CN107666022A - Lithium, the recovery method of nickel cobalt manganese in a kind of discarded tertiary cathode material - Google Patents
Lithium, the recovery method of nickel cobalt manganese in a kind of discarded tertiary cathode material Download PDFInfo
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- CN107666022A CN107666022A CN201710875966.3A CN201710875966A CN107666022A CN 107666022 A CN107666022 A CN 107666022A CN 201710875966 A CN201710875966 A CN 201710875966A CN 107666022 A CN107666022 A CN 107666022A
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- 238000000034 method Methods 0.000 title claims abstract description 38
- WHXSMMKQMYFTQS-UHFFFAOYSA-N Lithium Chemical compound [Li] WHXSMMKQMYFTQS-UHFFFAOYSA-N 0.000 title claims abstract description 36
- 229910052744 lithium Inorganic materials 0.000 title claims abstract description 36
- KFDQGLPGKXUTMZ-UHFFFAOYSA-N [Mn].[Co].[Ni] Chemical compound [Mn].[Co].[Ni] KFDQGLPGKXUTMZ-UHFFFAOYSA-N 0.000 title claims abstract description 29
- 238000011084 recovery Methods 0.000 title claims abstract description 20
- 239000010406 cathode material Substances 0.000 title claims description 35
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 claims abstract description 100
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims abstract description 62
- 238000006243 chemical reaction Methods 0.000 claims abstract description 62
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims abstract description 60
- 238000002386 leaching Methods 0.000 claims abstract description 55
- 229910017052 cobalt Inorganic materials 0.000 claims abstract description 50
- 239000010941 cobalt Substances 0.000 claims abstract description 50
- GUTLYIVDDKVIGB-UHFFFAOYSA-N cobalt atom Chemical compound [Co] GUTLYIVDDKVIGB-UHFFFAOYSA-N 0.000 claims abstract description 50
- 229910052759 nickel Inorganic materials 0.000 claims abstract description 49
- PWHULOQIROXLJO-UHFFFAOYSA-N Manganese Chemical compound [Mn] PWHULOQIROXLJO-UHFFFAOYSA-N 0.000 claims abstract description 48
- 239000002243 precursor Substances 0.000 claims abstract description 45
- 229910052748 manganese Inorganic materials 0.000 claims abstract description 38
- 239000011572 manganese Substances 0.000 claims abstract description 38
- 239000000706 filtrate Substances 0.000 claims abstract description 31
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 27
- 239000002002 slurry Substances 0.000 claims abstract description 21
- 239000003638 chemical reducing agent Substances 0.000 claims abstract description 16
- 239000000047 product Substances 0.000 claims abstract description 15
- 239000002994 raw material Substances 0.000 claims abstract description 11
- 239000012298 atmosphere Substances 0.000 claims abstract description 10
- 238000001556 precipitation Methods 0.000 claims abstract description 9
- 230000001681 protective effect Effects 0.000 claims abstract description 9
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 8
- 229910052799 carbon Inorganic materials 0.000 claims abstract description 8
- XGZVUEUWXADBQD-UHFFFAOYSA-L lithium carbonate Chemical compound [Li+].[Li+].[O-]C([O-])=O XGZVUEUWXADBQD-UHFFFAOYSA-L 0.000 claims abstract description 7
- 229910052808 lithium carbonate Inorganic materials 0.000 claims abstract description 7
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 claims abstract description 5
- 238000004090 dissolution Methods 0.000 claims description 29
- 238000003756 stirring Methods 0.000 claims description 17
- 239000000571 coke Substances 0.000 claims description 16
- 239000007787 solid Substances 0.000 claims description 16
- 238000002156 mixing Methods 0.000 claims description 12
- 239000000203 mixture Substances 0.000 claims description 10
- KTVIXTQDYHMGHF-UHFFFAOYSA-L cobalt(2+) sulfate Chemical compound [Co+2].[O-]S([O-])(=O)=O KTVIXTQDYHMGHF-UHFFFAOYSA-L 0.000 claims description 7
- 239000012153 distilled water Substances 0.000 claims description 7
- 238000001914 filtration Methods 0.000 claims description 7
- 229940099596 manganese sulfate Drugs 0.000 claims description 7
- 239000011702 manganese sulphate Substances 0.000 claims description 7
- 235000007079 manganese sulphate Nutrition 0.000 claims description 7
- SQQMAOCOWKFBNP-UHFFFAOYSA-L manganese(II) sulfate Chemical compound [Mn+2].[O-]S([O-])(=O)=O SQQMAOCOWKFBNP-UHFFFAOYSA-L 0.000 claims description 7
- LGQLOGILCSXPEA-UHFFFAOYSA-L nickel sulfate Chemical compound [Ni+2].[O-]S([O-])(=O)=O LGQLOGILCSXPEA-UHFFFAOYSA-L 0.000 claims description 7
- 229910000363 nickel(II) sulfate Inorganic materials 0.000 claims description 7
- 230000035484 reaction time Effects 0.000 claims description 7
- 238000000605 extraction Methods 0.000 claims description 3
- WPBNNNQJVZRUHP-UHFFFAOYSA-L manganese(2+);methyl n-[[2-(methoxycarbonylcarbamothioylamino)phenyl]carbamothioyl]carbamate;n-[2-(sulfidocarbothioylamino)ethyl]carbamodithioate Chemical compound [Mn+2].[S-]C(=S)NCCNC([S-])=S.COC(=O)NC(=S)NC1=CC=CC=C1NC(=S)NC(=O)OC WPBNNNQJVZRUHP-UHFFFAOYSA-L 0.000 claims description 2
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 claims 6
- 229910021529 ammonia Inorganic materials 0.000 claims 3
- HIRWGWMTAVZIPF-UHFFFAOYSA-N nickel;sulfuric acid Chemical compound [Ni].OS(O)(=O)=O HIRWGWMTAVZIPF-UHFFFAOYSA-N 0.000 claims 1
- 239000002699 waste material Substances 0.000 abstract description 38
- 239000007774 positive electrode material Substances 0.000 abstract description 17
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 abstract description 9
- 235000011114 ammonium hydroxide Nutrition 0.000 abstract description 9
- 239000000463 material Substances 0.000 abstract description 5
- 238000000926 separation method Methods 0.000 abstract description 5
- NLXLAEXVIDQMFP-UHFFFAOYSA-N Ammonium chloride Substances [NH4+].[Cl-] NLXLAEXVIDQMFP-UHFFFAOYSA-N 0.000 abstract description 3
- 230000008929 regeneration Effects 0.000 abstract 1
- 238000011069 regeneration method Methods 0.000 abstract 1
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 12
- 239000002245 particle Substances 0.000 description 11
- 229910021645 metal ion Inorganic materials 0.000 description 10
- 238000005070 sampling Methods 0.000 description 10
- 238000001878 scanning electron micrograph Methods 0.000 description 10
- HBBGRARXTFLTSG-UHFFFAOYSA-N Lithium ion Chemical compound [Li+] HBBGRARXTFLTSG-UHFFFAOYSA-N 0.000 description 7
- 229910001416 lithium ion Inorganic materials 0.000 description 7
- 229910000361 cobalt sulfate Inorganic materials 0.000 description 6
- 229940044175 cobalt sulfate Drugs 0.000 description 6
- 229940053662 nickel sulfate Drugs 0.000 description 6
- 229910052757 nitrogen Inorganic materials 0.000 description 6
- 239000012300 argon atmosphere Substances 0.000 description 5
- 238000000498 ball milling Methods 0.000 description 5
- 238000001514 detection method Methods 0.000 description 5
- 230000002572 peristaltic effect Effects 0.000 description 5
- 238000002360 preparation method Methods 0.000 description 5
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 description 4
- 239000002253 acid Substances 0.000 description 4
- 238000004064 recycling Methods 0.000 description 4
- 230000007613 environmental effect Effects 0.000 description 3
- 239000004615 ingredient Substances 0.000 description 3
- 229910052751 metal Inorganic materials 0.000 description 3
- XKRFYHLGVUSROY-UHFFFAOYSA-N Argon Chemical compound [Ar] XKRFYHLGVUSROY-UHFFFAOYSA-N 0.000 description 2
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 2
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 description 2
- MZZUATUOLXMCEY-UHFFFAOYSA-N cobalt manganese Chemical compound [Mn].[Co] MZZUATUOLXMCEY-UHFFFAOYSA-N 0.000 description 2
- RSNHXDVSISOZOB-UHFFFAOYSA-N lithium nickel Chemical compound [Li].[Ni] RSNHXDVSISOZOB-UHFFFAOYSA-N 0.000 description 2
- 239000002184 metal Substances 0.000 description 2
- 238000000746 purification Methods 0.000 description 2
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 1
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 description 1
- 229910013716 LiNi Inorganic materials 0.000 description 1
- 229910013100 LiNix Inorganic materials 0.000 description 1
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 description 1
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 description 1
- SOXUFMZTHZXOGC-UHFFFAOYSA-N [Li].[Mn].[Co].[Ni] Chemical compound [Li].[Mn].[Co].[Ni] SOXUFMZTHZXOGC-UHFFFAOYSA-N 0.000 description 1
- 239000011149 active material Substances 0.000 description 1
- 229910052782 aluminium Inorganic materials 0.000 description 1
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 1
- 239000010405 anode material Substances 0.000 description 1
- 229910052786 argon Inorganic materials 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 238000001354 calcination Methods 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- 229910052791 calcium Inorganic materials 0.000 description 1
- 238000009388 chemical precipitation Methods 0.000 description 1
- 229910052802 copper Inorganic materials 0.000 description 1
- 239000010949 copper Substances 0.000 description 1
- 230000001186 cumulative effect Effects 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 238000009854 hydrometallurgy Methods 0.000 description 1
- 238000009776 industrial production Methods 0.000 description 1
- 239000011261 inert gas Substances 0.000 description 1
- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
- 150000002500 ions Chemical class 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- PQXKHYXIUOZZFA-UHFFFAOYSA-M lithium fluoride Chemical compound [Li+].[F-] PQXKHYXIUOZZFA-UHFFFAOYSA-M 0.000 description 1
- 239000011777 magnesium Substances 0.000 description 1
- 229910052749 magnesium Inorganic materials 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 239000011707 mineral Substances 0.000 description 1
- 235000010755 mineral Nutrition 0.000 description 1
- 229910000029 sodium carbonate Inorganic materials 0.000 description 1
- 239000002910 solid waste Substances 0.000 description 1
- 238000000638 solvent extraction Methods 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
- 239000011701 zinc Substances 0.000 description 1
- 229910052725 zinc Inorganic materials 0.000 description 1
Classifications
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- H—ELECTRICITY
- H01—ELECTRIC ELEMENTS
- H01M—PROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
- H01M10/00—Secondary cells; Manufacture thereof
- H01M10/54—Reclaiming serviceable parts of waste accumulators
-
- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B23/00—Obtaining nickel or cobalt
-
- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B26/00—Obtaining alkali, alkaline earth metals or magnesium
- C22B26/10—Obtaining alkali metals
- C22B26/12—Obtaining lithium
-
- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B47/00—Obtaining manganese
-
- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B7/00—Working 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
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P10/00—Technologies related to metal processing
- Y02P10/20—Recycling
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/84—Recycling of batteries or fuel cells
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- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Manufacturing & Machinery (AREA)
- Materials Engineering (AREA)
- Organic Chemistry (AREA)
- Metallurgy (AREA)
- Mechanical Engineering (AREA)
- Life Sciences & Earth Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- General Life Sciences & Earth Sciences (AREA)
- Geology (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Electrochemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Manufacture And Refinement Of Metals (AREA)
Abstract
本发明公开了一种从废弃三元电池正极材料中锂、镍钴锰的回收方法,以废弃三元正极材料为原料,加入碳还原剂,经混合配料后在保护气氛下、500~700℃下进行焙烧还原,焙烧产物加入水中进行水溶反应,反应完毕后过滤得到碳酸锂滤液和滤渣一,滤渣一经硫酸浸出后过滤得到含镍钴锰滤液和滤渣二,添加硫酸盐调节含镍钴锰滤液中镍、钴、锰的比例,在保护气氛下与氢氧化钠溶液和氨水溶液进行沉淀反应,控制反应温度为50~70℃,反应pH值为10~11,沉淀反应后得到三元前驱体的浆料,过滤、洗涤、干燥得到三元前驱体。本发明相比现有技术,本发明碳酸锂分离条件简单,镍钴锰的浸出过程和再生三元材料前驱体过程成本低,回收率高。
The invention discloses a method for recovering lithium, nickel, cobalt and manganese from waste ternary battery positive electrode materials. The waste ternary positive electrode materials are used as raw materials, and a carbon reducing agent is added. Carry out roasting and reduction under low temperature, the roasted product is added into water for water-soluble reaction, after the reaction is completed, filter to obtain lithium carbonate filtrate and filter residue 1, filter residue 1 to obtain nickel-cobalt-manganese filtrate and filter residue 2 after sulfuric acid leaching, add sulfate to adjust nickel-cobalt-manganese filtrate The ratio of nickel, cobalt, and manganese in the medium is subjected to precipitation reaction with sodium hydroxide solution and ammonia solution under a protective atmosphere. The reaction temperature is controlled at 50~70°C, and the reaction pH value is 10~11. After the precipitation reaction, the ternary precursor is obtained The slurry is filtered, washed and dried to obtain a ternary precursor. Compared with the prior art, the present invention has simple lithium carbonate separation conditions, low cost in the leaching process of nickel, cobalt and manganese and regeneration of ternary material precursor, and high recovery rate.
Description
技术领域technical field
本发明属于固体废弃物回收领域,涉及一种回收废弃三元锂离子电池正极材料中锂、镍钴锰的方法。The invention belongs to the field of solid waste recovery, and relates to a method for recovering lithium, nickel, cobalt and manganese in the positive electrode material of a waste ternary lithium ion battery.
背景技术Background technique
锂离子电池以其高能量密度、循环寿命长、环境友好等优势受到了市场和消费者的青睐。目前,廉价并且安全的三元材料LiNixCoyMnzO2是市场上应用广泛的一种商业正极材料,主要应用于笔记本电脑、相机等便携式电子设备和电动汽车,新能源汽车从2009年推广至今,其数量爆发式增长,2016年我国新能源汽车生产量超过50.7万辆,而动力电池的使用年限一般是3年,因此今明两年将有大量锂离子电池报废,预计到2020年,锂离子电池报废量达到32.2Gwh,共计约50万吨电池材料。Lithium-ion batteries are favored by the market and consumers for their high energy density, long cycle life, and environmental friendliness. At present, the cheap and safe ternary material LiNi x Co y Mnz O 2 is a commercial cathode material widely used in the market, mainly used in portable electronic devices such as laptops and cameras and electric vehicles. Since its promotion, its number has grown explosively. In 2016, the production of new energy vehicles in China exceeded 507,000, and the service life of power batteries is generally 3 years. Therefore, a large number of lithium-ion batteries will be scrapped this year and next. It is expected that by 2020, The amount of scrapped lithium-ion batteries reached 32.2Gwh, a total of about 500,000 tons of battery materials.
我国每年报废的锂离子电池中以三元材料为正极的锂离子电池占比大约有40~50%,这些废旧三元电池正极材料中含有大量锂镍钴锰有价金属元素,且普遍高于自然界矿物中的金属含量,累计蕴藏量将分别达到5.0、3.0、2.0、1.5万吨。出于环保和经济持续发展的目的,回收废弃三元正极材料具有重要意义。Lithium-ion batteries with ternary materials as the positive electrode account for about 40-50% of the lithium-ion batteries scrapped every year in my country. The positive electrode materials of these waste ternary batteries contain a large amount of valuable metal elements such as lithium, nickel, cobalt, and manganese, which are generally higher than The cumulative reserves of metal content in natural minerals will reach 5.0, 3.0, 20, and 15,000 tons respectively. For the purpose of environmental protection and sustainable economic development, it is of great significance to recycle waste ternary cathode materials.
人们进行了大量废旧锂离子三元电池材料回收研究,目前主要以湿法冶金工艺为主,通常采用酸浸出锂镍钴锰;People have carried out a lot of research on the recycling of waste lithium-ion ternary battery materials. At present, the hydrometallurgical process is the main method, and acid leaching is usually used to extract lithium, nickel, cobalt and manganese;
中国专利公开号CN102956935A公开了一种废旧动力电池三元系正极材料处理方法,包括如下步骤:碱浸、酸浸出镍锂和锰钴、分离镍锂和锰钴、回收镍、回收锂、回收钴、回收锰;Chinese Patent Publication No. CN102956935A discloses a method for treating waste power battery ternary positive electrode materials, including the following steps: alkaline leaching, acid leaching to extract nickel lithium and manganese cobalt, separation of nickel lithium and manganese cobalt, recovery of nickel, recovery of lithium, recovery of cobalt , recovery of manganese;
中国专利公开号CN106505272A公开了一种锂电池正极材料废料的处理方法,包括如下步骤:A 焙烧、B 酸化浸出、C除铁铝、D 除铜锌、E 氟化沉锂、F除钙镁、G多级萃取、H 除油等;Chinese Patent Publication No. CN106505272A discloses a treatment method for lithium battery anode material waste, including the following steps: A roasting, B acid leaching, C removing iron and aluminum, D removing copper and zinc, E fluoride lithium precipitation, F removing calcium and magnesium, G multi-stage extraction, H oil removal, etc.;
上述专利通过添加双氧水为还原剂提高浸出效率,然后通过化学沉淀和溶剂萃取分离锂镍钴锰;工艺复杂,还原剂成本较高,并且后续的分离提纯工序繁多复杂,同时分离提纯后的溶液含有价金属浓度低,会产生大量废水。The above-mentioned patent improves the leaching efficiency by adding hydrogen peroxide as a reducing agent, and then separates lithium-nickel-cobalt-manganese through chemical precipitation and solvent extraction; the process is complex, the cost of the reducing agent is high, and the subsequent separation and purification procedures are numerous and complicated. At the same time, the solution after separation and purification contains The concentration of valence metals is low, and a large amount of waste water will be generated.
高效节能的回收废弃三元正极材料可以保护环境,实现二次资源循环利用、同时可以促进经济可持续发展,在环保意识日益提高和资源日趋紧张的当今社会,高效环保回收锂镍钴锰具有重要意义。High-efficiency and energy-saving recycling of waste ternary cathode materials can protect the environment, realize the recycling of secondary resources, and at the same time promote sustainable economic development. In today's society with increasing awareness of environmental protection and increasingly tight resources, efficient and environmentally friendly recycling of lithium, nickel, cobalt, and manganese is of great importance. significance.
发明内容Contents of the invention
针对上述问题,本发明的目的是提供一种高效分离回收废弃三元正极材料中锂、镍钴锰。In view of the above problems, the purpose of the present invention is to provide an efficient separation and recovery of lithium, nickel, cobalt and manganese in waste ternary positive electrode materials.
本发明的发明目的是通过以下技术方案实现:The purpose of the invention of the present invention is to be realized through the following technical solutions:
一种废弃三元正极材料中锂、镍钴锰的回收方法,以废弃三元正极材料为原料,加入碳还原剂,经混合配料后在保护气氛下、500~700℃下进行焙烧还原,焙烧产物加入到蒸馏水中进行水溶反应,反应完毕后过滤得到碳酸锂滤液和滤渣一,滤渣一经硫酸浸出后过滤得到含镍钴锰滤液和滤渣二,添加硫酸盐调节含镍钴锰滤液中镍、钴、锰的比例,然后在保护气氛下与氢氧化钠溶液和氨水溶液进行沉淀反应,控制反应温度为50~70℃,反应pH值为10~11,沉淀反应后得到三元前驱体的浆料,过滤、洗涤、干燥得到三元前驱体;A recovery method for lithium, nickel, cobalt and manganese in waste ternary positive electrode materials, using waste ternary positive electrode materials as raw materials, adding a carbon reducing agent, after mixing ingredients, performing roasting and reduction under a protective atmosphere at 500-700°C, roasting The product is added to distilled water for water-soluble reaction. After the reaction is completed, filter to obtain lithium carbonate filtrate and filter residue 1. After the filter residue is leached with sulfuric acid, filter to obtain nickel-cobalt-manganese filtrate and filter residue 2. Add sulfate to adjust nickel and cobalt in the nickel-cobalt-manganese filtrate. , manganese ratio, and then carry out precipitation reaction with sodium hydroxide solution and ammonia solution under protective atmosphere, control the reaction temperature at 50~70℃, and the reaction pH value is 10~11, and obtain the slurry of ternary precursor after precipitation reaction , filtered, washed, and dried to obtain a ternary precursor;
其中,氢氧化钠溶液可用碳酸钠溶液代替。Wherein, sodium hydroxide solution can be replaced by sodium carbonate solution.
优选地,本发明中涉及的保护气氛为氮气、氩气或者其他惰性气体。Preferably, the protective atmosphere involved in the present invention is nitrogen, argon or other inert gases.
优选地,本发明原料与还原剂混合配料过程使用球磨混合,进一步优选球磨时间为0.5~2h,转速100~300rpm。Preferably, the mixing process of the raw materials and the reducing agent in the present invention uses a ball mill for mixing, and more preferably the ball milling time is 0.5~2h, and the rotation speed is 100~300rpm.
优选地,所述碳还原剂加入量为废弃三元正极材料质量的5~30%;进一步优选所述碳还原剂为焦炭,所述焦炭碳含量大于或等于85%。Preferably, the added amount of the carbon reducing agent is 5-30% of the mass of the waste ternary cathode material; further preferably, the carbon reducing agent is coke, and the carbon content of the coke is greater than or equal to 85%.
优选地,所述水溶反应中所得焙烧产物与蒸馏水的液固比为10~100ml/g。Preferably, the liquid-solid ratio of the calcined product obtained in the water dissolution reaction to the distilled water is 10-100ml/g.
优选地,所述硫酸浸出过程中所得滤渣一与硫酸溶液的液固比为5~15ml/g。Preferably, the liquid-solid ratio of the filter residue obtained in the sulfuric acid leaching process to the sulfuric acid solution is 5-15ml/g.
优选地,添加硫酸盐调节含镍钴锰滤液中镍、钴、锰的比例为1~8:1~2:1~4;进一步优选为1:1:1、4:2:4、5:2:3、6:2:2、8:1:1中的一种。Preferably, the ratio of nickel, cobalt, and manganese in the filtrate containing nickel, cobalt, and manganese is 1 ~ 8: 1 ~ 2: 1 ~ 4 by adding sulfate; more preferably 1: 1: 1, 4: 2: 4, 5: One of 2:3, 6:2:2, 8:1:1.
本发明提供一种优化的一种废弃三元正极材料中锂、镍钴锰的回收方法,包括以下步骤:The invention provides an optimized recovery method for lithium, nickel, cobalt and manganese in waste ternary positive electrode materials, comprising the following steps:
S1.混料:以废弃三元正极材料为原料,加入碳还原剂,进行混合配料;S1. Mixing: use waste ternary cathode materials as raw materials, add carbon reducing agent, and mix ingredients;
S2.还原焙烧:将S1混合配料后的混合物在保护气氛、500~700℃下进行焙烧还原;S2. Reduction roasting: the mixture after mixing the ingredients of S1 is roasted and reduced in a protective atmosphere at 500~700°C;
S3.水溶:将步骤S2所得焙烧产物加入到蒸馏水中进行水溶反应,反应完毕后过滤得到碳酸锂滤液和滤渣一;S3. Water-soluble: the roasted product obtained in step S2 is added to distilled water for water-soluble reaction, and after the reaction is completed, filter to obtain lithium carbonate filtrate and filter residue one;
S4.硫酸浸出:将步骤S3得到的滤渣加入到配置好的硫酸溶液中进行浸出,浸出后过滤得到含镍钴锰滤液和滤渣二;S4. Sulfuric acid leaching: adding the filter residue obtained in step S3 to the configured sulfuric acid solution for leaching, and filtering after leaching to obtain the nickel-cobalt-manganese filtrate and filter residue II;
S5.制备前驱体:向步骤S4得到的含镍钴锰溶液中加入硫酸镍、硫酸钴、硫酸锰调节镍、钴、锰的比例,将镍钴锰溶液、氢氧化钠溶液和氨水溶液在保护气氛下并流加入反应釜中,控制反应温度为50~70℃,反应pH值为10~11,反应完毕后将含三元前驱体的浆料过滤、洗涤、干燥得到三元前驱体。S5. Preparing the precursor: adding nickel sulfate, cobalt sulfate, and manganese sulfate to the nickel-cobalt-manganese solution obtained in step S4 to adjust the ratio of nickel, cobalt, and manganese; Under the atmosphere, it is fed into the reactor in parallel flow, the reaction temperature is controlled at 50-70°C, and the reaction pH is 10-11. After the reaction is completed, the slurry containing the ternary precursor is filtered, washed, and dried to obtain the ternary precursor.
本发明的技术方案中利用焦炭作为还原剂对废弃三元正极材料进行还原焙烧,采用碳还原剂与活性物质LiNixCoyMnzO2进行还原焙烧得到焙烧产物Li2CO3、MnO、Ni、NiO、Co,然后将焙烧产物加入到蒸馏水中进行水溶反应,分离出碳酸锂溶液和含MnO、Ni、NiO、Co的滤渣一,然后进行硫酸浸出得到含镍钴锰滤液和滤渣二,调整离子比例之后加入氢氧化钠和氨水溶液进行沉淀反应得到三元前驱体浆料。In the technical solution of the present invention, coke is used as a reducing agent to reduce and roast waste ternary positive electrode materials, and carbon reducing agent and active material LiNix Co y Mnz O 2 are used for reduction and roasting to obtain roasted products Li 2 CO 3 , MnO, Ni , NiO, Co, and then the roasted product is added to distilled water for water-soluble reaction, and the lithium carbonate solution and the filter residue containing MnO, Ni, NiO, Co are separated. After the ion ratio, sodium hydroxide and ammonia solution are added to carry out precipitation reaction to obtain ternary precursor slurry.
优选地,步骤S1中焙烧还原时间0.5~3h。Preferably, the calcining reduction time in step S1 is 0.5~3h.
优选地,步骤S2中溶出温度为室温,溶出时间为2~5h。Preferably, the dissolution temperature in step S2 is room temperature, and the dissolution time is 2 to 5 hours.
优选在步骤S2水溶反应过程中进行搅拌,搅拌转速为100~500rpm。Preferably, stirring is carried out during the water-soluble reaction in step S2, and the stirring speed is 100-500 rpm.
优选地,步骤S3中硫酸溶液浓度为0.1~4mol/L,浸出时间为1~8h。Preferably, the concentration of the sulfuric acid solution in step S3 is 0.1-4mol/L, and the leaching time is 1-8h.
优选在步骤S3硫酸浸出过程进行搅拌,搅拌强度100~500 rpm。Stirring is preferably carried out during the sulfuric acid leaching process in step S3, and the stirring intensity is 100-500 rpm.
优选地,步骤S4中,镍钴锰溶液的浓度为0.5~5 mol/L,氢氧化钠溶液的浓度为0.5~4mol/L,氨水浓度为0.5~8 mol/L,反应时间为10~20h,通过控制氢氧化钠溶液流速控制反应pH值为10~11。Preferably, in step S4, the concentration of the nickel-cobalt-manganese solution is 0.5-5 mol/L, the concentration of the sodium hydroxide solution is 0.5-4 mol/L, the concentration of ammonia water is 0.5-8 mol/L, and the reaction time is 10-20 h , by controlling the flow rate of sodium hydroxide solution to control the reaction pH value of 10 ~ 11.
优选地,步骤S4干燥为在80~120℃下进行烘干。Preferably, step S4 is drying at 80-120°C.
与现有技术相比,本发明的有益效果:Compared with prior art, the beneficial effect of the present invention:
(1)本发明的技术方案中以废弃三元正极材料为对象,通过还原焙烧,然后水洗分离出锂,然后所得滤渣进行硫酸浸出得含镍钴锰滤液,根据不同的需求调节镍钴锰溶液中的镍、钴、锰比例,再进行沉淀反应可得不同的三元前驱体,本发明方法可实现废弃三元正极材料的高效无害利用,流程短、能耗低、过程清洁,易于开展工业化生产。(1) In the technical solution of the present invention, the discarded ternary positive electrode material is used as the object, and the lithium is separated by reduction and roasting, and then washed with water, and then the obtained filter residue is leached with sulfuric acid to obtain a nickel-cobalt-manganese filtrate, and the nickel-cobalt-manganese solution is adjusted according to different needs The ratio of nickel, cobalt, and manganese in the mixture, and then carry out precipitation reaction to obtain different ternary precursors. The method of the present invention can realize the efficient and harmless utilization of waste ternary cathode materials, with short process, low energy consumption, clean process, and easy to carry out Industrial production.
(2)本发明采用廉价的焦炭作为还原剂与废弃三元正极材料进行还原焙烧,浸出过程中不需要使用较昂贵的双氧水作还原剂,并且对还原产物分步采用水溶出和酸浸出,可以高效分离锂与镍钴锰元素,免去分离锂与镍钴锰的工序。(2) The present invention uses cheap coke as a reducing agent to carry out reduction roasting with waste ternary positive electrode materials, and does not need to use more expensive hydrogen peroxide as a reducing agent in the leaching process, and uses water dissolution and acid leaching for the reduction products step by step, which can be Efficiently separate lithium and nickel-cobalt-manganese elements, eliminating the need to separate lithium and nickel-cobalt-manganese elements.
(3)本发明混料、还原焙烧后,水溶出过程中,采用液固比为100ml/g,溶出温度为30℃,溶出时间为4h,搅拌强度为100rpm时,可以高效溶出锂,锂的溶出率可达到93.68%。硫酸浸出过程中,采用液固比为10ml/g,浸出温度为90℃,浸出时间为3h,搅拌强度为100rpm时,镍、钴、锰的浸出效率分别可以达到99.56%,99.14%,95.9%。(3) After the mixing and reduction roasting of the present invention, in the water dissolution process, when the liquid-solid ratio is 100ml/g, the dissolution temperature is 30°C, the dissolution time is 4h, and the stirring intensity is 100rpm, lithium and lithium can be dissolved efficiently. The dissolution rate can reach 93.68%. During the sulfuric acid leaching process, when the liquid-solid ratio is 10ml/g, the leaching temperature is 90°C, the leaching time is 3h, and the stirring intensity is 100rpm, the leaching efficiencies of nickel, cobalt, and manganese can reach 99.56%, 99.14%, and 95.9% respectively. .
(4)本发明制备的三元前驱体球形度良好,粒度均匀,表面光滑,达到市售普通前驱体程度。(4) The ternary precursor prepared by the present invention has good sphericity, uniform particle size, and smooth surface, reaching the level of commercially available common precursors.
附图说明Description of drawings
图1是本发明的实施工艺流程图。Fig. 1 is the implementation process flow chart of the present invention.
图2是实施例1制备所得三元前驱体的SEM图。Figure 2 is a SEM image of the ternary precursor prepared in Example 1.
图3是实施例2制备所得三元前驱体的SEM图。Figure 3 is a SEM image of the ternary precursor prepared in Example 2.
图4是实施例3制备所得三元前驱体的SEM图。Figure 4 is a SEM image of the ternary precursor prepared in Example 3.
图5是实施例4制备所得三元前驱体的SEM图。5 is an SEM image of the ternary precursor prepared in Example 4.
图6是实施例5制备所得三元前驱体的SEM图。6 is an SEM image of the ternary precursor prepared in Example 5.
具体实施方式detailed description
下面结合具体实施例进一步说明本发明。下述实施例仅用于示例性说明,不能理解为对本发明的限制。除非特别说明,下述实施例中使用的原材料和设备为本领域常规使用的原材料和设备。The present invention will be further described below in conjunction with specific examples. The following examples are for illustrative purposes only, and should not be construed as limiting the present invention. Unless otherwise specified, the raw materials and equipment used in the following examples are those conventionally used in the art.
实施例1Example 1
本发明工艺流程图如附图1所示。Process flow chart of the present invention is as shown in accompanying drawing 1.
本实施例一种废弃三元正极材料中回收锂、镍钴锰的方法,包括以下步骤:In this embodiment, a method for recovering lithium, nickel, cobalt, and manganese from waste ternary positive electrode materials comprises the following steps:
S1.球磨混料:将废弃三元正极材料和占废弃三元正极材料质量10%的焦炭在行星式球磨机以200rpm转速中球磨1h;S1. Ball milling and mixing: mill the waste ternary cathode material and coke accounting for 10% of the mass of the waste ternary cathode material in a planetary ball mill at a speed of 200 rpm for 1 hour;
S2.还原焙烧:将球磨完毕的废弃三元正极材料与焦炭的混合物在99.99%的氩气气氛中进行焙烧,焙烧温度为600℃,焙烧时间为2h;S2. Reduction roasting: the mixture of the waste ternary cathode material and coke after ball milling is roasted in 99.99% argon atmosphere, the roasting temperature is 600°C, and the roasting time is 2h;
S3.水溶出:将冷却后的焙烧产物加入到水中溶出,溶出温度为30℃,溶出时间为4h,液固比为100ml/g,搅拌强度为100rpm,反应完毕后将浆料过滤得到滤液和滤渣,取样分析检测滤液中锂的溶出率达到93.68%;S3. Water dissolution: add the cooled roasted product into water to dissolve, the dissolution temperature is 30°C, the dissolution time is 4h, the liquid-solid ratio is 100ml/g, and the stirring intensity is 100rpm. After the reaction is completed, the slurry is filtered to obtain the filtrate and Filter residue, sampling analysis detects that the dissolution rate of lithium in the filtrate reaches 93.68%;
S4.硫酸浸出:将水浸出后过滤得到的滤渣加入到配置好的硫酸溶液中,硫酸浓度为4mol/L,液固比为10ml/g,浸出温度为90℃,浸出时间为4 h,搅拌强度为100rpm,反应完毕后将浆料进行过滤得到含镍钴锰溶液和滤渣,取样分析检测滤液中镍钴锰的浸出率分别达到99.56%,99.14%,95.9%。S4. Sulfuric acid leaching: add the filter residue obtained by filtering after water leaching into the prepared sulfuric acid solution, the sulfuric acid concentration is 4mol/L, the liquid-solid ratio is 10ml/g, the leaching temperature is 90°C, and the leaching time is 4 h. Stir The intensity is 100rpm. After the reaction is completed, the slurry is filtered to obtain a solution containing nickel, cobalt and manganese and filter residue. Sampling analysis detects that the leaching rates of nickel, cobalt and manganese in the filtrate reach 99.56%, 99.14%, and 95.9%, respectively.
S5.制备前驱体:根据浸出液中镍、钴、锰金属离子的比例添加硫酸镍、硫酸钴、硫酸锰调节镍、钴、锰金属离子比例为1:1:1,镍钴锰溶液的浓度为2 mol/L,氢氧化钠溶液的浓度为2mol/L,氨水浓度为0.5mol/L,将三种溶液在氮气保护下蠕动泵并流加入到反应釜中,反应温度控制在60℃,反应时间为20 h,通过控制氢氧化钠溶液流速控制反应pH值为10~11,反应完毕后三元前驱体浆料过滤、洗涤后在100℃下烘干得到111型三元前驱体。S5. Preparation of precursor: add nickel sulfate, cobalt sulfate, and manganese sulfate according to the ratio of nickel, cobalt, and manganese metal ions in the leaching solution to adjust the ratio of nickel, cobalt, and manganese metal ions to 1:1:1, and the concentration of the nickel-cobalt-manganese solution is 2 mol/L, the concentration of sodium hydroxide solution is 2mol/L, and the concentration of ammonia water is 0.5mol/L. The three solutions are added to the reactor in parallel with the peristaltic pump under the protection of nitrogen. The reaction temperature is controlled at 60°C. The reaction time was 20 h, and the pH value of the reaction was controlled by controlling the flow rate of the sodium hydroxide solution to be 10-11. After the reaction, the ternary precursor slurry was filtered, washed, and dried at 100 °C to obtain the 111-type ternary precursor.
图2为本实施例制备所得111型三元前驱体的SEM图。SEM检测分析表明:本发明制备的三元前驱体颗粒分布均匀,球形度良好,表面光滑,颗粒分散均匀。Figure 2 is the SEM image of the 111-type ternary precursor prepared in this example. SEM detection and analysis shows that the ternary precursor particles prepared by the present invention are evenly distributed, have good sphericity, smooth surface, and evenly dispersed particles.
实施例2Example 2
实验原料、步骤同实施例1。Experimental raw material, step are with embodiment 1.
本实施例一种废弃三元正极材料中回收锂、镍钴锰的方法,包括以下步骤:In this embodiment, a method for recovering lithium, nickel, cobalt, and manganese from waste ternary positive electrode materials comprises the following steps:
S1.球磨混料:将废弃三元正极材料和占废弃三元正极材料质量5%的焦炭在行星式球磨机以100rpm转速中球磨2h;S1. Ball milling and mixing: mill the waste ternary cathode material and coke accounting for 5% of the mass of the waste ternary cathode material in a planetary ball mill at a speed of 100rpm for 2h;
S2.还原焙烧:将球磨完毕的废弃三元正极材料与焦炭的混合物在99.99%的氩气气氛中进行焙烧,焙烧温度为500℃,焙烧时间为0.5h;S2. Reduction roasting: the mixture of the ball milled waste ternary cathode material and coke is roasted in 99.99% argon atmosphere, the roasting temperature is 500°C, and the roasting time is 0.5h;
S3.水溶出:将冷却后的焙烧产物加入到水中溶出,溶出温度为25℃,溶出时间为2h,液固比为50ml/g,搅拌强度为200rpm,反应完毕后将浆料过滤得到滤液和滤渣,取样分析检测滤液中锂的溶出率达到91.98%;S3. Water dissolution: add the cooled roasted product into water to dissolve, the dissolution temperature is 25°C, the dissolution time is 2h, the liquid-solid ratio is 50ml/g, and the stirring intensity is 200rpm. After the reaction is completed, the slurry is filtered to obtain the filtrate and Filter residue, sampling analysis detects that the dissolution rate of lithium in the filtrate reaches 91.98%;
S4.硫酸浸出:将水浸出后过滤得到的滤渣加入到配置好的硫酸溶液中,硫酸浓度为3mol/L,液固比为5ml/g,浸出温度为70℃,浸出时间为2 h,搅拌强度为200rpm,反应完毕后将浆料进行过滤得到含镍钴锰溶液和滤渣,取样分析检测滤液中镍钴锰的浸出率分别达到92.36%,94.74%,90.16%。S4. Sulfuric acid leaching: Add the filter residue obtained by filtering after water leaching into the prepared sulfuric acid solution, the sulfuric acid concentration is 3mol/L, the liquid-solid ratio is 5ml/g, the leaching temperature is 70°C, and the leaching time is 2 h. Stir The intensity is 200rpm. After the reaction is completed, the slurry is filtered to obtain a solution containing nickel, cobalt and manganese and filter residue. Sampling analysis detects that the leaching rates of nickel, cobalt and manganese in the filtrate reach 92.36%, 94.74%, and 90.16%, respectively.
S5.制备前驱体:根据浸出液中镍、钴、锰金属离子的比例添加硫酸镍、硫酸钴、硫酸锰调节镍、钴、锰金属离子比例为4:2:4,镍钴锰溶液的浓度为4 mol/L,氢氧化钠溶液的浓度为4mol/L,氨水浓度为3mol/L,将三种溶液在氮气保护下蠕动泵并流加入到反应釜中,反应温度控制在50℃,反应时间为15 h,通过控制氢氧化钠溶液流速控制反应pH值为10~11,反应完毕后三元前驱体浆料过滤、洗涤后在80℃下烘干得到424型三元前驱体。S5. Preparation of precursor: add nickel sulfate, cobalt sulfate, and manganese sulfate according to the ratio of nickel, cobalt, and manganese metal ions in the leaching solution to adjust the ratio of nickel, cobalt, and manganese metal ions to 4:2:4, and the concentration of the nickel-cobalt-manganese solution is 4 mol/L, the concentration of sodium hydroxide solution is 4mol/L, and the concentration of ammonia water is 3mol/L. The three solutions are added to the reactor in parallel with the peristaltic pump under the protection of nitrogen. The reaction temperature is controlled at 50 ° C. The reaction time The reaction time was 15 h, and the pH value of the reaction was controlled by controlling the flow rate of sodium hydroxide solution to 10-11. After the reaction, the ternary precursor slurry was filtered, washed, and dried at 80 °C to obtain the 424-type ternary precursor.
图3为本实施例制备所得424型三元前驱体的SEM图。SEM检测分析表明:本发明制备的三元前驱体颗粒分布均匀,球形度良好,表面光滑,颗粒分散均匀。Figure 3 is the SEM image of the 424-type ternary precursor prepared in this example. SEM detection and analysis shows that the ternary precursor particles prepared by the present invention are evenly distributed, have good sphericity, smooth surface, and evenly dispersed particles.
实施例3Example 3
实验原料、步骤同实施例1。Experimental raw material, step are with embodiment 1.
本实施例一种废弃三元正极材料中回收锂、镍钴锰的方法,包括以下步骤:In this embodiment, a method for recovering lithium, nickel, cobalt, and manganese from waste ternary positive electrode materials comprises the following steps:
S1.球磨混料:将废弃三元正极材料和占废弃三元正极材料质量20%的焦炭在行星式球磨机以300rpm转速中球磨0.5h;S1. Ball mill mixing: mill the waste ternary cathode material and coke accounting for 20% of the mass of the waste ternary cathode material in a planetary ball mill at a speed of 300rpm for 0.5h;
S2.还原焙烧:将球磨完毕的废弃三元正极材料与焦炭的混合物在99.99%的氩气气氛中进行焙烧,焙烧温度为700℃,焙烧时间为3h;S2. Reduction roasting: the mixture of the ball milled waste ternary cathode material and coke is roasted in 99.99% argon atmosphere, the roasting temperature is 700°C, and the roasting time is 3h;
S3.水溶出:将冷却后的焙烧产物加入到水中溶出,溶出温度为28℃,溶出时间为5h,液固比为60ml/g,搅拌强度为500rpm,反应完毕后将浆料过滤得到滤液和滤渣,取样分析检测滤液中锂的溶出率达到92.68%;S3. Water dissolution: add the cooled roasted product into water to dissolve, the dissolution temperature is 28°C, the dissolution time is 5h, the liquid-solid ratio is 60ml/g, and the stirring intensity is 500rpm. After the reaction is completed, the slurry is filtered to obtain the filtrate and Filter residue, sampling analysis detects that the dissolution rate of lithium in the filtrate reaches 92.68%;
S4.硫酸浸出:将水浸出后过滤得到的滤渣加入到配置好的硫酸溶液中,硫酸浓度为2mol/L,液固比为15ml/g,浸出温度为70℃,浸出时间为8 h,搅拌强度为500rpm,反应完毕后将浆料进行过滤得到含镍钴锰溶液和滤渣,取样分析检测滤液中镍钴锰的浸出率分别达到98.76%,98.64%,94.9%。S4. Sulfuric acid leaching: Add the filter residue obtained by filtering after water leaching into the prepared sulfuric acid solution, the concentration of sulfuric acid is 2mol/L, the liquid-solid ratio is 15ml/g, the leaching temperature is 70°C, and the leaching time is 8 h. Stir The intensity is 500rpm. After the reaction is completed, the slurry is filtered to obtain a solution containing nickel, cobalt and manganese and filter residue. Sampling analysis detects that the leaching rates of nickel, cobalt and manganese in the filtrate reach 98.76%, 98.64%, and 94.9%, respectively.
S5.制备前驱体:根据浸出液中镍、钴、锰金属离子的比例添加硫酸镍、硫酸钴、硫酸锰调节镍、钴、锰金属离子比例为5:2:3,镍钴锰溶液的浓度为2 mol/L,氢氧化钠溶液的浓度为2mol/L,氨水浓度为0.5mol/L,将三种溶液在氮气保护下蠕动泵并流加入到反应釜中,反应温度控制在70℃,反应时间为16h,通过控制氢氧化钠溶液流速控制反应pH值为10~11,反应完毕后三元前驱体浆料过滤、洗涤后在100℃下烘干得到523型三元前驱体。S5. Preparation of precursor: add nickel sulfate, cobalt sulfate, and manganese sulfate according to the ratio of nickel, cobalt, and manganese metal ions in the leaching solution to adjust the ratio of nickel, cobalt, and manganese metal ions to 5:2:3, and the concentration of the nickel-cobalt-manganese solution is 2 mol/L, the concentration of sodium hydroxide solution is 2mol/L, and the concentration of ammonia water is 0.5mol/L. The three solutions are added to the reactor in parallel with the peristaltic pump under the protection of nitrogen. The reaction temperature is controlled at 70°C. The time is 16 hours, and the pH value of the reaction is controlled by controlling the flow rate of the sodium hydroxide solution to be 10-11. After the reaction is completed, the ternary precursor slurry is filtered, washed, and dried at 100°C to obtain the 523-type ternary precursor.
图4为本实施例制备所得523型三元前驱体的SEM图。SEM检测分析表明:本发明制备的三元前驱体颗粒分布均匀,球形度良好,表面光滑,颗粒分散均匀。Figure 4 is the SEM image of the 523-type ternary precursor prepared in this example. SEM detection and analysis shows that the ternary precursor particles prepared by the present invention are evenly distributed, have good sphericity, smooth surface, and evenly dispersed particles.
实施例4Example 4
实验原料、步骤同实施例1。Experimental raw material, step are with embodiment 1.
本实施例一种废弃三元正极材料中回收锂、镍钴锰的方法,包括以下步骤:In this embodiment, a method for recovering lithium, nickel, cobalt, and manganese from waste ternary positive electrode materials comprises the following steps:
S1.球磨混料:将废弃三元正极材料和占废弃三元正极材料质量20%的焦炭在行星式球磨机以300rpm转速中球磨0.5h;S1. Ball mill mixing: mill the waste ternary cathode material and coke accounting for 20% of the mass of the waste ternary cathode material in a planetary ball mill at a speed of 300rpm for 0.5h;
S2.还原焙烧:将球磨完毕的废弃三元正极材料与焦炭的混合物在99.99%的氩气气氛中进行焙烧,焙烧温度为600℃,焙烧时间为3h;S2. Reduction roasting: the mixture of the ball milled waste ternary cathode material and coke is roasted in 99.99% argon atmosphere, the roasting temperature is 600°C, and the roasting time is 3h;
S3.水溶出:将冷却后的焙烧产物加入到水中溶出,溶出温度为28℃,溶出时间为5h,液固比为10ml/g,搅拌强度为500rpm,反应完毕后将浆料过滤得到滤液和滤渣,取样分析检测滤液中锂的溶出率达到91.68%;S3. Water dissolution: add the cooled roasted product into water to dissolve, the dissolution temperature is 28°C, the dissolution time is 5h, the liquid-solid ratio is 10ml/g, and the stirring intensity is 500rpm. After the reaction is completed, the slurry is filtered to obtain the filtrate and Filter residue, sampling analysis detects that the dissolution rate of lithium in the filtrate reaches 91.68%;
S4.硫酸浸出:将水浸出后过滤得到的滤渣加入到配置好的硫酸溶液中,硫酸浓度为3mol/L,液固比为15ml/g,浸出温度为50℃,浸出时间为8 h,搅拌强度为500rpm,反应完毕后将浆料进行过滤得到含镍钴锰溶液和滤渣,取样分析检测滤液中镍钴锰的浸出率分别达到99.26%,98.94%,94.63%。S4. Sulfuric acid leaching: add the filter residue obtained by filtering after water leaching into the prepared sulfuric acid solution, the sulfuric acid concentration is 3mol/L, the liquid-solid ratio is 15ml/g, the leaching temperature is 50°C, and the leaching time is 8 h. Stir The intensity is 500rpm. After the reaction is completed, the slurry is filtered to obtain a solution containing nickel, cobalt and manganese and filter residue. Sampling analysis detects that the leaching rates of nickel, cobalt and manganese in the filtrate reach 99.26%, 98.94%, and 94.63%, respectively.
S5.制备前驱体:根据浸出液中镍、钴、锰金属离子的比例添加硫酸镍、硫酸钴、硫酸锰调节镍、钴、锰金属离子比例为6:2:2,镍钴锰溶液的浓度为1 mol/L,氢氧化钠溶液的浓度为2mol/L,氨水浓度为1mol/L,将三种溶液在氮气保护下蠕动泵并流加入到反应釜中,反应温度控制在70℃,反应时间为12h,通过控制氢氧化钠溶液流速控制反应pH值为10~11,反应完毕后三元前驱体浆料过滤、洗涤后在120℃下烘干得到622型三元前驱体。S5. Preparation of precursor: add nickel sulfate, cobalt sulfate, and manganese sulfate according to the ratio of nickel, cobalt, and manganese metal ions in the leaching solution to adjust the ratio of nickel, cobalt, and manganese metal ions to 6:2:2, and the concentration of the nickel-cobalt-manganese solution is 1 mol/L, the concentration of sodium hydroxide solution is 2 mol/L, and the concentration of ammonia water is 1 mol/L. The three solutions are added to the reactor in parallel with the peristaltic pump under the protection of nitrogen. The reaction temperature is controlled at 70 °C, and the reaction time is For 12 hours, the pH value of the reaction was controlled by controlling the flow rate of the sodium hydroxide solution to be 10-11. After the reaction, the ternary precursor slurry was filtered, washed, and dried at 120°C to obtain the 622-type ternary precursor.
图5为本实施例制备所得622型三元前驱体的SEM图。SEM检测分析表明:本发明制备的三元前驱体颗粒分布均匀,球形度良好,表面光滑,颗粒分散均匀。Fig. 5 is an SEM image of the 622-type ternary precursor prepared in this example. SEM detection and analysis shows that the ternary precursor particles prepared by the present invention are evenly distributed, have good sphericity, smooth surface, and evenly dispersed particles.
实施例5Example 5
实验原料、步骤同实施例1。Experimental raw material, step are with embodiment 1.
本实施例一种废弃三元正极材料中回收锂、镍钴锰的方法,包括以下步骤:In this embodiment, a method for recovering lithium, nickel, cobalt, and manganese from waste ternary positive electrode materials comprises the following steps:
S1.球磨混料:将废弃三元正极材料和占废弃三元正极材料质量15%的焦炭在行星式球磨机以400rpm转速中球磨2h;S1. Ball milling and mixing: mill the waste ternary cathode material and coke accounting for 15% of the mass of the waste ternary cathode material in a planetary ball mill at a speed of 400rpm for 2h;
S2.还原焙烧:将球磨完毕的废弃三元正极材料与焦炭的混合物在99.99%的氩气气氛中进行焙烧,焙烧温度为650℃,焙烧时间为2h;S2. Reduction roasting: the mixture of the ball milled waste ternary cathode material and coke is roasted in 99.99% argon atmosphere, the roasting temperature is 650°C, and the roasting time is 2h;
S3.水溶出:将冷却后的焙烧产物加入到水中溶出,溶出温度为30℃,溶出时间为4h,液固比为50ml/g,搅拌强度为200rpm,反应完毕后将浆料过滤得到滤液和滤渣,取样分析检测滤液中锂的溶出率达到90.68%;S3. Water dissolution: add the cooled roasted product into water to dissolve, the dissolution temperature is 30°C, the dissolution time is 4h, the liquid-solid ratio is 50ml/g, and the stirring intensity is 200rpm. After the reaction is completed, the slurry is filtered to obtain the filtrate and Filter residue, sampling analysis detects that the dissolution rate of lithium in the filtrate reaches 90.68%;
S4.硫酸浸出:将水浸出后过滤得到的滤渣加入到配置好的硫酸溶液中,硫酸浓度为2.5mol/L,液固比为5ml/g,浸出温度为65℃,浸出时间为7 h,搅拌强度为400rpm,反应完毕后将浆料进行过滤得到含镍钴锰溶液和滤渣,取样分析检测滤液中镍钴锰的浸出率分别达到98.86%,98.54%,94.93%。S4. Sulfuric acid leaching: add the filter residue obtained by filtering after water leaching into the prepared sulfuric acid solution, the sulfuric acid concentration is 2.5mol/L, the liquid-solid ratio is 5ml/g, the leaching temperature is 65°C, and the leaching time is 7 h. The stirring intensity was 400rpm. After the reaction was completed, the slurry was filtered to obtain a solution containing nickel, cobalt and manganese and filter residue. Sampling analysis detected that the leaching rates of nickel, cobalt and manganese in the filtrate reached 98.86%, 98.54%, and 94.93%, respectively.
S5.制备前驱体:根据浸出液中镍、钴、锰金属离子的比例添加硫酸镍、硫酸钴、硫酸锰调节镍、钴、锰金属离子比例为8:1:1,镍钴锰溶液的浓度为2mol/L,氢氧化钠溶液的浓度为2mol/L,氨水浓度为2mol/L,将三种溶液在氮气保护下蠕动泵并流加入到反应釜中,反应温度控制在70℃,反应时间为18h,通过控制氢氧化钠溶液流速控制反应pH值为10~11,反应完毕后三元前驱体浆料过滤、洗涤后在100℃下烘干得到811型三元前驱体。S5. Preparation of precursor: add nickel sulfate, cobalt sulfate, and manganese sulfate according to the ratio of nickel, cobalt, and manganese metal ions in the leaching solution to adjust the ratio of nickel, cobalt, and manganese metal ions to 8:1:1, and the concentration of the nickel-cobalt-manganese solution is 2mol/L, the concentration of sodium hydroxide solution is 2mol/L, and the concentration of ammonia water is 2mol/L. The three solutions are added to the reactor in parallel with the peristaltic pump under the protection of nitrogen. The reaction temperature is controlled at 70 °C, and the reaction time is After 18 hours, the pH value of the reaction was controlled to be 10-11 by controlling the flow rate of the sodium hydroxide solution. After the reaction was completed, the ternary precursor slurry was filtered, washed, and dried at 100°C to obtain the 811-type ternary precursor.
图6为本实施例制备所得811型三元前驱体的SEM图。SEM检测分析表明:本发明制备的三元前驱体颗粒分布均匀,球形度良好,表面光滑,颗粒分散均匀。Fig. 6 is an SEM image of the 811-type ternary precursor prepared in this example. SEM detection and analysis shows that the ternary precursor particles prepared by the present invention are evenly distributed, have good sphericity, smooth surface, and evenly dispersed particles.
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