, the leaching rate may decrease, and especially if it is less than 0.50 mol/L, the effect of the present invention may not be exhibited well.
- ammonium sulfate concentration can be measured by absorptiometry, ion chromatography, etc. If the ammonium sulfate concentration is outside the above range, it can be adjusted by the amount of ammonium sulfate added.
- free ammonia concentration in the slurry it is preferable to adjust the free ammonia concentration in the slurry to within the range of 0.1 to 1.3 mol/L. If the free ammonia concentration is within this range, nickel and cobalt can be leached stably in the form of ammine complexes. Even if the free ammonia concentration exceeds 1.3 mol/L, it has almost no effect on the stable leaching in the form of the above amine complexes, and it is not preferable because it increases costs and increases the load on wastewater treatment.
- free ammonia refers to molecular ammonia (NH 3 ), and its concentration can be measured by absorptiometry after separating it by distillation and converting it to NH 4 + . If the free ammonia concentration is outside the above range, it can be adjusted by adding an amount of ammonia water.
- the pyrolysis precipitation step is a step in which the leachate produced in the previous leaching step is heated by preferably maintaining the temperature at 60°C to 100°C for 0.50 to 2.0 hours, thereby pyrolyzing the ammine complexes of nickel and cobalt, precipitating the nickel and cobalt as hydroxides, and recovering them as precipitates.
- this pyrolysis precipitation step it is preferable to stir while blowing in an oxidizing agent such as air, which promotes the oxidation of cobalt, making it possible to recover both nickel and cobalt as hydroxides at a high recovery rate.
- ammine complex of cobalt is usually converted to divalent cobalt by pyrolysis, but by oxidizing it to trivalent cobalt, recovery as hydroxides is promoted. It is preferable to recover the ammonia and sulfur trioxide generated by pyrolysis in this pyrolysis precipitation step and reuse them as ammonia water containing ammonium sulfate in the previous leaching step.
- the alkaline washing step is a step in which the nickel-cobalt mixed hydroxide recovered in the preceding thermal decomposition precipitation step is washed, preferably with the same alkaline washing solution as that used in the alkaline washing and reduction step described above. This removes zinc, sulfur, and silicon that could not be completely removed in the alkaline washing and reduction step, as well as carbon derived from ammonium sulfate added in the leaching step, and makes it possible to produce a high-purity precursor with extremely few impurities that can be suitably used as a positive electrode active material for lithium-ion secondary batteries.
- the method for producing a leachate according to an embodiment of the present invention makes it possible to produce a leachate containing nickel and cobalt from the raw material nickel-cobalt mixed hydroxide particles without by-producing sodium sulfate, and also makes it possible to easily separate and remove impurities such as manganese, iron, and aluminum contained in the raw material, so that the leachate can be produced more inexpensively than when expensive metallic nickel is used as the raw material.
- MHP nickel-cobalt mixed hydroxide
- the nickel leaching rate was 45.6% and the cobalt leaching rate was 15.4%, and a leachate consisting of an aqueous ammonia solution containing a large amount of nickel ions and cobalt ions was produced.
- Comparative Example 200 mL of 25% ammonia water was placed in a container, and 20 g of powdered nickel-cobalt mixed hydroxide (MHP) having the composition shown in Table 1 was mixed to form a slurry, which was stirred with a stirrer and held for 2 hours while adjusting the liquid temperature to 50° C., to carry out a leaching treatment. Thereafter, solid-liquid separation was carried out in the same manner as in the examples, and 200 mL of leachate was obtained. The element concentrations of this leachate were measured in the same manner as in the examples, and the leaching rate of each element was determined.
- MHP powdered nickel-cobalt mixed hydroxide
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Abstract
Description
本発明は、ニッケル及びコバルトを含有する水酸化物からニッケルイオン及びコバルトイオンを含有する浸出液を製造する方法に関する。 The present invention relates to a method for producing a leachate containing nickel ions and cobalt ions from a hydroxide containing nickel and cobalt.
正極と負極の間をリチウムイオンが移動することで充放電を行なうリチウムイオン二次電池は、エネルギー密度が高く、繰り返し充放電しても劣化しにくいので、携帯電話やノートパソコン等の電子機器用の電池のほか、電気自動車等の駆動用電源、スマートグリットの蓄電池等として近年需要が増加している。リチウムイオン二次電池は、セパレーターを挟んで対向する正極と負極の間に電解質を満たした構造を有しており、これらのうち、主要な構成品である正極の活物質材料として、ニッケル酸リチウムが用いられている。ニッケル酸リチウムは、前駆体としての水酸化ニッケルに水酸化リチウムを混合して焼成することで製造することができる。 Lithium-ion secondary batteries, which charge and discharge by the movement of lithium ions between the positive and negative electrodes, have a high energy density and do not deteriorate easily even when repeatedly charged and discharged, so in recent years demand has been increasing for them as power sources for electric vehicles and smart grid storage batteries, as well as for electronic devices such as mobile phones and laptops. Lithium-ion secondary batteries have a structure in which an electrolyte is filled between the positive and negative electrodes that face each other with a separator in between, and lithium nickel oxide is used as the active material for the positive electrode, which is the main component. Lithium nickel oxide can be manufactured by mixing lithium hydroxide with nickel hydroxide as a precursor and firing the mixture.
上記の前駆体としての水酸化ニッケルは、原料の硫酸ニッケル水溶液に水酸化ナトリウム水溶液を添加することで生じる中和反応により生成することができる。この硫酸ニッケル原料の中和反応では、下記式1に示すように水酸化ニッケルと等モル量で副生する硫酸ナトリウム(芒硝)が問題になることがあった。すなわち、硫酸ナトリウムは、地域によっては排水の総量規制が設定されているため、排水基準を満たすようにコストをかけて処理設備を設けるか、あるいは硫酸ナトリウムの排出量を抑えるために水酸化ニッケルの生産量を制限せざるを得ない場合があった。
[式1]
NiSO4+2NaOH→Ni(OH)2+Na2SO4
The above-mentioned nickel hydroxide as a precursor can be produced by a neutralization reaction caused by adding an aqueous sodium hydroxide solution to an aqueous nickel sulfate solution as a raw material. In this neutralization reaction of the nickel sulfate raw material, sodium sulfate (mirabilite) produced as a by-product in an equimolar amount with nickel hydroxide as shown in the following formula 1 can be problematic. That is, since total wastewater volume regulations are set for sodium sulfate in some regions, there have been cases where it has been necessary to install costly treatment facilities to meet the wastewater standards, or to limit the production volume of nickel hydroxide in order to suppress the discharge of sodium sulfate.
[Formula 1]
NiSO 4 +2NaOH→Ni(OH) 2 +Na 2 SO 4
そこで、硫酸ナトリウムを副生しない水酸化ニッケルの製造方法が提案されている。例えば特許文献1には、金属ニッケルの粉末を含むアンモニア水溶液に酸素を導入して該金属ニッケルを該アンモニア水溶液中に浸出させた後、ニッケル及び水酸基のイオンを含むアンモニア水溶液に対して必要に応じて種結晶を添加してから大気圧下又は減圧下でアンモニア水溶液を蒸発させることで水酸化ニッケルを沈殿回収する技術が提案されている。 Therefore, a method for producing nickel hydroxide that does not produce sodium sulfate as a by-product has been proposed. For example, Patent Document 1 proposes a technology in which oxygen is introduced into an aqueous ammonia solution containing powder of metallic nickel to leach the metallic nickel into the aqueous ammonia solution, and then seed crystals are added as necessary to the aqueous ammonia solution containing nickel and hydroxyl ions, and the aqueous ammonia solution is evaporated under atmospheric pressure or reduced pressure to precipitate and recover nickel hydroxide.
上記特許文献1の技術を用いることにより、硫酸ナトリウムを副生させることなく水酸化ニッケルを製造することができるが、この技術は金属ニッケルを前駆体の原料に用いるので経済的な観点から有利とはいえない。すなわち、金属ニッケルは一般的にニッケル鉱石を処理することで得たマット、硫化物、又は水酸化物などの中間原料に対して酸や塩素などを用いてニッケルを浸出した後、該ニッケルと共に浸出される不純物を精製処理により分離してから電解採取することによって製造されるため、最終的に得られる金属ニッケルの形状は板状や塊状になる。従って、金属ニッケルをアンモニア水溶液で効率よく浸出させるために粉末状に加工する工程が必要になる。 By using the technology of Patent Document 1, nickel hydroxide can be produced without producing sodium sulfate as a by-product, but this technology uses metallic nickel as the precursor raw material, and therefore is not economically advantageous. In other words, metallic nickel is generally produced by leaching nickel from intermediate raw materials such as matte, sulfide, or hydroxide obtained by processing nickel ore using acid or chlorine, and then separating the impurities leached together with the nickel through a refining process before electrolytic winning, so that the metallic nickel finally obtained is in the form of a plate or lump. Therefore, a process is required to process metallic nickel into powder so that it can be efficiently leached with an aqueous ammonia solution.
また、ニッケルの一部をコバルト等の元素で置換した三元系のニッケルコバルトマンガン酸リチウム(NCM)やニッケルコバルトアルミニウム酸リチウム(NCA)等の正極活物質のように、上記のニッケル酸リチウムの製造段階において前駆体にコバルトを添加する場合があり、この場合は前駆体の原料に用いるニッケルにコバルトが含まれることは問題ではなく、むしろある程度コバルトを含んでいるのが好ましい。しかしながら、上記の金属ニッケルの製造に用いる中間原料の多くには、コバルトが含まれているにもかかわらず、電解採取に先立って溶媒抽出工程などの精製処理によりニッケルからコバルトを分離除去する処理が行われており、結果的に無駄な分離コストをかけていることになる。このように、金属ニッケルを原料として水酸化ニッケルを製造する方法は、コスト増の要因となる多くの処理を要するので、これに代わる例えばニッケル酸化鉱石やスクラップを処理して得た多種多様な不純物を含んだ未精製の中間原料を用いて水酸化ニッケルを製造する方法が求められている。 In addition, as in the case of ternary positive electrode active materials such as lithium nickel cobalt manganate (NCM) and lithium nickel cobalt aluminate (NCA) in which part of the nickel is replaced with an element such as cobalt, cobalt may be added to the precursor during the manufacturing stage of the lithium nickel oxide. In this case, it is not a problem if the nickel used as the raw material for the precursor contains cobalt, and it is preferable that it contains a certain amount of cobalt. However, although many of the intermediate raw materials used in the manufacture of metallic nickel contain cobalt, a process is carried out to separate and remove cobalt from nickel by a refining process such as a solvent extraction process prior to electrowinning, which results in unnecessary separation costs. As such, the method of manufacturing nickel hydroxide using metallic nickel as a raw material requires many processes that increase costs, so there is a demand for an alternative method of manufacturing nickel hydroxide using unrefined intermediate raw materials containing a wide variety of impurities obtained, for example, by processing nickel oxide ore or scrap.
本発明は、上記事情に鑑みてなされたものであり、金属ニッケルよりも安価なニッケル及びコバルトを含む原料を用いてニッケルイオン及びコバルトイオンを含有する浸出液を製造する方法を提供することを目的とする。 The present invention was made in consideration of the above circumstances, and aims to provide a method for producing a leachate containing nickel ions and cobalt ions using raw materials containing nickel and cobalt, which are cheaper than metallic nickel.
上記の目的を達成するため、本発明に係る浸出液の製造方法は、ニッケル及びコバルトを含有する水酸化物粒子と、硫酸アンモニウムを含有するアンモニア水とを混合することで得たスラリーを所定の温度条件下で浸出処理することによって、該水酸化物粒子から浸出させたニッケルイオン及びコバルトイオンを含有する浸出液を得ることを特徴とする。 In order to achieve the above object, the method for producing a leachate according to the present invention is characterized in that a slurry is obtained by mixing hydroxide particles containing nickel and cobalt with ammonia water containing ammonium sulfate, and the slurry is subjected to a leaching treatment under a specified temperature condition to obtain a leachate containing nickel ions and cobalt ions leached from the hydroxide particles.
本発明によれば、硫酸ナトリウムを副生させることなく金属ニッケルよりも安価なニッケル及びコバルトを含む原料を用いてニッケルイオン及びコバルトイオンを含有する浸出液を製造することができる。 According to the present invention, it is possible to produce a leachate containing nickel ions and cobalt ions using raw materials containing nickel and cobalt, which are cheaper than metallic nickel, without producing sodium sulfate as a by-product.
以下、本発明に係るニッケルイオン及びコバルトイオンを含有する浸出液の製造方法の実施形態について説明する。この本発明の実施形態の浸出液の製造方法は、図1に示すように、原料のニッケルコバルト混合水酸化物に対して一連の処理を施すことで前駆体としてのコバルトを含む水酸化ニッケルを製造する方法に含まれるものである。この原料のニッケルコバルト混合水酸化物は、不純物として例えばカルシウム、マグネシウム、亜鉛、硫黄、ケイ素、マンガン、鉄、アルミニウムなどを含んでいる。このような様々な不純物を含んだニッケルコバルト混合水酸化物は、混合水酸化物沈殿物(MHP)と称することがある。 Below, an embodiment of the method for producing a leachate containing nickel ions and cobalt ions according to the present invention will be described. The method for producing a leachate according to this embodiment of the present invention is included in the method for producing nickel hydroxide containing cobalt as a precursor by subjecting a raw material nickel-cobalt mixed hydroxide to a series of treatments, as shown in Figure 1. This raw material nickel-cobalt mixed hydroxide contains impurities such as calcium, magnesium, zinc, sulfur, silicon, manganese, iron, and aluminum. Nickel-cobalt mixed hydroxide containing such various impurities is sometimes called a mixed hydroxide precipitate (MHP).
すなわち、この図1のコバルトを含む水酸化ニッケルの製造方法は、ニッケルコバルト混合水酸化物粒子(MHP)を好適には常温の水で洗浄することで主としてカルシウム及びマグネシウムを除去する水洗工程と、該水洗工程で洗浄されたニッケルコバルト混合水酸化物粒子を、亜硫酸ナトリウムなどの還元剤を含んだ好適には濃度8mol/L程度の常温の苛性ソーダ水溶液からなるアルカリ洗浄液で洗浄すると共に還元処理することで、亜鉛、硫黄、及びケイ素を主として除去するアルカリ洗浄還元工程と、該アルカリ洗浄及び還元処理されたニッケルコバルト混合水酸化物粒子を硫酸アンモニウムを含むアンモニア含有水溶液で浸出処理する浸出工程と、該浸出処理により得た浸出液を加熱して硫酸アンモニウムをアンモニア及び三酸化硫黄に熱分解すると共に、前駆体としての水酸化ニッケル及び水酸化コバルトを析出させる熱分解沈殿工程と、該析出した水酸化ニッケル及び水酸化コバルトを、好適には濃度4mol/L程度の常温の苛性ソーダ水溶液等からなるアルカリ洗浄液で洗浄して主として炭素分を除去するアルカリ洗浄工程とを含んでいる。以下、これら一連の工程の各々について説明する。 In other words, the method for producing nickel hydroxide containing cobalt in FIG. 1 includes a water washing step in which nickel-cobalt mixed hydroxide particles (MHP) are washed, preferably with water at room temperature, to mainly remove calcium and magnesium, an alkaline washing reduction step in which the nickel-cobalt mixed hydroxide particles washed in the water washing step are washed and reduced with an alkaline washing solution consisting of an aqueous caustic soda solution at room temperature and preferably with a concentration of about 8 mol/L, which contains a reducing agent such as sodium sulfite, to mainly remove zinc, sulfur, and silicon, and a process for reducing the nickel-cobalt mixed hydroxide particles washed in the water washing step. The process includes a leaching process in which the reduced nickel-cobalt mixed hydroxide particles are leached with an ammonia-containing aqueous solution containing ammonium sulfate, a thermal decomposition precipitation process in which the leaching solution obtained by the leaching process is heated to thermally decompose the ammonium sulfate into ammonia and sulfur trioxide and precipitate the precursors nickel hydroxide and cobalt hydroxide, and an alkaline washing process in which the precipitated nickel hydroxide and cobalt hydroxide are washed with an alkaline washing solution, preferably an aqueous caustic soda solution at room temperature with a concentration of about 4 mol/L, to mainly remove the carbon content. Each of these steps will be described below.
(1)水洗工程
水洗工程は、原料のニッケルコバルト混合水酸化物に含まれる不純物としての主としてカルシウム及びマグネシウムを好ましくは液温10~90℃、より好ましくは常温の洗浄水を用いて除去する工程である。この水洗工程では、限定するものではないが、例えば撹拌機付きの容器に予め装入しておいた洗浄水にニッケルコバルト混合水酸化物を投入し、該撹拌機で撹拌しながら0.50~1.0時間かけて洗浄する方法を採用するのが好ましい。洗浄後は、ニッケルコバルト混合水酸化物粒子を含むスラリーを遠心分離機や濾過器などの固液分離装置に導入して固液分離することで、洗浄済みの湿潤状態のニッケルコバルト混合水酸化物を回収することができる。
(1) Water washing step The water washing step is a step of removing mainly calcium and magnesium as impurities contained in the raw material nickel-cobalt mixed hydroxide using washing water preferably at a liquid temperature of 10 to 90°C, more preferably at room temperature. In this water washing step, although there is no limitation, it is preferable to adopt a method in which the nickel-cobalt mixed hydroxide is introduced into washing water previously charged in a container equipped with a stirrer, and washed for 0.50 to 1.0 hours while stirring with the stirrer. After washing, the slurry containing the nickel-cobalt mixed hydroxide particles is introduced into a solid-liquid separation device such as a centrifuge or a filter for solid-liquid separation, whereby the washed wet nickel-cobalt mixed hydroxide can be recovered.
(2)アルカリ洗浄還元工程
アルカリ洗浄還元工程は、前工程の水洗工程では除去が困難な不純物である主として亜鉛、硫黄、及び珪素を例えば濃度1.0~8.0mol/Lの苛性ソーダ水溶液などのアルカリ洗浄液を用いて洗浄することで除去する工程である。この洗浄後に排出される洗浄排液は、亜鉛、硫黄、ケイ素などの不純物を含んでいるため、沈殿法などによりこれら不純物を除去した後、アルカリ洗浄液として繰り返される。ここで、沈殿法とは、溶液中に溶解している溶質を沈殿粒子として取り出す手法のことを言い、例えば、上記溶液を不飽和な状態から過飽和な状態とし、結晶核の生成と成長を促すことにより上記沈殿粒子を得ることができる。また、上記の浸出工程で浸出されないマンガン、鉄、アルミニウムは浸出残渣として残留するので、ろ過などの固液分離手段により浸出液から分離除去される。更に、熱分解沈殿手段での熱分解で発生するアンモニア及び三酸化硫黄は回収して前工程の浸出工程の硫酸アンモニウムを含むアンモニア水として再利用され、アルカリ洗浄工程において洗浄後に排出される洗浄液中の炭素分は、洗浄排液の液温が下がれば炭素分の溶解度が低下するため、この場合も上記と同様に沈殿法を用いることで、炭素分を炭酸ナトリウムとして沈殿させることが可能である。このようにして炭酸ナトリウムを除去した後、洗浄排液はアルカリ洗浄液として繰り返される。
(2) Alkaline Washing Reduction Step The alkaline washing reduction step is a step for removing impurities that are difficult to remove in the previous water washing step, mainly zinc, sulfur, and silicon, by washing with an alkaline washing solution such as a caustic soda solution with a concentration of 1.0 to 8.0 mol/L. The washing wastewater discharged after this washing contains impurities such as zinc, sulfur, and silicon, and is then repeatedly used as an alkaline washing solution after removing these impurities by a precipitation method or the like. Here, the precipitation method refers to a method for extracting solutes dissolved in a solution as precipitate particles, and for example, the above-mentioned precipitate particles can be obtained by changing the above-mentioned solution from an unsaturated state to a supersaturated state and promoting the generation and growth of crystal nuclei. In addition, manganese, iron, and aluminum that are not leached in the above-mentioned leaching step remain as leaching residue, and are separated and removed from the leaching solution by solid-liquid separation means such as filtration. Furthermore, the ammonia and sulfur trioxide generated by the thermal decomposition in the thermal decomposition precipitation means are recovered and reused as the ammonia water containing ammonium sulfate in the previous leaching step, and the carbon content in the cleaning solution discharged after cleaning in the alkaline cleaning step is reduced in solubility as the temperature of the cleaning wastewater drops, so in this case too, it is possible to precipitate the carbon content as sodium carbonate by using the precipitation method in the same manner as above. After removing the sodium carbonate in this way, the cleaning wastewater is repeatedly used as the alkaline cleaning solution.
(3)浸出工程
浸出工程は、前工程のアルカリ洗浄還元工程で洗浄したニッケルコバルト混合水酸化物を硫酸アンモニウム水溶液で浸出処理する工程である。具体的には、まず撹拌機を備えた容器内に水を装入し、そこにアンモニア(NH3)水及び硫酸アンモニウム((NH4)2SO4)を添加することで、硫酸アンモニウム水溶液を調製する。次に、調製した硫酸アンモニウム溶液が入った上記容器内に、ニッケルコバルト混合水酸化物粒子を投入し、該撹拌機で撹拌混合することで、均質な濃度を有するスラリーを調製する。この状態でスラリーの温度を好ましくは20℃以上60℃以下の温度条件下に保持することで浸出処理を行なう。これにより、該ニッケルコバルト混合水酸化物粒子からニッケルイオン及びコバルトイオンを浸出させることができる。このスラリー温度が20℃未満では反応速度が遅すぎて生産効率が低下し、逆に60℃を超えると硫酸アンモニウムが熱分解しやすくなるので良好に浸出させることができなくなる。なお、スラリー温度が0℃以下では水が凍結するので硫酸アンモニウム溶液の調製が困難になる。
(3) Leaching process The leaching process is a process in which the nickel-cobalt mixed hydroxide washed in the previous alkaline washing and reduction process is leached with an ammonium sulfate aqueous solution. Specifically, water is first charged into a container equipped with a stirrer, and ammonia (NH 3 ) water and ammonium sulfate ((NH 4 ) 2 SO 4 ) are added thereto to prepare an ammonium sulfate aqueous solution. Next, nickel-cobalt mixed hydroxide particles are charged into the container containing the prepared ammonium sulfate solution, and a slurry having a homogeneous concentration is prepared by stirring and mixing with the stirrer. In this state, the temperature of the slurry is preferably maintained under a temperature condition of 20°C or higher and 60°C or lower to perform the leaching process. This allows nickel ions and cobalt ions to be leached from the nickel-cobalt mixed hydroxide particles. If the slurry temperature is lower than 20°C, the reaction rate is too slow and the production efficiency is reduced, and conversely, if it exceeds 60°C, ammonium sulfate is easily thermally decomposed, making it difficult to leach it well. If the slurry temperature is below 0° C., the water will freeze, making it difficult to prepare the ammonium sulfate solution.
この浸出処理に際して、硫酸アンモニウム水溶液中の硫酸アンモニウム濃度は0.50mol/L以上4.1mol/L以下の範囲内に調製するのが好ましく、1.5mol/L以上3.5mol/L以下の範囲内に調製するのがより好ましく、2.0mol/L以上3.0mol/L以下の範囲内に調製するのが最も好ましい。この硫酸アンモニウム濃度が1.5mol/L未満では浸出率が低下するおそれがあり、特に0.50mol/L未満では本発明の効果が良好に発揮されなくなるおそれがある。逆に、硫酸アンモニウム濃度が3.5mol/L程度を超えて増加させても浸出率があまり変わらないのにかかわらず、中和に要するコストが増加するので好ましくなく、さらに4.1mol/Lを超えると硫酸アンモニウムが過飽和になって析出するので、浸出処理に悪影響を及ぼすおそれがある。なお、硫酸アンモニウム濃度は、吸光光度法、イオンクロマト法等により測定することができる。硫酸アンモニウム濃度が上記の範囲から外れたときは、硫酸アンモニウムの添加量で調整することができる。 In this leaching treatment, the ammonium sulfate concentration in the ammonium sulfate aqueous solution is preferably adjusted to a range of 0.50 mol/L to 4.1 mol/L, more preferably 1.5 mol/L to 3.5 mol/L, and most preferably 2.0 mol/L to 3.0 mol/L. If the ammonium sulfate concentration is less than 1.5 mol/L, the leaching rate may decrease, and especially if it is less than 0.50 mol/L, the effect of the present invention may not be exhibited well. On the other hand, even if the ammonium sulfate concentration is increased beyond about 3.5 mol/L, the leaching rate does not change much, but the cost required for neutralization increases, which is not preferable, and if it exceeds 4.1 mol/L, ammonium sulfate becomes supersaturated and precipitates, which may have a negative effect on the leaching treatment. The ammonium sulfate concentration can be measured by absorptiometry, ion chromatography, etc. If the ammonium sulfate concentration is outside the above range, it can be adjusted by the amount of ammonium sulfate added.
また、上記の浸出処理に際して、スラリー中の遊離アンモニア濃度を0.1~1.3mol/Lの範囲内に調製することが好ましい。遊離アンモニア濃度がこの範囲内であれば、ニッケルやコバルトをアンミン錯体の形態で安定的に浸出させることができる。この遊離アンモニア濃度が1.3mol/Lを超えても上記のアミン錯体の形態での安定的な浸出にはほとんど影響がなく、かえってコスト増になるうえ、排水処理への負荷が増加するので好ましくない。なお、遊離アンモニアとは分子状のアンモニア(NH3)のことであり、その濃度は蒸留法で分離した後、形態をNH4 +に変換し、吸光光度法により測定することができる。遊離アンモニア濃度が上記の範囲から外れたときは、アンモニア水の添加量により調整することができる。 In addition, during the above leaching treatment, it is preferable to adjust the free ammonia concentration in the slurry to within the range of 0.1 to 1.3 mol/L. If the free ammonia concentration is within this range, nickel and cobalt can be leached stably in the form of ammine complexes. Even if the free ammonia concentration exceeds 1.3 mol/L, it has almost no effect on the stable leaching in the form of the above amine complexes, and it is not preferable because it increases costs and increases the load on wastewater treatment. Note that free ammonia refers to molecular ammonia (NH 3 ), and its concentration can be measured by absorptiometry after separating it by distillation and converting it to NH 4 + . If the free ammonia concentration is outside the above range, it can be adjusted by adding an amount of ammonia water.
(4)熱分解沈殿工程
熱分解沈殿工程は、前工程の浸出処理で生成した浸出液を好適には液温が60℃以上100℃以下で0.50時間以上2.0時間以下保持することで加熱し、これによりニッケル及びコバルトのアンミン錯体を熱分解してこれらニッケル及びコバルトを水酸化物として析出させ、沈殿物として回収する工程である。この熱分解沈殿工程では例えば空気などの酸化剤を吹き込みながら撹拌することが好ましく、これによりコバルトの酸化が促進されるので、ニッケル及びコバルトをいずれも水酸化物として高い回収率で回収することが可能になる。すなわち、コバルトのアンミン錯体は、通常は熱分解により2価のコバルトとなるが、これを3価のコバルトに酸化することで水酸化物としての回収が促進される。なお、この熱分解沈殿工程における熱分解で発生するアンモニア及び三酸化硫黄は、回収して前工程の浸出工程の硫酸アンモニウムを含むアンモニア水として再利用するのが好ましい。
(4) Pyrolysis precipitation step The pyrolysis precipitation step is a step in which the leachate produced in the previous leaching step is heated by preferably maintaining the temperature at 60°C to 100°C for 0.50 to 2.0 hours, thereby pyrolyzing the ammine complexes of nickel and cobalt, precipitating the nickel and cobalt as hydroxides, and recovering them as precipitates. In this pyrolysis precipitation step, it is preferable to stir while blowing in an oxidizing agent such as air, which promotes the oxidation of cobalt, making it possible to recover both nickel and cobalt as hydroxides at a high recovery rate. That is, the ammine complex of cobalt is usually converted to divalent cobalt by pyrolysis, but by oxidizing it to trivalent cobalt, recovery as hydroxides is promoted. It is preferable to recover the ammonia and sulfur trioxide generated by pyrolysis in this pyrolysis precipitation step and reuse them as ammonia water containing ammonium sulfate in the previous leaching step.
(5)アルカリ洗浄工程
アルカリ洗浄工程は、前工程の熱分解沈殿工程で回収したニッケルコバルト混合水酸化物を好ましくは前述したアルカリ洗浄還元工程で用いたものと同様のアルカリ洗浄液を用いて洗浄する工程であり、これにより上記のアルカリ洗浄還元工程で除去しきれなかった亜鉛、硫黄、及び珪素のほか、浸出工程で添加される硫酸アンモニウム由来の炭素分が除去され、リチウムイオン二次電池の正極活物質用として好適に使用可能な不純物が極めて少ない高純度の前駆体を製造することができる。
(5) Alkaline Washing Step The alkaline washing step is a step in which the nickel-cobalt mixed hydroxide recovered in the preceding thermal decomposition precipitation step is washed, preferably with the same alkaline washing solution as that used in the alkaline washing and reduction step described above. This removes zinc, sulfur, and silicon that could not be completely removed in the alkaline washing and reduction step, as well as carbon derived from ammonium sulfate added in the leaching step, and makes it possible to produce a high-purity precursor with extremely few impurities that can be suitably used as a positive electrode active material for lithium-ion secondary batteries.
上記のように、本発明の実施形態の浸出液の製造方法により、硫酸ナトリウムを副生させることなく原料のニッケルコバルト混合水酸化物粒子からニッケル及びコバルトを含有する浸出液を製造することができるうえ、該原料に含まれるマンガン、鉄、アルミニウムなどの不純物を簡易に分離除去できるので、高価な金属ニッケルを原料とする場合に比べて安価に該浸出液を製造することができる。次に実施例を挙げて本発明をより具体的に説明するが、本発明は以下の実施例により何ら限定されるものではない。 As described above, the method for producing a leachate according to an embodiment of the present invention makes it possible to produce a leachate containing nickel and cobalt from the raw material nickel-cobalt mixed hydroxide particles without by-producing sodium sulfate, and also makes it possible to easily separate and remove impurities such as manganese, iron, and aluminum contained in the raw material, so that the leachate can be produced more inexpensively than when expensive metallic nickel is used as the raw material. The present invention will now be described in more detail with reference to examples, but the present invention is not limited in any way to the following examples.
(実施例)
容器内に装入した純水185mL及び濃度25質量%のアンモニア水15mLに、硫酸アンモニウム((NH4)2SO4)を39.64g添加し、硫酸アンモニウム濃度1.5mol/Lの硫酸アンモニウム水溶液を調製した。得られた硫酸アンモニウム水溶液に、下記表1に示す組成を有する粉末状のニッケルコバルト混合水酸化物(MHP)の20gを混合してスラリーとし、撹拌機で撹拌すると共にその液温を50℃に維持した状態で2時間保持することで浸出処理を行った。
(Example)
39.64 g of ammonium sulfate (( NH4 ) 2SO4 ) was added to 185 mL of pure water and 15 mL of 25% ammonia water placed in a container to prepare an ammonium sulfate aqueous solution with an ammonium sulfate concentration of 1.5 mol/L. 20 g of powdered nickel-cobalt mixed hydroxide (MHP) having the composition shown in Table 1 below was mixed with the resulting ammonium sulfate aqueous solution to prepare a slurry, which was stirred with a stirrer while maintaining the liquid temperature at 50°C for 2 hours to carry out a leaching treatment.
上記の浸出処理後はろ過により固液分離を行ったところ、乾燥質量12.5gの浸出残渣及び204mLの浸出液が得られた。これら浸出残渣及び浸出液の元素濃度を誘導結合プラズマ発光分光分析法(ICP-AES)により測定し、各元素の浸出率を下記式2により求めた。
[式2]
元素αの浸出率=浸出液中の元素αの質量/(浸出液中の元素αの質量+浸出残渣中の元素αの質量)×100
After the above leaching treatment, solid-liquid separation was performed by filtration to obtain a leaching residue with a dry mass of 12.5 g and a leaching solution of 204 mL. The element concentrations of the leaching residue and the leaching solution were measured by inductively coupled plasma atomic emission spectrometry (ICP-AES), and the leaching rate of each element was calculated by the following formula 2.
[Formula 2]
Leaching rate of element α=mass of element α in leaching solution/(mass of element α in leaching solution+mass of element α in leaching residue)×100
その結果、ニッケルの浸出率は45.6%、コバルトの浸出率は15.4%となり、ニッケルイオン及びコバルトイオンを多く含有するアンモニア水溶液からなる浸出液を製造することができた。 As a result, the nickel leaching rate was 45.6% and the cobalt leaching rate was 15.4%, and a leachate consisting of an aqueous ammonia solution containing a large amount of nickel ions and cobalt ions was produced.
(比較例)
容器内に装入した濃度25%のアンモニア水200mLに、上記表1に示す組成を有する粉末状のニッケルコバルト混合水酸化物(MHP)の20gを混合してスラリーとし、撹拌機で撹拌すると共にその液温を50℃に調節しながら2時間保持することで浸出処理を行った。以降は実施例と同様に固液分離して200mLの浸出液を得た。この浸出液の元素濃度を実施例と同様に測定して各元素の浸出率を求めた。
Comparative Example
200 mL of 25% ammonia water was placed in a container, and 20 g of powdered nickel-cobalt mixed hydroxide (MHP) having the composition shown in Table 1 was mixed to form a slurry, which was stirred with a stirrer and held for 2 hours while adjusting the liquid temperature to 50° C., to carry out a leaching treatment. Thereafter, solid-liquid separation was carried out in the same manner as in the examples, and 200 mL of leachate was obtained. The element concentrations of this leachate were measured in the same manner as in the examples, and the leaching rate of each element was determined.
その結果、ニッケルの浸出率は14.6%、コバルトの浸出率は0.2%となり、同じ温度で浸出処理を行った実施例に比べてニッケルを約1/3程度浸出させることができたが、コバルトはほとんど浸出させることができなかった。なお、この比較例では各元素の浸出率を下記式3により求めた。上記実施例及び比較例の測定結果をまとめて下記表2に示す。
[式3]
元素αの浸出率=浸出液中の元素αの質量/MHP中の元素αの質量×100
As a result, the leaching rate of nickel was 14.6%, and that of cobalt was 0.2%, which means that about 1/3 of the nickel was leached compared to the example in which the leaching treatment was performed at the same temperature, but almost no cobalt was leached. In this comparative example, the leaching rate of each element was calculated using the following formula 3. The measurement results of the above example and comparative example are summarized in Table 2 below.
[Formula 3]
Leaching rate of element α=mass of element α in leaching solution/mass of element α in MHP×100
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