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WO2025192009A1 - Aqueous solution recovery method - Google Patents

Aqueous solution recovery method

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Publication number
WO2025192009A1
WO2025192009A1 PCT/JP2025/000808 JP2025000808W WO2025192009A1 WO 2025192009 A1 WO2025192009 A1 WO 2025192009A1 JP 2025000808 W JP2025000808 W JP 2025000808W WO 2025192009 A1 WO2025192009 A1 WO 2025192009A1
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Prior art keywords
lithium
aqueous solution
chlorine
composite oxide
recovering
Prior art date
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Pending
Application number
PCT/JP2025/000808
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French (fr)
Japanese (ja)
Inventor
風彦 永田
陽太郎 井上
雄太 日野
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JFE Steel Corp
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JFE Steel Corp
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Application filed by JFE Steel Corp filed Critical JFE Steel Corp
Publication of WO2025192009A1 publication Critical patent/WO2025192009A1/en
Pending legal-status Critical Current
Anticipated expiration legal-status Critical

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Classifications

    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01DCOMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
    • C01D15/00Lithium compounds
    • C01D15/04Halides
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B1/00Preliminary treatment of ores or scrap
    • C22B1/02Roasting processes
    • C22B1/08Chloridising roasting
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B26/00Obtaining alkali, alkaline earth metals or magnesium
    • C22B26/10Obtaining alkali metals
    • C22B26/12Obtaining lithium
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B3/00Extraction of metal compounds from ores or concentrates by wet processes
    • C22B3/04Extraction of metal compounds from ores or concentrates by wet processes by leaching
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B7/00Working up raw materials other than ores, e.g. scrap, to produce non-ferrous metals and compounds thereof; Methods of a general interest or applied to the winning of more than two metals
    • HELECTRICITY
    • H01ELECTRIC ELEMENTS
    • H01MPROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
    • H01M10/00Secondary cells; Manufacture thereof
    • H01M10/54Reclaiming serviceable parts of waste accumulators
    • 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling
    • 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
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/84Recycling of batteries or fuel cells

Definitions

  • the present invention relates to an aqueous solution recovery method for recovering lithium contained in a composite oxide obtained by dissolving lithium-ion batteries as an aqueous solution containing lithium.
  • lithium-ion batteries Batteries that use lithium (hereinafter referred to as “lithium-ion batteries”) are used in a wide range of devices, from relatively small devices such as personal computers and smartphones to large devices such as electric vehicles and solar power storage facilities.
  • Lithium-ion batteries are constructed using exterior materials made from metals such as iron or aluminum. Inside the exterior material are positive electrode materials, which consist of aluminum foil with a positive electrode active material such as lithium nickel oxide or lithium cobalt oxide adhered to it, and negative electrode materials, which consist of copper foil with a negative electrode active material such as graphite adhered to its surface. A separator made of a porous resin film such as polypropylene is placed between the positive and negative electrode materials, and the interior of the exterior material is filled with an electrolyte such as lithium hexafluorophosphate and sealed inside.
  • positive electrode materials consist of aluminum foil with a positive electrode active material such as lithium nickel oxide or lithium cobalt oxide adhered to it
  • negative electrode materials which consist of copper foil with a negative electrode active material such as graphite adhered to its surface.
  • a separator made of a porous resin film such as polypropylene is placed between the positive and negative electrode materials, and the interior of the exterior material is filled with an electrolyte such as lithium hex
  • Patent Document 1 discloses a method for producing slag with a high lithium content, by specifying the ranges of Al/Li and Si/Li values and the Al and Si contents for Li-containing slag obtained by melting raw materials such as waste lithium-ion batteries.
  • Patent Document 2 discloses a method for recovering lithium chloride produced in molten metal obtained by melting waste lithium-ion batteries using a pyrometallurgical process, by adding a chloride source to the molten metal, as metal fumes.
  • the present invention was made in consideration of the above circumstances, and its purpose is to provide an aqueous solution recovery method that can recover lithium contained in a composite oxide as an aqueous solution containing lithium.
  • a method for recovering lithium contained in a composite oxide as an aqueous solution containing lithium comprising: a contacting step of contacting the composite oxide with chlorine or a chlorine compound, the chlorine or chlorine compound being adjusted so that the substance amount 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 recovering step of contacting the chlorine or chlorine compound and the composite oxide that have been subjected to the contacting step with an aqueous solution to recover the aqueous solution into which the lithium has permeated.
  • lithium contained in the composite oxide can be recovered as an aqueous solution containing lithium.
  • the aqueous solution recovery method of the present invention is a method for recovering lithium contained in a composite oxide as an aqueous solution containing lithium.
  • slag remaining after metals containing one or two of cobalt and nickel are recovered from molten metal obtained by dissolving lithium-ion batteries using a pyrometallurgical process may be used.
  • the aqueous solution recovery method of the present invention includes a contacting step in which chlorine or a chlorine compound, which has been adjusted so that the mass ratio of chlorine to lithium contained in the composite oxide is 1.0 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.
  • the ratio of chlorine to lithium contained in the composite oxide by mass is preferably 5.5 or less, and more preferably 5.0 or less.
  • the chlorine or chlorine compound may be adjusted by calculating the mass of lithium contained in the composite oxide before contacting it with the composite oxide, and adjusting the mass ratio of chlorine to lithium based on the calculated mass of lithium so that the mass ratio of chlorine to lithium is 1.0 or more and 5.5 or less. More specifically, the amount of chlorine or chlorine compound to be contacted with the composite oxide may be adjusted so that the mass ratio of chlorine to lithium is 1.0 or more and 5.5 or less.
  • 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 composite oxide. For example, a portion of the composite oxide may be dissolved in acid, and measurement and calculation may be performed using inductively coupled plasma atomic emission spectroscopy (ICP-AES). Alternatively, in the process of producing the composite oxide, the mass concentration of lithium may be calculated 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.
  • ICP-AES inductively coupled plasma atomic emission spectroscopy
  • Chlorine or chlorine compounds are contacted with the composite oxide at a temperature of 500°C or higher and 1350°C or lower. This is because contact at temperatures below 500°C does not promote the chlorination reaction between the lithium contained in the composite oxide and chlorine or chlorine compounds. The higher the temperature, the more promoted the chlorination reaction between lithium and chlorine or chlorine compounds. Therefore, contact at 600°C or higher is preferred, and contact at 800°C or higher is even more preferred. Furthermore, at temperatures above 1350°C, although the chlorination reaction between lithium and chlorine or chlorine compounds is promoted to produce lithium chloride, volatilization of the lithium chloride occurs, preventing its subsequent penetration into an aqueous solution and reducing the lithium recovery rate.
  • chlorine gas may be used as the chlorine.
  • a metal chloride may be used as the chlorine compound.
  • the chlorine compound may include at least one of an alkali metal chloride and an alkaline earth metal chloride.
  • alkaline earth metals also include beryllium and magnesium.
  • the temperature at the time of contact between chlorine or a chlorine compound and the composite oxide may be controlled as the temperature of the composite oxide.
  • it may be controlled as the temperature of the atmosphere inside the reaction vessel into which the chlorine or a chlorine compound and the composite oxide are charged.
  • the aqueous solution recovery method of the present invention includes an aqueous solution recovery step in which an aqueous solution is contacted with chlorine or a chlorine compound that has undergone a contact step and a composite oxide, thereby recovering an aqueous solution into which lithium has permeated.
  • the time for contacting the composite oxide with chlorine or a chlorine compound is preferably 20 minutes or more and 180 minutes or less.
  • the chlorination reaction between lithium and chlorine or a chlorine compound is further promoted, and the lithium contained in the composite oxide can be more reliably recovered as lithium that permeates into the aqueous solution. Note that if the contact time exceeds 180 minutes, no improvement in lithium recovery efficiency will be observed even if the time is extended.
  • the aqueous solution that is brought into contact with the chlorine or chlorine compound and the composite oxide preferably has a pH value of 5.0 or higher and 10.0 or lower.
  • a pH value of 5.0 or higher and 10.0 or lower By setting the pH value of the aqueous solution within this range, the dissolution of heavy metals (nickel, cobalt, manganese, etc.) into the aqueous solution is suppressed, and the penetration of lithium, which contains few coexisting elements, into the aqueous solution is promoted. Pure water, etc. may be used as the aqueous solution.
  • 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, calculated as elemental lithium.
  • the results of implementing the aqueous solution recovery method of the present invention will be described.
  • one of four types of oxides (A to D) was used as the lithium-containing composite oxide, which differed in the substance ratio of calcium oxide to silicon dioxide (CaO/SiO 2 ) and the mass (mass %) of lithium contained.
  • the component information of the oxides (A to D) used in the examples is shown in Table 1.
  • a chlorine compound was contacted with the oxides (A to D) shown in Table 1 so that the mass ratio of chlorine to lithium contained in each oxide was a predetermined value, and the mixture was maintained at a predetermined temperature for 60 minutes.
  • An aqueous solution with a weight ratio of 30 times the chlorine compound and oxide was then prepared, and the chlorine compound and oxide were immersed in the aqueous solution while stirring for 120 minutes and filtered to obtain an aqueous solution containing lithium.
  • Calcium chloride (CaCl 2 ) was used as the chlorine compound. Pure water with a pH value of 5.0 to 10.0 was used as the aqueous solution.
  • the aqueous solution recovery method of the present invention can recover lithium contained in a composite oxide as an aqueous solution containing lithium. Furthermore, it was confirmed that the aqueous solution recovery method of the present invention can be applied to composite oxides containing lithium and having various compositions, and can recover an aqueous solution containing lithium without causing volatilization of chlorine or chlorine compounds.

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  • 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)

Abstract

Provided is an aqueous solution recovery method with which it is possible to recover lithium contained in a composite oxide as a lithium-containing aqueous solution. This aqueous solution recovery method for recovering lithium contained in a composite oxide as a lithium-containing aqueous solution includes: a contact step for bringing chlorine or a chlorine compound adjusted so that the substance amount ratio of chlorine to lithium contained in the composite oxide is 1.0-5.5 into contact with the composite oxide at a temperature of 500-1350°C; and an aqueous solution recovery step for bringing the aqueous solution into contact with the composite oxide and the chlorine or chlorine compound that underwent the contact step, thereby recovering the aqueous solution permeated with the lithium.

Description

水性溶液回収方法Aqueous solution recovery method

 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。 The present invention relates to an aqueous solution recovery method for recovering lithium contained in a composite oxide obtained by dissolving lithium-ion batteries 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。 Batteries that use lithium (hereinafter referred to as "lithium-ion batteries") are used in a wide range of devices, from relatively small devices such as personal computers and smartphones to large devices such as electric vehicles and solar power storage facilities.

 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 constructed using exterior materials made from metals such as iron or aluminum. Inside the exterior material are positive electrode materials, which consist of aluminum foil with a positive electrode active material such as lithium nickel oxide or lithium cobalt oxide adhered to it, and negative electrode materials, which consist of copper foil with a negative electrode active material such as graphite adhered to its surface. A separator made of a porous resin film such as polypropylene is placed between the positive and negative electrode materials, and the interior of the exterior material is filled with an electrolyte such as lithium hexafluorophosphate and sealed inside.

 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 caused by repeated charging and discharging, or due to the disposal of the equipment. They are also disposed of as waste lithium-ion batteries when defective products are discovered during the manufacturing process. Therefore, with the increase in the number of electric vehicles manufactured in recent years, it is expected that the number of lithium-ion batteries manufactured for electric vehicles (the number of waste lithium-ion batteries) that are disposed of will also 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, with regard to the disposal of waste lithium-ion batteries, technologies are being developed to recover and recycle valuable metals as a measure to conserve 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 used lithium-ion batteries, a pyrometallurgical process has been proposed, in which the batteries are melted at high temperatures and metals including copper, nickel, and cobalt are recovered from the molten metal obtained by the melting. In the pyrometallurgical process, metals with low resource value, such as aluminum, are oxidized and turn into slag, which has the advantage that they can be easily separated from valuable metals such as 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 pyrometallurgical process, the lithium contained in the waste lithium-ion batteries is oxidized to lithium oxide, which forms slag together with aluminum oxide, silicon oxide, calcium oxide, magnesium oxide, etc. Because the lithium content in the slag that is formed is low, it is not easy to recover and reuse the lithium.

 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。 For this reason, research and development is being conducted into 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 ranges of Al/Li and Si/Li values and the Al and Si contents for Li-containing slag obtained by melting raw materials such as waste lithium-ion batteries. Furthermore, Patent Document 2 discloses a method for recovering lithium chloride produced in molten metal obtained by melting waste lithium-ion batteries using a pyrometallurgical process, by adding a chloride source to the molten metal, as metal fumes.

特開2023-173717号公報Japanese Patent Application Laid-Open No. 2023-173717 特表2022-507413号公報Special Publication No. 2022-507413

 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 components of the flux added to the molten metal during the pyrometallurgical refining process, making it difficult to recycle (reuse) industrial by-products when using this flux, and therefore not easy to apply to actual operations. Furthermore, the method disclosed in Patent Document 2, when recovering the produced lithium chloride as metal fumes, can cause damage to surrounding furnace walls and other equipment due to the adhesion of metal fumes. This is likely to increase the costs required for equipment maintenance and renovation, making it difficult to apply to actual operations.

 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 was made in consideration of the above circumstances, and its purpose 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, the method comprising: a contacting step of contacting the composite oxide with chlorine or a chlorine compound, the chlorine or chlorine compound being adjusted so that the substance amount 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 recovering step of contacting the chlorine or chlorine compound and the composite oxide that have been subjected to the contacting step with an aqueous solution to recover the aqueous solution into which the lithium has permeated.
[2] The method for recovering an aqueous solution according to [1], wherein the chlorine compound contains at least one of an alkali metal chloride and an alkaline earth metal chloride.
[3] The aqueous solution recovery method according to [1] or [2], wherein the composite oxide is slag remaining after a metal containing one or two elements selected from cobalt and nickel is recovered from molten metal obtained by dissolving lithium-ion batteries in a process.
[4] The aqueous solution recovery method according to any one of [1] to [3], wherein the aqueous solution to be brought into contact with the chlorine or chlorine compound that has undergone the contacting step and the composite oxide 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 the composite oxide can be recovered as an aqueous solution containing lithium.

 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 following describes an embodiment of the present invention. The aqueous solution recovery method of the present invention is a method for recovering lithium contained in a composite 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, slag remaining after metals containing one or two of cobalt and nickel are recovered from molten metal obtained by dissolving lithium-ion batteries using a pyrometallurgical process 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 includes a contacting step in which chlorine or a chlorine compound, which has been adjusted so that the mass ratio of chlorine to lithium contained in the composite oxide is 1.0 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.

 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 ensuring that the mass ratio of chlorine to lithium contained in the composite oxide is 1.0 or greater, the chlorination reaction between lithium and chlorine or a chlorine compound 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 ratio of chlorine to lithium contained in the composite oxide by mass is less than 1.0, the chlorination reaction between lithium and chlorine or chlorine compounds is not promoted, and lithium cannot be sufficiently recovered. Furthermore, if the ratio of chlorine to lithium contained in the composite oxide by mass is too high, the amount of chlorine added relative to lithium will be excessive, and even if the supply of chlorine or chlorine compounds is further increased, there will be no change in the effectiveness of lithium recovery, and processing costs will increase. Therefore, the ratio of chlorine to lithium contained in the composite oxide by mass 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 chlorine or chlorine compound may be adjusted by calculating the mass of lithium contained in the composite oxide before contacting it with the composite oxide, and adjusting the mass ratio of chlorine to lithium based on the calculated mass of lithium so that the mass ratio of chlorine to lithium is 1.0 or more and 5.5 or less. More specifically, the amount of chlorine or chlorine compound to be contacted with the composite oxide may be adjusted so that the mass ratio of chlorine to lithium is 1.0 or more and 5.5 or less. 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 composite oxide. For example, a portion of the composite oxide may be dissolved in acid, and measurement and calculation may be performed using inductively coupled plasma atomic emission spectroscopy (ICP-AES). Alternatively, in the process of producing the composite oxide, the mass concentration of lithium may be calculated 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。 Chlorine or chlorine compounds are contacted with the composite oxide at a temperature of 500°C or higher and 1350°C or lower. This is because contact at temperatures below 500°C does not promote the chlorination reaction between the lithium contained in the composite oxide and chlorine or chlorine compounds. The higher the temperature, the more promoted the chlorination reaction between lithium and chlorine or chlorine compounds. Therefore, contact at 600°C or higher is preferred, and contact at 800°C or higher is even more preferred. Furthermore, at temperatures above 1350°C, although the chlorination reaction between lithium and chlorine or chlorine compounds is promoted to produce lithium chloride, volatilization of the lithium chloride occurs, preventing its subsequent penetration into an 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 gas may be used as the chlorine. A metal chloride may be used as the chlorine compound. Specifically, the chlorine compound may include at least one of an alkali metal chloride and an alkaline earth metal chloride. Note that alkaline earth metals also include beryllium and magnesium. These chlorine compounds and chlorine have higher boiling points than compounds of heavy metals and chlorine. For this reason, by setting the temperature during contact between the chlorine or chlorine compound and the composite oxide to 500°C or higher and 1350°C or lower, the volatilization of the chlorine compound and chlorine is suppressed, and the production of lithium contained in the composite oxide as lithium chloride 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。 More specifically, the temperature at the time of contact between chlorine or a chlorine compound and the composite oxide may be controlled as the temperature of the composite oxide. Alternatively, it may be controlled as the temperature of the atmosphere inside the reaction vessel into which the chlorine or a chlorine compound and the composite 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 aqueous solution recovery method of the present invention includes an aqueous solution recovery step in which an aqueous solution is contacted with chlorine or a chlorine compound that has undergone a contact step and a composite oxide, 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。 Contacting the composite oxide with chlorine or a chlorine compound promotes the chlorination reaction between the lithium contained in the composite oxide and the chlorine or chlorine compound, producing lithium chloride. Therefore, by bringing an aqueous solution into contact with the chlorine or chlorine compound and composite oxide that have undergone the contacting step, the produced lithium chloride is incorporated into the aqueous solution, resulting in lithium permeating the aqueous solution. As a result, the lithium contained in the composite 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 time for contacting the composite oxide with chlorine or a chlorine compound is preferably 20 minutes or more and 180 minutes or less. By setting the time for the contact step within this range, the chlorination reaction between lithium and chlorine or a chlorine compound is further promoted, and the lithium contained in the composite oxide can be more reliably recovered as lithium that permeates into the aqueous solution. Note that if the contact time exceeds 180 minutes, no improvement in lithium recovery efficiency will be 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 that is brought into contact with the chlorine or chlorine compound and the composite oxide preferably has a pH value of 5.0 or higher and 10.0 or lower. By setting the pH value of the aqueous solution within this range, the dissolution of heavy metals (nickel, cobalt, manganese, etc.) into the aqueous solution is suppressed, and the penetration of lithium, which contains few coexisting elements, into the aqueous solution is promoted. Pure water, etc. 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 perspective of recovering an aqueous solution permeated with lithium 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, calculated as elemental lithium.

 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/SiO)、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) was used as the lithium-containing composite oxide, which differed in the substance ratio of calcium oxide to silicon dioxide (CaO/SiO 2 ) and the mass (mass %) of lithium contained. The component information of the oxides (A to D) used in the examples is shown in Table 1.

 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(CaCl)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, a chlorine compound was contacted with the oxides (A to D) shown in Table 1 so that the mass ratio of chlorine to lithium contained in each oxide was a predetermined value, and the mixture was maintained at a predetermined temperature for 60 minutes. An aqueous solution with a weight ratio of 30 times the chlorine compound and oxide was then prepared, and the chlorine compound and oxide were immersed in the aqueous solution while stirring for 120 minutes and filtered to obtain an aqueous solution containing lithium. Calcium chloride (CaCl 2 ) 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 resulting aqueous solution was measured, and the percentage (%) of the lithium content (mass%) in the aqueous solution relative to the mass (mass%) of lithium contained in the oxides (A-D) was calculated as the lithium recovery rate. 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。 In Comparative Examples 1 to 19 shown in Table 3, the ratio of chlorine to lithium (Cl/Li) contained in each of oxides A to D as composite oxides was set to 0.5, or the temperature at which each oxide was brought into contact with the chlorine compound was set to 1400°C, or the temperature at which each oxide was brought into contact with the chlorine compound was set to 400°C. As a result, the maximum recovery rate of lithium was only 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。 Inventive Examples 1 to 31 shown in Table 2 were carried out with the molar ratio of chlorine to lithium contained in oxide A (Cl/Li) set to 1.0 or more and 5.5 or less, and the temperature during contact between oxide A and the chlorine compound set to 500°C or more and 1350°C or less. 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。 Inventive Examples 32 to 46 used oxides B, C, and D as the composite oxides. The molar ratio of chlorine to lithium (Cl/Li) contained in oxides B, C, and D was set to 1.8 or more and 5.5 or less, and the temperature during contact 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 was 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 was confirmed that the aqueous solution recovery method of the present invention can recover lithium contained in a composite oxide as an aqueous solution containing lithium. Furthermore, it was confirmed that the aqueous solution recovery method of the present invention can be applied to composite oxides containing lithium and having various compositions, and can recover an aqueous solution containing lithium without causing volatilization of chlorine or chlorine compounds.


Claims (4)

 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。
1. A method for recovering an aqueous solution in which lithium contained in a composite oxide is recovered as an aqueous solution containing lithium, comprising:
a contacting step of contacting the composite oxide with the chlorine or chlorine compound, the chlorine or chlorine compound being adjusted so that the mass ratio of chlorine to lithium contained in the composite oxide is 1.0 to 5.5, at a temperature of 500°C to 1350°C;
an aqueous solution recovery step of contacting an aqueous solution with the chlorine or chlorine compound and the composite oxide that have been subjected to the contact step, and recovering the aqueous solution into which the lithium has been permeated;
The method for recovering an aqueous solution, comprising:
 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、請求項1に記載の水性溶液回収方法。 The aqueous solution recovery method according to claim 1, wherein the chlorine compound includes at least one of an alkali metal chloride and an alkaline earth metal chloride.  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、請求項1又は2に記載の水性溶液回収方法。 The aqueous solution recovery method described in claim 1 or 2, wherein the composite oxide is slag remaining after metals containing one or two of cobalt and nickel are recovered from molten metal obtained by dissolving lithium-ion batteries in a process for recovering the metals.  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にと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、請求項1~3のいずれか1項に記載の水性溶液回収方法。

 
The method for recovering an aqueous solution according to any one of claims 1 to 3, wherein the aqueous solution that has been subjected to the contacting step and is brought into contact with the complex oxide has a pH value of 5.0 or more and 10.0 or less.

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JP2003031229A (en) * 2001-07-12 2003-01-31 Tmc Kk Collection of valuable metals
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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
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