CN114854989B - Method for leaching anode active material of photocatalytic reinforced waste lithium ion battery - Google Patents

Method for leaching anode active material of photocatalytic reinforced waste lithium ion battery Download PDF

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CN114854989B
CN114854989B CN202210457557.2A CN202210457557A CN114854989B CN 114854989 B CN114854989 B CN 114854989B CN 202210457557 A CN202210457557 A CN 202210457557A CN 114854989 B CN114854989 B CN 114854989B
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leaching
active material
lithium ion
ion battery
waste lithium
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CN114854989A (en
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杨舜
骆思源
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Jiangsu Normal University
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    • 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
    • C22B7/006Wet processes
    • C22B7/007Wet processes by acid 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
    • C22B23/00Obtaining nickel or cobalt
    • C22B23/04Obtaining nickel or cobalt by wet processes
    • C22B23/0407Leaching processes
    • C22B23/0415Leaching processes with acids or salt solutions except ammonium salts solutions
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B23/00Obtaining nickel or cobalt
    • C22B23/04Obtaining nickel or cobalt by wet processes
    • C22B23/0407Leaching processes
    • C22B23/0415Leaching processes with acids or salt solutions except ammonium salts solutions
    • C22B23/0423Halogenated acids or salts thereof
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B23/00Obtaining nickel or cobalt
    • C22B23/04Obtaining nickel or cobalt by wet processes
    • C22B23/0407Leaching processes
    • C22B23/0415Leaching processes with acids or salt solutions except ammonium salts solutions
    • C22B23/043Sulfurated acids or salts thereof
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B23/00Obtaining nickel or cobalt
    • C22B23/04Obtaining nickel or cobalt by wet processes
    • C22B23/0407Leaching processes
    • C22B23/0415Leaching processes with acids or salt solutions except ammonium salts solutions
    • C22B23/0438Nitric acids or salts thereof
    • 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
    • C22B47/00Obtaining manganese
    • 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
    • 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

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  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Manufacturing & Machinery (AREA)
  • Materials Engineering (AREA)
  • Mechanical Engineering (AREA)
  • Metallurgy (AREA)
  • Organic Chemistry (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Geology (AREA)
  • Electrochemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Processing Of Solid Wastes (AREA)
  • Manufacture And Refinement Of Metals (AREA)

Abstract

The invention discloses a method for leaching out an anode active material of a photocatalytic reinforced waste lithium ion battery and application thereof. The method solves the problems of high cost, high subsequent treatment difficulty and the like caused by the addition of the traditional reducing agent, has high leaching rate of valuable metals, low energy consumption, can recycle the photocatalyst, does not produce secondary pollution, and is an efficient and safe environment-friendly leaching method.

Description

Method for leaching anode active material of photocatalytic reinforced waste lithium ion battery
Technical Field
The invention relates to the field of waste battery recovery treatment, in particular to a method for leaching out anode active substances of a photocatalytic reinforced waste lithium ion battery and application of the method in reinforcing the recovery of the anode active substances of the waste lithium ion battery.
Background
Lithium ion batteries, one of the most popular types of rechargeable batteries in portable electronic devices that have emerged since the 90 s of the 20 th century, have been widely used in mobile electronic devices such as cellular phones and computers, and have been increasingly popular in the fields of military, aerospace navigation, electric vehicles, medical devices, and the like. Although the large-scale use of lithium ion batteries brings great convenience to the life of people, the influence of a large number of abandoned lithium ion batteries on the environment and resource waste is immeasurable. The waste lithium battery contains a plurality of valuable resources such as cobalt, lithium, nickel, manganese and the like, and particularly the metal cobalt and lithium contained in the positive electrode active material are internationally accepted strategic substances. If the effective recovery treatment cannot be obtained, the environment is polluted, and the waste of resources is also caused. Therefore, developing a method for efficiently recovering rare noble metals in the anode material of the waste lithium ion battery becomes one of the current research hot spot fields.
At present, after pretreatment such as discharging and disassembling, the waste lithium ion batteries are divided into three main categories according to main key extraction process technologies: physical recovery techniques, chemical recovery techniques, biological recovery techniques. The chemical recovery technology, mainly wet method, is widely used for separating and recovering metals, which is to leach the metal ions in the positive electrode of the waste battery by using proper acid, alkali, reducing agent and the like, and then separate the metal elements in the leaching solution by methods of precipitation, ion exchange, extraction, salting-out, electrochemistry and the like. Among them, acid leaching is the most commonly used method for recovering metal elements in the positive electrode waste, and acids generally used are inorganic acids (e.g., HCl, HNO 3, and H 2SO4), organic acids (e.g., citric acid, oxalic acid, and ascorbic acid), and the like. However, since cobalt in the positive electrode lithium cobaltate active material exists in the form of Co (III), only Co (II) is easily extracted by leaching acid.
In the present stage, more research is still needed to add hydrogen peroxide, iron powder, sodium thiosulfate, sodium bisulfate and the like as reducing agents to reduce the active substances of the positive electrode so as to promote the dissolution of valuable metals such as cobalt, lithium, nickel, manganese and the like. For example, patent CN101381817a is leached by a hydrochloric acid and hydrogen peroxide system, however, hydrogen peroxide is easy to self-decompose, has low utilization rate and severe reaction under acidic conditions, has potential safety hazards, and the addition of a reducing agent also causes cost rise and subsequent treatment difficulty increase; CN108504865A discloses that adding a reducing agent with chloride salt or chlorine-containing solution still causes cost increase and secondary pollution, and the subsequent treatment difficulty increases, although the steps are complex, the cost recovery cost is high, and the application of the acid leaching method in industry is greatly limited. Therefore, it is very necessary to seek an economical and environment-friendly method to improve the leaching efficiency of the anode material of the waste lithium ion battery.
Disclosure of Invention
Aiming at the technical defects, the invention aims to provide a leaching method for leaching the anode active material of the waste lithium ion battery by utilizing the reducing functions of the photocatalyst, such as photoelectrons, hydrogen peroxide and the like under the illumination condition, which solves the problems of high cost, increased subsequent treatment difficulty and the like caused by the addition of the traditional reducing agent, has high leaching rate of valuable metals, low energy consumption, can be recycled, does not produce secondary pollution, and is an efficient and safe environment-friendly leaching method.
In order to achieve the purpose, the method for leaching the anode active material of the photocatalytic reinforced waste lithium ion battery comprises the step of leaching the anode active material of the waste lithium ion battery through a leaching agent and a photocatalyst, wherein the leaching agent is an aqueous solution of organic acid or inorganic acid.
Further, the method for leaching the anode active material of the photocatalytic enhanced waste lithium ion battery according to claim 1 is characterized by comprising the following steps:
s1: uniformly mixing the leaching agent and the photocatalyst;
S2: and adding the positive electrode active material of the waste lithium ion battery into the mixed solution obtained in the step S1, leaching under the illumination condition, and collecting the leaching solution.
Further, the method for leaching the anode active material of the photocatalytic enhanced waste lithium ion battery according to claim 1 or 2, wherein the organic acid is any one or a combination of more than two of citric acid, acetic acid, oxalic acid, ascorbic acid and aspartic acid; the inorganic acid is any one or the combination of more than two of hydrochloric acid, sulfuric acid or nitric acid.
Further, the method for leaching the anode active material of the photocatalytic enhanced waste lithium ion battery according to any one of claims 1 or 2, wherein the photocatalyst is selected from at least one of TiO 2、WO3、Fe2O3、CdS、Ag3PO4、g-C3N4 and/or at least one modified photocatalyst of TiO 2、WO3、Fe2O3、CdS、Ag3PO4、g-C3N4.
Further, the method for leaching the anode active material of the photocatalytic enhanced waste lithium ion battery according to claim 1 is characterized in that the active material in the anode sheet is any one or more than two mixtures of LiCoO2、LiNiO2、LiMn2O4、LiNixCoyMn1-x-yO2、LiNixCoyAl1-x-yO2.
Further, the method for leaching the anode active material of the photocatalytic enhanced waste lithium ion battery according to claim 1 is characterized in that the molar ratio of H + to the anode active material in the leaching agent in the leaching process is (3-5): 1, and the mass ratio of the photocatalyst to the anode active material is (0.2-0.7): 1.
Further, the method for leaching the anode active material of the photocatalytic enhanced waste lithium ion battery according to claim 1 is characterized in that the leaching process temperature is 20-80 ℃; the leaching time is more than or equal to 30min.
The invention also aims to provide application of the method in reinforcing recovery of the positive electrode active material of the waste lithium ion battery.
The invention has the beneficial effects that:
1. According to the invention, the photocatalyst is used for replacing the reducing agent to leach the positive electrode active material of the waste lithium ion battery, the leaching rate of valuable metals is more than 97%, and the problems of cost increase, subsequent treatment difficulty increase and the like caused by the addition of the traditional reducing agent are solved;
2. The invention can generate photoelectron, hydrogen peroxide and other reducing functions by utilizing the photocatalyst under the illumination condition, has low energy consumption, can be recycled, does not generate secondary pollution in the whole process, and is an efficient and safe environment-friendly leaching method.
Detailed Description
The inventive method of the present invention is described and illustrated in detail below in conjunction with specific examples. The content of which is to be interpreted as an explanation of the invention and not to limit the scope of the invention.
The method for leaching the anode active material of the photocatalytic enhanced waste lithium ion battery is characterized by comprising the following steps of:
s1: uniformly mixing the leaching agent and the photocatalyst;
S2: and adding the positive electrode active material of the waste lithium ion battery into the mixed solution obtained in the step S1, leaching under the illumination condition, and collecting the leaching solution.
The organic acid is any one or the combination of more than two of citric acid, acetic acid, oxalic acid, ascorbic acid or aspartic acid; the inorganic acid is any one or the combination of more than two of hydrochloric acid, sulfuric acid or nitric acid.
The photocatalyst is selected from any one or more than two of TiO 2、WO3、Fe2O3、CdS、Ag3PO4、g-C3N4 and modified TiO 2、WO3、Fe2O3、CdS、Ag3PO4、g-C3N4.
The active material in the positive plate is any one or more than two mixtures of LiCoO2、LiNiO2、LiMn2O4、LiNixCoyMn1-x-yO2、LiNixCoyAl1-x-yO2.
The molar ratio of H + to the positive electrode active material in the leaching agent in the leaching process is (3-5) 1, and the mass ratio of the photocatalyst to the positive electrode active material is (0.2-0.7) 1.
The temperature of the leaching process is 20-80 ℃; the leaching time is more than or equal to 30min.
Example 1
Diluting 13mL of concentrated sulfuric acid, magnetically stirring for assistance, fully dissolving, finally fixing the volume to 100mL, adding 2.5g g-C 3N4, and performing ultrasonic dispersion. And (3) adding the LiNi xCoyMn1-x-yO2 anode powder material obtained by disassembling the scrapped lithium ion battery on the new energy automobile into the solution, controlling the solid-to-liquid ratio to be 120 (g/L), and leaching at 40 ℃ for 60min under the illumination condition, wherein leaching rates of Ni, co and Mn are 98.62%,99.29% and 99.91% respectively.
Example 2
Diluting 20mL of concentrated hydrochloric acid, magnetically stirring for assistance, fully dissolving, finally fixing the volume to 100mL, adding 2g of TiO 2, and performing ultrasonic dispersion. And (3) adding the LiNi xCoyMn1-x-yO2 anode powder material obtained by disassembling the waste batteries of the mobile phone into the solution, controlling the solid-liquid ratio to be 100 (g/L), and leaching at 60 ℃ for 60min under the illumination condition, wherein leaching rates of Ni, co and Mn are 98.62%,99.29% and 99.91%, respectively.
Example 3
Taking 10g of citric acid, fully dissolving, finally fixing the volume to 100mL, adding 2g of CdS, and performing ultrasonic dispersion. LiCoO 2 positive electrode powder material obtained by disassembling waste batteries of mobile phones is added into the solution, the solid-to-liquid ratio is controlled to be 110 (g/L), leaching is carried out for 60min at 50 ℃ under the illumination condition, and the leaching rate of Co is 98.29%.
Example 4
Diluting 13mL of concentrated sulfuric acid, magnetically stirring for assistance, fully dissolving, finally fixing the volume to 100mL, adding 2.5g g-C 3N4, and performing ultrasonic dispersion. The composition of the waste battery positive electrode material provided by the waste battery disassembly workshop comprises LiCoO2、LiNiO2、LiMn2O4、LiNixCoyMn1-x-yO2、LiNixCoyAl1-x-yO2 powder materials, the solid-to-liquid ratio is controlled to be 120 (g/L), leaching is carried out for 120min at 40 ℃ under the illumination condition, and leaching rates of Ni, co and Mn are 98.53%,98.92% and 99.85% respectively.
Example 5
Diluting 20mL of concentrated nitric acid, magnetically stirring for assistance, fully dissolving, finally fixing the volume to 100mL, adding 2g of WO 3, and performing ultrasonic dispersion. The LiMn 2O4 positive electrode plate powder material of a certain battery factory is added into the solution, the solid-liquid ratio is controlled to be 120 (g/L), leaching is carried out for 120min at 40 ℃ under the illumination condition, and leaching rates of Li and Mn are 97.36% and 98.47% respectively.
Example 6
Taking 12g of oxalic acid, fully dissolving, finally fixing the volume to 100mL, adding 2g of Ag 3PO4, and performing ultrasonic dispersion. And (3) adding the LiNi xCoyMn1-x-yO2 anode powder material obtained by disassembling the waste batteries of the mobile phone into the solution, controlling the solid-to-liquid ratio to be 120 (g/L), and leaching for 120min at 70 ℃ under the illumination condition, wherein leaching rates of Ni, co and Mn are 98.39%,99.56% and 98.98% respectively.
Example 7
10G of ascorbic acid is taken and fully dissolved, the volume is finally fixed to 100mL, 4g of Fe 2O3 is added, and ultrasonic dispersion is carried out. And (3) adding the LiNi xCoyMn1-x-yO2 anode powder material obtained by disassembling the waste batteries of the mobile phone into the solution, controlling the solid-to-liquid ratio to be 120 (g/L), and leaching for 120min at 70 ℃ under the illumination condition, wherein leaching rates of Ni, co and Mn are 97.46%,99.35% and 99.12% respectively.
Example 8
Taking 12g of aspartic acid, fully dissolving, finally fixing the volume to 100mL, adding 4g g-C 3N4, and performing ultrasonic dispersion. The LiMn 2O4 positive electrode plate powder material of a certain battery factory is added into the solution, the solid-liquid ratio is controlled to be 110 (g/L), leaching is carried out for 120min at 60 ℃ under the illumination condition, and leaching rates of Li and Mn are 98.24% and 98.36% respectively.
While the foregoing is directed to embodiments of the present invention, other and further details of the invention may be had by the present invention, it should be understood that the foregoing description is merely illustrative of the present invention and that no limitations are intended to the scope of the invention, except insofar as modifications, equivalents, improvements or modifications are within the spirit and principles of the invention.

Claims (7)

1. A method for leaching a photo-catalytic reinforced anode active material of a waste lithium ion battery is characterized in that the anode active material of the waste lithium ion battery is leached by a leaching agent and a photo-catalyst, wherein the leaching agent is an aqueous solution of organic acid or inorganic acid;
the method comprises the following steps:
s1: uniformly mixing the leaching agent and the photocatalyst;
S2: and adding the positive electrode active material of the waste lithium ion battery into the mixed solution obtained in the step S1, leaching under the illumination condition, and collecting the leaching solution.
2. The method for leaching the anode active material of the photocatalytic enhanced waste lithium ion battery according to claim 1, wherein the organic acid is any one or more of citric acid, acetic acid, oxalic acid, ascorbic acid and aspartic acid; the inorganic acid is any one or the combination of more than two of hydrochloric acid, sulfuric acid or nitric acid.
3. The method for leaching the anode active material of the photocatalytic enhanced waste lithium ion battery according to any one of claims 1 or 2, wherein the photocatalyst is selected from any one or a combination of more than two of TiO 2、WO3、Fe2O3、CdS、Ag3PO4、g-C3N4 and modified TiO 2、WO3、Fe2O3、CdS、Ag3PO4、g-C3N4.
4. The method for leaching the anode active material of the photocatalytic enhanced waste lithium ion battery according to claim 1, wherein the active material in the anode plate is any one or more than two mixtures of LiCoO2、LiNiO2、LiMn2O4、LiNixCoyMn1-x-yO2、LiNixCoyAl1-x-yO2.
5. The method for leaching the anode active material of the photocatalytic enhanced waste lithium ion battery according to claim 1, wherein the molar ratio of H + to the anode active material in the leaching agent in the leaching process is (3-5): 1, and the mass ratio of the photocatalyst to the anode active material is (0.2-0.7): 1.
6. The method for leaching the anode active material of the photocatalytic enhanced waste lithium ion battery according to claim 1, wherein the leaching process temperature is 20-80 ℃; the leaching time is more than or equal to 30 min.
7. The method of claim 1, wherein the method is used for enhancing recovery of positive electrode active materials of waste lithium ion batteries.
CN202210457557.2A 2022-04-27 2022-04-27 Method for leaching anode active material of photocatalytic reinforced waste lithium ion battery Active CN114854989B (en)

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CN116103499B (en) * 2023-02-16 2024-07-16 西安金藏膜环保科技有限公司 Method for leaching valuable metals from waste lithium batteries by photoelectrocatalysis of double photoelectrodes

Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2014105944A1 (en) * 2012-12-28 2014-07-03 Flsmidth A/S Use of enzymes for recovering a metal from a metal-containing ore
CN103915661A (en) * 2013-01-09 2014-07-09 中国科学院过程工程研究所 Method for direct recovery and restoration of lithium ion battery positive electrode material
CN104561544A (en) * 2015-01-23 2015-04-29 中南大学 Light-intensified bioleaching method for semiconductor minerals
DE102014209314A1 (en) * 2014-05-16 2015-11-19 Conrad Kunze Process for processing mineral raw materials
WO2016148446A1 (en) * 2015-03-13 2016-09-22 주식회사 정수뉴테크 Method for manufacturing zinc compound from electric arc furnace dust
CN108504865A (en) * 2018-03-30 2018-09-07 中国科学院过程工程研究所 A method of strengthening waste lithium ion cell anode active material and leaches
CN110629023A (en) * 2019-10-17 2019-12-31 中南大学 Multifunctional biological metallurgical reactor
CN111394745A (en) * 2020-03-25 2020-07-10 意定(上海)信息科技有限公司 Method for preparing lithium hydroxide from lithium-containing low-magnesium brine
CN111809052A (en) * 2020-06-23 2020-10-23 江苏理工学院 Method for leaching lithium cobaltate by photocatalytic microbial fuel cell

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20210277531A1 (en) * 2020-02-27 2021-09-09 Massachusetts Institute Of Technology Selective sulfidation and desulfidation

Patent Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2014105944A1 (en) * 2012-12-28 2014-07-03 Flsmidth A/S Use of enzymes for recovering a metal from a metal-containing ore
CN103915661A (en) * 2013-01-09 2014-07-09 中国科学院过程工程研究所 Method for direct recovery and restoration of lithium ion battery positive electrode material
DE102014209314A1 (en) * 2014-05-16 2015-11-19 Conrad Kunze Process for processing mineral raw materials
CN104561544A (en) * 2015-01-23 2015-04-29 中南大学 Light-intensified bioleaching method for semiconductor minerals
WO2016148446A1 (en) * 2015-03-13 2016-09-22 주식회사 정수뉴테크 Method for manufacturing zinc compound from electric arc furnace dust
CN108504865A (en) * 2018-03-30 2018-09-07 中国科学院过程工程研究所 A method of strengthening waste lithium ion cell anode active material and leaches
CN110629023A (en) * 2019-10-17 2019-12-31 中南大学 Multifunctional biological metallurgical reactor
CN111394745A (en) * 2020-03-25 2020-07-10 意定(上海)信息科技有限公司 Method for preparing lithium hydroxide from lithium-containing low-magnesium brine
CN111809052A (en) * 2020-06-23 2020-10-23 江苏理工学院 Method for leaching lithium cobaltate by photocatalytic microbial fuel cell

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
Recyclable and Reusable Fe3O4@Polydopanime for Valuable Metal Recovery from Spent Lithium-Ion Batteries;Xuhui Zhu;ACS sustainable Chem. Eng.;5045-5054 *
光催化氧化预处理对硫酸浸出硫化铜精矿的影响;张泽强, 沈上越;有色金属(选矿部分)(第05期);13-15 *

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