CN107871912A - In a kind of used Li ion cell from recovery in leachate caused by valuable metal iron removaling aluminium method - Google Patents

In a kind of used Li ion cell from recovery in leachate caused by valuable metal iron removaling aluminium method Download PDF

Info

Publication number
CN107871912A
CN107871912A CN201710872175.5A CN201710872175A CN107871912A CN 107871912 A CN107871912 A CN 107871912A CN 201710872175 A CN201710872175 A CN 201710872175A CN 107871912 A CN107871912 A CN 107871912A
Authority
CN
China
Prior art keywords
aluminium
iron
slag
leachate
valuable metal
Prior art date
Legal status (The legal status 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 status listed.)
Granted
Application number
CN201710872175.5A
Other languages
Chinese (zh)
Other versions
CN107871912B (en
Inventor
张银亮
谭群英
唐红辉
王杜
韦立剑
王致富
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.)
Hunan Brunp Recycling Technology Co Ltd
Guangdong Brunp Recycling Technology Co Ltd
Original Assignee
Hunan Brunp Recycling Technology Co Ltd
Guangdong Brunp Recycling Technology Co Ltd
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 Hunan Brunp Recycling Technology Co Ltd, Guangdong Brunp Recycling Technology Co Ltd filed Critical Hunan Brunp Recycling Technology Co Ltd
Priority to CN201710872175.5A priority Critical patent/CN107871912B/en
Publication of CN107871912A publication Critical patent/CN107871912A/en
Application granted granted Critical
Publication of CN107871912B publication Critical patent/CN107871912B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • 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
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B3/00Extraction of metal compounds from ores or concentrates by wet processes
    • C22B3/20Treatment or purification of solutions, e.g. obtained by leaching
    • C22B3/44Treatment or purification of solutions, e.g. obtained by leaching by chemical processes
    • 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

Abstract

The invention belongs to solution purification field in hydrometallurgy, the method for disclosing iron removaling aluminium in leachate caused by valuable metal (sulfuric acid nickel cobalt manganese solution) in a kind of used Li ion cell from recovery.The inventive method comprises the following steps:(1) pH for adjusting leachate is 1.5~2.0, and addition oxidant makes ferrous oxidising into ferric iron;(2) regulation system pH is 2.5~3.5, is aged, and filtering, obtains filtrate and iron aluminum slag;(3) regulation system pH is 4.5~5.0 again, is aged, and filtering, is purified liquid and aluminium slag.The aluminium slag that step (3) obtains is used to be used for regulation system pH in step (2) as conditioning agent.The inventive method can not only make iron in solution, aluminium content be reduced to production requirement value, and caused slag strainability is good, the valuable metal carried secretly in slag is few, and gained aluminium slag can be repeated for iron removaling in system, the minimizing target of slag is realized, there is preferable economic benefit and environmental benefit.

Description

Iron removaling in leachate caused by valuable metal in a kind of used Li ion cell from recovery The method of aluminium
Technical field
It is valuable in more particularly to a kind of used Li ion cell from recovery the invention belongs to solution purification field in hydrometallurgy The method of iron removaling aluminium in leachate caused by metal (sulfuric acid nickel cobalt manganese solution).
Background technology
Lithium ion battery since commercialization, because its have, small volume higher than energy, light weight, temperature limit it is wide, Unique advantage such as have extended cycle life, have a safety feature, and is widely used in civilian and military domain, such as video camera, mobile electricity Words, notebook computer and Portable Measurement Instrument etc., while lithium ion battery has turned into the light-duty of New-energy electric vehicle first choice One of high-energy power battery.For lithium ion battery after 500~1500 charge and discharge cycles, its active material will lose work Property, cause the capacity of battery to decline and scrap battery.Widely using for lithium ion battery certainly will bring substantial amounts of old and useless battery, If its random discarding can not only be caused seriously to pollute to environment, the even more waste to resource.In lithium ion battery contain compared with The metals resources such as more nickel (Ni), cobalt (Co), copper (Cu), lithium (Li), aluminium (Al), manganese (Mn), wherein cobalt, nickel, manganese and lithium contain Amount is respectively up to 30%, 20%, 20% and 35%, even more high.Therefore it is the economic value in waste and old lithium ion battery is high Metal is recycled, and no matter in terms of the environmental protection or from the aspects of the recycling of resource, is all significant.
The enterprise of recovery used Li ion cell will mainly be prepared into battery material, but electricity again at present after valuable metal recovery Pond material requires very high to impurity content.Containing elements such as iron, aluminium, zinc, copper, carbon in used Li ion cell, therefore in recovery electricity Need to purify leachate during valuable metal in pond, and how can make iron in leachate, aluminium remove it is clean and The problems such as the amount of metal carried secretly in slag is few, slag yield is few, removal of impurities cost is low are always perplex battery recycling industry several big Problem.Found by consulting substantial amounts of bibliography, domestic technical staff no so far was engaged in be carried out using two-step method The research of iron removaling aluminium.
The content of the invention
In order to overcome the shortcomings and deficiencies of the prior art described above, primary and foremost purpose of the invention is to provide a kind of simple, height Effect from recovery used Li ion cell in leachate caused by valuable metal (sulfuric acid nickel cobalt manganese solution) iron removaling aluminium method, For solving to reclaim the various problems that iron removaling aluminium runs into during valuable metal in used Li ion cell.
The purpose of the present invention is realized by following proposal:
A kind of simple, efficient leachate (the sulfuric acid nickel cobalt manganese caused by valuable metal from recovery used Li ion cell Solution) in iron removaling aluminium method, comprise the following steps:
(1) pH for adjusting leachate is 1.5~2.0, and addition oxidant makes ferrous oxidising into ferric iron;
(2) regulation system pH is 2.5~3.5, is aged, and filtering, obtains filtrate and iron aluminum slag;
(3) regulation system pH is 4.5~5.0 again, is aged, and filtering, is purified liquid and aluminium slag.
The aluminium slag that step (3) obtains is used as conditioning agent and is used for regulation system pH in step (2).So as to be removed Iron, obtain iron aluminum slag.
Above-mentioned aluminium slag, which is used to preferably add aluminium slag in step (2) system in step (2), first reacts 0.5h or more, followed by Continuous regulation system pH;More preferably react 0.5~1h.
Leachate described in step (1) is preferably the nickel sulfate caused by valuable metal from recovery used Li ion cell Sulfuric acid nickel cobalt manganese solution after cobalt manganese solution, more preferably copper removal.
Oxidant described in step (1) is oxidant commonly used in the art, such as hydrogen peroxide, sodium chlorate, height Potassium manganate etc..
The amount of oxidant used is so that ferrous iron is fully oxidized to three-level iron and is defined in system.
Step (1)~step (3) regulation pH can use alkali or acid to be adjusted, and described alkali can be sodium carbonate, hydrogen At least one of sodium oxide molybdena, calcium carbonate, calcium hydroxide, calcium oxide etc..
The time of ageing is preferably respectively 0.5h or more, preferably 0.5~1h in step (2) and step (3).
Iron aluminum slag obtained by step (2) can use water or diluted acid to be washed.
Iron aluminum slag obtained by step (2) can be used for selling outside.
Step (3) described scavenging solution is solution after target iron removaling aluminium, available for the processing of follow-up valuable metal recovery.
The inventive method, preferably include following steps:
(1) pH for adjusting leachate is 1.5~2.0, and addition oxidant makes ferrous oxidising into ferric iron;
(2) regulation system pH is 2.5~3.5, is aged, and filtering, obtains filtrate and iron aluminum slag;
(3) regulation system pH is 4.5~5.0 again, is aged, and filtering, is purified liquid and aluminium slag;
(4) regulation system pH in step (2) is added using the aluminium slag that step (3) obtains as pH adjusting agent, so as to iron removaling, obtained To iron aluminum slag;
(5) circulation above-mentioned steps realize the lasting iron removaling of leachate, aluminium.
The present invention is using two-step method to the sulfuric acid nickel cobalt manganese solution caused by valuable metal from recovery used Li ion cell Iron removaling aluminium is carried out, the iron in solution, aluminium content can not only be made to be reduced to production requirement value, and caused slag strainability is good, The valuable metal carried secretly in slag is few, it is often more important that the quantity of slag significantly reduces than a step iron removaling aluminium method, realizes the minimizing mesh of slag Mark, therefore there is preferable economic benefit and environmental benefit with two-step method iron removaling aluminium.
The present invention is had the following advantages and beneficial effect relative to prior art:
The inventive method using from recovery used Li ion cell during valuable metal caused sulfuric acid nickel cobalt manganese solution as Raw material, the iron aluminium in the sulfuric acid nickel cobalt manganese solution after copper removal is removed totally with two step iron removaling aluminium methods.Present invention process is simple, behaviour Make simplicity, caused iron aluminum slag amount is few, it is few to be mingled with the valuable metal amount such as nickel cobalt manganese in slag, and gained aluminium slag can be repeated for system Middle iron removaling, the purification of iron in solution, aluminium is not only realized, also achieve the minimizing of slag, there is preferable environmental benefit and economy Benefit.
Brief description of the drawings
Fig. 1 is the process chart of the present invention.
Embodiment
With reference to embodiment, the present invention is described in further detail, but the implementation of the present invention is not limited to this.
The material being related in the following example can obtain from commercial channel.
Embodiment 1
Fig. 1 is shown in technological process.The sulfuric acid nickel cobalt manganese solution after 500mL copper removals is taken, its pH is adjusted to 1.5 with sodium carbonate, so The hydrogen peroxide that mass fraction is 20% is added in backward solution makes ferrous iron in system be fully oxidized to ferric iron, available iron cyaniding Whether ferrous iron is oxidized completely in potassium sampling Detection system.Aluminium slag reaction 0.5h is added into the solution after oxidation, is added Calcium carbonate soln makes pH be adjusted to 2.5, and (when first processing does not have aluminium slag, can be directly added into calcium carbonate soln makes pH be adjusted to 2.5), old Filtered after changing 30min, filtered fluid, which flows into, removes reactive aluminum kettle, and iron aluminum slag is outer after washing to sell.With sodium carbonate liquor by filtered fluid PH is aged 1h after being adjusted to 4.5, then filter, and is purified liquid and aluminium slag, and scavenging solution flows into next process, and aluminium slag returns again to previous Step carries out iron removaling and obtains iron aluminum slag.After testing, the solution concentration of iron after purified is 5mg/L, aluminum concentration 75mg/L, is reached Production requirement;Nickel content is 0.5wt% in iron aluminum slag (butt), cobalt content 0.2wt%, manganese content 0.8wt%, is met Produce control standard.
Embodiment 2
The sulfuric acid nickel cobalt manganese solution after 500mL copper removals is taken, its pH is adjusted to 2.0 with sodium carbonate, then added into solution The hydrogen peroxide that mass fraction is 20% makes ferrous iron be fully oxidized to ferric iron, can use divalence in potassium ferricyanide sampling Detection system Whether iron is oxidized completely.Aluminium slag is added into the solution after oxidation, adding calcium carbonate soln after reaction 1h is adjusted to pH 3.5, filtered after being aged 30min, filtered fluid, which flows into, removes reactive aluminum kettle, and iron aluminum slag is outer after washing to sell.Be tod with sodium carbonate liquor The pH of filtrate is aged 0.5h after being adjusted to 5.0, then filter, and is purified liquid and aluminium slag, and scavenging solution flows into next process, and aluminium slag is again Return to previous step progress iron removaling and obtain iron aluminum slag.After testing, the solution concentration of iron after purified is 8mg/L, and aluminum concentration is 51mg/L, production requirement is reached;Nickel content is 0.36wt% in iron aluminum slag (butt), cobalt content 0.15wt%, manganese content For 0.57wt%, meet production control standard.
Embodiment 3
The sulfuric acid nickel cobalt manganese solution after 500mL copper removals is taken, its pH is adjusted to 1.5 with sodium carbonate, then added into solution Whether completely the hydrogen peroxide that mass fraction is 20% makes ferrous iron be fully oxidized to ferric iron, ferrous iron quilt is detected with the potassium ferricyanide Oxidation.Aluminium slag is added into the solution after oxidation, calcium carbonate soln is added after reaction 40min makes pH be adjusted to 3.5, ageing Filtered after 30min, filtered fluid, which flows into, removes reactive aluminum kettle, and iron aluminum slag is outer after washing to sell.With sodium carbonate liquor by the pH of filtered fluid 50min is aged after being adjusted to 4.8, is then filtered, is purified liquid and aluminium slag, scavenging solution flows into next process, before aluminium slag returns again to One step carries out iron removaling and obtains iron aluminum slag.After testing, the solution concentration of iron after purified is 4mg/L, aluminum concentration 63mg/L, is reached Production requirement is arrived;Nickel content is 0.40wt% in iron aluminum slag (butt), cobalt content 0.11wt%, and manganese content is 0.52wt%, meet production control standard.
Embodiment 4
The sulfuric acid nickel cobalt manganese solution after 500mL copper removals is taken, its pH is adjusted to 1.8 with sodium carbonate, then added into solution Whether completely the hydrogen peroxide that mass fraction is 20% makes ferrous iron be fully oxidized to ferric iron, ferrous iron quilt is detected with the potassium ferricyanide Oxidation.Aluminium slag is added into the solution after oxidation, adding calcium carbonate soln after reaction 0.5h makes pH be adjusted to 3.0, is aged 30min After filter, filtered fluid is flowed into and remove reactive aluminum kettle, and iron aluminum slag is sold outside after washing.The pH of filtered fluid is adjusted to sodium carbonate liquor 0.5h is aged after 4.5, is then filtered, is purified liquid and aluminium slag, scavenging solution flows into next process, and aluminium slag returns again to previous step Carry out iron removaling and obtain iron aluminum slag.After testing, the solution concentration of iron after purified is 4mg/L, aluminum concentration 72mg/L, has reached life Production requires;Nickel content is 0.32wt% in iron aluminum slag (butt), cobalt content 0.11wt%, manganese content 0.48wt%, is met Produce control standard.
Embodiment 5
The sulfuric acid nickel cobalt manganese solution after 500mL copper removals is taken, its pH is adjusted to 2.0 with sodium carbonate, then added into solution Whether completely the hydrogen peroxide that mass fraction is 20% makes ferrous iron be fully oxidized to ferric iron, ferrous iron quilt is detected with the potassium ferricyanide Oxidation.Aluminium slag is added into the solution after oxidation, adding calcium carbonate soln after reaction 0.5h makes pH be adjusted to 3.5, is aged 30min After filter, filtered fluid is flowed into and remove reactive aluminum kettle, and iron aluminum slag is sold outside after washing.The pH of filtered fluid is adjusted to sodium carbonate liquor 45min is aged after 4.8, is then filtered, is purified liquid and aluminium slag, scavenging solution flows into next process, and aluminium slag returns again to back The rapid iron removaling that carries out obtains iron aluminum slag.After testing, the solution concentration of iron after purified is 9mg/L, aluminum concentration 59mg/L, is reached Production requirement;Nickel content is 0.45wt%, cobalt content 0.21wt%, manganese content 0.65wt% in iron aluminum slag (butt), is accorded with Control standard is produced in symphysis.
Embodiment 6
The sulfuric acid nickel cobalt manganese solution after 500mL copper removals is taken, its pH is adjusted to 2.0 with sodium carbonate, then added into solution Whether completely the hydrogen peroxide that mass fraction is 20% makes ferrous iron be fully oxidized to ferric iron, ferrous iron quilt is detected with the potassium ferricyanide Oxidation.Aluminium slag is added into the solution after oxidation, calcium carbonate soln is added after reaction 45min makes pH be adjusted to 3.0, ageing Filtered after 30min, filtered fluid, which flows into, removes reactive aluminum kettle, and iron aluminum slag is outer after washing to sell.With sodium carbonate liquor by the pH of filtered fluid 1h is aged after being adjusted to 4.6, is then filtered, is purified liquid and aluminium slag, scavenging solution flows into next process, and aluminium slag returns again to back The rapid iron removaling that carries out obtains iron aluminum slag.After testing, the solution concentration of iron after purified is 6mg/L, aluminum concentration 76mg/L, is reached Production requirement;Nickel content is 0.43wt%, cobalt content 0.16wt%, manganese content 0.71wt% in iron aluminum slag (butt), is accorded with Control standard is produced in symphysis.
The inventive method using from recovery used Li ion cell during valuable metal caused sulfuric acid nickel cobalt manganese solution as Raw material, the iron aluminium in the sulfuric acid nickel cobalt manganese solution after copper removal is removed totally with two step iron removaling aluminium methods.The letter of the inventive method technique Single, easy to operate, caused iron aluminum slag amount is few, it is few to be mingled with the valuable metal amount such as nickel cobalt manganese in slag, not only realize iron in solution, The removal of aluminium, the minimizing of slag is also achieved, there is preferable environmental benefit and economic benefit.
Above-described embodiment is the preferable embodiment of the present invention, but embodiments of the present invention are not by above-described embodiment Limitation, other any Spirit Essences without departing from the present invention with made under principle change, modification, replacement, combine, simplification, Equivalent substitute mode is should be, is included within protection scope of the present invention.

Claims (10)

  1. It is 1. a kind of from the method for reclaiming iron removaling aluminium in leachate caused by valuable metal in used Li ion cell, it is characterised in that Comprise the following steps:
    (1) pH for adjusting leachate is 1.5~2.0, and addition oxidant makes ferrous oxidising into ferric iron;
    (2) regulation system pH is 2.5~3.5, is aged, and filtering, obtains filtrate and iron aluminum slag;
    (3) regulation system pH is 4.5~5.0 again, is aged, and filtering, is purified liquid and aluminium slag.
  2. 2. iron removaling aluminium in leachate caused by valuable metal in the used Li ion cell according to claim 1 from recovery Method, it is characterised in that:The aluminium slag that step (3) obtains is used to be used for regulation system pH in step (2) as conditioning agent.
  3. 3. iron removaling aluminium in leachate caused by valuable metal in the used Li ion cell according to claim 2 from recovery Method, it is characterised in that:The aluminium slag be used for step (2) in for will aluminium slag add step (2) system in first react 0.5h or with On, it is further continued for regulation system pH.
  4. 4. iron removaling aluminium in leachate caused by valuable metal in the used Li ion cell according to claim 1 from recovery Method, it is characterised in that:Leachate described in step (1) is the sulphur caused by valuable metal from recovery used Li ion cell Sour nickel cobalt manganese solution.
  5. 5. iron removaling aluminium in leachate caused by valuable metal in the used Li ion cell according to claim 1 from recovery Method, it is characterised in that:Oxidant described in step (1) is at least one of hydrogen peroxide, sodium chlorate and potassium permanganate.
  6. 6. iron removaling aluminium in leachate caused by valuable metal in the used Li ion cell according to claim 1 from recovery Method, it is characterised in that:Step (1)~step (3) regulation pH is adjusted using alkali or acid.
  7. 7. iron removaling aluminium in leachate caused by valuable metal in the used Li ion cell according to claim 6 from recovery Method, it is characterised in that:Described alkali is at least one in sodium carbonate, sodium hydroxide, calcium carbonate, calcium hydroxide and calcium oxide Kind.
  8. 8. iron removaling aluminium in leachate caused by valuable metal in the used Li ion cell according to claim 1 from recovery Method, it is characterised in that:The time of ageing is respectively 0.5h or more in step (2) and step (3).
  9. 9. iron removaling aluminium in leachate caused by valuable metal in the used Li ion cell according to claim 1 from recovery Method, it is characterised in that:The time of ageing is respectively 0.5~1h in step (2) and step (3).
  10. 10. iron removaling aluminium in leachate caused by valuable metal in the used Li ion cell according to claim 1 from recovery Method, it is characterised in that comprise the following steps:
    (1) pH for adjusting leachate is 1.5~2.0, and addition oxidant makes ferrous oxidising into ferric iron;
    (2) regulation system pH is 2.5~3.5, is aged, and filtering, obtains filtrate and iron aluminum slag;
    (3) regulation system pH is 4.5~5.0 again, is aged, and filtering, is purified liquid and aluminium slag;
    (4) regulation system pH in step (2) is added using the aluminium slag that step (3) obtains as pH adjusting agent, so as to iron removaling, obtains iron Aluminium slag;
    (5) circulation above-mentioned steps realize the lasting iron removaling of leachate, aluminium.
CN201710872175.5A 2017-09-25 2017-09-25 Method for removing iron and aluminum from leachate generated during recovery of valuable metals in waste lithium ion batteries Active CN107871912B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201710872175.5A CN107871912B (en) 2017-09-25 2017-09-25 Method for removing iron and aluminum from leachate generated during recovery of valuable metals in waste lithium ion batteries

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201710872175.5A CN107871912B (en) 2017-09-25 2017-09-25 Method for removing iron and aluminum from leachate generated during recovery of valuable metals in waste lithium ion batteries

Publications (2)

Publication Number Publication Date
CN107871912A true CN107871912A (en) 2018-04-03
CN107871912B CN107871912B (en) 2020-05-12

Family

ID=61752475

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201710872175.5A Active CN107871912B (en) 2017-09-25 2017-09-25 Method for removing iron and aluminum from leachate generated during recovery of valuable metals in waste lithium ion batteries

Country Status (1)

Country Link
CN (1) CN107871912B (en)

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109439907A (en) * 2018-11-22 2019-03-08 湖南邦普循环科技有限公司 A method of iron aluminium is removed from the pickle liquor during recycling used Li ion cell
CN109574091A (en) * 2018-11-23 2019-04-05 湖南中伟新能源科技有限公司 The method of ternary precursor sulfate liquor purification iron
CN111020194A (en) * 2019-11-16 2020-04-17 银隆新能源股份有限公司 Method for synthesizing titanium-aluminum alloy from waste lithium titanate anode and cathode powder
CN111471864A (en) * 2020-04-24 2020-07-31 广东邦普循环科技有限公司 Method for recovering copper, aluminum and iron from waste lithium ion battery leachate
CN112126783A (en) * 2020-08-25 2020-12-25 湖南邦普循环科技有限公司 Recycling method of iron and aluminum in nickel-cobalt-manganese solution
CN114853078A (en) * 2022-05-12 2022-08-05 中国科学院过程工程研究所 Method for removing iron and aluminum from iron and aluminum-containing solution and recycling aluminum
CN115180661A (en) * 2022-07-22 2022-10-14 余姚市鑫和电池材料有限公司 Method for recovering nickel-cobalt-copper mixed sulfate from iron-aluminum waste residues
US20230231216A1 (en) * 2020-08-24 2023-07-20 Green Li-Ion Pte. Ltd. Process For Removing Impurities In The Recycling Of Lithium-Ion Batteries

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1718784A (en) * 2005-07-07 2006-01-11 孙涛 Method of recovery copper, nickel and noble metal in waste water and slag by combined technology of wet method and fire method
CN102057064A (en) * 2008-06-06 2011-05-11 悉尼大学 Multi-stage leaching process
CN104310467A (en) * 2014-10-15 2015-01-28 陆世强 Comprehensive utilization method of high titanium slag
CN106558739A (en) * 2016-11-28 2017-04-05 安徽得盈再生资源回收有限公司 Separating technology is reclaimed based on lithium ion battery environment-friendly high-efficiency in waste mobile phone
CN106636651A (en) * 2016-12-16 2017-05-10 江苏理工学院 Method for separating chromium from iron and aluminum in sulfuric acid system solution containing chromium, iron and aluminum

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1718784A (en) * 2005-07-07 2006-01-11 孙涛 Method of recovery copper, nickel and noble metal in waste water and slag by combined technology of wet method and fire method
CN102057064A (en) * 2008-06-06 2011-05-11 悉尼大学 Multi-stage leaching process
CN104310467A (en) * 2014-10-15 2015-01-28 陆世强 Comprehensive utilization method of high titanium slag
CN106558739A (en) * 2016-11-28 2017-04-05 安徽得盈再生资源回收有限公司 Separating technology is reclaimed based on lithium ion battery environment-friendly high-efficiency in waste mobile phone
CN106636651A (en) * 2016-12-16 2017-05-10 江苏理工学院 Method for separating chromium from iron and aluminum in sulfuric acid system solution containing chromium, iron and aluminum

Cited By (17)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109439907A (en) * 2018-11-22 2019-03-08 湖南邦普循环科技有限公司 A method of iron aluminium is removed from the pickle liquor during recycling used Li ion cell
CN109574091A (en) * 2018-11-23 2019-04-05 湖南中伟新能源科技有限公司 The method of ternary precursor sulfate liquor purification iron
CN111020194A (en) * 2019-11-16 2020-04-17 银隆新能源股份有限公司 Method for synthesizing titanium-aluminum alloy from waste lithium titanate anode and cathode powder
CN111020194B (en) * 2019-11-16 2023-10-13 银隆新能源股份有限公司 Method for synthesizing titanium-aluminum alloy from waste lithium titanate anode and cathode powder
CN111471864A (en) * 2020-04-24 2020-07-31 广东邦普循环科技有限公司 Method for recovering copper, aluminum and iron from waste lithium ion battery leachate
CN111471864B (en) * 2020-04-24 2022-02-18 广东邦普循环科技有限公司 Method for recovering copper, aluminum and iron from waste lithium ion battery leachate
US11876196B2 (en) * 2020-08-24 2024-01-16 Green Li-Ion Pte. Ltd. Process for removing impurities in the recycling of lithium-ion batteries
US20230231216A1 (en) * 2020-08-24 2023-07-20 Green Li-Ion Pte. Ltd. Process For Removing Impurities In The Recycling Of Lithium-Ion Batteries
WO2022042228A1 (en) * 2020-08-25 2022-03-03 湖南邦普循环科技有限公司 Method for recycling iron and aluminum in nickel-cobalt-manganese solution
EP4194572A4 (en) * 2020-08-25 2024-01-24 Hunan Brunp Recycling Tech Co Ltd Method for recycling iron and aluminum in nickel-cobalt-manganese solution
CN112126783B (en) * 2020-08-25 2022-06-14 湖南邦普循环科技有限公司 Recycling method of iron and aluminum in nickel-cobalt-manganese solution
US11760655B2 (en) 2020-08-25 2023-09-19 Hunan Brunp Recycling Technology Co., Ltd. Method for recycling iron and aluminum in nickel-cobalt-manganese solution
CN112126783A (en) * 2020-08-25 2020-12-25 湖南邦普循环科技有限公司 Recycling method of iron and aluminum in nickel-cobalt-manganese solution
CN114853078A (en) * 2022-05-12 2022-08-05 中国科学院过程工程研究所 Method for removing iron and aluminum from iron and aluminum-containing solution and recycling aluminum
CN114853078B (en) * 2022-05-12 2023-09-29 中国科学院过程工程研究所 Method for removing iron and aluminum from iron-aluminum-containing solution and recycling aluminum
CN115180661A (en) * 2022-07-22 2022-10-14 余姚市鑫和电池材料有限公司 Method for recovering nickel-cobalt-copper mixed sulfate from iron-aluminum waste residues
CN115180661B (en) * 2022-07-22 2024-02-13 余姚市鑫和电池材料有限公司 Method for recovering nickel-cobalt-copper mixed sulfate from iron-aluminum waste residues

Also Published As

Publication number Publication date
CN107871912B (en) 2020-05-12

Similar Documents

Publication Publication Date Title
CN107871912A (en) In a kind of used Li ion cell from recovery in leachate caused by valuable metal iron removaling aluminium method
CN107267759B (en) A kind of comprehensive recovering process of anode material for lithium-ion batteries
CN111187913B (en) Method for selectively recovering lithium and copper in waste lithium iron phosphate batteries
CN112158894A (en) Method for recovering anode material of waste lithium battery
EP3269832B1 (en) Method of recycling and processing waste battery
CN107017443A (en) A kind of method of the comprehensively recovering valuable metal from waste and old lithium ion battery
CN109022793B (en) Method for selectively leaching lithium from waste powder of cathode material containing at least one of cobalt, nickel and manganese
CN109346741B (en) Method for recycling waste positive electrode material of lithium battery
CN108486376A (en) A method of leaching metal in waste lithium ion cell anode material
CN101555030A (en) Method for recovering and recycling waste lithium ion battery cathode material
CN108470952B (en) Method for selectively recovering lithium in waste lithium iron phosphate cathode material by low-temperature liquid phase method
CN109055757B (en) Method for recovering manganese dioxide and lead in anode slag of electrolytic manganese or electrolytic zinc
CN108390120A (en) A kind of method of lithium in selective recovery waste lithium ion cell anode material
CN109439907A (en) A method of iron aluminium is removed from the pickle liquor during recycling used Li ion cell
CN108504865A (en) A method of strengthening waste lithium ion cell anode active material and leaches
CN111961839A (en) Method for synchronously leaching valuable metals from positive and negative electrode active materials of waste lithium ion batteries and removing impurities
CN108808147A (en) A kind of method that manganese is recycled in waste and old lithium ion battery
US20240088468A1 (en) Method for extracting lithium from waste lithium battery
CN111304441A (en) Method for removing impurities from waste battery leachate
CN107046154A (en) A kind of method that useless ternary lithium battery strengthens reducing leaching
CN115369248A (en) Wet recovery method for waste ternary lithium battery
CN109609761A (en) A kind of recovery method of waste and old lithium ion battery
CN109599602B (en) Method for resource utilization of waste positive electrode material of lithium battery
CN111041218A (en) Comprehensive extraction method for metals in waste lithium ion batteries
CN108306071A (en) A kind of waste lithium ion cell anode material recovery technique

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant