JP7845576B2 - Aqueous solution recovery method - Google Patents
Aqueous solution recovery methodInfo
- Publication number
- JP7845576B2 JP7845576B2 JP2025522115A JP2025522115A JP7845576B2 JP 7845576 B2 JP7845576 B2 JP 7845576B2 JP 2025522115 A JP2025522115 A JP 2025522115A JP 2025522115 A JP2025522115 A JP 2025522115A JP 7845576 B2 JP7845576 B2 JP 7845576B2
- Authority
- JP
- Japan
- Prior art keywords
- lithium
- aqueous solution
- chlorine
- composite oxide
- contact
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Active
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01D—COMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
- C01D15/00—Lithium compounds
- C01D15/04—Halides
-
- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B1/00—Preliminary treatment of ores or scrap
- C22B1/02—Roasting processes
- C22B1/08—Chloridising roasting
-
- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B26/00—Obtaining alkali, alkaline earth metals or magnesium
- C22B26/10—Obtaining alkali metals
- C22B26/12—Obtaining lithium
-
- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B3/00—Extraction of metal compounds from ores or concentrates by wet processes
- C22B3/04—Extraction of metal compounds from ores or concentrates by wet processes by leaching
-
- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B7/00—Working 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
-
- H—ELECTRICITY
- H01—ELECTRIC ELEMENTS
- H01M—PROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
- H01M10/00—Secondary cells; Manufacture thereof
- H01M10/54—Reclaiming serviceable parts of waste accumulators
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P10/00—Technologies related to metal processing
- Y02P10/20—Recycling
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/84—Recycling of batteries or fuel cells
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Materials Engineering (AREA)
- Organic Chemistry (AREA)
- Manufacturing & Machinery (AREA)
- Metallurgy (AREA)
- Life Sciences & Earth Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- General Life Sciences & Earth Sciences (AREA)
- Geology (AREA)
- Mechanical Engineering (AREA)
- Geochemistry & Mineralogy (AREA)
- Electrochemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Inorganic Chemistry (AREA)
- Manufacture And Refinement Of Metals (AREA)
- Secondary Cells (AREA)
- Processing Of Solid Wastes (AREA)
Description
本発明は、リチウムイオン電池を溶解して得られる複合酸化物に含有されるリチウムについて、リチウムを含有する水性溶液として回収する水性溶液回収方法に関する。This invention relates to an aqueous solution recovery method for recovering lithium contained in a composite oxide obtained by dissolving a lithium-ion battery, as an aqueous solution containing lithium.
リチウムを用いた電池(以下、「リチウムイオン電池」という。)は、パソコン、スマートフォンといった比較的小型な機器から、電気自動車や太陽光蓄電設備といった大型の機器にも利用されている。Lithium-based batteries (hereinafter referred to as "lithium-ion batteries") are used in a range of devices, from relatively small devices such as personal computers and smartphones to large devices such as electric vehicles and solar energy storage systems.
リチウムイオン電池は、鉄やアルミニウム等の金属による外装材を用いて形成されている。また、外装材の内部には、アルミニウム箔にニッケル酸リチウムやコバルト酸リチウム等の正極活物質をアルミニウム箔に固着させた正極材と、銅箔の表面に黒鉛等の負極活物質を固着させた負極材とを有する。そして、正極材と負極材との間に、ポリプロピレンの多孔質樹脂フィルム等からなるセパレータを設けると共に、外装材の内部を六フッ化リン酸リチウム等の電解液を充填して封入した構造を有する。Lithium-ion batteries are formed using metal casings such as iron or aluminum. Inside the casing, there is a positive electrode material, where a positive electrode active material such as lithium nickelate or lithium cobaltate is fixed to aluminum foil, and a negative electrode material, where a negative electrode active material such as graphite is fixed to the surface of copper foil. A separator made of a porous polypropylene resin film or the like is placed between the positive and negative electrode materials, and the inside of the casing is filled with an electrolyte such as lithium hexafluoride phosphate and sealed.
リチウムイオン電池は、充放電の繰り返し等による性能の劣化や機器の処分等に起因して、廃リチウムイオン電池として処分される。また、製造工程において不良品が発生した際にも、廃リチウムイオン電池として処分される。このため、近年の電気自動車の製造台数の増加に伴い、電気自動車用として製造されたリチウムイオン電池の処分数(廃リチウムイオン電池の数)が増加することが予想される。Lithium-ion batteries are disposed of as waste lithium-ion batteries due to performance degradation from repeated charging and discharging, as well as equipment disposal. They are also disposed of as waste lithium-ion batteries when defective products are produced during the manufacturing process. Therefore, with the recent increase in the number of electric vehicles manufactured, the number of lithium-ion batteries to be disposed of (the number of waste lithium-ion batteries) manufactured for electric vehicles is expected to increase.
廃リチウムイオン電池には、銅、ニッケル、コバルト、リチウム等の有価金属が含まれている。そのため、廃リチウムイオン電池の処分に関して、資源保護や環境汚染への対策として、有価金属の回収及びリサイクル技術の開発が行われている。Waste lithium-ion batteries contain valuable metals such as copper, nickel, cobalt, and lithium. Therefore, in relation to the disposal of waste lithium-ion batteries, technologies for recovering and recycling these valuable metals are being developed as a measure to protect resources and prevent environmental pollution.
廃リチウムイオン電池から有価金属を回収する方法として、廃リチウムイオン電池を高温で溶解すると共に、溶解により得られる溶融金属から銅、ニッケル、コバルトを含む金属を回収する乾式製錬法が提案されている。そして、乾式製錬法においては、アルミニウム等の資源価値の低い金属が酸化しスラグとなるため、銅、ニッケル、コバルトといった有価金属と容易に分離できることが利点である。As a method for recovering valuable metals from waste lithium-ion batteries, a dry smelting method has been proposed in which waste lithium-ion batteries are melted at high temperatures, and metals including copper, nickel, and cobalt are recovered from the molten metal obtained by the melting process. A key advantage of this dry smelting method is that metals with low resource value, such as aluminum, oxidize and become slag, making them easily separate from valuable metals like copper, nickel, and cobalt.
なお、乾式製錬法において、廃リチウムイオン電池に含まれていたリチウムは酸化して酸化リチウムとなり、酸化アルミニウム、酸化ケイ素、酸化カルシウム、酸化マグネシウム等と共にスラグを形成する。形成されたスラグにおいては、リチウムの含有量が低いことから、当該リチウムを回収し再利用することは容易ではない。In the dry smelting process, lithium contained in waste lithium-ion batteries oxidizes to lithium oxide, which, along with aluminum oxide, silicon oxide, calcium oxide, magnesium oxide, etc., forms slag. Because the lithium content in the formed slag is low, recovering and reusing the lithium is not easy.
このため、リチウムの含有量が低いスラグから当該リチウムを回収する方法について、研究及び開発が行われている。例えば、特許文献1は、廃リチウムイオン電池等の原料を溶融して得られるLi含有スラグについて、Al/Li及びSi/Liの値の範囲や、Al及びSiの含有量を規定し、リチウムの含有率を高めたスラグの製造方法を開示する。また、特許文献2は、廃リチウムイオン電池を対象とした乾式製錬法において、溶融して得られた溶融金属に塩化物源を添加することで、当該溶融金属にて生成された塩化リチウムを金属ヒュームとして回収する方法を開示する。Therefore, research and development are being conducted on methods for recovering lithium from slag with a low lithium content. For example, Patent Document 1 discloses a method for producing slag with a high lithium content by specifying the range of Al/Li and Si/Li values and the Al and Si content for Li-containing slag obtained by melting raw materials such as waste lithium-ion batteries. Patent Document 2 also discloses a method for recovering lithium chloride generated in molten metal as a metal fume by adding a chloride source to the molten metal obtained in a dry smelting method for waste lithium-ion batteries.
しかしながら、特許文献1に開示された方法では、乾式製錬法の際に溶融金属に添加するフラックスの成分を厳選する必要があり、当該フラックスの適用につき、リサイクルとしての産業副産物の適用(再利用)が難しく、実際の操業への適用が容易ではない。また、特許文献2に開示された方法では、生成された塩化リチウムを金属ヒュームとして回収する際に、金属ヒュームの付着等に起因する周囲の炉壁等の設備の損傷を招く。このため、設備のメンテナンス及び改修等に要するコストの上昇が見込まれ、実際の操業への適用は困難である。However, the method disclosed in Patent Document 1 requires careful selection of the flux components added to the molten metal during the dry smelting process. Applying this flux as a recycled industrial by-product (reuse) is difficult, making its practical application in actual operations challenging. Furthermore, the method disclosed in Patent Document 2, when recovering the generated lithium chloride as metal fumes, can cause damage to surrounding equipment such as furnace walls due to the adhesion of metal fumes. Therefore, an increase in the costs required for equipment maintenance and repair is anticipated, making practical application in actual operations difficult.
本発明は上記事情に鑑みてなされたもので、その目的とするところは、複合酸化物に含有されるリチウムについて、リチウムを含有する水性溶液として回収できる水性溶液回収方法を提供することにある。The present invention has been made in view of the above circumstances, and its object is to provide an aqueous solution recovery method that can recover lithium contained in a composite oxide as an aqueous solution containing lithium.
[1]複合酸化物に含有されるリチウムについて、リチウムを含有する水性溶液として回収する水性溶液回収方法であって、前記複合酸化物に含有されるリチウムに対する塩素の物質量比が1.0以上5.5以下となるように調整された前記塩素又は塩素化合物と、前記複合酸化物とを、500℃以上1350℃以下の状態で接触させる接触工程と、前記接触工程を経た前記塩素又は塩素化合物と前記複合酸化物とに水性溶液を接触させることで、前記リチウムが浸透した前記水性溶液を回収する水性溶液回収工程と、を有する、水性溶液回収方法。
[2]前記塩素化合物は、アルカリ金属の塩化物、アルカリ土類金属の塩化物のうち少なくとも1種を含む、[1]に記載の水性溶液回収方法。
[3]前記複合酸化物は、リチウムイオン電池を溶解させた溶融金属からコバルト及びニッケルのうち1種又は2種の元素を含む金属を回収するプロセスにより、当該金属が回収された後のスラグである、[1]又は[2]に記載の水性溶液回収方法。
[4]前記接触工程を経た前記塩素又は塩素化合物と前記複合酸化物とに接触させる前記水性溶液はpH値が5.0以上10.0以下である、[1]~[3]のいずれか1つに記載の水性溶液回収方法。
[1] A method for recovering lithium contained in a composite oxide as an aqueous solution containing lithium, comprising: a contact step of contacting the composite oxide with chlorine or a chlorine compound, which has been adjusted so that the molar ratio of chlorine to lithium contained in the composite oxide is 1.0 or more and 5.5 or less, at a temperature of 500°C or more and 1350°C or less; and an aqueous solution recovery step of recovering the aqueous solution in which the lithium has permeated by contacting the chlorine or chlorine compound and the composite oxide that have undergone the contact step with an aqueous solution.
[2] The aqueous solution recovery method according to [1], wherein the chlorine compound comprises at least one of alkali metal chlorides and alkaline earth metal chlorides.
[3] The aqueous solution recovery method according to [1] or [2], wherein the composite oxide is the slag remaining after the metal is recovered by a process of recovering a metal containing one or two elements of cobalt and nickel from the molten metal obtained by dissolving a lithium-ion battery.
[4] The aqueous solution recovery method according to any one of [1] to [3], wherein the aqueous solution that is brought into contact with the chlorine or chlorine compound and the composite oxide after the contact step has a pH value of 5.0 or more and 10.0 or less.
本発明によれば、複合酸化物に含有されるリチウムについて、リチウムを含有する水性溶液として回収できる。According to the present invention, lithium contained in a complex oxide can be recovered as a lithium-containing aqueous solution.
以下、本発明の実施形態について説明する。本発明の水性溶液回収方法は、複合酸化物に含有されるリチウムについて、リチウムを含有する水性溶液として回収する方法である。The embodiments of the present invention will be described below. The aqueous solution recovery method of the present invention is a method for recovering lithium contained in a complex oxide as an aqueous solution containing lithium.
複合酸化物として、乾式製錬法を用いて、リチウムイオン電池を溶解させた溶融金属からコバルト及びニッケルのうち1種又は2種の元素を含む金属を回収するプロセスにより、当該金属が回収された後のスラグを用いてもよい。As a composite oxide, the slag remaining after the recovery of a metal containing one or two elements from cobalt and nickel from the molten metal obtained by dissolving lithium-ion batteries using a dry smelting method may be used.
本発明の水性溶液回収方法は、複合酸化物に含有されるリチウムに対する塩素の物質量比が1.0以上5.5以下となるように調整された塩素又は塩素化合物と、複合酸化物とを、500℃以上1350℃以下の状態で接触させる接触工程を有する。The aqueous solution recovery method of the present invention comprises a contact step of bringing chlorine or a chlorine compound, which has been adjusted so that the molar ratio of chlorine to lithium contained in the composite oxide is 1.0 or more and 5.5 or less, into contact with the composite oxide at a temperature of 500°C or more and 1350°C or less.
複合酸化物に含有されるリチウムに対する塩素の物質量比を1.0以上とすることで、リチウムと塩素又は塩素化合物との塩化反応が促進される。By setting the molar ratio of chlorine to lithium in the composite oxide to 1.0 or higher, the chlorination reaction between lithium and chlorine or chlorine compounds is promoted.
なお、複合酸化物に含有されるリチウムに対する塩素の物質量比が1.0未満である場合、リチウムと塩素又は塩素化合物との塩化反応が促進されず、リチウムの回収を十分に行うことができない。また、複合酸化物に含有されるリチウムに対する塩素の物質量比が高すぎても、リチウムに対する塩素の添加量が過剰になり、更に塩素又は塩素化合物の供給を増やしてもリチウムの回収の効果に変化が見られず、処理コストが増加してしまう。従って、複合酸化物に含有されるリチウムに対する塩素の物質量比は5.5以下が好ましく、5.0以下がさらに好ましい。Furthermore, if the molar ratio of chlorine to lithium contained in the composite oxide is less than 1.0, the chlorination reaction between lithium and chlorine or chlorine compounds will not be promoted, and lithium cannot be sufficiently recovered. Also, if the molar ratio of chlorine to lithium contained in the composite oxide is too high, the amount of chlorine added to the lithium will be excessive, and even if the supply of chlorine or chlorine compounds is further increased, there will be no change in the effect of lithium recovery, and processing costs will increase. Therefore, the molar ratio of chlorine to lithium contained in the composite oxide is preferably 5.5 or less, and more preferably 5.0 or less.
ここで、塩素又は塩素化合物の調整は、複合酸化物と接触させる前に、複合酸化物に含有されるリチウムの質量を算出し、算出されたリチウムの質量に基づき、リチウムに対する塩素の物質量比が1.0以上5.5以下となるように調整してよい。より詳細には、リチウムに対する塩素の物質量比が1.0以上5.5以下となるように、複合酸化物と接触させる塩素の量又は塩素化合物の量を調整してよい。リチウムの質量の算出方法については、複合酸化物に含有されるリチウムの質量を算出し得る方法である限り、限定するものではない。例えば、複合酸化物の一部を酸溶解し、誘導結合プラズマ発光分光分析法(ICP-AES)を用いて測定及び算出を行ってよい。また、複合酸化物を生成するプロセスにおいて、各原料に含まれるリチウムの質量濃度と各原料の全原料に対する重量割合とに基づいて算出してもよい。Here, the adjustment of chlorine or chlorine compounds may be performed by calculating the mass of lithium contained in the complex oxide before contact with the complex oxide, and adjusting the amount of chlorine to lithium based on the calculated mass of lithium so that the molar ratio of chlorine to lithium is between 1.0 and 5.5. More specifically, the amount of chlorine or chlorine compound to be contacted with the complex oxide may be adjusted so that the molar ratio of chlorine to lithium is between 1.0 and 5.5. The method for calculating the mass of lithium is not limited as long as it is a method that can calculate the mass of lithium contained in the complex oxide. For example, a portion of the complex oxide may be dissolved in acid, and the measurement and calculation may be performed using inductively coupled plasma atomic emission spectrometry (ICP-AES). Alternatively, in the process of producing the complex oxide, the calculation may be based on the mass concentration of lithium contained in each raw material and the weight ratio of each raw material to the total raw materials.
塩素又は塩素化合物と複合酸化物との接触は、500℃以上1350℃以下の状態で行う。500℃未満の状態で接触させた場合には、複合酸化物に含有されるリチウムと塩素又は塩素化合物との塩化反応が促進されないためである。塩素又は塩素化合物と複合酸化物との接触は、高温であるほどリチウムと塩素又は塩素化合物との塩化反応が促進されるため、600℃以上の状態で接触させることが好ましく、800℃以上の状態で接触させることがより好ましい。また、1350℃を超えた場合には、リチウムと塩素又は塩素化合物との塩化反応が促進されて塩化リチウムが生成されるものの、塩化リチウムの揮発が発生し、その後の水性溶液への浸透が促進されず、リチウムの回収率が低下するためである。Contact between chlorine or chlorine compounds and complex oxides should be carried out at a temperature between 500°C and 1350°C. If contact occurs below 500°C, the chlorination reaction between lithium contained in the complex oxide and chlorine or chlorine compounds will not be promoted. Since the chlorination reaction between lithium and chlorine or chlorine compounds is promoted at higher temperatures, contact at 600°C or higher is preferable, and contact at 800°C or higher is more preferable. Furthermore, if the temperature exceeds 1350°C, although the chlorination reaction between lithium and chlorine or chlorine compounds is promoted and lithium chloride is produced, the volatilization of lithium chloride occurs, hindering subsequent penetration into the aqueous solution and reducing the lithium recovery rate.
ここで、塩素は、塩素ガスを適用してよい。塩素化合物は、金属塩化物を適用してよい。具体的に、塩素化合物は、アルカリ金属の塩化物、アルカリ土類金属の塩化物のうち少なくとも1種を含んでよい。なお、アルカリ土類金属にはベリリウム及びマグネシウムも含まれる。これらの塩素化合物及び塩素は、重金属と塩素との化合物に比べて沸点が高い。このため、塩素又は塩素化合物と複合酸化物との接触時の温度を500℃以上1350℃以下とすることで、塩素化合物及び塩素の揮発が抑制され、複合酸化物に含有されるリチウムの塩化リチウムとしての生成を促進させることができる。Here, chlorine may be provided by chlorine gas. The chlorine compound may be a metal chloride. Specifically, the chlorine compound may include at least one of alkali metal chlorides or alkaline earth metal chlorides. Alkaline earth metals also include beryllium and magnesium. These chlorine compounds and chlorine have higher boiling points than compounds of heavy metals and chlorine. Therefore, by setting the temperature at which chlorine or a chlorine compound comes into contact with the composite oxide to between 500°C and 1350°C, the volatilization of the chlorine compound and chlorine can be suppressed, and the formation of lithium as lithium chloride from the lithium contained in the composite oxide can be promoted.
また、塩素又は塩素化合物と複合酸化物との接触時における温度は、より具体的には、複合酸化物の温度として管理されてよい。あるいは、塩素又は塩素化合物と複合酸化物とを装入させる反応容器内の雰囲気の温度として管理されてもよい。Furthermore, the temperature at the time of contact between chlorine or a chlorine compound and the complex oxide may be controlled more specifically as the temperature of the complex oxide. Alternatively, it may be controlled as the temperature of the atmosphere inside the reaction vessel into which the chlorine or chlorine compound and the complex oxide are charged.
本発明の水性溶液回収方法は、接触工程を経た塩素又は塩素化合物と複合酸化物とに水性溶液を接触させることで、リチウムが浸透した水性溶液を回収する水性溶液回収工程を有する。The present invention provides an aqueous solution recovery method which includes an aqueous solution recovery step in which an aqueous solution is brought into contact with chlorine or a chlorine compound and a complex oxide that has undergone a contact step, thereby recovering an aqueous solution into which lithium has permeated.
塩素又は塩素化合物と複合酸化物との接触により、複合酸化物に含有されるリチウムと塩素又は塩素化合物との塩化反応が促進され、塩化リチウムが生成される。このため、接触工程を経た塩素又は塩素化合物と複合酸化物とに水性溶液を接触させることで、生成された塩化リチウムが水性溶液に取り込まれ、水性溶液にリチウムが浸透した状態となる。その結果、複合酸化物に含有されていたリチウムは、リチウムが浸透した水性溶液として回収される。Contact between chlorine or a chlorine compound and a complex oxide accelerates the chlorination reaction between the lithium contained in the complex oxide and the chlorine or chlorine compound, producing lithium chloride. Therefore, by bringing the chlorine or chlorine compound and the complex oxide, which have undergone the contact process, into contact with an aqueous solution, the generated lithium chloride is incorporated into the aqueous solution, resulting in a state where lithium permeates the aqueous solution. As a result, the lithium contained in the complex oxide is recovered as an aqueous solution permeated with lithium.
塩素又は塩素化合物と複合酸化物とを接触させる時間は、20分以上180分以下とすることが好ましい。接触工程の時間を当該範囲にすることで、リチウムと塩素又は塩素化合物との塩化反応がより促進され、複合酸化物に含有されるリチウムを、水溶液に浸透するリチウムとしてより確実に回収できるためである。なお、接触させる時間について、180分を超える時間とした場合、時間を延長したとしてもリチウムの回収効率の向上が見られないためである。The contact time between chlorine or a chlorine compound and the complex oxide is preferably 20 minutes or more and 180 minutes or less. This is because setting the contact time within this range further promotes the chlorination reaction between lithium and chlorine or the chlorine compound, allowing for more reliable recovery of the lithium contained in the complex oxide as lithium permeating the aqueous solution. Furthermore, if the contact time exceeds 180 minutes, no improvement in lithium recovery efficiency is observed, even if the time is extended.
塩素又は塩素化合物と複合酸化物とに接触させる水性溶液は、pH値を5.0以上10.0以下とすることが好ましい。水性溶液のpH値を当該範囲の値にすることで、水性溶液への重金属(ニッケル、コバルト、マンガン等)の溶解が抑制され、共存元素の少ないリチウムの水性溶液への浸透が促進されるためである。水性溶液は、純水等を適用してよい。The aqueous solution used to contact chlorine or a chlorine compound with a complex oxide preferably has a pH value of 5.0 to 10.0. This is because setting the pH value of the aqueous solution within this range suppresses the dissolution of heavy metals (nickel, cobalt, manganese, etc.) into the aqueous solution, while promoting the penetration of lithium, which has few coexisting elements, into the aqueous solution. Pure water or the like may be used as the aqueous solution.
本発明の水性溶液回収方法によりリチウムが浸透した水性溶液を回収する観点から、リチウムを含有する複合酸化物は、リチウムの含有量がリチウム元素換算で0.5質量%以上であることが好ましく、1.0質量%以上であることがより好ましい。From the viewpoint of recovering an aqueous solution in which lithium has permeated using the aqueous solution recovery method of the present invention, the lithium-containing composite oxide preferably has a lithium content of 0.5% by mass or more, and more preferably 1.0% by mass or more, in terms of lithium element.
次に、本発明の水性溶液回収方法を実施した結果について説明する。各実施例においては、リチウムを含有する複合酸化物として、酸化カルシウムと二酸化珪素との物質量比(CaO/SiO2)、及び、含有されるリチウムの質量(質量%)が異なる4種類の酸化物(A~D)の何れかを用いた。実施例に用いた酸化物(A~D)の成分情報を表1に示す。 Next, the results of implementing the aqueous solution recovery method of the present invention will be described. In each example, one of four types of oxides (A to D) with different molar ratios of calcium oxide and silicon dioxide (CaO/ SiO₂ ) and mass (mass%) of lithium was used as the lithium-containing composite oxide. Table 1 shows the component information of the oxides (A to D) used in the examples.
そして、表1に示す酸化物(A~D)に、各酸化物に含有されるリチウムに対する塩素の物質量比が所定の値となるように塩素化合物を接触させ、所定の温度で60分保持した。そして、塩素化合物及び酸化物に対して重量比で30倍の水性溶液を用意し、塩素化合物及び酸化物を水性溶液の中に浸漬させると共に120分間撹拌して濾過し、リチウムを含有する水性溶液を得た。塩素化合物として、塩化カルシウム(CaCl2)を用いた。水性溶液として、pH値が5.0以上10.0以下とする純水を用いた。 Then, chlorine compounds were brought into contact with the oxides (A to D) shown in Table 1, such that the molar ratio of chlorine to lithium contained in each oxide was a predetermined value, and the mixture was held at a predetermined temperature for 60 minutes. Next, an aqueous solution was prepared in a weight ratio of 30 times that of the chlorine compound and oxide. The chlorine compound and oxide were immersed in the aqueous solution and stirred for 120 minutes, then filtered to obtain an aqueous solution containing lithium. Calcium chloride ( CaCl₂ ) was used as the chlorine compound. Pure water with a pH value of 5.0 to 10.0 was used as the aqueous solution.
次に、得られた水性溶液におけるリチウムの含有量(質量%)を測定し、酸化物(A~D)に含有されるリチウムの質量(質量%)に対する水性溶液のリチウムの含有量(質量%)の百分率(%)をリチウム回収率として計算した。実施の結果を表2及び表3に示す。Next, the lithium content (mass%) in the obtained aqueous solution was measured, and the lithium recovery rate was calculated as the percentage (%) of the lithium content (mass%) in the aqueous solution relative to the total mass (mass%) of lithium contained in the oxides (A to D). The results are shown in Tables 2 and 3.
表3に示す比較例1~19は、複合酸化物としての酸化物A~Dに対し、各酸化物に含有されるリチウムに対する塩素の物質量比(Cl/Li)を0.5とし、又は、各酸化物と塩素化合物との接触時の温度を1400℃とし、あるいは、各酸化物と塩素化合物との接触時の温度を400℃として実施した。その結果、各酸化物に含有される全リチウムのうち、最大値として40%の量のリチウムの回収率に留まった。Comparative Examples 1 to 19, shown in Table 3, were conducted with oxides A to D as composite oxides, using a molar ratio of chlorine to lithium (Cl/Li) of 0.5, or with a contact temperature of 1400°C between each oxide and the chlorine compound, or with a contact temperature of 400°C between each oxide and the chlorine compound. As a result, the recovery rate of lithium was limited to a maximum of 40% of the total lithium contained in each oxide.
表2に示す本発明例1~31は、酸化物Aに含有されるリチウムに対する塩素の物質量比(Cl/Li)を1.0以上5.5以下とし、酸化物Aと塩素化合物との接触時の温度を500℃以上1350℃以下として実施した。そして、酸化物Aに含有される全リチウムの50%以上の量を水性溶液として回収できた。Examples 1 to 31 of the present invention, shown in Table 2, were carried out with a molar ratio of chlorine to lithium (Cl/Li) contained in oxide A of 1.0 to 5.5, and a contact temperature of 500°C to 1350°C between oxide A and the chlorine compound. In these cases, more than 50% of the total lithium contained in oxide A was recovered as an aqueous solution.
本発明例32~46は、複合酸化物として酸化物B、C、Dを使用した。そして、酸化物B、C、Dに含有されるリチウムに対する塩素の物質量比(Cl/Li)を1.8以上5.5以下とし、酸化物B、C、Dと塩素化合物との接触時の温度を800℃以上1000℃以下として実施した。その結果、酸化物B、C、Dに含有される全リチウムの70%以上の量を水性溶液として回収できた。Examples 32 to 46 of the present invention used oxides B, C, and D as composite oxides. The molar ratio of chlorine to lithium contained in oxides B, C, and D (Cl/Li) was set to 1.8 or more and 5.5 or less, and the contact temperature between oxides B, C, and D and the chlorine compound was set to 800°C or more and 1000°C or less. As a result, more than 70% of the total lithium contained in oxides B, C, and D could be recovered as an aqueous solution.
以上から、本発明の水性溶液回収方法により、複合酸化物に含有されるリチウムについて、リチウムを含有する水性溶液として回収できることが確認できた。また、本発明の水性溶液回収方法によれば、リチウムを含有しつつ様々な組成を有する複合酸化物に適用でき、塩素又は塩素化合物の揮発を生じること無く、リチウムを含有する水性溶液を回収できることが確認できた。
From the above, it has been confirmed that the aqueous solution recovery method of the present invention can recover lithium contained in a composite oxide as a lithium-containing aqueous solution. Furthermore, it has been confirmed that the aqueous solution recovery method of the present invention can be applied to composite oxides having various compositions while containing lithium, and that a lithium-containing aqueous solution can be recovered without the volatilization of chlorine or chlorine compounds.
Claims (5)
前記複合酸化物に含有されるリチウムに対する塩素の物質量比が2.7以上5.5以下となるように調整された前記塩素又は塩素化合物と、前記複合酸化物とを、500℃以上1350℃以下の状態で接触させる接触工程と、
前記接触工程を経た前記塩素又は塩素化合物と前記複合酸化物とに水性溶液を接触させることで、前記リチウムが浸透した前記水性溶液を回収する水性溶液回収工程と、
を有する、水性溶液回収方法。 A method for recovering lithium contained in a complex oxide as an aqueous solution containing lithium,
A contact step in which the chlorine or chlorine compound, which has been adjusted so that the molar ratio of chlorine to lithium contained in the composite oxide is 2.7 or more and 5.5 or less, is brought into contact with the composite oxide at a temperature of 500°C or more and 1350°C or less,
A water solution recovery step involves contacting the chlorine or chlorine compound and the composite oxide that have undergone the contact step with an aqueous solution to recover the aqueous solution in which the lithium has permeated;
A method for recovering an aqueous solution, comprising the following characteristics.
Applications Claiming Priority (3)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2024039683 | 2024-03-14 | ||
| JP2024039683 | 2024-03-14 | ||
| PCT/JP2025/000808 WO2025192009A1 (en) | 2024-03-14 | 2025-01-14 | Aqueous solution recovery method |
Publications (3)
| Publication Number | Publication Date |
|---|---|
| JPWO2025192009A1 JPWO2025192009A1 (en) | 2025-09-18 |
| JPWO2025192009A5 JPWO2025192009A5 (en) | 2026-02-18 |
| JP7845576B2 true JP7845576B2 (en) | 2026-04-14 |
Family
ID=97063156
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP2025522115A Active JP7845576B2 (en) | 2024-03-14 | 2025-01-14 | Aqueous solution recovery method |
Country Status (2)
| Country | Link |
|---|---|
| JP (1) | JP7845576B2 (en) |
| WO (1) | WO2025192009A1 (en) |
Citations (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2003031229A (en) | 2001-07-12 | 2003-01-31 | Tmc Kk | Collection of valuable metals |
| JP2005042189A (en) | 2003-07-25 | 2005-02-17 | Ise Chemicals Corp | Cobalt recovery method |
| WO2023002048A1 (en) | 2021-07-23 | 2023-01-26 | Basf Se | Process for recycling lithium ion battery materials |
| WO2023048196A1 (en) | 2021-09-22 | 2023-03-30 | 株式会社アサカ理研 | Treatment method for chlorine gas |
| JP2023529256A (en) | 2021-05-07 | 2023-07-10 | ヨン・ブン・コーポレーション | Method for recovering lithium from waste lithium secondary batteries using dry melting method |
| JP2023103937A (en) | 2022-01-14 | 2023-07-27 | 株式会社アサカ理研 | Method for recovering lithium from waste lithium-ion batteries |
| WO2024024589A1 (en) | 2022-07-28 | 2024-02-01 | Jfeスチール株式会社 | Valuable element recovery method and metal production method |
-
2025
- 2025-01-14 JP JP2025522115A patent/JP7845576B2/en active Active
- 2025-01-14 WO PCT/JP2025/000808 patent/WO2025192009A1/en active Pending
Patent Citations (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2003031229A (en) | 2001-07-12 | 2003-01-31 | Tmc Kk | Collection of valuable metals |
| JP2005042189A (en) | 2003-07-25 | 2005-02-17 | Ise Chemicals Corp | Cobalt recovery method |
| JP2023529256A (en) | 2021-05-07 | 2023-07-10 | ヨン・ブン・コーポレーション | Method for recovering lithium from waste lithium secondary batteries using dry melting method |
| WO2023002048A1 (en) | 2021-07-23 | 2023-01-26 | Basf Se | Process for recycling lithium ion battery materials |
| WO2023048196A1 (en) | 2021-09-22 | 2023-03-30 | 株式会社アサカ理研 | Treatment method for chlorine gas |
| JP2023103937A (en) | 2022-01-14 | 2023-07-27 | 株式会社アサカ理研 | Method for recovering lithium from waste lithium-ion batteries |
| WO2024024589A1 (en) | 2022-07-28 | 2024-02-01 | Jfeスチール株式会社 | Valuable element recovery method and metal production method |
Also Published As
| Publication number | Publication date |
|---|---|
| WO2025192009A1 (en) | 2025-09-18 |
| JPWO2025192009A1 (en) | 2025-09-18 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| Forte et al. | Lithium iron phosphate batteries recycling: An assessment of current status | |
| Verma et al. | Retracted Article: Metal-ion batteries for electric vehicles: current state of the technology, issues and future perspectives | |
| Bankole et al. | Battery recycling technologies: Recycling waste lithium ion batteries with the impact on the environment in-view | |
| JP6314814B2 (en) | Method for recovering valuable metals from waste lithium-ion batteries | |
| Al-Asheh et al. | Treatment and recycling of spent lithium-based batteries: a review | |
| Fan et al. | Room-temperature extraction of individual elements from charged spent LiFePO4 batteries | |
| JP5062262B2 (en) | Battery member processing method | |
| CA2319285A1 (en) | A method for neutralizing and recycling spent lithium metal polymer rechargeable batteries | |
| KR100448273B1 (en) | Recovery Method of Cobalt from spent lithium ion battery | |
| CN116194604B (en) | Methods for reusing active materials from cathode waste | |
| JP7357801B2 (en) | How to reuse active materials using cathode scraps | |
| Yao et al. | Recycling of spent lithium iron phosphate cathodes: challenges and progress | |
| KR20190121857A (en) | Nitrate process for preparing transition metal hydroxide precursors | |
| CN115104213A (en) | Method for recycling active material by using anode waste | |
| Hayagan et al. | A holistic review on the direct recycling of lithium-ion batteries from electrolytes to electrodes | |
| KR20230107003A (en) | Method for selective recovery of nickel and cobalt from nickel-cobalt-manganese mixture | |
| CN117597457A (en) | Manufacturing methods of valuable metals | |
| WO2025030307A1 (en) | Method for full-chain integrated regeneration of waste lithium iron phosphate positive electrode sheets, and regenerated lithium iron phosphate positive electrode sheet | |
| JP7845576B2 (en) | Aqueous solution recovery method | |
| Visone et al. | Recovery of LiFePO4 cathodes: Criticalities and prospect towards a long-term eco-friendly solution | |
| Chang et al. | CaCl2-assisted roasting for high-efficiency lithium extraction and fluorine stabilization in LFP battery recycling | |
| JP4815763B2 (en) | Method for dissolving lithium-containing positive electrode active material | |
| Bai et al. | Enabling Sustainable Lithium-Ion Battery Manufacturing via Recycling | |
| KR102957631B1 (en) | Reuse method of active material of positive electrode scrap | |
| Benjamasutin et al. | Recycling of lithium-ion batteries |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20250417 |
|
| A621 | Written request for application examination |
Free format text: JAPANESE INTERMEDIATE CODE: A621 Effective date: 20250417 |
|
| A131 | Notification of reasons for refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A131 Effective date: 20250930 |
|
| A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20251127 |
|
| TRDD | Decision of grant or rejection written | ||
| A01 | Written decision to grant a patent or to grant a registration (utility model) |
Free format text: JAPANESE INTERMEDIATE CODE: A01 Effective date: 20260303 |
|
| A61 | First payment of annual fees (during grant procedure) |
Free format text: JAPANESE INTERMEDIATE CODE: A61 Effective date: 20260316 |