WO2008022413A1 - Process for the separation and extraction of used li-ion batteries - Google Patents

Process for the separation and extraction of used li-ion batteries Download PDF

Info

Publication number
WO2008022413A1
WO2008022413A1 PCT/BR2007/000031 BR2007000031W WO2008022413A1 WO 2008022413 A1 WO2008022413 A1 WO 2008022413A1 BR 2007000031 W BR2007000031 W BR 2007000031W WO 2008022413 A1 WO2008022413 A1 WO 2008022413A1
Authority
WO
WIPO (PCT)
Prior art keywords
graffiti
agglutinant
copper
acid solution
extraction
Prior art date
Application number
PCT/BR2007/000031
Other languages
French (fr)
Inventor
Marcelo Bozzo
Maria Do Rosário Fabeni HURTADO
Maria Angela Brotto Baldini Lance
Original Assignee
Lg Eletronics De São Paulo Ltda
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Lg Eletronics De São Paulo Ltda filed Critical Lg Eletronics De São Paulo Ltda
Publication of WO2008022413A1 publication Critical patent/WO2008022413A1/en

Links

Classifications

    • HELECTRICITY
    • H01ELECTRIC ELEMENTS
    • H01MPROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
    • H01M6/00Primary cells; Manufacture thereof
    • H01M6/52Reclaiming serviceable parts of waste cells or batteries, e.g. recycling
    • 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 refers to a process that allows the separation of negative electrode materials from lithium-ion batteries at the end of their lifespan.
  • the lithium batteries When compared to nickel-cadmium and nickel-metal-hydride, because of the high energy density and the high pressure of lithium, the lithium batteries have been thoroughly investigated and used in cellular phones, as this technology enables the manufacturing of higher capacity and lighter batteries, Consequently, the use of ion-lithium batteries has grown exponentially and, as a result, the disposal increases each year.
  • the process comprises the following stages: i) Battery opening; ii) Previous separation of some compounds (metal can, polymeric carcass, metal tapes, etc); iii) The negative electrode is processed, resulting in the separation of the graffiti and the agglutinant in the copper collector, thus obtaining a metallic copper and a mixture of graffiti and agglutinant.
  • the process to obtain the metallic copper does not comprise the copper dissolution and the precipitation and purification of the compounds obtained. Potential copper contamination of other products obtained during the whole recycling process is also eliminated.
  • the copper is usually used as a conductive material (wires and cables), responsible for 45% of its annual consumption.
  • Other applications are: i) in condenser and piping tubes; ii) in electromagnets; iii) in electric motors; iv) in switches and relays, vacuum tubes and microwave oven magnets; v) as a substitute to aluminum (less conductive) in integrated circuits; vi) in the mint process (copper-nickel alloy), in the manufacturing of sculptures, statues, bells and ornaments (nickel, bronze and silver alloys); and vii) in copper crystal lens for ultra-high-sensitivity medical imaging (radiology).
  • the batteries that are not disposed of correctly may result in their compounds being carried away by rivers, rain, wind, and other ways. Copper combined with certain solutions (chloride, acid, etc.) forms copper oxide, which can be leached and carried away. Copper at certain concentrations becomes extremely toxic to animal life, and, depending on the species, it is much more toxic to animals closer to the base of the food chain. Copper toxicity is directly related to the distribution of its individual chemical and physical forms, which, together, contribute to the total concentration. The rate of copper incorporation is high and related to the type of sediment/clay, pH, competitive cations and the presence of iron and manganese oxides.
  • the scientific literature describes a process in which the negative electrode materials are extracted from the collector using ethyl acetate as solvent.
  • the ground material produced during the extraction consists of carbon and agglutinant, which were mechanically removed through grinding, for example.
  • present invention intends to describe a method to separate the graffiti and the agglutinant from the negative collector and to recover copper in its metallic form.
  • Another objective is to provide a system to separate the copper from the graffiti and the agglutinant.
  • Such container is placed inside a becker and, next, a hydrochloric acid solution at 5% is added to the electrodes so that both graffiti and agglutinant are removed. After ten minutes of mechanical stirring, the graffiti and the agglutinant are released, passing through the holes. The copper remains in the perforated container.
  • the acid solution is filtered, the graffiti and the agglutinant remain in the filter-paper, and the acid solution remains in the filtrate. It can be reused in the process for a couple of times.
  • the invention is described in details as follows:
  • Figure 1 shows the flowchart of the whole process.
  • Figure 2 illustrates the design of the system to separate graffiti and agglutinant from the copper collector.
  • the negative electrodes after the extraction of the lithium compounds, are placed in a container with holes, proper to allow the passage of the pulverized material composed of graffiti and agglutinant (PVDF, PAN, PMMA on the negative electrodes). It is recommended to use a plastic, metallic or polymeric container resistant to the acid solution.
  • the perforated container is placed inside another container and then a hydrochloric acid solution at 2 to 10% is added to the electrodes.
  • the hydrochloric acid solution must be stirred mechanically or through another method that allows the graffiti and the agglutinant to expand and then to release from the copper cutting device. After ten minutes of mechanical stirring, the graffiti and the agglutinant are released, passing through the holes.
  • the copper remains in the perforated container.
  • the acid solution is filtered, the graffiti and the agglutinant remain in the filter-paper, and the acid solution remains in the filtrate. It can be reused in the process for at least four times.
  • the graffiti and the agglutinant are dried and can be used in the manufacturing of new batteries. They are weighed, generating a mass of 12g/10 batteries (copper) and 31g/10 batteries (graffiti). Besides the economical aspects regarding the recovery and reuse of materials described previously, this invention also contributes to the conservation and preservation of the environment. Although a preferable solution has been described and illustrated, it is important to stress that other solutions can be performed within the same scope.

Abstract

Process for the extraction of graffiti and agglutinant in the copper collector to proceed with the separation of negative electrodes, such process comprises the following stages: i) after the extraction of lithium compounds, the negative electrodes are placed in a perforated container, proper to allow the passage of the pulverized material composed of graffiti and agglutinant; such container should be made from plastic, metallic or polymeric material resistant to the acid solution and placed inside a becker, ii) a solution of hydrochloric acid at 2 to 10% is then added to the electrodes for the removal of the graffiti and agglutinant; iii) after ten minutes of mechanical stirring, the graffiti and the agglutinant are released, passing through the holes and the copper remains in the perforated container; iv) such acid solution is filtered, the graffiti and the agglutinant remain in the filter-paper and the acid solution remains in the filtrate; it can be reused in the process for a is few other times; e v) the graffiti and the agglutinant are then dried and weighed and they can be used in the manufacturing of new batteries.

Description

Process for the separation and extraction of used Li-ion batteries "
The present invention refers to a process that allows the separation of negative electrode materials from lithium-ion batteries at the end of their lifespan.
When compared to nickel-cadmium and nickel-metal-hydride, because of the high energy density and the high pressure of lithium, the lithium batteries have been thoroughly investigated and used in cellular phones, as this technology enables the manufacturing of higher capacity and lighter batteries, Consequently, the use of ion-lithium batteries has grown exponentially and, as a result, the disposal increases each year.
In addition to environmental benefits, the lithium-ion batteries reuse assumes great importance, as their components hold a significant economic value, The process comprises the following stages: i) Battery opening; ii) Previous separation of some compounds (metal can, polymeric carcass, metal tapes, etc); iii) The negative electrode is processed, resulting in the separation of the graffiti and the agglutinant in the copper collector, thus obtaining a metallic copper and a mixture of graffiti and agglutinant.
The process to obtain the metallic copper does not comprise the copper dissolution and the precipitation and purification of the compounds obtained. Potential copper contamination of other products obtained during the whole recycling process is also eliminated.
As it is common knowledge among the specialists in the area, the copper is usually used as a conductive material (wires and cables), responsible for 45% of its annual consumption. Other applications are: i) in condenser and piping tubes; ii) in electromagnets; iii) in electric motors; iv) in switches and relays, vacuum tubes and microwave oven magnets; v) as a substitute to aluminum (less conductive) in integrated circuits; vi) in the mint process (copper-nickel alloy), in the manufacturing of sculptures, statues, bells and ornaments (nickel, bronze and silver alloys); and vii) in copper crystal lens for ultra-high-sensitivity medical imaging (radiology).
The growing worldwide demand for high purity metals, the creation of more restrictive environmental regulations, the need to reduce operating costs and achieve economic viability and the gradual reduction of precious metal ores lead the industry to develop increasingly more complex metal purification processes. Reusing metallic copper extracted from lithium batteries through the proposed process is a way of meeting these needs.
The batteries that are not disposed of correctly may result in their compounds being carried away by rivers, rain, wind, and other ways. Copper combined with certain solutions (chloride, acid, etc.) forms copper oxide, which can be leached and carried away. Copper at certain concentrations becomes extremely toxic to animal life, and, depending on the species, it is much more toxic to animals closer to the base of the food chain. Copper toxicity is directly related to the distribution of its individual chemical and physical forms, which, together, contribute to the total concentration. The rate of copper incorporation is high and related to the type of sediment/clay, pH, competitive cations and the presence of iron and manganese oxides.
When the negative electrode is grinded and the copper is dissolved, the traditional chemical precipitation methods are used, which are less selective in some cases.
In most cases, thø extraction of copper from copper oxide is a high energy-consumption process, and therefore can be extremely expensive. Also, there has been an increase in the demand for a process to recover copper from the negative electrode that does not include the grounding and dissolving stages. Another aspect to be considered is that the described process uses only low-cost solvents that are easy to be obtained and handled.
The scientific literature describes a process in which the negative electrode materials are extracted from the collector using ethyl acetate as solvent. The ground material produced during the extraction consists of carbon and agglutinant, which were mechanically removed through grinding, for example.
Based on the aspects related above, *» present invention intends to describe a method to separate the graffiti and the agglutinant from the negative collector and to recover copper in its metallic form.
Another objective is to provide a system to separate the copper from the graffiti and the agglutinant.
The objectives stated previously will be achieved through the process of separating and extracting graffiti and agglutinant from the copper collector, which consists of a method and a system to separate graffiti and agglutinant from the copper collector. After the batteries are opened, the positive and negative electrodes and separators are placed in a water solution in order to liquefy the lithium compounds. When the solubilization process was completed, tile positive electrode material was dissolved in another water solvent in order to obtain aluminum and cobalt compounds and pulverized material containing graffiti and agglutinant. To proceed with the separation of the negative electrodes, they are placed into a container with holes. Such container is placed inside a becker and, next, a hydrochloric acid solution at 5% is added to the electrodes so that both graffiti and agglutinant are removed. After ten minutes of mechanical stirring, the graffiti and the agglutinant are released, passing through the holes. The copper remains in the perforated container. The acid solution is filtered, the graffiti and the agglutinant remain in the filter-paper, and the acid solution remains in the filtrate. It can be reused in the process for a couple of times. The invention is described in details as follows:
Figure 1 shows the flowchart of the whole process. Figure 2 illustrates the design of the system to separate graffiti and agglutinant from the copper collector.
According to the figures, the negative electrodes, after the extraction of the lithium compounds, are placed in a container with holes, proper to allow the passage of the pulverized material composed of graffiti and agglutinant (PVDF, PAN, PMMA on the negative electrodes). It is recommended to use a plastic, metallic or polymeric container resistant to the acid solution. The perforated container is placed inside another container and then a hydrochloric acid solution at 2 to 10% is added to the electrodes. The hydrochloric acid solution must be stirred mechanically or through another method that allows the graffiti and the agglutinant to expand and then to release from the copper cutting device. After ten minutes of mechanical stirring, the graffiti and the agglutinant are released, passing through the holes. The copper remains in the perforated container. The acid solution is filtered, the graffiti and the agglutinant remain in the filter-paper, and the acid solution remains in the filtrate. It can be reused in the process for at least four times. The graffiti and the agglutinant are dried and can be used in the manufacturing of new batteries. They are weighed, generating a mass of 12g/10 batteries (copper) and 31g/10 batteries (graffiti). Besides the economical aspects regarding the recovery and reuse of materials described previously, this invention also contributes to the conservation and preservation of the environment. Although a preferable solution has been described and illustrated, it is important to stress that other solutions can be performed within the same scope.

Claims

Claims
1- "PROCESS FOR THE EXTRACTION OF GRAFFITI AND AGGLUTINANT IN THE COPPER COLLECTOR", characterized by the fact that, to proceed with the separation of negative electrodes, such process comprises the foffowing stages: i) after the extraction of lithium compounds, the negative electrodes are placed in a perforated container, proper to allow the passage of the pulverized material composed of graffiti and aggfutinant; such container should be made of plastic, metallic or polymeric material resistant to the acid solution and placed inside a becker; H) a solution of hydrochfσric acid at 2 to 10% is then added to the electrodes for the removal of the graffiti and aggfutinant; iiϊ) after ten minutes of mechanical stirring, the graffiti and the agglutinant are released, passing through the holes and the copper remains in the perforated container; iv) such acid solution is filtered, the graffiti and the agglutinant remain in the filter-paper and the acid solution remains in the filtrate; it can be reused in the process for a few other times; and v) the graffiti and the agglutinant are then dried and weighed and they can be used in the manufacturing of new batteries.
PCT/BR2007/000031 2006-08-21 2007-02-08 Process for the separation and extraction of used li-ion batteries WO2008022413A1 (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
BRPI0605048-4 2006-08-21
BRPI0605048-4A BRPI0605048A (en) 2006-08-21 2006-08-21 process for graphite extraction and copper collector binder

Publications (1)

Publication Number Publication Date
WO2008022413A1 true WO2008022413A1 (en) 2008-02-28

Family

ID=39106410

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/BR2007/000031 WO2008022413A1 (en) 2006-08-21 2007-02-08 Process for the separation and extraction of used li-ion batteries

Country Status (2)

Country Link
BR (1) BRPI0605048A (en)
WO (1) WO2008022413A1 (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102110825A (en) * 2009-12-25 2011-06-29 上海市民办尚德实验学校 Recovery processing method of waste dry battery
CN105304967A (en) * 2015-10-28 2016-02-03 东莞市凯金新能源科技有限公司 Method for recycling scrapped lithium ion battery graphite cathode pieces

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1819326A (en) * 2006-01-10 2006-08-16 东南大学 Resource separation of waste lithium ion battery

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1819326A (en) * 2006-01-10 2006-08-16 东南大学 Resource separation of waste lithium ion battery

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102110825A (en) * 2009-12-25 2011-06-29 上海市民办尚德实验学校 Recovery processing method of waste dry battery
CN105304967A (en) * 2015-10-28 2016-02-03 东莞市凯金新能源科技有限公司 Method for recycling scrapped lithium ion battery graphite cathode pieces

Also Published As

Publication number Publication date
BRPI0605048A (en) 2008-04-08

Similar Documents

Publication Publication Date Title
CA3085965C (en) A method for recycling lithium batteries
Ordoñez et al. Processes and technologies for the recycling and recovery of spent lithium-ion batteries
CN100595970C (en) Method for selectively removing copper from waste lithium ion battery
Xu et al. A review of processes and technologies for the recycling of lithium-ion secondary batteries
JP4865745B2 (en) Method for recovering valuable metals from lithium batteries containing Co, Ni, Mn
KR100930453B1 (en) How to Recover Metals from Battery Residues
Provazi et al. Metal separation from mixed types of batteries using selective precipitation and liquid–liquid extraction techniques
Zheng et al. Leaching procedure and kinetic studies of cobalt in cathode materials from spent lithium ion batteries using organic citric acid as leachant
US20170170532A1 (en) Method for recycling valuable metals from spent batteries
CN109207730A (en) A kind of method and system recycling lithium from waste lithium iron phosphate battery
US20160030987A1 (en) Process for the recycling of waste batteries and waste printed circuit boards in molten salts or molten metals
US11509000B2 (en) Process for the recovery of cathode materials in the recycling of batteries by removing aluminum and iron
CN109256597A (en) A kind of method and system recycling lithium and cobalt from waste and old cobalt acid lithium battery
JP6375258B2 (en) Method for removing metal from mixed metal aqueous solution
JP2007122885A (en) Valuable metal recovery method from lithium ion battery
CN106450542A (en) Recycling method of waste lithium manganate lithium-ion battery
CN107204495A (en) A kind of method of the environmentally friendly recycling of discarded anode material of lithium battery
KR20110088356A (en) Method for separating aluminium foil and positive electrode active material
JP2016009613A (en) Method of withdrawing valuable materials from positive electrode of lithium ion secondary battery
WO2008022413A1 (en) Process for the separation and extraction of used li-ion batteries
FI128333B (en) Processes for production of micronutrients from spent alkaline batteries
EP4257710A1 (en) Lithium-ion battery recycling method
JP6363459B2 (en) Metal leaching method and metal recovery method using the same
CN103221557A (en) Method for producing nickel-ontaining acidic solution
WO2008022414A1 (en) Process for the extraction of chemical compounds found in secondary lithium batteries

Legal Events

Date Code Title Description
121 Ep: the epo has been informed by wipo that ep was designated in this application

Ref document number: 07701615

Country of ref document: EP

Kind code of ref document: A1

NENP Non-entry into the national phase

Ref country code: DE

NENP Non-entry into the national phase

Ref country code: RU

122 Ep: pct application non-entry in european phase

Ref document number: 07701615

Country of ref document: EP

Kind code of ref document: A1