CN102956937A - Waste lithium battery treatment method - Google Patents

Waste lithium battery treatment method Download PDF

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Publication number
CN102956937A
CN102956937A CN2012104963786A CN201210496378A CN102956937A CN 102956937 A CN102956937 A CN 102956937A CN 2012104963786 A CN2012104963786 A CN 2012104963786A CN 201210496378 A CN201210496378 A CN 201210496378A CN 102956937 A CN102956937 A CN 102956937A
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CN
China
Prior art keywords
battery
waste
dissolving
hydrochloric acid
metal
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Pending
Application number
CN2012104963786A
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Chinese (zh)
Inventor
陈刚
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
DALIAN DONGTAI INDUSTRIAL WASTE TREATMENT Co Ltd
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DALIAN DONGTAI INDUSTRIAL WASTE TREATMENT Co Ltd
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Application filed by DALIAN DONGTAI INDUSTRIAL WASTE TREATMENT Co Ltd filed Critical DALIAN DONGTAI INDUSTRIAL WASTE TREATMENT Co Ltd
Priority to CN2012104963786A priority Critical patent/CN102956937A/en
Publication of CN102956937A publication Critical patent/CN102956937A/en
Pending legal-status Critical Current

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    • 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

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  • Processing Of Solid Wastes (AREA)

Abstract

The invention provides a waste lithium battery treatment method which comprises the following steps: crushing a waste battery; removing electrolyte; removing irony metal through magnetic separation; dissolving surplus scrap materials of the treated battery into hydrochloric acid; adding hydrogen peroxide to promote dissolving; filtering the above dissolving solution to obtain a solution containing metal ions; carrying out electrolytic deposition on the obtained solution containing the metal ions step by step to obtain zinc and manganese dioxide; and finally extracting other metals by adopting ion exchange resin.

Description

The waste lithium cell processing method
Technical field
The invention belongs to the solid waste process field, be specifically related to the method that a kind of waste lithium cell is innoxious, resource recycles.
Background technology
The environmental type energy products that lithium ion battery is earned foreign exchange as high-tech, high production, high profit, height are referred to as one of one of large high-tech of 21 centurys ten or ten large money-making industries by external expert.In addition, along with the electronic product consumption increases day by day, its consumption figure is just with at double speed increment.And along with the development of lithium ion battery industry, its cost reduces gradually, and lithium battery is expected to occupy whole world Battery Market lion's share, is used widely.In the U.S., chargeable lithium cell accounts for 11% of U.S.'s lithium consumption figure with the lithium amount, and Japanese chargeable lithium cell accounts for 54% of Japanese lithium consumption figure with the lithium amount, and lithium battery has surpassed ickel-cadmium cell and Ni-MH battery aspect sale.
The negative material that uses in the lithium ion battery mostly is graphite, and positive electrode is then for the embedding lithium transition-metal oxide, and such as LiCoO2, LiNiO2, LiVO2 and LiMn2O4 etc., wherein using maximum is LiCoO2.In addition, along with to the going deep into of anode material for lithium-ion batteries research, people mix a small amount of nickel in LiCoO2, are used for the production of lithium ion battery as positive electrode with their mixed oxide.
Contain a large amount of expensive metallic cobalts in the waste and old lithium ion battery.Cobalt is a kind of rare precious metal, content in various ore deposits is very low, resource scarcity, and metal recovery rate is low in the production process, complex process, production cost is high, its content in lithium ion battery is then relatively high, if the cobalt resource in the waste and old lithium ion battery can be recycled, no matter is from the environmental protection aspect, or the recycling aspect of resource all is significant.
Summary of the invention
The object of the present invention is to provide a kind of recycling processing method of waste lithium cell, adopt the dissolving with hydrochloric acid battery waste, and to wherein adding hydrogen peroxide to promote the dissolving of metal in acid, the metal maximization in the refuse battery is reclaimed.
For reaching above-mentioned wood, the present invention adopts following technical scheme:
The waste lithium cell processing method, adopt following method:
(1) refuse battery is broken: refuse battery is broken, remove electrolyte, and remove ferrous metal by magnetic separation again;
(2) dissolving: the remaining power waste material after step (1) processing is dissolved in the hydrochloric acid, and adds hydrogen peroxide promotion dissolving;
(3) filter: the lysate of filtration step (2) obtains the solution of metal ion;
(4) ion-exchange: adopt the metal in ion exchange resin extraction step (3) the gained solution.
In the technical scheme provided by the invention, the described concentration of hydrochloric acid of step (2) is 6mol/L; The mass ratio of the described battery waste of step (2) and hydrochloric acid is 1:3 ~ 5.
In the technical scheme provided by the invention, the addition of the described hydrogen peroxide of step (2) is 12 ~ 18wt% of battery waste.
For the metal in the battery waste better is dissolved in the hydrochloric acid, the present invention adds hydrogen peroxide in the process of dissolving.The adding of hydrogen peroxide not only promotes the dissolving of metal in hydrochloric acid, and makes the process of dissolving also can obtain very high dissolution rate at normal temperatures.In addition, the present invention continues other heavy metal ion is extracted by ion exchange resin, has reduced to greatest extent the pollution of heavy metal to environment, and heavy metal ion has been realized recovery.
Embodiment
The following examples can make the present invention of those of ordinary skill in the art's comprehend, but do not limit the present invention in any way.
Embodiment 1
The waste lithium cell processing method, adopt following method:
(1) refuse battery is broken: refuse battery is broken, remove electrolyte, and remove ferrous metal by magnetic separation again;
(2) dissolving: battery waste and the hydrochloric acid remaining power waste material after to be 1:3 with step (1) process is dissolved in the 6mol/L hydrochloric acid in mass ratio, and the hydrogen peroxide that adds battery waste quality 12% promotes to dissolve;
(3) filter: the lysate of filtration step (2) obtains the solution of metal ion;
(4) electrolysis: the solution that adopts the metal ion that dc electrolysis obtains step (3) progressively electrolytic deposition obtains metallic zinc and manganese dioxide;
(5) ion-exchange: the metals such as the cobalt in employing ion exchange resin extraction step (3) the gained solution, copper, aluminium, iron, lithium.
Embodiment 2
The waste lithium cell processing method, adopt following method:
(1) refuse battery is broken: refuse battery is broken, remove electrolyte, and remove ferrous metal by magnetic separation again;
(2) dissolving: battery waste and the hydrochloric acid remaining power waste material after to be 1:5 with step (1) process is dissolved in the 6mol/L hydrochloric acid in mass ratio, and the hydrogen peroxide that adds battery waste quality 18% promotes to dissolve;
(3) filter: the lysate of filtration step (2) obtains the solution of metal ion;
(4) ion-exchange: the metals such as the cobalt in employing ion exchange resin extraction step (3) the gained solution, copper, aluminium, iron, lithium.
Embodiment 3
The waste lithium cell processing method, adopt following method:
(1) refuse battery is broken: refuse battery is broken, remove electrolyte, and remove ferrous metal by magnetic separation again;
(2) dissolving: battery waste and the hydrochloric acid remaining power waste material after to be 1:4 with step (1) process is dissolved in the 6mol/L hydrochloric acid in mass ratio, and the hydrogen peroxide that adds battery waste quality 15% promotes to dissolve;
(3) filter: the lysate of filtration step (2) obtains the solution of metal ion;
(4) ion-exchange: the metals such as the cobalt in employing ion exchange resin extraction step (3) the gained solution, copper, aluminium, iron, lithium.

Claims (4)

1. waste lithium cell processing method, adopt following method:
(1) refuse battery is broken: refuse battery is broken, remove electrolyte, and remove ferrous metal by magnetic separation again;
(2) dissolving: the remaining power waste material after step (1) processing is dissolved in the hydrochloric acid, and adds hydrogen peroxide promotion dissolving;
(3) filter: the lysate of filtration step (2) obtains the solution of metal ion;
(4) ion-exchange: adopt the metal ion metal in ion exchange resin extraction step (3) the gained solution.
2. method according to claim 1, it is characterized in that: the described concentration of hydrochloric acid of step (2) is 6mol/L.
3. method according to claim 2, it is characterized in that: the mass ratio of the described battery waste of step (2) and hydrochloric acid is 1:3 ~ 5.
4. the described method of each claim according to claim 1 ~ 3 is characterized in that: the addition of the described hydrogen peroxide of step (2) is 12 ~ 18wt% of battery waste.
CN2012104963786A 2012-11-28 2012-11-28 Waste lithium battery treatment method Pending CN102956937A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN2012104963786A CN102956937A (en) 2012-11-28 2012-11-28 Waste lithium battery treatment method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN2012104963786A CN102956937A (en) 2012-11-28 2012-11-28 Waste lithium battery treatment method

Publications (1)

Publication Number Publication Date
CN102956937A true CN102956937A (en) 2013-03-06

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CN (1) CN102956937A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104037468A (en) * 2014-06-05 2014-09-10 浙江工业大学 Method for recycling manganese and copper resources from waste lithium ion batteries
CN111559912A (en) * 2020-05-14 2020-08-21 湖北中环新材料科技有限公司 Method for preparing high-purity graphite by recycling waste lithium batteries
CN111697283A (en) * 2020-06-24 2020-09-22 衢州超越环保科技有限公司 Waste battery wet treatment recovery device
WO2022242186A1 (en) * 2021-05-19 2022-11-24 广东邦普循环科技有限公司 Method for preparing high-purity iron phosphate by using ferrophosphorus waste

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104037468A (en) * 2014-06-05 2014-09-10 浙江工业大学 Method for recycling manganese and copper resources from waste lithium ion batteries
CN104037468B (en) * 2014-06-05 2016-06-22 浙江工业大学 A kind of method reclaiming manganese and copper resource from waste and old lithium ion battery
CN111559912A (en) * 2020-05-14 2020-08-21 湖北中环新材料科技有限公司 Method for preparing high-purity graphite by recycling waste lithium batteries
CN111697283A (en) * 2020-06-24 2020-09-22 衢州超越环保科技有限公司 Waste battery wet treatment recovery device
CN111697283B (en) * 2020-06-24 2021-08-03 南京溧水高新产业股权投资有限公司 Waste battery wet treatment recovery device
WO2022242186A1 (en) * 2021-05-19 2022-11-24 广东邦普循环科技有限公司 Method for preparing high-purity iron phosphate by using ferrophosphorus waste

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Application publication date: 20130306