TWI741603B - Method for recovering valuable metals from waste lithium batteries - Google Patents
Method for recovering valuable metals from waste lithium batteries Download PDFInfo
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- TWI741603B TWI741603B TW109116117A TW109116117A TWI741603B TW I741603 B TWI741603 B TW I741603B TW 109116117 A TW109116117 A TW 109116117A TW 109116117 A TW109116117 A TW 109116117A TW I741603 B TWI741603 B TW I741603B
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- 229910052751 metal Inorganic materials 0.000 title claims abstract description 44
- 239000002184 metal Substances 0.000 title claims abstract description 43
- 229910052744 lithium Inorganic materials 0.000 title claims abstract description 40
- 238000000034 method Methods 0.000 title claims abstract description 39
- WHXSMMKQMYFTQS-UHFFFAOYSA-N Lithium Chemical compound [Li] WHXSMMKQMYFTQS-UHFFFAOYSA-N 0.000 title claims abstract description 34
- 150000002739 metals Chemical class 0.000 title claims abstract description 26
- 239000002699 waste material Substances 0.000 title claims abstract description 25
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 claims abstract description 65
- 229910052759 nickel Inorganic materials 0.000 claims abstract description 34
- 229910017052 cobalt Inorganic materials 0.000 claims abstract description 31
- 239000010941 cobalt Substances 0.000 claims abstract description 31
- GUTLYIVDDKVIGB-UHFFFAOYSA-N cobalt atom Chemical compound [Co] GUTLYIVDDKVIGB-UHFFFAOYSA-N 0.000 claims abstract description 31
- 239000011572 manganese Substances 0.000 claims abstract description 23
- 229910052748 manganese Inorganic materials 0.000 claims abstract description 22
- PWHULOQIROXLJO-UHFFFAOYSA-N Manganese Chemical compound [Mn] PWHULOQIROXLJO-UHFFFAOYSA-N 0.000 claims abstract description 13
- 238000000926 separation method Methods 0.000 claims abstract description 12
- 239000011347 resin Substances 0.000 claims description 32
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- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 29
- 238000003795 desorption Methods 0.000 claims description 21
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- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims description 15
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- 150000001450 anions Chemical class 0.000 claims description 6
- AMWRITDGCCNYAT-UHFFFAOYSA-L hydroxy(oxo)manganese;manganese Chemical compound [Mn].O[Mn]=O.O[Mn]=O AMWRITDGCCNYAT-UHFFFAOYSA-L 0.000 claims description 6
- 238000002386 leaching Methods 0.000 claims description 6
- 238000001914 filtration Methods 0.000 claims description 5
- 239000012286 potassium permanganate Substances 0.000 claims description 5
- 238000003756 stirring Methods 0.000 claims description 4
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- 238000005191 phase separation Methods 0.000 claims description 2
- 239000008346 aqueous phase Substances 0.000 claims 1
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- 229910052782 aluminium Inorganic materials 0.000 description 10
- HBBGRARXTFLTSG-UHFFFAOYSA-N Lithium ion Chemical compound [Li+] HBBGRARXTFLTSG-UHFFFAOYSA-N 0.000 description 9
- 229910001416 lithium ion Inorganic materials 0.000 description 9
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 8
- 238000005868 electrolysis reaction Methods 0.000 description 8
- 230000008569 process Effects 0.000 description 8
- 238000011084 recovery Methods 0.000 description 7
- 229910052742 iron Inorganic materials 0.000 description 6
- 239000007788 liquid Substances 0.000 description 6
- 238000004064 recycling Methods 0.000 description 6
- 239000000126 substance Substances 0.000 description 6
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 description 5
- 238000006243 chemical reaction Methods 0.000 description 5
- 238000005342 ion exchange Methods 0.000 description 5
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 description 4
- 239000003795 chemical substances by application Substances 0.000 description 4
- 238000005470 impregnation Methods 0.000 description 4
- 150000002500 ions Chemical class 0.000 description 4
- 239000011734 sodium Substances 0.000 description 4
- -1 aluminum ions Chemical class 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 238000005516 engineering process Methods 0.000 description 3
- XGZVUEUWXADBQD-UHFFFAOYSA-L lithium carbonate Chemical compound [Li+].[Li+].[O-]C([O-])=O XGZVUEUWXADBQD-UHFFFAOYSA-L 0.000 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 description 3
- 239000010926 waste battery Substances 0.000 description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 3
- BVKZGUZCCUSVTD-UHFFFAOYSA-L Carbonate Chemical compound [O-]C([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-L 0.000 description 2
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 description 2
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 2
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 description 2
- QSNQXZYQEIKDPU-UHFFFAOYSA-N [Li].[Fe] Chemical compound [Li].[Fe] QSNQXZYQEIKDPU-UHFFFAOYSA-N 0.000 description 2
- 239000002253 acid Substances 0.000 description 2
- 239000010406 cathode material Substances 0.000 description 2
- 238000009388 chemical precipitation Methods 0.000 description 2
- 229910052802 copper Inorganic materials 0.000 description 2
- 239000010949 copper Substances 0.000 description 2
- 239000011889 copper foil Substances 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 239000011888 foil Substances 0.000 description 2
- 229910001385 heavy metal Inorganic materials 0.000 description 2
- 229910052808 lithium carbonate Inorganic materials 0.000 description 2
- 229910021645 metal ion Inorganic materials 0.000 description 2
- 239000012071 phase Substances 0.000 description 2
- 230000001376 precipitating effect Effects 0.000 description 2
- 238000002203 pretreatment Methods 0.000 description 2
- 238000009853 pyrometallurgy Methods 0.000 description 2
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- 238000011069 regeneration method Methods 0.000 description 2
- 229910052725 zinc Inorganic materials 0.000 description 2
- 239000011701 zinc Substances 0.000 description 2
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 description 1
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 1
- BPKGOZPBGXJDEP-UHFFFAOYSA-N [C].[Zn] Chemical compound [C].[Zn] BPKGOZPBGXJDEP-UHFFFAOYSA-N 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
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- 235000011114 ammonium hydroxide Nutrition 0.000 description 1
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- 230000009286 beneficial effect Effects 0.000 description 1
- 229910052793 cadmium Inorganic materials 0.000 description 1
- BDOSMKKIYDKNTQ-UHFFFAOYSA-N cadmium atom Chemical compound [Cd] BDOSMKKIYDKNTQ-UHFFFAOYSA-N 0.000 description 1
- OJIJEKBXJYRIBZ-UHFFFAOYSA-N cadmium nickel Chemical compound [Ni].[Cd] OJIJEKBXJYRIBZ-UHFFFAOYSA-N 0.000 description 1
- 229910002091 carbon monoxide Inorganic materials 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 239000003638 chemical reducing agent Substances 0.000 description 1
- 239000012141 concentrate Substances 0.000 description 1
- 238000009833 condensation Methods 0.000 description 1
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- 238000000502 dialysis Methods 0.000 description 1
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- PCHJSUWPFVWCPO-UHFFFAOYSA-N gold Chemical compound [Au] PCHJSUWPFVWCPO-UHFFFAOYSA-N 0.000 description 1
- 229910052737 gold Inorganic materials 0.000 description 1
- 239000010931 gold Substances 0.000 description 1
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- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 description 1
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- 229910001220 stainless steel Inorganic materials 0.000 description 1
- 239000001117 sulphuric acid Substances 0.000 description 1
- 235000011149 sulphuric acid Nutrition 0.000 description 1
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- 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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- Manufacture And Refinement Of Metals (AREA)
Abstract
本發明係關於一種廢棄鋰電池中回收有價金屬之方法,主要係以一種對廢鋰電池之含有鋰鈷鎳錳粉末提出一個萃取、純化與分離之濕法冶金流程。 The present invention relates to a method for recovering valuable metals from waste lithium batteries, and mainly proposes a hydrometallurgical process of extraction, purification and separation of lithium, cobalt, nickel and manganese powders contained in waste lithium batteries.
Description
本發明係關於一種資源獲取之方式,尤指一種廢棄鋰電池中回收有價金屬之方法。 The present invention relates to a method of resource acquisition, in particular to a method of recovering valuable metals from waste lithium batteries.
鋰離子電池成功並導入市場後,由於重量相對較輕、體積較小以及壽命較長,因此受到全球各種3C產品、儲能設備甚至於電動車等普遍搭配使用。然而鋰離子電池含有鋰、鈷、鎳、錳等有價金屬,使用後若任意拋棄,容易使得環境受到重金屬汙染,甚置改變環境生態。而由於環保意識抬頭,以及環保課題也受到普世重視,產業或是學界也有開發資源回收之技術。例如:臺灣發明專利I286850號「廢鋰電池資源再生方法」,就其專利說明書所載,揭示將而鋰、鈷所在的正極部分,藉由鹽酸浸漬二小時後,以氫氧化鈉(NaOH)調整浸漬液之pH值至八,則此時可藉由過濾加以分離含鈷(Co)、鋁(Al)、鎳(Ni)之膠凝物,最後再加入碳酸鈉飽合溶液於浸漬液後,即可得到碳酸鋰粉末;另經過濾所得含鈷(Co)、鋁(Al)、鎳(Ni)之膠凝物,先以硫酸酸洗並調整pH值為二使所含金屬溶解後,再加入氨水調整pH值為八以過濾去除含鋁離子之膠凝物,最後再將過濾後之酸洗液利用硫酸將pH值調整至4.3後倒入電解槽內予以電解回收,利用恆溫水浴使電解液溫度保持在55℃,通以固定電流後,則鈷及鎳金屬將沉積在陰極不鏽鋼片上,經乾燥後可回收取得鈷及鎳金屬,以達到廢棄物資源再生之目的。 After the successful introduction of lithium-ion batteries into the market, due to their relatively light weight, small size and long life, they are widely used in various 3C products, energy storage equipment and even electric vehicles around the world. However, lithium-ion batteries contain valuable metals such as lithium, cobalt, nickel, and manganese. If they are discarded arbitrarily after use, the environment will easily be polluted by heavy metals and even change the environment. And because of the rising awareness of environmental protection and the importance of environmental protection issues worldwide, industry or academia also develops technology for resource recovery. For example: Taiwan Invention Patent No. I286850 "Method for Recycling Waste Lithium Battery Resources", according to its patent specification, discloses that the positive electrode part where lithium and cobalt are located is immersed in hydrochloric acid for two hours and then adjusted with sodium hydroxide (NaOH). The pH value of the dipping solution reaches eight, then the gelled substance containing cobalt (Co), aluminum (Al), and nickel (Ni) can be separated by filtration at this time, and finally sodium carbonate saturated solution is added to the dipping solution. Lithium carbonate powder can be obtained; in addition, the gelled substance containing cobalt (Co), aluminum (Al), and nickel (Ni) obtained by filtration is first pickled with sulfuric acid and adjusted to a pH of two to dissolve the contained metals. Add ammonia water to adjust the pH to 8 to filter and remove the gelatinous material containing aluminum ions. Finally, the filtered pickling solution is adjusted to pH 4.3 with sulfuric acid and then poured into the electrolytic cell for electrolysis and recovery, and electrolysis is carried out with a constant temperature water bath. The temperature of the liquid is maintained at 55°C, and after a fixed current is applied, the cobalt and nickel metal will be deposited on the cathode stainless steel sheet, and the cobalt and nickel metal can be recovered after drying, so as to achieve the purpose of waste resource regeneration.
臺灣發明公告第501294號「使用硫酸從廢鋰離子電池回收金屬之方法」,其專利說明書揭示流程是將使用過之廢棄鋰離子電池於高溫爐中焙燒分解除去有機電 解質後粉碎加予篩分,篩上物可經磁選及渦電流分選處理,分離出碎解之鐵殼、銅箔與鋁箔等;而篩下物則以硫酸及過氧化氫的混合液進行溶蝕,過濾出溶蝕所獲得的溶液再通過酸鹼值的調整將其中的鐵及鋁離子沈澱出,其間並藉由電解分別電解析出金屬銅與金屬鈷,而經電解後富含鋰離子之溶液,則被添加碳酸根於是形成鋰之碳酸鹽沈澱而將鋰有效回收。 Taiwan Invention Announcement No. 501294 "Method for Recovering Metals from Waste Lithium Ion Batteries Using Sulfuric Acid", its patent specification discloses the process of roasting and decomposing used waste lithium ion batteries in a high-temperature furnace to remove organic electricity. After digestion, it is crushed and sieved. The material on the sieve can be processed by magnetic separation and eddy current separation to separate the broken iron shell, copper foil and aluminum foil. The material under the sieve is a mixture of sulfuric acid and hydrogen peroxide. Dissolution is carried out, the solution obtained by the dissolution is filtered out, and the iron and aluminum ions are precipitated by adjusting the acid-base value. In the meantime, the metal copper and the metal cobalt are electrolytically separated by electrolysis, and the electrolysis is rich in lithium ions In the solution, carbonate is added to form lithium carbonate precipitation and the lithium is effectively recovered.
而臺灣發明公告第399347號「一種混合廢電池的回收處理方法」,其中欲回收之金屬化合物在高溫下直接與還原氣體(主要為一氧化碳)充分接觸並進行還原反應,而有效還原成金屬元素,並藉由串聯分段式的冷凝,可以將廢電池中所含的金屬物質回收成各種單一的富集金屬物質,如鋰、鋅、鎘、水銀等再資源化產品,而且處理後的殘留物質亦不再具有重金屬污染。 And Taiwan Invention Announcement No. 399347 "A method for recycling waste batteries", in which the metal compound to be recycled is fully contacted with reducing gas (mainly carbon monoxide) at high temperature and undergoes a reduction reaction, effectively reducing it to metal elements. And by series-staged condensation, the metal substances contained in the waste battery can be recycled into a variety of single enriched metal substances, such as lithium, zinc, cadmium, mercury and other recycled products, and the residual substances after treatment It also no longer has heavy metal pollution.
臺灣新型第M341943號「廢電池處理及再利用裝置」說明書則揭示一乾式冶金熱電漿熔融處理程序取代感應高溫爐處理鹼錳、碳鋅、鋅空氣及鎳鎘等廢乾電池,不僅可得到更良好之回收率。 Taiwan's new M341943 "Waste Battery Treatment and Recycling Device" manual reveals that a dry metallurgical thermal plasma melting process replaces the induction high-temperature furnace to process waste dry batteries such as alkaline manganese, carbon zinc, zinc air and nickel cadmium, which not only can get better The recovery rate.
臺灣發明專利I535479號「回收有價金屬之方法」,說明書則揭示包含利用硫酸與過氧化氫之酸液及超音波裝置,以及現存之回收程序以進行金屬回收。 Taiwan Invention Patent No. I535479 "Method for Recovering Valuable Metals", the specification discloses the use of sulfuric acid and hydrogen peroxide acid solution and ultrasonic device, and existing recovery procedures for metal recovery.
臺灣發明公告第511306號「廢鋰離子電池中金屬之清淨回收方法」之專利說明書揭示將廢棄鋰離子電池於高溫爐中焙燒,分解除去有機電解質,粉碎後篩分,篩上物再以磁選及渦電流分選處理,分離出碎解之鐵殼、銅箔與鋁箔等;而篩下物則逕行溶蝕、過濾,並藉由pH值及電解條件之控制,分別以隔膜電解法電解析出金屬銅與鈷,電解過程中於陰極側所產生之酸可經由擴散透析處理被回收並再循環至溶蝕步驟使用,成一封閉流程。而經電解後富含鋰離子之溶液,於調整酸鹼值沉澱金屬雜質後,則可以添加碳酸根形成鋰之高純度碳酸鹽而將鋰回收。 The patent specification of Taiwan Invention Bulletin No. 511306 "Method for Purifying and Recycling Metal in Waste Lithium-ion Batteries" discloses that waste lithium-ion batteries are roasted in a high-temperature furnace to decompose and remove organic electrolytes, crushed, sieved, and the sieved material is then magnetically separated. The eddy current sorting process separates the broken iron shell, copper foil and aluminum foil, etc.; and the under-sieve is eroded and filtered, and the pH value and electrolysis conditions are controlled to electrolytically separate the metal by the diaphragm electrolysis method. Copper and cobalt, the acid generated on the cathode side during the electrolysis process can be recovered by diffusion dialysis and recycled to the dissolution step for use, forming a closed process. The solution rich in lithium ions after electrolysis, after adjusting the pH value to precipitate metal impurities, can add carbonate to form a high-purity lithium carbonate to recover the lithium.
臺灣發明專利I392745號「自含有Co、Ni、Mn之鋰電池殘渣回收有價金屬之方法」則揭示係以250g/l以上之濃度的鹽酸溶液,對含有鋰酸金屬鹽(含有大致等量之Co、Ni及Mn)之鋰電池殘渣進行攪拌浸洗,或者以200g/l以上之濃度的硫酸溶液,一邊加熱至65~80℃,一邊加以攪拌浸洗,或者以混合有200g/l以上之濃度的硫酸溶液與20g/l以上之過氧化氫溶液的溶液來進行攪拌浸洗處理後,對浸洗液以酸性萃取劑進行溶劑萃取,萃取出98%以上之Mn、Co及Ni三種金屬,生成含有各金屬之溶液,然後從此等之溶液與萃取後含有Li之剩餘液體來回收Mn、Co、Ni及Li等有價金屬。 Taiwan Invention Patent No. I392745 "Method for Recovering Valuable Metals from Lithium Battery Residues Containing Co, Ni, and Mn" discloses that a hydrochloric acid solution with a concentration of 250g/l or more is used for the treatment of lithium metal salt (containing approximately the same amount of Co). , Ni and Mn) lithium battery residues are stirred and dipped, or a sulfuric acid solution with a concentration of more than 200g/l, while heating to 65~80℃, while stirring and dipping, or mixed with a concentration of more than 200g/l After stirring and immersing the sulphuric acid solution and the hydrogen peroxide solution above 20g/l, the leaching solution is solvent-extracted with an acidic extractant to extract more than 98% of Mn, Co and Ni three metals, resulting in Recover valuable metals such as Mn, Co, Ni, and Li from the solution containing each metal and the remaining liquid containing Li after extraction.
臺灣發明專利I625882號「廢鋰鐵電池中正極材料資源回收方法」專利說明書揭示其包含下述步驟:一浸漬步驟,係將廢鋰鐵電池中正極材料浸漬於濃度約為1N左右濃度的一浸漬液,兩者的固液比約為3g/50ml左右,且浸漬溫度約為27℃左右,約經0.75hr左右後,過濾出含鋁的濾渣而得出一鋰、鋁、鐵浸漬液;一pH調整步驟,係將一pH調整劑對前述鋰、鋁、鐵浸漬液調整其pH值約為7左右後,過濾出含鋰、鋁、鐵的濾渣,而得一含鋰濾液;及一晶析步驟,係將含鋰濾液加熱至約70℃左右並維持至少5hr後而得一白色晶析產物。 Taiwan Invention Patent No. I625882 "Method for Recycling Cathode Materials in Waste Lithium-Iron Battery" patent specification discloses that it includes the following steps: an impregnation step is to immerse the cathode material in the waste lithium-iron battery in an impregnation with a concentration of about 1N. The solid-to-liquid ratio of the two is about 3g/50ml, and the immersion temperature is about 27°C. After about 0.75hr, the filter residue containing aluminum is filtered out to obtain a lithium, aluminum, and iron impregnation liquid; The pH adjustment step is to adjust a pH adjuster to the aforementioned lithium, aluminum, and iron immersion liquid to a pH of about 7, and then filter out the filter residue containing lithium, aluminum, and iron to obtain a lithium-containing filtrate; and In the analysis step, the lithium-containing filtrate is heated to about 70° C. and maintained for at least 5 hours to obtain a white crystallized product.
由前述之各種方法可以發現,個別發明人對於個別之待解決問題進行解決與改善,例如強調欲取出之有價金屬之著重性,或者有部分乃是屬於基本之物理與化學之手法。然而就整套處理流程,並未發現有以結合濕式冶金技術中的離子交換法與化學沉澱法分離Ni、Co、Li、Mn等有價金屬,因此對於個別有價金屬之回收純度仍有改善之空間。 From the various methods mentioned above, it can be found that individual inventors have solved and improved individual problems to be solved, such as emphasizing the importance of the valuable metals to be removed, or some of them are basic physical and chemical methods. However, for the entire treatment process, it has not been found to combine the ion exchange method in the hydrometallurgical technology with the chemical precipitation method to separate valuable metals such as Ni, Co, Li, and Mn. Therefore, there is still room for improvement in the purity of individual valuable metals. .
有鑑於先前技術之問題,本發明人認為應有一種解決先前問題之必要,為此設計一種廢棄鋰電池中回收有價金屬之方法,對廢鋰電池之含有鋰鈷鎳錳粉末提出一個萃取、純化與分離之濕法冶金流程。其錳鋰鎳鈷回收率皆達到為:99.9%, 且錳鋰鎳鈷各元素純度分別達到98%、99%、98.5%、99.9%。本發明之方法步驟包括:前置處理步驟:將廢棄鋰電池前置處理並予以粉碎形成粉碎物;浸漬溶出步驟:將含有Ni、Co、Li、Mn金屬之粉碎物以鹽酸浸液浸漬;沈澱分離錳步驟:加入過錳酸鉀於該鹽酸浸液中;將錳沈澱為氧化錳,經過濾後與其他三元素分離,得到過濾液;吸附鈷鎳步驟:將過濾液調整ph至4以上;再使用Na+型IRC748陰離子交換樹脂將鈷與鎳吸附於該Na+型IRC748陰離子交換樹脂,鋰呈現離子態留在液相與之分離;第一樹脂脫附步驟:將留在樹脂中之鈷鎳以HCl進行脫附;吸附鈷將鎳於液相分離步驟:加入HCl至Cl-濃度為8N,誤差5%範圍內,使Co錯合形成[CoCl4]2-,利用強鹼型陰離子樹脂將Co吸附於樹脂,Ni於液相與之分離;第二樹脂脫附步驟:加入硫酸將吸附於樹脂之鈷沖洗於水相。 In view of the problems of the prior art, the inventor believes that there should be a need to solve the previous problems. To this end, the inventor designs a method for recovering valuable metals from waste lithium batteries. Separation of the hydrometallurgical process. The recovery rate of manganese, lithium, nickel and cobalt is 99.9%, and the purity of each element of manganese, lithium, nickel and cobalt reaches 98%, 99%, 98.5%, and 99.9% respectively. The method steps of the present invention include: pre-treatment step: pre-treating the waste lithium battery and pulverizing to form a pulverized product; dipping and dissolving step: impregnating the pulverized product containing Ni, Co, Li, and Mn metal with hydrochloric acid immersion solution; precipitation; Separation of manganese step: adding potassium permanganate to the hydrochloric acid leaching solution; precipitating manganese into manganese oxide, which is separated from the other three elements after filtration to obtain a filtrate; step of adsorbing cobalt and nickel: adjusting the pH of the filtrate to above 4; Then use the Na + type IRC748 anion exchange resin to adsorb cobalt and nickel on the Na + type IRC748 anion exchange resin, and the lithium is left in the liquid phase in an ionic state and separated from it; the first resin desorption step: the cobalt remaining in the resin The nickel is desorbed by HCl; the nickel is separated in the liquid phase by adsorption of cobalt: adding HCl to a Cl - concentration of 8N, within the error range of 5%, so that Co is complexed to form [CoCl 4 ] 2- , using a strong base anion resin Co is adsorbed on the resin, and Ni is separated from it in the liquid phase; the second resin desorption step: adding sulfuric acid to wash the cobalt adsorbed on the resin into the water phase.
S1:前置處理步驟 S1: Pre-processing steps
S2:浸漬溶出步驟 S2: Dipping and dissolution step
S3:沈澱分離錳步驟 S3: Separation of manganese by precipitation
S4:吸附鈷鎳步驟 S4: Adsorption of cobalt and nickel step
S5:第一樹脂脫附步驟 S5: The first resin desorption step
S6:吸附鈷將鎳於液相分離步驟 S6: Adsorption of cobalt to separate nickel in the liquid phase
S7:第二樹脂脫附步驟 S7: Second resin desorption step
第一圖係本發明之方法流程圖 The first figure is the flow chart of the method of the present invention
以下藉由圖式之配合,說明本發明之構造、特點以及實施例,俾使貴審查委員 對本發明有更進一步之理解。 In the following, the structure, features and embodiments of the present invention will be explained by the coordination of the drawings, so as to make your reviewer Have a further understanding of the present invention.
一般而言,欲取出有價金屬,在資源化之處理過程,大致可分為火法冶金與濕法冶金兩種,火法(Pyrometallurgy)為將物料、還原劑與助熔劑等進行加熱熔融,使金屬成分還原或形成合金達成資源化;濕法(Hydrometallurgy)則是將物料裡的金屬成分溶於溶劑中形成溶液,再藉由離子交換、溶劑萃取及化學沉澱等的處理程序回收金屬,本發明係採取濕式。 Generally speaking, if you want to take out valuable metals, the process of resource recycling can be roughly divided into pyrometallurgy and hydrometallurgy. Pyrometallurgy is to heat and melt materials, reducing agents and fluxes to make Metal components are reduced or alloys are formed to achieve resource utilization; the hydrometallurgy method is to dissolve the metal components in the material in a solvent to form a solution, and then recover the metal through processing procedures such as ion exchange, solvent extraction, and chemical precipitation. The present invention The department adopts the wet method.
請參閱第一圖,本發明係關於一種廢棄鋰電池中回收有價金屬之方法,步驟至少包括: Please refer to the first figure. The present invention relates to a method for recovering valuable metals from waste lithium batteries. The steps at least include:
前置處理步驟(S1):將廢棄鋰電池前置處理並予以粉碎形成粉碎物;在利用濕法冶金技術回收廢棄鋰電池中有價金屬前,須先透過破碎、分選、篩選等程序(Mineral Processing)將廢棄鋰離子電池進行預處理,主要係將大部份非金屬之物質與目標金屬分離。 Pre-treatment step (S1): pre-treat the waste lithium batteries and crush them to form pulverized products; before using hydrometallurgical technology to recover valuable metals in waste lithium batteries, it must first go through crushing, sorting, screening and other procedures (Mineral Processing) The pretreatment of waste lithium-ion batteries is mainly to separate most non-metallic substances from target metals.
浸漬(Leaching)溶出步驟(S2):將含有Ni、Co、Li、Mn金屬之粉碎物以鹽酸浸液浸漬;在具體實施中鹽酸採用濃度6N,其中該浸漬溶出步驟以溫度60±5℃,攪拌轉速350±50rpm。使得四種元素均能達到99%溶出,當PH達0時,可以加NaOH調整酸鹼度達PH達2。此種浸漬手段,主要係將有價金屬在最佳反應條件下溶解至液態相中,固液分離後的液相部分則成為後續回收處理程序的進料。 Leaching dissolution step (S2): immerse the crushed material containing Ni, Co, Li, and Mn metals with hydrochloric acid immersion solution; in specific implementation, the concentration of hydrochloric acid is 6N, and the immersion dissolution step is performed at a temperature of 60±5°C, The stirring speed is 350±50rpm. So that the four elements can reach 99% dissolution, when the PH reaches 0, NaOH can be added to adjust the pH to reach 2. This impregnation method is mainly to dissolve valuable metals into the liquid phase under optimal reaction conditions, and the liquid phase after solid-liquid separation becomes the feed for the subsequent recovery process.
沈澱分離錳步驟(S3):加入過錳酸鉀於該鹽酸浸液中;將錳沈澱為氧化錳,經過濾後與其他三元素分離,得到過濾液;換言之,利用KMnO4與Mn2+離子產生氧化沉澱反應,將錳從溶液中分離,其中該沈澱分離錳步驟pH=2,並在45℃、Mn2+/KMnO4莫耳比為2.3環境,且數值誤差5%條件下為宜。 Separation of manganese by precipitation (S3): adding potassium permanganate to the hydrochloric acid leaching solution; precipitating manganese into manganese oxide, which is separated from the other three elements after filtration to obtain a filtrate; in other words, using KMnO 4 and Mn 2+ ions An oxidative precipitation reaction occurs, and manganese is separated from the solution. The pH of the precipitation and separation step of manganese is 2, and the environment should be at 45° C., Mn2+/KMnO4 molar ratio of 2.3, and a numerical error of 5%.
吸附鈷鎳步驟(S4):將過濾液調整ph至4以上;再使用Na+型IRC748陰離子交換樹脂將鈷與鎳吸附於該Na+型IRC748陰離子交換樹脂,鋰呈現離子態留在液相與之分離;按,離子交換法(Ion-exchange Process)是一具可逆性的化學反應,發生在固相與液相之間,在反應過程需維持在電中性的條件下,當液體中的離子被離子交換固體吸附後,則會釋放等價的離子於液相中,此過程也需符合熱力學及質量平衡,其優點有:(1)不同交換基團的樹脂可應用於不同的領域(2)選擇性高,有利於使用在含有多種有價金屬離子的溶液(3)操作手法較容易。 Adsorption of cobalt and nickel step (S4): adjust the pH of the filtrate to above 4; then use the Na + type IRC748 anion exchange resin to adsorb cobalt and nickel on the Na + type IRC748 anion exchange resin, and the lithium remains in the liquid phase in an ionic state. The separation; according to, the ion exchange process (Ion-exchange Process) is a reversible chemical reaction that occurs between the solid phase and the liquid phase. The reaction process needs to be maintained under electrically neutral conditions. After the ions are adsorbed by the ion exchange solid, they will release equivalent ions in the liquid phase. This process also needs to comply with thermodynamics and mass balance. Its advantages are: (1) Resins with different exchange groups can be used in different fields ( 2) High selectivity, which is beneficial to use in solutions containing a variety of valuable metal ions. (3) The operation method is easier.
第一樹脂脫附步驟(S5): 將留在樹脂中之鈷鎳以HCl進行脫附;該HCl以2N為宜。脫附主要係將吸附在樹脂上的目標金屬富集濃縮,後利用再生液使樹脂官能基回復到原先所攜帶的離子,常見的脫附劑及再生劑為HCl、H2SO4、NaCl、NaOH等溶液,脫附效果以目標金富集效果及脫附率高低進行判斷,選擇脫附率高且富集效果好者做為脫附劑,而脫附率計算為目標金屬總脫附量與樹脂吸附量之比例。 The first resin desorption step (S5): The cobalt and nickel remaining in the resin are desorbed with HCl; the HCl is preferably 2N. Desorption is mainly to enrich and concentrate the target metal adsorbed on the resin, and then use the regeneration solution to restore the resin functional groups to the original ions. Common desorption agents and regenerating agents are HCl, H 2 SO 4 , NaCl, For solutions such as NaOH, the desorption effect is judged by the target gold enrichment effect and desorption rate. Choose the desorption agent with high desorption rate and good enrichment effect as the desorption agent, and the desorption rate is calculated as the total desorption amount of the target metal The ratio of adsorption to resin.
吸附鈷將鎳於液相分離步驟(S6):加入HCl至Cl-濃度為8±1N,使Co錯合形成[CoCl4]2-,利用強鹼型陰離子樹脂將Co吸附於樹脂,Ni於液相與之分離;該強鹼型陰離子樹脂為IRA900C1。由於Co2+與Cl-形成陰離子錯合物[CoCl4]2-而Ni2+則否,故可透過陰離子交換樹脂進行吸附反應,使Co與脫附液內的Ni分離。 Adsorption of cobalt to nickel in the liquid phase separation step (S6): add HCl to a Cl - concentration of 8±1N to make Co complex to form [CoCl 4 ] 2- , use strong base anion resin to adsorb Co on the resin, and Ni in the resin The liquid phase is separated from it; the strong base anion resin is IRA900C1. Since Co 2+ and Cl - form an anion complex [CoCl 4 ] 2- but Ni 2+ does not, the adsorption reaction can be carried out through an anion exchange resin to separate Co from Ni in the desorption solution.
第二樹脂脫附步驟(S7):加入硫酸將吸附於樹脂之鈷沖洗於水相。樹脂達飽和吸附後,利用相同Cl-離子濃度的溶液將殘留進料沖出,後通入脫附劑將負載於樹脂上的金屬離子脫附富集。 The second resin desorption step (S7): adding sulfuric acid to wash the cobalt adsorbed on the resin into the water phase. After the resin reaches saturation adsorption, the residual feed is flushed out with a solution of the same Cl- ion concentration, and then a desorbent is introduced to desorb and enrich the metal ions loaded on the resin.
綜上所述,本發明確實符合產業利用性,且未於申請前見於刊物或公開使用,亦未為公眾所知悉,且具有非顯而易知性,符合可專利之要件,爰依法提出專利申請。惟上述所陳,為本發明產業上一較佳實施例,舉凡依本發明申請專利範圍所作之均等變化,皆屬本案訴求標的之範疇。 In summary, the present invention is indeed in line with industrial applicability, and has not been seen in publications or publicly used before the application, and has not been known to the public, and it is non-obvious and easy to know, and meets the requirements of patentability. Therefore, a patent application is filed in accordance with the law. . However, what has been described above is a preferred embodiment in the industry of the invention, and all the equivalent changes made in accordance with the scope of the patent application of the invention belong to the scope of the claims of this case.
S1:前置處理步驟 S1: Pre-processing steps
S2:浸漬溶出步驟 S2: Dipping and dissolution step
S3:沈澱分離錳步驟 S3: Separation of manganese by precipitation
S4:吸附鈷鎳步驟 S4: Adsorption of cobalt and nickel step
S5:第一樹脂脫附步驟 S5: The first resin desorption step
S6:吸附鈷將鎳於液相分離步驟 S6: Adsorption of cobalt to separate nickel in the liquid phase
S7:第二樹脂脫附步驟 S7: Second resin desorption step
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| TWI535479B (en) * | 2014-09-18 | 2016-06-01 | 朝陽科技大學 | Valuable metals recovering method |
| TWI625882B (en) * | 2016-11-02 | 2018-06-01 | Dayeh University | Method for recovering positive electrode material resources in waste lithium iron battery |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN119265427A (en) * | 2024-08-28 | 2025-01-07 | 中国第一汽车股份有限公司 | A method and application of recycling waste lithium batteries |
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| TW202145632A (en) | 2021-12-01 |
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