EP1656463A1 - Process for the high yield recovery of lead from spent lead-acid batteries with reduced associated production of slag and gaseous emissions - Google Patents

Process for the high yield recovery of lead from spent lead-acid batteries with reduced associated production of slag and gaseous emissions

Info

Publication number
EP1656463A1
EP1656463A1 EP20040743947 EP04743947A EP1656463A1 EP 1656463 A1 EP1656463 A1 EP 1656463A1 EP 20040743947 EP20040743947 EP 20040743947 EP 04743947 A EP04743947 A EP 04743947A EP 1656463 A1 EP1656463 A1 EP 1656463A1
Authority
EP
European Patent Office
Prior art keywords
lead
desulphating
carbonate
sulphate
process according
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.)
Withdrawn
Application number
EP20040743947
Other languages
German (de)
English (en)
French (fr)
Inventor
Antonio Sommariva
Giovanni Modica
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.)
Kandy SA
Original Assignee
Kandy SA
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 Kandy SA filed Critical Kandy SA
Publication of EP1656463A1 publication Critical patent/EP1656463A1/en
Withdrawn legal-status Critical Current

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
    • C22B13/00Obtaining lead
    • C22B13/04Obtaining lead by wet processes
    • C22B13/045Recovery from waste materials
    • 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
    • C22B7/008Wet processes by an alkaline or ammoniacal leaching
    • HELECTRICITY
    • H01ELECTRIC ELEMENTS
    • H01MPROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
    • H01M10/00Secondary cells; Manufacture thereof
    • H01M10/06Lead-acid 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
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E60/00Enabling technologies; Technologies with a potential or indirect contribution to GHG emissions mitigation
    • Y02E60/10Energy storage using batteries
    • 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

Definitions

  • Secondary lead is recovered from the electrode slime recovered from end-of-life lead-acid batteries using pyrometallurgical processes operating at high temperature and in the presence of iron to reduce the furnace operating temperature to approximately 1100 °C. These processes have a potentially high environmental impact, both as regards gaseous emissions and the large associated output of slag, which is classified as a hazardous material requiring disposal in special dumps . As far as gaseous emissions are concerned, the procedures adopted by lead recyclers make it possible to reduce and control these, although at a high cost, while the problem associated with the large output of associated slag persists. Conversion of the lead sulphate present in the electrode slime into carbonate through a "carbonatation" process is a technique which is well known among secondary lead producers.
  • a method for virtually wholly desulphating the slime by reaction with an aqueous solution containing ammonium carbonate or alkali (sodium, ammonium, potassium) carbonates in addition to other substances which have the power to dissolve the insoluble lanarkite has now been found and is the subject of this invention.
  • the treatment temperature may be between ambient temperature and the boiling point of the solution, preferably between 60 and 100°C.
  • the ratio by weight between the water in the solution and the slime lies between 0.6 and 5, preferably between 0.7 and 1.2.
  • the sodium carbonate present in the solution is the stoichiometric quantity appropriate for the sulphate levels present in the electrode slimes with an excess of between 0.01% and 10%.
  • the sodium hydroxide is added in such a way that the carbonate/hydroxide ratio by weight lies between 6.4 and 5.5 so as to accelerate the desulphating reactions without plumbites being present in solution.
  • the water/slime ratio may also be chosen in relation to the subsequent treatment separating the desulphated slime from the solution (normally by sedimentation, filtration and/or centrifuging) . This does not apply any constraint on desulphating.
  • the water/slime/quantity of sodium carbonate ratio also depends on the subsequent treatment which it is intended to use to separate the sodium sulphate which forms as a result of the desulphating reaction described.
  • the efficiency of lead recovery with reference to the weight of the non-desulphated dry slime was 71-72% in comparison with the maximum of 66% which can be obtained by known methods, while the maximum theoretical yield is 72-73%, depending on the composition of the slime.
  • the amount of slag formed essentially depends on substances present in the slime
  • lanarkite substances having the ability to dissolve lanarkite, such as : amines, amides, MEA (monoethanolamine) , DEA (diethanolamine) , TEA (triethanolamine) , tartaric acid and tartrates, citric acid and citrates, glycolic acid, gluconates, alkali and ammonium acetates, alkali and ammonium nitrates, ammonia, EDTA and other complexing agents, and with ammonium carbonate alone.
  • amines, amides MEA (monoethanolamine) , DEA (diethanolamine) , TEA (triethanolamine) , tartaric acid and tartrates, citric acid and citrates, glycolic acid, gluconates, alkali and ammonium acetates, alkali and ammonium nitrates, ammonia, EDTA and other complexing agents, and with ammonium carbonate alone.
  • 100 kg of electrode slimes were charged into a cylindrical mill reactor and suspended in a solution comprising 100 kg of water, 24 kg of 99% pure sodium carbonate and 3 kg of 99.5% pure sodium hydroxide.
  • the suspension was heated to a temperature of 70 °C and held at that temperature for 90 minutes.
  • the solid part of the suspension was subjected to a strong compression and shearing force through rotating brushes brushing against the inside walls of the reactor.
  • the solid part of the suspension was separated out from the suspension and on analysis was found to have a total sulphur content of less than 0.06%.
  • 100 kg of electrode slime was charged into a cylindrical reactor with a paddle stirrer and suspended in a solution comprising 100 kg of water, 24 kg of 99% pure sodium carbonate and 8 kg of 99.5% pure sodium hydroxide.
  • the suspension was heated to a temperature of 70 °C and held at that temperature for 90 minutes. Again in this case the grinding action was applied throughout the duration of the test.
  • the solid part of the suspension was separated out from the and on analysis was found to have a total sulphur content of less than 0.04%.
  • 100 kg of electrode slime was charged into the same cylindrical reactor as in example no. 1 and suspended in a solution comprising 100 kg of water, 24 kg of 99% pure sodium carbonate and 6 kg of monoethanolamine.
  • the suspension was heated to a temperature of 70 °C and held at that temperature for 90 minutes. Again in this case the grinding action was maintained throughout the duration of the test.
  • the solid part of the suspension was separated out and on analysis was found to have a total sulphur content of less than 0.07%.

Landscapes

  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Manufacturing & Machinery (AREA)
  • Mechanical Engineering (AREA)
  • Organic Chemistry (AREA)
  • Metallurgy (AREA)
  • Materials Engineering (AREA)
  • Environmental & Geological Engineering (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Geology (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Electrochemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)
  • Processing Of Solid Wastes (AREA)
  • Secondary Cells (AREA)
EP20040743947 2003-07-18 2004-07-12 Process for the high yield recovery of lead from spent lead-acid batteries with reduced associated production of slag and gaseous emissions Withdrawn EP1656463A1 (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
CH12572003 2003-07-18
PCT/IB2004/002285 WO2005007904A1 (en) 2003-07-18 2004-07-12 Process for the high yield recovery of lead from spent lead-acid batteries with reduced associated production of slag and gaseous emissions

Publications (1)

Publication Number Publication Date
EP1656463A1 true EP1656463A1 (en) 2006-05-17

Family

ID=34069956

Family Applications (1)

Application Number Title Priority Date Filing Date
EP20040743947 Withdrawn EP1656463A1 (en) 2003-07-18 2004-07-12 Process for the high yield recovery of lead from spent lead-acid batteries with reduced associated production of slag and gaseous emissions

Country Status (4)

Country Link
US (1) US20070028720A1 (zh)
EP (1) EP1656463A1 (zh)
CN (1) CN1846005A (zh)
WO (1) WO2005007904A1 (zh)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2008087684A1 (en) 2007-01-17 2008-07-24 Millbrook Lead Recycling Technologies Limited Recovery of lead in form of high purity lead carbonates from spent lead batteries incl. electrode paste
US9533273B2 (en) 2014-06-20 2017-01-03 Johnson Controls Technology Company Systems and methods for isolating a particulate product when recycling lead from spent lead-acid batteries
US9670565B2 (en) 2014-06-20 2017-06-06 Johnson Controls Technology Company Systems and methods for the hydrometallurgical recovery of lead from spent lead-acid batteries and the preparation of lead oxide for use in new lead-acid batteries
US10062933B2 (en) 2015-12-14 2018-08-28 Johnson Controls Technology Company Hydrometallurgical electrowinning of lead from spent lead-acid batteries

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* Cited by examiner, † Cited by third party
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GB0622249D0 (en) * 2006-11-08 2006-12-20 Univ Cambridge Tech Lead recycling
CN100400683C (zh) * 2006-12-30 2008-07-09 同济大学 一种用含铅锌废渣或氧化铅锌矿生产金属铅和锌的方法
CN100521364C (zh) * 2007-11-20 2009-07-29 浙江工业大学 一种废铅酸蓄电池破碎分选方法及专用塔式重力分选器
ITMI20072257A1 (it) * 2007-11-30 2009-06-01 Engitec Technologies S P A Processo per produrre piombo metallico a partire da pastello desolforato
PL216507B1 (pl) * 2009-11-23 2014-04-30 Inst Metali Nieżelaznych Sposób odsiarczania pasty akumulatorowej
CN102102154A (zh) * 2010-12-22 2011-06-22 中南大学 一种锡的低温熔盐清洁冶金方法
CN102689921B (zh) * 2011-03-24 2017-08-08 杨春晓 用于铅酸蓄电池回收和制造的Pb氧化物纳米粉体的制法
CN103947017B (zh) * 2011-06-03 2017-11-17 巴斯福股份公司 用于混合能量存储装置中的碳‑铅共混物
CN102275982A (zh) * 2011-06-07 2011-12-14 沈阳化工大学 一种溶解硫酸铅的混合溶剂
CN105981212B (zh) 2013-11-19 2018-08-07 艾库伊金属有限公司 用于铅酸蓄电池的非冶炼回收的设备和方法
CN103773972B (zh) * 2014-01-10 2016-06-15 张超 一种含铅原料的处理方法
LT3294929T (lt) 2015-05-13 2021-11-10 Aqua Metals Inc. Uždaro kontūro sistemos ir švino rūgštinių akumuliatorių utilizavimo būdai
US10689769B2 (en) 2015-05-13 2020-06-23 Aqua Metals Inc. Electrodeposited lead composition, methods of production, and uses
SI3294916T1 (sl) 2015-05-13 2021-04-30 Aqua Metals Inc. Sistemi in postopki za pridobivanje svinca iz svinčevo-kislinskih akumulatorjev
US10316420B2 (en) 2015-12-02 2019-06-11 Aqua Metals Inc. Systems and methods for continuous alkaline lead acid battery recycling
CN106637298A (zh) * 2016-11-16 2017-05-10 昆明冶金研究院 一种含铅多金属物料电积沉铅的方法
IT201800005267A1 (it) * 2018-05-11 2019-11-11 Procedimento per la desolforazione di materiali e/o residui contenenti solfato di piombo mediante un composto amminico
WO2020076778A1 (en) 2018-10-08 2020-04-16 Marsulex Environmental Technologies Corporation Systems and methods for producing potassium sulfate
CA3143384A1 (en) * 2020-07-22 2022-01-22 Ecometales Limited Procedure for leaching valuable elements from metallurgical residues

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US3689253A (en) * 1970-08-27 1972-09-05 Minerals Technology Corp Reclaiming lead from storage batteries
US4018567A (en) * 1973-05-14 1977-04-19 James P. La Point, Jr. Apparatus for separating the constituents of lead-acid storage batteries
US3883348A (en) * 1973-09-06 1975-05-13 R S R Corp Process for the removal of sulfur from battery wrecker material using ammonium carbonate solution
US4269810A (en) * 1978-10-10 1981-05-26 Nl Industries, Inc. Method for desulfation of battery mud
GB2073725A (en) * 1980-04-11 1981-10-21 Ass Lead Mfg Ltd A Method of Recovering Lead Values from Scrap Batteries
US5690718A (en) * 1995-10-06 1997-11-25 Global Aener/Cology Corp. Battery paste recycling process
ITMI20041456A1 (it) * 2004-07-20 2004-10-20 Engitec S R L Processo di desolforazione di pastello e griglie degli accumulatori al piombo+

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Cited By (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2008087684A1 (en) 2007-01-17 2008-07-24 Millbrook Lead Recycling Technologies Limited Recovery of lead in form of high purity lead carbonates from spent lead batteries incl. electrode paste
US10777858B2 (en) 2014-06-20 2020-09-15 Cps Technology Holdings Llc Methods for purifying and recycling lead from spent lead-acid batteries
US9555386B2 (en) 2014-06-20 2017-01-31 Johnson Controls Technology Company Systems and methods for closed-loop recycling of a liquid component of a leaching mixture when recycling lead from spent lead-acid batteries
US9670565B2 (en) 2014-06-20 2017-06-06 Johnson Controls Technology Company Systems and methods for the hydrometallurgical recovery of lead from spent lead-acid batteries and the preparation of lead oxide for use in new lead-acid batteries
US9751067B2 (en) 2014-06-20 2017-09-05 Johnson Controls Technology Company Methods for purifying and recycling lead from spent lead-acid batteries
US9757702B2 (en) 2014-06-20 2017-09-12 Johnson Controls Technology Company Systems and methods for purifying and recycling lead from spent lead-acid batteries
US10122052B2 (en) 2014-06-20 2018-11-06 Johnson Controls Technology Company Systems and methods for purifying and recycling lead from spent lead-acid batteries
US10403940B2 (en) 2014-06-20 2019-09-03 Cps Technology Holdings Llc Systems and methods for closed-loop recycling of a liquid component of a leaching mixture when recycling lead from spent lead-acid batteries
US9533273B2 (en) 2014-06-20 2017-01-03 Johnson Controls Technology Company Systems and methods for isolating a particulate product when recycling lead from spent lead-acid batteries
US11005129B2 (en) 2014-06-20 2021-05-11 Clarios Germany Gmbh & Co. Kgaa Systems and methods for closed-loop recycling of a liquid component of a leaching mixture when recycling lead from spent lead-acid batteries
US11791505B2 (en) 2014-06-20 2023-10-17 Cps Technology Holdings Llc Methods for purifying and recycling lead from spent lead-acid batteries
US11923518B2 (en) 2014-06-20 2024-03-05 Clarios Advanced Germany Gmbh & Co. KG Systems and methods for closed-loop recycling of a liquid component of a leaching mixture when recycling lead from spent lead-acid batteries
US10062933B2 (en) 2015-12-14 2018-08-28 Johnson Controls Technology Company Hydrometallurgical electrowinning of lead from spent lead-acid batteries

Also Published As

Publication number Publication date
US20070028720A1 (en) 2007-02-08
CN1846005A (zh) 2006-10-11
WO2005007904A1 (en) 2005-01-27

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