WO2024036700A1 - Sodium-ion battery prussian sodium positive electrode material recovery method and use thereof - Google Patents
Sodium-ion battery prussian sodium positive electrode material recovery method and use thereof Download PDFInfo
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- WO2024036700A1 WO2024036700A1 PCT/CN2022/120627 CN2022120627W WO2024036700A1 WO 2024036700 A1 WO2024036700 A1 WO 2024036700A1 CN 2022120627 W CN2022120627 W CN 2022120627W WO 2024036700 A1 WO2024036700 A1 WO 2024036700A1
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
- B09B3/30—Destroying solid waste or transforming solid waste into something useful or harmless involving mechanical treatment
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
- B09B3/70—Chemical treatment, e.g. pH adjustment or oxidation
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- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01C—AMMONIA; CYANOGEN; COMPOUNDS THEREOF
- C01C3/00—Cyanogen; Compounds thereof
- C01C3/08—Simple or complex cyanides of metals
- C01C3/12—Simple or complex iron cyanides
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- 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
- H01M10/05—Accumulators with non-aqueous electrolyte
- H01M10/054—Accumulators with insertion or intercalation of metals other than lithium, e.g. with magnesium or aluminium
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- H—ELECTRICITY
- H01—ELECTRIC ELEMENTS
- H01M—PROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
- H01M4/00—Electrodes
- H01M4/02—Electrodes composed of, or comprising, active material
- H01M4/36—Selection of substances as active materials, active masses, active liquids
- H01M4/58—Selection of substances as active materials, active masses, active liquids of inorganic compounds other than oxides or hydroxides, e.g. sulfides, selenides, tellurides, halogenides or LiCoFy; of polyanionic structures, e.g. phosphates, silicates or borates
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B2101/00—Type of solid waste
- B09B2101/15—Electronic waste
- B09B2101/16—Batteries
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
- B09B3/40—Destroying solid waste or transforming solid waste into something useful or harmless involving thermal treatment, e.g. evaporation
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- 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
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- 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
Definitions
- the invention belongs to the technical field of sodium-ion battery recycling and relates to a method for recycling Prussian sodium positive electrode materials of sodium-ion batteries and its application.
- Prussian derivative materials are currently one of the most promising cathode materials for sodium-ion batteries. It has the characteristics of an open nanoframe structure, large space gaps and ion channels, high specific surface area and controllable functionalization, which is conducive to the rapid insertion and extraction of sodium ions, and has been widely favored and studied.
- Prussian derivative materials have shortcomings that are difficult to produce due to their structural properties: The first is that the Prussian-like structure contains a large amount of ferrocyanide ions and cyanide ions, resulting in low toxicity of the material itself and a large amount of waste. Prussian sodium-like cathode materials will have a huge impact on environmental pollution and human activities.
- the second is that China has high standards and strict requirements for the treatment and discharge of cyanide-containing substances, which has caused certain difficulties in production and mass production. This has become a thorny problem for the use of Prussia and its derivatives in cathode materials.
- CN114229875A discloses a comprehensive recycling method for waste sodium ion batteries, which includes mixing and grinding battery black powder with a pre-leaching agent, then adding reducing agent and ammonia liquid for leaching, solid-liquid separation to obtain leachate and solid, adding acid to the solid to dissolve the solid-liquid Separate to obtain carbon residue and filtrate, add alkali to the filtrate to adjust the pH, separate to obtain aluminum hydroxide, continue to add alkali to the filtrate to adjust the pH, separate to obtain manganese hydroxide, add the first oxidant, chelating agent and alkali to the leachate, and proceed Ammonia is evaporated, and solid-liquid separation is performed to obtain cobalt-containing insoluble matter and nickel-containing chelate solution.
- the object of the present invention is to provide a method for recycling Prussian sodium cathode materials of sodium ion batteries and its application.
- the recycling process of the present invention is ingenious, simple to operate, and the raw materials are cheap.
- the solvent used is an alkaline solution, which is environmentally friendly and pollution-free, and The obtained product is easy to purify and separate, and can realize industrial large-scale production.
- the invention provides a method for recycling Prussian sodium cathode materials for sodium ion batteries.
- the recycling method includes the following steps:
- step (2) Mix the mixed solution obtained in step (1) with an alkali solution, and filter to obtain a ferrocyanide solution and a transition metal precipitate.
- the present invention recycles decommissioned or discarded Prussian-type positive electrode material resources of sodium-ion batteries.
- the Prussian-type positive electrode materials are dissolved in the alkaline solution, and then the Prussian-type positive electrode materials are dissolved in the alkaline solution.
- the process prepares sodium ferrocyanide or potassium ferrocyanide and corresponding transition metal precipitates, realizing the recovery of sodium cathode material resources. This method avoids the loss of Prussian cathode material resources, and this recycling method technology Simple, no pollution to the environment, and obvious economic benefits.
- the Prussian sodium-ion battery in step (1) includes any one or a combination of at least two of button batteries, soft pack batteries, cylindrical batteries or prismatic batteries.
- the cathode material of the Prussian-based sodium ion battery in step (1) includes manganese-based Prussian derivatives, iron-based Prussian-based derivatives, nickel-based Prussian-based derivatives, cobalt-based Prussian-based derivatives, and copper-based Prussian-based derivatives. Any one or a combination of at least two of the derivatives or zinc-based Prussian derivatives.
- the temperature of the water washing treatment in step (1) is 25-90°C, for example: 25°C, 30°C, 50°C, 60°C or 90°C, etc.
- the time of the water washing treatment in step (1) is 2 to 120h, for example: 2h, 10h, 20h, 60h or 120h, etc.
- an inert gas is introduced during the water washing process in step (1).
- the alkali solution in step (2) includes sodium hydroxide solution and/or potassium hydroxide solution.
- the molar ratio of the solute in the alkali solution and the Prussian cathode material in the mixed solution in step (2) is (2-4):1, for example: 2:1, 2.5:1, 3:1, 3.5:1 Or 4:1 etc.
- the mixing temperature in step (2) is 25-90°C, for example: 25°C, 30°C, 50°C, 60°C or 90°C, etc.
- the mixing time in step (2) is 2 to 120h, for example: 2h, 10h, 20h, 60h or 120h.
- the solute of the ferrocyanide solution in step (2) includes sodium ferrocyanide or potassium ferrocyanide.
- the present invention provides an application of the recycling method as described in the first aspect, wherein the ferrocyanide solution prepared by the recycling method is used to synthesize Prussian sodium cathode materials.
- the present invention has the following beneficial effects:
- the recycling process of the present invention is ingenious, simple to operate, and the raw materials are cheap.
- the solvent used is an alkaline solution, which is environmentally friendly and pollution-free.
- the obtained product is easy to purify and separate, and can realize industrial large-scale production.
- the present invention recycles Prussian-type cathode materials, reduces the discharge of cyanide-containing wastewater, reduces industrial costs, and avoids environmental pollution.
- Figure 1 is a process flow chart of the Prussian sodium cathode material recovery method for sodium ion batteries described in Example 1.
- Figure 2 is an SEM image of the Prussian white material prepared by the recycling method described in Example 1.
- Figure 3 is an SEM image of Mn 3 O 4 produced by the recovery method described in Example 1.
- Figure 4 is an SEM image of the filter obtained by the recovery method described in Example 7.
- Figure 5 is an XRD pattern of the Prussian white material prepared by the recycling method described in Example 1.
- Figure 6 is an XRD pattern of Mn 3 O 4 prepared by the recovery method described in Example 1.
- This embodiment provides a method for recycling Prussian sodium cathode materials for sodium ion batteries.
- the process flow chart of the recycling method is shown in Figure 1.
- the recycling method includes the following steps:
- the obtained sodium ferrocyanide (Na 4 Fe(CN) 6 ) solution can continue to be used to synthesize Prussian sodium cathode materials.
- the manganese hydroxide (Mn(OH) 2 ) precipitate is recovered and dried in the air to remove the water to obtain the corresponding manganese tetraoxide (Mn 3 O 4 ), which can be used for the synthesis of ternary cathode materials and can also be used for Prussian type
- the synthesis of cathode materials provides sources of raw materials.
- the chemical equation of the recovery method is: Na 2 MnFe(CN) 6 +2NaOH+O 2 ⁇ Na 4 Fe(CN) 6 +Mn 3 O 4 ⁇ .
- This embodiment provides a method for recycling Prussian sodium cathode materials for sodium ion batteries.
- the recycling method includes the following steps:
- the obtained sodium ferrocyanide (Na 4 Fe(CN) 6 ) solution can continue to be used to synthesize Prussian sodium cathode materials.
- the recovered iron hydroxide (Fe(OH) 3 ) precipitate can be used for the synthesis of ternary cathode materials, and can also be used to provide a raw material source for the synthesis of Prussian cathode materials.
- the chemical equation of the recovery method is: Na 2 Fe[Fe(CN) 6 ]+3NaOH ⁇ Na 4 Fe(CN) 6 +Fe(OH) 3 ⁇ .
- This embodiment provides a method for recycling Prussian sodium cathode materials for sodium ion batteries.
- the recycling method includes the following steps:
- the obtained sodium ferrocyanide (Na 4 Fe(CN) 6 ) solution can continue to be used to synthesize Prussian sodium cathode materials.
- the recovered cobalt hydroxide (Co(OH) 2 ) precipitate can be used for the synthesis of ternary cathode materials or cobalt carbonate, and can also be used to provide a raw material source for the synthesis of Prussian cathode materials.
- the chemical equation of the recovery method is: Na 2 Co[Fe(CN) 6 ]+2NaOH ⁇ Na 4 Fe(CN) 6 +Co(OH) 2 ⁇ .
- This embodiment provides a method for recycling Prussian sodium cathode materials for sodium ion batteries.
- the recycling method includes the following steps:
- the obtained sodium ferrocyanide (Na 4 Fe(CN) 6 ) solution can continue to be used to synthesize Prussian sodium cathode materials.
- the recovered nickel hydroxide (Ni(OH) 2 ) precipitate can be used for the synthesis of ternary cathode materials or cobalt carbonate, and can also be used to provide a raw material source for the synthesis of Prussian cathode materials.
- the chemical equation of the recovery method is: Na 2 Ni[Fe(CN) 6 ]+2NaOH ⁇ Na 4 Fe(CN) 6 +Ni(OH) 2 ⁇ .
- This embodiment provides a method for recycling Prussian sodium cathode materials for sodium ion batteries.
- the recycling method includes the following steps:
- the obtained sodium ferrocyanide (Na 4 Fe(CN) 6 ) solution can continue to be used to synthesize Prussian sodium cathode materials.
- the recovered copper hydroxide (Cu(OH) 2 ) precipitate can be used for the doping synthesis of ternary cathode materials or cobalt carbonate, and can also be used to provide a raw material source for the synthesis of Prussian cathode materials.
- the chemical equation of the recovery method is: Na 2 Cu[Fe(CN) 6 ]+2NaOH ⁇ Na 4 Fe(CN) 6 + Cu(OH) 2 ⁇ .
- This embodiment provides a method for recycling Prussian sodium cathode materials for sodium ion batteries.
- the recycling method includes the following steps:
- the obtained sodium ferrocyanide (Na 4 Fe(CN) 6 ) solution can continue to be used to synthesize Prussian sodium cathode materials.
- the recovered zinc hydroxide (Zn(OH) 2 ) precipitate can be used for the doping synthesis of ternary cathode materials or cobalt carbonate, and can also be used to provide a raw material source for the synthesis of Prussian cathode materials.
- the chemical equation of the recovery method is: Na 2 Cu[Fe(CN) 6 ]+2NaOH ⁇ Na 4 Fe(CN) 6 +Zn(OH) 2 ⁇ .
- Example 1 The only difference between this example and Example 1 is that the molar ratio of Prussian white (Na 2 MnFe(CN) 6 ) to sodium hydroxide is 1:1. Other conditions and parameters are exactly the same as Example 1. SEM of the system after the reaction The diagram is shown in Figure 4. It can be seen from Figure 4 that if the amount of alkali solution is too small, the positive electrode material cannot react completely, which in turn leads to a significant decrease in the recovery efficiency of the material.
- Example 1 The only difference between this embodiment and Example 1 is that the molar ratio of Prussian white (Na 2 MnFe(CN) 6 ) to sodium hydroxide is 1:5, and other conditions and parameters are exactly the same as those in Example 1.
- Example 1 it can be seen from the comparison between Example 1 and Examples 7-8 that in the recovery method of the present invention, the molar ratio of the Prussian cathode material and the alkali will affect the recovery effect. If the amount of alkali solution added is too large, the alkali solution will overflow. It is wasteful.
- the obtained sodium ferrocyanide or potassium ferrocyanide solution contains a large amount of sodium ions or potassium ions, which increases the subsequent processing of sodium ions or potassium ions; if the amount of alkali added is too small, As a result, the reaction is insufficient, the final product is impure, and the Prussian material with a changed structure and the corresponding metal oxidation or hydroxide mixture are obtained, resulting in complicated separation and purification and increased costs.
- Example 1 From the comparison between Example 1 and Comparative Example 1, it can be seen that the present invention recycles retired or discarded Prussian-type positive electrode material resources of sodium-ion batteries, and makes Prussian-type materials in the positive electrode sheets by rinsing and soaking them in alkaline solutions.
- the cathode material is dissolved in an alkaline solution, and then subjected to subsequent processing to prepare sodium ferrocyanide or potassium ferrocyanide and the corresponding transition metal precipitate, realizing the recovery of sodium cathode material resources.
- This method avoids the Prussian-type There is no loss of cathode material resources, and this recycling method has a simple process, no pollution to the environment, and obvious economic benefits.
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Abstract
Description
本发明属于钠离子电池回收技术领域,涉及一种钠离子电池普鲁士类钠正极材料回收方法及其应用。The invention belongs to the technical field of sodium-ion battery recycling and relates to a method for recycling Prussian sodium positive electrode materials of sodium-ion batteries and its application.
近几年来,由于锂离子电池在新能源行业的赛道上高速奔跑,且在电动汽车及便携式电子设备和智能生活用品中得到广泛应用,导致本就稀有的锂资源更加匮乏。同时,锂资源短缺和价格上涨等问题严重阻碍了社会发展。然而同主族的Na元素在地壳中分布较为丰富,分布范围相对广泛,且两者物理化学性质相似。因此,钠离子电池有望替代锂离子电池,成为今后的储能设备。In recent years, as lithium-ion batteries have been running at high speed on the track of the new energy industry and have been widely used in electric vehicles, portable electronic devices and smart daily necessities, the already rare lithium resources have become even more scarce. At the same time, problems such as the shortage of lithium resources and rising prices have seriously hindered social development. However, Na elements of the same main group are more abundant in the earth's crust, and their distribution range is relatively wide, and the physical and chemical properties of the two are similar. Therefore, sodium-ion batteries are expected to replace lithium-ion batteries and become energy storage devices in the future.
普鲁士类衍生物材料是目前最有希望作为钠离子电池正极材料中的一种。其具有开放的纳米框架结构、较大的空间间隙和离子通道、高比表面积及可控的功能化等特点,有利于钠离子的快速嵌入和脱出,备受广泛的青睐和研究。然而,普鲁士类衍生物材料由于本身结构属性原因,存在难于生产的缺点:第一个就是普鲁士类结构中含有大量的亚铁氰根离子和氰根离子,导致材料本身具有低毒性,大量废弃的普鲁士类钠正极材料将会对环境污染和人类活动造成巨大的影响。第二个就是中国对含氰物质的处理和排放具有高标准和严要求,对生产和量产造成了一定的困难,这成为普鲁士类及其衍生物用在正极材料中的一个棘手难题。Prussian derivative materials are currently one of the most promising cathode materials for sodium-ion batteries. It has the characteristics of an open nanoframe structure, large space gaps and ion channels, high specific surface area and controllable functionalization, which is conducive to the rapid insertion and extraction of sodium ions, and has been widely favored and studied. However, Prussian derivative materials have shortcomings that are difficult to produce due to their structural properties: The first is that the Prussian-like structure contains a large amount of ferrocyanide ions and cyanide ions, resulting in low toxicity of the material itself and a large amount of waste. Prussian sodium-like cathode materials will have a huge impact on environmental pollution and human activities. The second is that China has high standards and strict requirements for the treatment and discharge of cyanide-containing substances, which has caused certain difficulties in production and mass production. This has become a thorny problem for the use of Prussia and its derivatives in cathode materials.
为了解决以上难题,只能对退役或废旧的普鲁士类衍生物钠正极材料进行回收利用。In order to solve the above problems, retired or discarded Prussian derivative sodium cathode materials can only be recycled.
CN114229875A公开了一种废旧钠离子电池综合回收方法,包括将电池黑粉与预浸出剂混合研磨,再加入还原剂和氨液进行浸出,固液分离得到浸出液和固体,固体加酸溶解,固液分离得到碳渣和滤液,向滤液中加碱调节pH,分离得到氢氧化铝,继续向滤液中加碱调节pH,分离得到氢氧化锰,向浸出液中加入第一氧化剂、螯合剂和碱,进行蒸氨,固液分离得到含钴不溶物和含镍螯合物溶液。CN114229875A discloses a comprehensive recycling method for waste sodium ion batteries, which includes mixing and grinding battery black powder with a pre-leaching agent, then adding reducing agent and ammonia liquid for leaching, solid-liquid separation to obtain leachate and solid, adding acid to the solid to dissolve the solid-liquid Separate to obtain carbon residue and filtrate, add alkali to the filtrate to adjust the pH, separate to obtain aluminum hydroxide, continue to add alkali to the filtrate to adjust the pH, separate to obtain manganese hydroxide, add the first oxidant, chelating agent and alkali to the leachate, and proceed Ammonia is evaporated, and solid-liquid separation is performed to obtain cobalt-containing insoluble matter and nickel-containing chelate solution.
上述方案针对的是常规钠离子电池,目前针对普鲁士类钠正极材料的回收研究较少,因此,亟需开发一种可以解决普鲁士类钠正极材料的污染和资源回用问题的回收方法。The above scheme is aimed at conventional sodium-ion batteries. There are currently few studies on the recycling of Prussian sodium cathode materials. Therefore, there is an urgent need to develop a recycling method that can solve the pollution and resource recycling problems of Prussian sodium cathode materials.
发明内容Contents of the invention
本发明的目的在于提供一种钠离子电池普鲁士类钠正极材料回收方法及其应用,本发明的回收工艺流程巧妙,操作简单,原料低廉,所用溶剂为碱性溶液,对环境友好无污染,并且所得产物易提纯分离,能实现工业化大规模生产。The object of the present invention is to provide a method for recycling Prussian sodium cathode materials of sodium ion batteries and its application. The recycling process of the present invention is ingenious, simple to operate, and the raw materials are cheap. The solvent used is an alkaline solution, which is environmentally friendly and pollution-free, and The obtained product is easy to purify and separate, and can realize industrial large-scale production.
为达到此发明目的,本发明采用以下技术方案:In order to achieve the purpose of this invention, the present invention adopts the following technical solutions:
第一方面,本发明提供了一种钠离子电池普鲁士类钠正极材料回收方法,所述回收方法包括以下步骤:In a first aspect, the invention provides a method for recycling Prussian sodium cathode materials for sodium ion batteries. The recycling method includes the following steps:
(1)取退役和/或废旧的普鲁士类钠离子电池进行拆解,分离出普鲁士类正极极片,对得到的普鲁士类正极极片进行水洗处理,过滤得到正极载体片和混合液;(1) Disassemble retired and/or used Prussian-type sodium-ion batteries, separate the Prussian-type positive electrode pieces, wash the obtained Prussian-type positive electrode pieces, and filter to obtain the positive electrode carrier pieces and mixed liquid;
(2)将步骤(1)得到的混合液与碱液混合,过滤得到亚铁氰化物溶液和过渡金属沉淀物。(2) Mix the mixed solution obtained in step (1) with an alkali solution, and filter to obtain a ferrocyanide solution and a transition metal precipitate.
本发明对退役或废旧的钠离子电池普鲁士类正极材料资源进行回收利用,通过对正极片中普鲁士类材料进行冲洗和碱性溶液浸泡,使普鲁士类正极材料 溶解在碱性溶液中,再经后续处理制备出亚铁氰化钠或亚铁氰化钾以及相应的过渡金属沉淀物,实现了钠正极材料资源的回收,这种方式避免了普鲁士类正极材料资源的损失,且这种回收方式工艺简单,环境无污染,经济效益明显。The present invention recycles decommissioned or discarded Prussian-type positive electrode material resources of sodium-ion batteries. By washing the Prussian-type materials in the positive electrode sheets and soaking them in alkaline solution, the Prussian-type positive electrode materials are dissolved in the alkaline solution, and then the Prussian-type positive electrode materials are dissolved in the alkaline solution. The process prepares sodium ferrocyanide or potassium ferrocyanide and corresponding transition metal precipitates, realizing the recovery of sodium cathode material resources. This method avoids the loss of Prussian cathode material resources, and this recycling method technology Simple, no pollution to the environment, and obvious economic benefits.
优选地,步骤(1)所述普鲁士类钠离子电池包括扣式电池、软包电池、圆柱形电池或方形电池中的任意一种或至少两种的组合。Preferably, the Prussian sodium-ion battery in step (1) includes any one or a combination of at least two of button batteries, soft pack batteries, cylindrical batteries or prismatic batteries.
优选地,步骤(1)所述普鲁士类钠离子电池的正极材料包括锰基普鲁士类衍生物、铁基普鲁士类衍生物、镍基普鲁士类衍生物、钴基普鲁士类衍生物、铜基普鲁士类衍生物或锌基普鲁士类衍生物中的任意一种或至少两种的组合。Preferably, the cathode material of the Prussian-based sodium ion battery in step (1) includes manganese-based Prussian derivatives, iron-based Prussian-based derivatives, nickel-based Prussian-based derivatives, cobalt-based Prussian-based derivatives, and copper-based Prussian-based derivatives. Any one or a combination of at least two of the derivatives or zinc-based Prussian derivatives.
优选地,步骤(1)水洗处理的温度为25~90℃,例如:25℃、30℃、50℃、60℃或90℃等。Preferably, the temperature of the water washing treatment in step (1) is 25-90°C, for example: 25°C, 30°C, 50°C, 60°C or 90°C, etc.
优选地,步骤(1)所述水洗处理的时间为2~120h,例如:2h、10h、20h、60h或120h等。Preferably, the time of the water washing treatment in step (1) is 2 to 120h, for example: 2h, 10h, 20h, 60h or 120h, etc.
优选地,步骤(1)所述水洗处理的过程中通入惰性气体。Preferably, an inert gas is introduced during the water washing process in step (1).
优选地,步骤(2)所述碱液包括氢氧化钠溶液和/或氢氧化钾溶液。Preferably, the alkali solution in step (2) includes sodium hydroxide solution and/or potassium hydroxide solution.
优选地,步骤(2)所述碱液中溶质和混合液中普鲁士类正极材料的摩尔比为(2~4):1,例如:2:1、2.5:1、3:1、3.5:1或4:1等。Preferably, the molar ratio of the solute in the alkali solution and the Prussian cathode material in the mixed solution in step (2) is (2-4):1, for example: 2:1, 2.5:1, 3:1, 3.5:1 Or 4:1 etc.
优选地,步骤(2)所述混合的温度为25~90℃,例如:25℃、30℃、50℃、60℃或90℃等。Preferably, the mixing temperature in step (2) is 25-90°C, for example: 25°C, 30°C, 50°C, 60°C or 90°C, etc.
优选地,步骤(2)所述混合的时间为2~120h,例如:2h、10h、20h、60h或120h。Preferably, the mixing time in step (2) is 2 to 120h, for example: 2h, 10h, 20h, 60h or 120h.
优选地,步骤(2)所述亚铁氰化物溶液的溶质包括亚铁氰化钠或亚铁氰化钾。Preferably, the solute of the ferrocyanide solution in step (2) includes sodium ferrocyanide or potassium ferrocyanide.
第二方面,本发明提供了一种如第一方面所述回收方法的应用,所述回收 方法制得亚铁氰化物溶液用于合成普鲁士类钠正极材料。In a second aspect, the present invention provides an application of the recycling method as described in the first aspect, wherein the ferrocyanide solution prepared by the recycling method is used to synthesize Prussian sodium cathode materials.
相对于现有技术,本发明具有以下有益效果:Compared with the existing technology, the present invention has the following beneficial effects:
(1)本发明的回收工艺流程巧妙,操作简单,原料低廉,所用溶剂为碱性溶液,对环境友好无污染,并且所得产物易提纯分离,能实现工业化大规模生产。(1) The recycling process of the present invention is ingenious, simple to operate, and the raw materials are cheap. The solvent used is an alkaline solution, which is environmentally friendly and pollution-free. The obtained product is easy to purify and separate, and can realize industrial large-scale production.
(2)本发明对普鲁士类正极材料的回收,减少了含氰废水的排放,减少工业成本,避免了对环境的污染。(2) The present invention recycles Prussian-type cathode materials, reduces the discharge of cyanide-containing wastewater, reduces industrial costs, and avoids environmental pollution.
图1是实施例1所述钠离子电池普鲁士类钠正极材料回收方法的工艺流程图。Figure 1 is a process flow chart of the Prussian sodium cathode material recovery method for sodium ion batteries described in Example 1.
图2是实施例1所述回收方法制得普鲁士白类材料的SEM图。Figure 2 is an SEM image of the Prussian white material prepared by the recycling method described in Example 1.
图3是实施例1所述回收方法制得Mn 3O 4的SEM图。 Figure 3 is an SEM image of Mn 3 O 4 produced by the recovery method described in Example 1.
图4是实施例7所述回收方法制得过滤物的SEM图。Figure 4 is an SEM image of the filter obtained by the recovery method described in Example 7.
图5是实施例1所述回收方法制得普鲁士白类材料的XRD图。Figure 5 is an XRD pattern of the Prussian white material prepared by the recycling method described in Example 1.
图6是实施例1所述回收方法制得Mn 3O 4的XRD图。 Figure 6 is an XRD pattern of Mn 3 O 4 prepared by the recovery method described in Example 1.
下面通过具体实施方式来进一步说明本发明的技术方案。本领域技术人员应该明了,所述实施例仅仅是帮助理解本发明,不应视为对本发明的具体限制。The technical solution of the present invention will be further described below through specific implementations. Those skilled in the art should understand that the embodiments are only to help understand the present invention and should not be regarded as specific limitations of the present invention.
实施例1Example 1
本实施例提供了一种钠离子电池普鲁士类钠正极材料回收方法,所述回收方法的工艺流程图如图1所示,所述回收方法包括以下步骤:This embodiment provides a method for recycling Prussian sodium cathode materials for sodium ion batteries. The process flow chart of the recycling method is shown in Figure 1. The recycling method includes the following steps:
(1)将完全放电处理后的普鲁士类钠离子电池单体进行拆解,将正、负极片、隔膜分别拣出来,把含锰基普鲁士白(Na 2MnFe(CN) 6)正极材料的正极片 溶于去离子水中,进行水洗处理,待正极片充分搅拌溶解完全后,将铝箔金属载体片过滤提出,剩下定量的锰基普鲁士白悬浊液。铝箔片卖给金属加工厂,再次循环利用; (1) Disassemble the Prussian sodium-ion battery cells after complete discharge treatment, pick out the positive and negative electrode sheets and separators respectively, and remove the positive electrode containing manganese-based Prussian white (Na 2 MnFe(CN) 6 ) positive electrode material. The sheet is dissolved in deionized water and washed with water. After the positive electrode sheet is fully stirred and dissolved, the aluminum foil metal carrier sheet is filtered and extracted, leaving a quantitative manganese-based Prussian white suspension. The aluminum foil is sold to metal processing plants and recycled again;
(2)将过滤好的锰基普鲁士白(Na 2MnFe(CN) 6)悬浊液加入特定的反应釜,加入定量氢氧化钠(NaOH),其普鲁士白(Na 2MnFe(CN) 6)与氢氧化钠的摩尔比为1:3。然后进行剧烈搅拌,加热到50℃下充分混合反应24h,全程通入氮气保护气体,将反应结束后的溶液进行过滤处理,得到了亚铁氰化钠(Na 4Fe(CN) 6)溶液与氢氧化锰(Mn(OH) 2)沉淀物滤渣,除去滤渣就得到亚铁氰化钠溶液; (2) Add the filtered manganese-based Prussian white (Na 2 MnFe(CN) 6 ) suspension into a specific reaction kettle, add a certain amount of sodium hydroxide (NaOH), and its Prussian white (Na 2 MnFe(CN) 6 ) The molar ratio to sodium hydroxide is 1:3. Then stir vigorously, heat to 50°C and fully mix the reaction for 24 hours. Nitrogen protective gas is introduced throughout the process. The solution after the reaction is filtered to obtain sodium ferrocyanide (Na 4 Fe(CN) 6 ) solution and Manganese hydroxide (Mn(OH) 2 ) precipitates the filter residue, and removes the filter residue to obtain sodium ferrocyanide solution;
得到的亚铁氰化钠(Na 4Fe(CN) 6)溶液可以继续使用,用于合成普鲁士类钠正极材料。回收氢氧化锰(Mn(OH) 2)沉淀物在空气中干燥去水得到相应的四氧化三锰(Mn 3O 4),可以用于三元正极材料的合成,也可以用于为普鲁士类正极材料的合成提供原料来源。 The obtained sodium ferrocyanide (Na 4 Fe(CN) 6 ) solution can continue to be used to synthesize Prussian sodium cathode materials. The manganese hydroxide (Mn(OH) 2 ) precipitate is recovered and dried in the air to remove the water to obtain the corresponding manganese tetraoxide (Mn 3 O 4 ), which can be used for the synthesis of ternary cathode materials and can also be used for Prussian type The synthesis of cathode materials provides sources of raw materials.
所述普鲁士白类材料的SEM图如图2所示,所述普鲁士白类材料的XRD图如图5所示。The SEM image of the Prussian white material is shown in Figure 2, and the XRD pattern of the Prussian white material is shown in Figure 5.
所述Mn 3O 4的SEM图如图3所示,所述Mn 3O 4的XRD图如图6所示。 The SEM picture of Mn 3 O 4 is shown in Figure 3, and the XRD pattern of Mn 3 O 4 is shown in Figure 6.
所述回收方法的化学方程式为:Na 2MnFe(CN) 6+2NaOH+O 2→Na 4Fe(CN) 6+Mn 3O 4↓。 The chemical equation of the recovery method is: Na 2 MnFe(CN) 6 +2NaOH+O 2 →Na 4 Fe(CN) 6 +Mn 3 O 4 ↓.
实施例2Example 2
本实施例提供了一种钠离子电池普鲁士类钠正极材料回收方法,所述回收方法包括以下步骤:This embodiment provides a method for recycling Prussian sodium cathode materials for sodium ion batteries. The recycling method includes the following steps:
(1)将完全放电处理后的普鲁士类钠离子电池单体进行拆解,将正、负极片、隔膜分别拣出来,把含铁基普鲁士白(Na 2Fe[Fe(CN) 6])正极材料的正极片溶于去离子水中,进行水洗处理,待正极片充分搅拌溶解完全后,将铝箔金属 载体片过滤提出,剩下定量的铁基普鲁士白悬浊液。铝箔片卖给金属加工厂,再次循环利用; (1) Disassemble the Prussian sodium-ion battery cells after complete discharge treatment, pick out the positive and negative electrode sheets and separators respectively, and remove the iron-based Prussian white (Na 2 Fe[Fe(CN) 6 ]) positive electrode. The positive electrode sheet of the material is dissolved in deionized water and washed with water. After the positive electrode sheet is fully stirred and dissolved, the aluminum foil metal carrier sheet is filtered and extracted, leaving a quantitative iron-based Prussian white suspension. The aluminum foil is sold to metal processing plants and recycled again;
(2)将过滤好的铁基普鲁士白(Na 2Fe[Fe(CN) 6])悬浊液加入特定的反应釜,加入定量氢氧化钠(NaOH),其铁基普鲁士白(Na 2Fe[Fe(CN) 6])与氢氧化钠的摩尔比为1:2。然后进行剧烈搅拌,在室温下使两者充分混合反应12h,全程通入氮气保护气体,将反应结束后的溶液进行过滤处理,得到了亚铁氰化钠(Na 4Fe(CN) 6)溶液与氢氧化铁(Fe(OH) 3)沉淀物滤渣,除去滤渣就得到亚铁氰化钠溶液。 (2) Add the filtered iron-based Prussian white (Na 2 Fe [Fe(CN) 6 ]) suspension into a specific reaction kettle, add a certain amount of sodium hydroxide (NaOH), and add the iron-based Prussian white (Na 2 Fe The molar ratio of [Fe(CN) 6 ]) to sodium hydroxide is 1:2. Then stir vigorously, and mix the two thoroughly for 12 hours at room temperature. Nitrogen protective gas is passed through the whole process. The solution after the reaction is filtered to obtain sodium ferrocyanide (Na 4 Fe(CN) 6 ) solution. Precipitate the filter residue with iron hydroxide (Fe(OH) 3 ), and remove the filter residue to obtain sodium ferrocyanide solution.
得到的亚铁氰化钠(Na 4Fe(CN) 6)溶液可以继续使用,用于合成普鲁士类钠正极材料。回收氢氧化铁(Fe(OH) 3)沉淀物可以用于三元正极材料的合成,也可以用于为普鲁士类正极材料的合成提供原料来源。 The obtained sodium ferrocyanide (Na 4 Fe(CN) 6 ) solution can continue to be used to synthesize Prussian sodium cathode materials. The recovered iron hydroxide (Fe(OH) 3 ) precipitate can be used for the synthesis of ternary cathode materials, and can also be used to provide a raw material source for the synthesis of Prussian cathode materials.
所述回收方法的化学方程式为:Na 2Fe[Fe(CN) 6]+3NaOH→Na 4Fe(CN) 6+Fe(OH) 3↓。 The chemical equation of the recovery method is: Na 2 Fe[Fe(CN) 6 ]+3NaOH→Na 4 Fe(CN) 6 +Fe(OH) 3 ↓.
实施例3Example 3
本实施例提供了一种钠离子电池普鲁士类钠正极材料回收方法,所述回收方法包括以下步骤:This embodiment provides a method for recycling Prussian sodium cathode materials for sodium ion batteries. The recycling method includes the following steps:
(1)将完全放电处理后的普鲁士类钠离子电池单体进行拆解,将正、负极片、隔膜分别拣出来,把含钴基普鲁士白(Na 2CoFe(CN) 6)正极材料的正极片溶于去离子水中,进行水洗处理,待正极片充分搅拌溶解完全后,将铝箔金属载体片过滤提出,剩下定量的钴基普鲁士白悬浊液。铝箔片卖给金属加工厂,再次循环利用; (1) Disassemble the Prussian sodium-ion battery cells after complete discharge treatment, pick out the positive and negative electrode sheets and separators respectively, and remove the positive electrode containing cobalt-based Prussian white (Na 2 CoFe (CN) 6 ) positive electrode material. The sheet is dissolved in deionized water and washed with water. After the positive electrode sheet is fully stirred and dissolved, the aluminum foil metal carrier sheet is filtered and extracted, leaving a quantitative cobalt-based Prussian white suspension. The aluminum foil is sold to metal processing plants and recycled again;
(2)将过滤好的钴基普鲁士白(Na 2CoFe(CN) 6)悬浊液加入特定的反应釜,加入定量氢氧化钠(NaOH),其钴基普鲁士白(Na 2CoFe(CN) 6)与氢氧化钠的 摩尔比为1:2。然后进行剧烈搅拌,在室温下使两者充分混合反应12h,全程通入氮气保护气体,将反应结束后的溶液进行过滤处理,得到了亚铁氰化钠(Na 4Fe(CN) 6)溶液与氢氧化钴(Co(OH) 2)沉淀物滤渣,除去滤渣就得到亚铁氰化钠溶液。 (2) Add the filtered cobalt-based Prussian white (Na 2 CoFe(CN) 6 ) suspension into a specific reaction kettle, add a certain amount of sodium hydroxide (NaOH), and the cobalt-based Prussian white (Na 2 CoFe(CN) 6 ) The molar ratio to sodium hydroxide is 1:2. Then stir vigorously, and mix the two thoroughly for 12 hours at room temperature. Nitrogen protective gas is passed through the whole process. The solution after the reaction is filtered to obtain sodium ferrocyanide (Na 4 Fe(CN) 6 ) solution. Precipitate the filter residue with cobalt hydroxide (Co(OH) 2 ), and remove the filter residue to obtain sodium ferrocyanide solution.
得到的亚铁氰化钠(Na 4Fe(CN) 6)溶液可以继续使用,用于合成普鲁士类钠正极材料。回收氢氧化钴(Co(OH) 2)沉淀物可以用于三元正极材料或碳酸钴的合成,也可以用于为普鲁士类正极材料的合成提供原料来源。 The obtained sodium ferrocyanide (Na 4 Fe(CN) 6 ) solution can continue to be used to synthesize Prussian sodium cathode materials. The recovered cobalt hydroxide (Co(OH) 2 ) precipitate can be used for the synthesis of ternary cathode materials or cobalt carbonate, and can also be used to provide a raw material source for the synthesis of Prussian cathode materials.
所述回收方法的化学方程式为:Na 2Co[Fe(CN) 6]+2NaOH→Na 4Fe(CN) 6+Co(OH) 2↓。 The chemical equation of the recovery method is: Na 2 Co[Fe(CN) 6 ]+2NaOH→Na 4 Fe(CN) 6 +Co(OH) 2 ↓.
实施例4Example 4
本实施例提供了一种钠离子电池普鲁士类钠正极材料回收方法,所述回收方法包括以下步骤:This embodiment provides a method for recycling Prussian sodium cathode materials for sodium ion batteries. The recycling method includes the following steps:
(1)将完全放电处理后的普鲁士类钠离子电池单体进行拆解,将正、负极片、隔膜分别拣出来,把含镍基普鲁士蓝(Na 2NiFe(CN) 6)正极材料的正极片溶于去离子水中,进行水洗处理,待正极片充分搅拌溶解完全后,将铝箔金属载体片过滤提出,剩下定量的镍基普鲁士蓝悬浊液。铝箔片卖给金属加工厂,再次循环利用; (1) Disassemble the Prussian sodium-ion battery cells after complete discharge treatment, pick out the positive and negative electrode sheets and separators respectively, and remove the positive electrode containing nickel-based Prussian blue (Na 2 NiFe(CN) 6 ) positive electrode material. The sheet is dissolved in deionized water and washed with water. After the positive electrode sheet is fully stirred and dissolved, the aluminum foil metal carrier sheet is filtered and extracted, leaving a quantitative nickel-based Prussian blue suspension. The aluminum foil is sold to metal processing plants and recycled again;
(2)将过滤好的镍基普鲁士蓝(Na 2NiFe(CN) 6)悬浊液加入特定的反应釜,加入定量氢氧化钠(NaOH),其镍基普鲁士蓝(Na 2NiFe(CN) 6)与氢氧化钠的摩尔比为1:3。然后进行剧烈搅拌,在室温下使两者充分混合反应12h,全程通入氮气保护气体,将反应结束后的溶液进行过滤处理,得到了亚铁氰化钠(Na 4Fe(CN) 6)溶液与氢氧化镍(Ni(OH) 2)沉淀物滤渣,除去滤渣就得到亚铁氰化钠溶液。 (2) Add the filtered nickel-based Prussian blue (Na 2 NiFe(CN) 6 ) suspension into a specific reaction kettle, add a certain amount of sodium hydroxide (NaOH), and the nickel-based Prussian blue (Na 2 NiFe(CN) 6 ) The molar ratio to sodium hydroxide is 1:3. Then stir vigorously, and mix the two thoroughly for 12 hours at room temperature. Nitrogen protective gas is passed through the whole process. The solution after the reaction is filtered to obtain sodium ferrocyanide (Na 4 Fe(CN) 6 ) solution. Precipitate the filter residue with nickel hydroxide (Ni(OH) 2 ), and remove the filter residue to obtain sodium ferrocyanide solution.
得到的亚铁氰化钠(Na 4Fe(CN) 6)溶液可以继续使用,用于合成普鲁士类钠正极材料。回收氢氧化镍(Ni(OH) 2)沉淀物可以用于三元正极材料或碳酸钴的合成,也可以用于为普鲁士类正极材料的合成提供原料来源。 The obtained sodium ferrocyanide (Na 4 Fe(CN) 6 ) solution can continue to be used to synthesize Prussian sodium cathode materials. The recovered nickel hydroxide (Ni(OH) 2 ) precipitate can be used for the synthesis of ternary cathode materials or cobalt carbonate, and can also be used to provide a raw material source for the synthesis of Prussian cathode materials.
所述回收方法的化学方程式为:Na 2Ni[Fe(CN) 6]+2NaOH→Na 4Fe(CN) 6+Ni(OH) 2↓。 The chemical equation of the recovery method is: Na 2 Ni[Fe(CN) 6 ]+2NaOH→Na 4 Fe(CN) 6 +Ni(OH) 2 ↓.
实施例5Example 5
本实施例提供了一种钠离子电池普鲁士类钠正极材料回收方法,所述回收方法包括以下步骤:This embodiment provides a method for recycling Prussian sodium cathode materials for sodium ion batteries. The recycling method includes the following steps:
(1)将完全放电处理后的普鲁士类钠离子电池单体进行拆解,将正、负极片、隔膜分别拣出来,把含铜基普鲁士蓝(Na 2CuFe(CN) 6)正极材料的正极片溶于去离子水中,进行水洗处理,待正极片充分搅拌溶解完全后,将铝箔金属载体片过滤提出,剩下定量的铜基普鲁士蓝悬浊液。铝箔片卖给金属加工厂,再次循环利用; (1) Disassemble the Prussian sodium-ion battery cells after complete discharge treatment, pick out the positive and negative electrode sheets and separators respectively, and remove the positive electrode containing copper-based Prussian blue (Na 2 CuFe(CN) 6 ) positive electrode material. The sheet is dissolved in deionized water and washed with water. After the positive electrode sheet is fully stirred and dissolved, the aluminum foil metal carrier sheet is filtered and extracted, leaving a quantitative copper-based Prussian blue suspension. The aluminum foil is sold to metal processing plants and recycled again;
(2)将过滤好的铜基普鲁士蓝(Na 2CuFe(CN) 6)悬浊液加入特定的反应釜,加入定量氢氧化钠(NaOH),其铜基普鲁士蓝(Na 2CuFe(CN) 6)与氢氧化钠的摩尔比为1:3。然后进行剧烈搅拌,在室温下使两者充分混合反应12h,全程通入氮气保护气体,将反应结束后的溶液进行过滤处理,得到了亚铁氰化钠(Na 4Fe(CN) 6)溶液与氢氧化铜(Cu(OH) 2)沉淀物滤渣,除去滤渣就得到亚铁氰化钠溶液。 (2) Add the filtered copper-based Prussian blue (Na 2 CuFe(CN) 6 ) suspension into a specific reaction kettle, add a certain amount of sodium hydroxide (NaOH), and add the copper-based Prussian blue (Na 2 CuFe(CN) 6 ) The molar ratio to sodium hydroxide is 1:3. Then stir vigorously, mix the two thoroughly at room temperature, and react for 12 hours. Nitrogen protective gas is introduced throughout the process. The solution after the reaction is filtered to obtain sodium ferrocyanide (Na 4 Fe(CN) 6 ) solution. Precipitate the filter residue with copper hydroxide (Cu(OH) 2 ), and remove the filter residue to obtain sodium ferrocyanide solution.
得到的亚铁氰化钠(Na 4Fe(CN) 6)溶液可以继续使用,用于合成普鲁士类钠正极材料。回收氢氧化铜(Cu(OH) 2)沉淀物可以用于三元正极材料或碳酸钴的掺杂合成,也可以用于为普鲁士类正极材料的合成提供原料来源。 The obtained sodium ferrocyanide (Na 4 Fe(CN) 6 ) solution can continue to be used to synthesize Prussian sodium cathode materials. The recovered copper hydroxide (Cu(OH) 2 ) precipitate can be used for the doping synthesis of ternary cathode materials or cobalt carbonate, and can also be used to provide a raw material source for the synthesis of Prussian cathode materials.
所述回收方法的化学方程式为:Na 2Cu[Fe(CN) 6]+2NaOH→Na 4Fe(CN) 6+ Cu(OH) 2↓。 The chemical equation of the recovery method is: Na 2 Cu[Fe(CN) 6 ]+2NaOH→Na 4 Fe(CN) 6 + Cu(OH) 2 ↓.
实施例6Example 6
本实施例提供了一种钠离子电池普鲁士类钠正极材料回收方法,所述回收方法包括以下步骤:This embodiment provides a method for recycling Prussian sodium cathode materials for sodium ion batteries. The recycling method includes the following steps:
(1)将完全放电处理后的普鲁士类钠离子电池单体进行拆解,将正、负极片、隔膜分别拣出来,把含锌基普鲁士蓝(Na 2ZnFe(CN) 6)正极材料的正极片溶于去离子水中,进行水洗处理,待正极片充分搅拌溶解完全后,将铝箔金属载体片过滤提出,剩下定量的锌基普鲁士蓝悬浊液。铝箔片卖给金属加工厂,再次循环利用; (1) Disassemble the Prussian sodium-ion battery cells after complete discharge treatment, pick out the positive and negative electrode sheets and separators respectively, and remove the positive electrode containing zinc-based Prussian blue (Na 2 ZnFe(CN) 6 ) positive electrode material. The sheet is dissolved in deionized water and washed with water. After the positive electrode sheet is fully stirred and dissolved, the aluminum foil metal carrier sheet is filtered and extracted, leaving a quantitative zinc-based Prussian blue suspension. The aluminum foil is sold to metal processing plants and recycled again;
(2)将过滤好的锌基普鲁士蓝(Na 2ZnFe(CN) 6)悬浊液加入特定的反应釜,加入定量氢氧化钠(NaOH),其锌基普鲁士蓝(Na 2ZnFe(CN) 6)与氢氧化钠的摩尔比为1:3。然后进行剧烈搅拌,在室温下使两者充分混合反应12h,全程通入氮气保护气体,将反应结束后的溶液进行过滤处理,得到了亚铁氰化钠(Na 4Fe(CN) 6)溶液与氢氧化锌(Zn(OH) 2)沉淀物滤渣,除去滤渣就得到亚铁氰化钠溶液。 (2) Add the filtered zinc-based Prussian blue (Na 2 ZnFe(CN) 6 ) suspension into a specific reaction kettle, add a certain amount of sodium hydroxide (NaOH), and add the zinc-based Prussian blue (Na 2 ZnFe(CN) 6 ) The molar ratio to sodium hydroxide is 1:3. Then stir vigorously, and mix the two thoroughly for 12 hours at room temperature. Nitrogen protective gas is passed through the whole process. The solution after the reaction is filtered to obtain sodium ferrocyanide (Na 4 Fe(CN) 6 ) solution. Precipitate the filter residue with zinc hydroxide (Zn(OH) 2 ), and remove the filter residue to obtain sodium ferrocyanide solution.
得到的亚铁氰化钠(Na 4Fe(CN) 6)溶液可以继续使用,用于合成普鲁士类钠正极材料。回收氢氧化锌(Zn(OH) 2)沉淀物可以用于三元正极材料或碳酸钴的掺杂合成,也可以用于为普鲁士类正极材料的合成提供原料来源。 The obtained sodium ferrocyanide (Na 4 Fe(CN) 6 ) solution can continue to be used to synthesize Prussian sodium cathode materials. The recovered zinc hydroxide (Zn(OH) 2 ) precipitate can be used for the doping synthesis of ternary cathode materials or cobalt carbonate, and can also be used to provide a raw material source for the synthesis of Prussian cathode materials.
所述回收方法的化学方程式为:Na 2Cu[Fe(CN) 6]+2NaOH→Na 4Fe(CN) 6+Zn(OH) 2↓。 The chemical equation of the recovery method is: Na 2 Cu[Fe(CN) 6 ]+2NaOH→Na 4 Fe(CN) 6 +Zn(OH) 2 ↓.
实施例7Example 7
本实施例与实施例1区别仅在于,普鲁士白(Na 2MnFe(CN) 6)与氢氧化钠的摩尔比为1:1,其他条件与参数与实施例1完全相同,反应后的体系SEM图 如图4所示,由图4可以看出,碱液用量过少,正极材料不能完全反应,进而导致材料的回收效率明显下降。 The only difference between this example and Example 1 is that the molar ratio of Prussian white (Na 2 MnFe(CN) 6 ) to sodium hydroxide is 1:1. Other conditions and parameters are exactly the same as Example 1. SEM of the system after the reaction The diagram is shown in Figure 4. It can be seen from Figure 4 that if the amount of alkali solution is too small, the positive electrode material cannot react completely, which in turn leads to a significant decrease in the recovery efficiency of the material.
实施例8Example 8
本实施例与实施例1区别仅在于,普鲁士白(Na 2MnFe(CN) 6)与氢氧化钠的摩尔比为1:5,其他条件与参数与实施例1完全相同。 The only difference between this embodiment and Example 1 is that the molar ratio of Prussian white (Na 2 MnFe(CN) 6 ) to sodium hydroxide is 1:5, and other conditions and parameters are exactly the same as those in Example 1.
由实施例1和实施例7-8对比可以看出,本发明所述回收方法中,普鲁士类正极材料和碱的摩尔比会影响回收效果,若碱液的加入量过大,导致碱液过多浪费,所得到的亚铁氰化钠或亚铁氰化钾溶液中含有大量的钠离子或钾离子,增加了后续处理钠离子或钾离子的工序;若碱液的加入量过小,则导致反应不充分,最终产物不纯,得到结构发生变化的普鲁士材料和相应的金属氧化或氢氧化物混合物,导致分离提纯复杂,增加成本。It can be seen from the comparison between Example 1 and Examples 7-8 that in the recovery method of the present invention, the molar ratio of the Prussian cathode material and the alkali will affect the recovery effect. If the amount of alkali solution added is too large, the alkali solution will overflow. It is wasteful. The obtained sodium ferrocyanide or potassium ferrocyanide solution contains a large amount of sodium ions or potassium ions, which increases the subsequent processing of sodium ions or potassium ions; if the amount of alkali added is too small, As a result, the reaction is insufficient, the final product is impure, and the Prussian material with a changed structure and the corresponding metal oxidation or hydroxide mixture are obtained, resulting in complicated separation and purification and increased costs.
由实施例1和对比例1对比可得,本发明对退役或废旧的钠离子电池普鲁士类正极材料资源进行回收利用,通过对正极片中普鲁士类材料进行冲洗和碱性溶液浸泡,使普鲁士类正极材料溶解在碱性溶液中,再经后续处理制备出亚铁氰化钠或亚铁氰化钾以及相应的过渡金属沉淀物,实现了钠正极材料资源的回收,这种方式避免了普鲁士类正极材料资源的损失,且这种回收方式工艺简单,环境无污染,经济效益明显。From the comparison between Example 1 and Comparative Example 1, it can be seen that the present invention recycles retired or discarded Prussian-type positive electrode material resources of sodium-ion batteries, and makes Prussian-type materials in the positive electrode sheets by rinsing and soaking them in alkaline solutions. The cathode material is dissolved in an alkaline solution, and then subjected to subsequent processing to prepare sodium ferrocyanide or potassium ferrocyanide and the corresponding transition metal precipitate, realizing the recovery of sodium cathode material resources. This method avoids the Prussian-type There is no loss of cathode material resources, and this recycling method has a simple process, no pollution to the environment, and obvious economic benefits.
申请人声明,以上所述仅为本发明的具体实施方式,但本发明的保护范围并不局限于此,所属技术领域的技术人员应该明了,任何属于本技术领域的技术人员在本发明揭露的技术范围内,可轻易想到的变化、组合或替换,均落在本发明的保护范围和公开范围之内。The applicant declares that the above are only specific embodiments of the present invention, but the protection scope of the present invention is not limited thereto. Those skilled in the technical field should understand that any person skilled in the technical field will not use the invention disclosed in the present invention. Within the technical scope, easily conceivable changes, combinations or substitutions fall within the protection scope and disclosure scope of the present invention.
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| GB190304513A (en) * | 1903-02-26 | 1904-02-25 | Grossmann S Cyanide Patents Sy | Improvements in the Manufacture of Cyanides, and the Recovery of Bye-products. |
| CN113054163A (en) * | 2021-03-11 | 2021-06-29 | 中国电力科学研究院有限公司 | Prussian blue-based sodium ion full-cell and preparation method thereof |
| CN114388922A (en) * | 2021-12-23 | 2022-04-22 | 广东邦普循环科技有限公司 | Method for recovering electrode material of retired lithium ion battery and application thereof |
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| GB190304513A (en) * | 1903-02-26 | 1904-02-25 | Grossmann S Cyanide Patents Sy | Improvements in the Manufacture of Cyanides, and the Recovery of Bye-products. |
| CN113054163A (en) * | 2021-03-11 | 2021-06-29 | 中国电力科学研究院有限公司 | Prussian blue-based sodium ion full-cell and preparation method thereof |
| CN114388922A (en) * | 2021-12-23 | 2022-04-22 | 广东邦普循环科技有限公司 | Method for recovering electrode material of retired lithium ion battery and application thereof |
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