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TWM650076U - Recycling equipment for valuable metal in lithium-ion battery - Google Patents

Recycling equipment for valuable metal in lithium-ion battery Download PDF

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TWM650076U
TWM650076U TW112208652U TW112208652U TWM650076U TW M650076 U TWM650076 U TW M650076U TW 112208652 U TW112208652 U TW 112208652U TW 112208652 U TW112208652 U TW 112208652U TW M650076 U TWM650076 U TW M650076U
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aqueous solution
tank
filter residue
lithium
filtering device
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許凱捷
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三旺科技股份有限公司
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    • 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
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    • Y02P10/00Technologies related to metal processing
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Abstract

本創作係提供鋰離子電池中有價金屬之回收設備包含:鹼浸裝置、酸浸裝置、除銅裝置、除鐵裝置、鎳錳回收裝置、鈷回收裝置及鋰回收裝置。本創作之鋰離子電池中有價金屬之回收方法可以從廢棄的鋰離子電池中的正極材料之碳墨粉末中,去除鋁、銅及鐵等雜質金屬,並回收鎳、錳、鈷及鋰等有價金屬。This creation provides equipment for recycling valuable metals in lithium-ion batteries, including: alkali leaching equipment, acid leaching equipment, copper removal equipment, iron removal equipment, nickel-manganese recovery equipment, cobalt recovery equipment and lithium recovery equipment. The method for recycling valuable metals in lithium-ion batteries of this invention can remove impurity metals such as aluminum, copper and iron from the carbon ink powder of the cathode material in discarded lithium-ion batteries, and recover valuable metals such as nickel, manganese, cobalt and lithium. metal.

Description

鋰離子電池中有價金屬之回收設備Recycling equipment for valuable metals in lithium-ion batteries

本創作係有關鋰離子電池中有價金屬之回收方法及設備,特別是指去除廢棄的鋰離子電池中的鋁、銅及鐵等雜質金屬及回收鎳、錳、鈷及鋰等鋰離子電池中有價金屬之回收方法及設備。This creation is about the methods and equipment for recycling valuable metals in lithium-ion batteries, especially the removal of impurity metals such as aluminum, copper and iron from discarded lithium-ion batteries and the recovery of valuable metals such as nickel, manganese, cobalt and lithium from lithium-ion batteries. Metal recycling methods and equipment.

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。目前已知的有價金屬回收之方法有如下數種。After lithium-ion batteries were successfully introduced into the market, due to their relatively light weight, small size and long life, they are commonly 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, they can easily pollute the environment with heavy metals and even change the environment and ecology. Due to the rise in environmental awareness and the widespread attention given to environmental issues, industry or academia are also developing resource recycling technologies. There are several methods currently known for recycling valuable metals as follows.

臺灣發明專利I286850(下稱文獻1),其揭示將而鋰、鈷所在的正極部分,藉由鹽酸浸漬二小時後,以氫氧化鈉調整浸漬液之pH值至8,則此時可藉由過濾加以分離含鈷、鋁、鎳之膠凝物,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、鋁、鎳之膠凝物,先以硫酸酸洗並調整pH值為2使所含金屬溶解後,再加入氨水調整pH值為8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。換言之,文獻1是採用電解的方式取得鈷及鎳。Taiwan invention patent I286850 (hereinafter referred to as Document 1) discloses that the positive electrode part where lithium and cobalt are located is immersed in hydrochloric acid for two hours, and then the pH value of the immersion solution is adjusted to 8 with sodium hydroxide. At this time, it can be Filter to separate the gels containing cobalt, aluminum and nickel, and finally add saturated sodium carbonate solution to the impregnation solution to obtain lithium carbonate powder; in addition, filter the gels containing cobalt, aluminum and nickel, first After pickling with sulfuric acid and adjusting the pH value to 2 to dissolve the contained metal, add ammonia water to adjust the pH value to 8 to filter out the gel containing aluminum ions. Finally, use sulfuric acid to adjust the pH value of the filtered pickling solution. After adjusting to 4.3, pour it into the electrolytic tank for electrolysis recovery. Use a constant temperature water bath to keep the electrolyte temperature at 55°C. After passing a fixed current, the cobalt and nickel metal will be deposited on the cathode stainless steel sheet. After drying, the cobalt can be recovered. and nickel metal to achieve the purpose of recycling waste resources. In other words, Document 1 uses electrolysis to obtain cobalt and nickel.

臺灣發明專利第501294(下稱文獻2),其揭示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,期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。換言之,文獻2也是採用電解的方式取得鈷。Taiwan Invention Patent No. 501294 (hereinafter referred to as Document 2) discloses that used waste lithium-ion batteries are roasted and decomposed in a high-temperature furnace to remove the organic electrolyte, then crushed and sieved. The materials above the sieve can be processed by magnetic separation and eddy current separation. , separate the broken iron shell, copper foil, aluminum foil, etc.; and the material under the sieve is dissolved with a mixture of sulfuric acid and hydrogen peroxide, the solution obtained by the dissolution is filtered, and the iron in it is removed by adjusting the pH value. And aluminum ions are precipitated, during which metal copper and metal cobalt are electrolyzed respectively through electrolysis. After electrolysis, carbonate is added to the solution rich in lithium ions to form a carbonate precipitation of lithium and effectively recover lithium. In other words, Document 2 also uses electrolysis to obtain cobalt.

臺灣發明專利第511306號(下稱文獻3),其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。換言之,文獻3也是採用電解的方式取得鈷。Taiwan Invention Patent No. 511306 (hereinafter referred to as Document 3) discloses that waste lithium-ion batteries are roasted in a high-temperature furnace to decompose and remove the organic electrolyte, crushed and screened, and the materials above the screen are separated by magnetic separation and eddy current separation. The broken iron shell, copper foil, aluminum foil, etc. are removed; while the material under the sieve is directly dissolved and filtered, and through the control of pH value and electrolysis conditions, metallic copper and cobalt are electrolyzed by diaphragm electrolysis method. During the electrolysis process The acid generated on the cathode side can be recovered through diffusion dialysis treatment and recycled to the dissolution step, forming a closed process. After electrolysis of the solution rich in lithium ions, after adjusting the pH value to precipitate metal impurities, carbonate can be added to form a high-purity carbonate of lithium and the lithium can be recovered. In other words, Document 3 also uses electrolysis to obtain cobalt.

臺灣發明專利第I392745號(下稱文獻4),係限定於自三元系鋰金屬鹽與碳、N-甲基-2-吡咯烷酮,聚乙烯醇等之溶劑等所構成之漿狀物質,其是於鋰二次電池製造步驟上所產生之殘渣。漿狀物質中的金屬組成一般為10~12質量%之Co、10~12質量%之Ni、10~12質量%之Mn、4~5質量%之Li,也就是除了限定Co、Ni、Mn為等量之外,並無對鋁、銅、鐵等雜質的處理方式。文獻4揭示係以250g/l以上之濃度的鹽酸溶液,對含有鋰酸金屬鹽(含有大致等量之鈷、鎳及錳)之三元系鋰金屬鹽的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200 g/l以上之濃度的硫酸溶液與20 g/l以上之過氧化氫溶液的溶液來進行攪拌浸洗處理後,對浸洗液以特別的萃取劑進行溶劑萃取,例如DE2HPA萃取劑處理錳及PC-88A萃取劑處理鈷及鎳,以萃取出98%以上之錳、鈷及鎳三種金屬,生成含有各金屬之溶液,然後從此等之溶液與萃取後含有鋰之剩餘液體來回收錳、鈷、鎳及鋰等有價金屬。換言之,文獻4雖然不是採用文獻1至3的電解方式,但是卻無法處理鋰電池回收過程必須面對的鋁、銅、鐵等雜質金屬的處理問題,而且必須以特別的萃取劑進行溶劑萃取。Taiwan Invention Patent No. I392745 (hereinafter referred to as Document 4) is limited to a slurry composed of a ternary lithium metal salt and a solvent such as carbon, N-methyl-2-pyrrolidone, polyvinyl alcohol, etc. It is a residue produced during the manufacturing process of lithium secondary batteries. The metal composition in the slurry is generally 10~12% by mass Co, 10~12% by mass Ni, 10~12% by mass Mn, and 4~5% by mass Li. That is, in addition to limiting Co, Ni, and Mn Apart from equal amounts, there is no treatment method for impurities such as aluminum, copper, and iron. Document 4 discloses that the lithium battery residue containing the ternary lithium metal salt of lithium acid metal salt (containing approximately equal amounts of cobalt, nickel and manganese) is stirred and leached with a hydrochloric acid solution with a concentration of 250g/l or more, or Use a sulfuric acid solution with a concentration of 200g/l or more, while heating to 65~80℃ while stirring and leaching, or mix a sulfuric acid solution with a concentration of 200g/l or more and a hydrogen peroxide solution with a concentration of 20g/l or more After the solution is stirred and leached, the leaching solution is solvent extracted with a special extractant, such as DE2HPA extractant for manganese and PC-88A extractant for cobalt and nickel, to extract more than 98% of manganese and cobalt. and nickel to generate solutions containing each metal, and then recover valuable metals such as manganese, cobalt, nickel and lithium from these solutions and the remaining liquid containing lithium after extraction. In other words, although Document 4 does not use the electrolysis method of Documents 1 to 3, it cannot deal with the treatment problems of aluminum, copper, iron and other impurity metals that must be faced in the lithium battery recycling process, and must use a special extraction agent for solvent extraction.

由前述文獻1至4可以發現,文獻1至3皆採用電解方式會耗費大量的電而導致成本較高,而文獻4則使用特別的萃取劑進行溶劑萃取而會造成環保問題,且文獻4無法處理鋁、銅、鐵等雜質金屬的處理問題。From the aforementioned documents 1 to 4, it can be found that documents 1 to 3 all use electrolysis, which consumes a lot of electricity and leads to higher costs, while document 4 uses a special extraction agent for solvent extraction, which will cause environmental problems, and document 4 cannot Dealing with the treatment of impurity metals such as aluminum, copper, iron, etc.

有鑑於上述習知之問題,本創作之創作者思索並設計一種自廢棄的鋰離子電池之正極材料的碳墨粉末中回收有價金屬之方法及裝置,以期針對習知技術之缺失加以改善,進而增進產業上之實施利用。In view of the above-mentioned known problems, the creator of this creation thought about and designed a method and device for recovering valuable metals from the carbon ink powder of the cathode material of discarded lithium-ion batteries, in order to improve the deficiencies of the conventional technology and thereby promote Industrial implementation and utilization.

基於上述目的,本創作提供一種鋰離子電池中有價金屬之回收方法依序包含材料檢測步驟、鹼浸步驟、酸浸步驟、金屬置換步驟、除鐵步驟、回收鎳及錳步驟、回收鈷步驟及回收鋰步驟。Based on the above purpose, this invention provides a method for recovering valuable metals in lithium-ion batteries, which sequentially includes a material detection step, an alkali leaching step, an acid leaching step, a metal replacement step, an iron removal step, a nickel and manganese recovery step, a cobalt recovery step, and Lithium recovery step.

材料檢測步驟,係將取自廢棄的鋰離子電池中的正極材料之一碳墨粉末進行該碳墨粉末中的金屬含量分析,以取得其中的鋰、鎳、鈷、錳、鋁、銅及鐵的含量數值,該碳墨粉末中還包含有碳。The material testing step is to analyze the metal content of carbon ink powder, which is one of the positive electrode materials in discarded lithium-ion batteries, to obtain lithium, nickel, cobalt, manganese, aluminum, copper and iron. The content value of the carbon ink powder also contains carbon.

鹼浸步驟,係將一鹼性水溶液與該碳墨粉末混合後,使該碳墨粉末中的鋰、鎳、鈷、錳、銅、鐵及碳沉澱為一第一濾渣,其中鋁溶於該鹼性水溶液而為一第一水溶液,去除該第一水溶液而保留該第一濾渣。The alkali leaching step involves mixing an alkaline aqueous solution with the carbon ink powder to precipitate lithium, nickel, cobalt, manganese, copper, iron and carbon in the carbon ink powder into a first filter residue, in which aluminum is dissolved in the carbon ink powder. The alkaline aqueous solution becomes a first aqueous solution, and the first aqueous solution is removed while retaining the first filter residue.

酸浸步驟,係將一酸性水溶液與該第一濾渣混合後,使該第一濾渣中的鋰、鎳、鈷、錳、銅及鐵溶於該酸性水溶液而成為一第二水溶液,該第一濾渣中的碳則沉澱為一第二濾渣,去除該第二濾渣而保留該第二水溶液。The acid leaching step is to mix an acidic aqueous solution with the first filter residue, so that the lithium, nickel, cobalt, manganese, copper and iron in the first filter residue are dissolved in the acidic aqueous solution to form a second aqueous solution. The carbon in the filter residue precipitates as a second filter residue, and the second filter residue is removed while retaining the second aqueous solution.

金屬置換步驟,係將該第二水溶液與一外加含鐵物質混合後,該外加含鐵物質中鐵的當量數大於該第二水溶液中銅的當量數或該碳墨粉末中銅的當量數,使該第二水溶液中的硫酸銅的銅被置換成鐵而成為硫酸鐵並析出銅金屬而使該第二水溶液轉而成為一第三水溶液,所析出的該銅金屬則沉澱為一第三濾渣,去除該第三濾渣而保留該第三水溶液。The metal replacement step is to mix the second aqueous solution with an additional iron-containing substance, and the equivalent number of iron in the additional iron-containing substance is greater than the equivalent number of copper in the second aqueous solution or the equivalent number of copper in the carbon ink powder, The copper in the copper sulfate in the second aqueous solution is replaced with iron to become iron sulfate and copper metal is precipitated, so that the second aqueous solution is turned into a third aqueous solution, and the precipitated copper metal is precipitated into a third filter residue. , remove the third filter residue and retain the third aqueous solution.

除鐵步驟,係將該第三水溶液以一第一鹼性物質調整使pH值為介於4至5之間後,使該第三水溶液中的硫酸鐵的鐵與該第一鹼性物質形成一第一鹼性化合物並析出該第一鹼性化合物而使該第三水溶液轉而成為一第四水溶液,所析出的該第一鹼性化合物為鐵的化合物且沉澱為一第四濾渣,去除該第四濾渣而保留該第四水溶液;The iron removal step is to adjust the third aqueous solution with a first alkaline substance to make the pH value between 4 and 5, and then allow the iron of ferric sulfate in the third aqueous solution to form with the first alkaline substance. A first alkaline compound is precipitated and the third aqueous solution is converted into a fourth aqueous solution. The precipitated first alkaline compound is an iron compound and precipitates into a fourth filter residue, which is removed The fourth filter residue retains the fourth aqueous solution;

回收鎳及錳步驟:係將該第四水溶液以一第二鹼性物質調整使pH值為介於6至8之間並加入一碳酸鹽後,使該第四水溶液中的硫酸鎳的鎳及硫酸錳的錳與該碳酸鹽形成碳酸鎳及碳酸錳,並析出該碳酸鎳及該碳酸錳而使該第四水溶液轉而成為一第五水溶液,所析出的該碳酸鎳及該碳酸錳則沉澱為一第五濾渣,分離出該第五濾渣並保留該第五水溶液;The step of recovering nickel and manganese: the fourth aqueous solution is adjusted with a second alkaline substance to make the pH value between 6 and 8 and a carbonate is added, so that the nickel and nickel of the nickel sulfate in the fourth aqueous solution are The manganese of manganese sulfate and the carbonate form nickel carbonate and manganese carbonate, and the nickel carbonate and the manganese carbonate are precipitated, so that the fourth aqueous solution is converted into a fifth aqueous solution, and the precipitated nickel carbonate and manganese carbonate are precipitated. As a fifth filter residue, separate the fifth filter residue and retain the fifth aqueous solution;

回收鈷步驟,係將第五水溶液以一第三鹼性物質調整使pH值為介於11至13之間後,使該第五水溶液中的硫酸鈷的鈷與該第三鹼性物質形成一第三鹼性化合物並析出該第三鹼性化合物而使該第五水溶液轉而成為一第六水溶液,所析出的該第三鹼性化合物為鈷的化合物並沉澱為第六濾渣,分離出第六濾渣並保留第六水溶液;The step of recovering cobalt is to adjust the fifth aqueous solution with a third alkaline substance so that the pH value is between 11 and 13, so that the cobalt of cobalt sulfate in the fifth aqueous solution and the third alkaline substance form a The third basic compound precipitates out and turns the fifth aqueous solution into a sixth aqueous solution. The precipitated third basic compound is a cobalt compound and precipitates into the sixth filter residue, and the third basic compound is separated into a sixth filter residue. Sixth filter residue and retain the sixth aqueous solution;

回收鋰步驟,係將該第六水溶液與磷酸鹽混合後,該磷酸鹽中的磷酸根離子的當量數大於該第六水溶液中鋰的當量數或碳墨粉末中鋰的當量數,磷酸鹽與該第六水溶液中的硫酸鋰進行復分解反應,使該第六水溶液中的硫酸鋰的鋰因復分解反應而被交換成該磷酸鹽中的金屬而成為可溶於水的硫酸鹽並析出磷酸鋰而使該第六水溶液轉而成為一第七水溶液,所析出的該磷酸鋰則沉澱為一第七濾渣,去除該第七水溶液而保留該第七濾渣。The step of recovering lithium is to mix the sixth aqueous solution with phosphate. The equivalent number of phosphate ions in the phosphate is greater than the equivalent number of lithium in the sixth aqueous solution or the equivalent number of lithium in the carbon ink powder. The phosphate and The lithium sulfate in the sixth aqueous solution undergoes a metathesis reaction, so that the lithium in the lithium sulfate in the sixth aqueous solution is exchanged for the metal in the phosphate due to the metathesis reaction to become a water-soluble sulfate and precipitate phosphoric acid The sixth aqueous solution is converted into a seventh aqueous solution by adding lithium, and the precipitated lithium phosphate is precipitated into a seventh filter residue. The seventh aqueous solution is removed and the seventh filter residue is retained.

本創作還提供一種鋰離子電池中有價金屬之回收設備,用以執行前述鋰離子電池中有價金屬之回收方法,該鋰離子電池中有價金屬之回收設備其包含:鹼浸裝置、酸浸裝置、除銅裝置、除鐵裝置、鎳錳回收裝置、鈷回收裝置及鋰回收裝置。This invention also provides an equipment for recycling valuable metals in lithium-ion batteries, which is used to perform the aforementioned method of recycling valuable metals in lithium-ion batteries. The equipment for recycling valuable metals in lithium-ion batteries includes: an alkali leaching device, an acid leaching device, Copper removal device, iron removal device, nickel manganese recovery device, cobalt recovery device and lithium recovery device.

藉以,本創作先去除碳墨粉末中的鋁、銅、鐵等雜質金屬及碳,然後接著藉由收集碳酸鎳及碳酸錳、氫氧化鈷或氧化鈷、磷酸鋰,而達到分離及回收有價金屬鋰、鎳、鈷及錳的目的,因此能夠達到準確自鋰離子電池的碳墨粉末分離出有價金屬之目的,且分離過程中不使用電解,也不使用特別的萃取劑。In this way, this invention first removes impurity metals such as aluminum, copper, and iron and carbon from the carbon ink powder, and then collects nickel carbonate and manganese carbonate, cobalt hydroxide or cobalt oxide, and lithium phosphate to separate and recover valuable metals. It can accurately separate valuable metals from the carbon ink powder of lithium-ion batteries without using electrolysis or special extraction agents during the separation process.

為利瞭解本創作之技術特徵、內容與優點及其所能達成之功效,茲將本創作配合附圖之表達形式詳細說明如下,而其中所使用之圖式,其主旨僅為示意及輔助說明書之用,未必為本創作實施後之真實比例與精準配置,故不應就所附之圖式的比例與配置關係解讀、侷限本創作於實際實施上的權利範圍,合先敘明。In order to facilitate understanding of the technical features, content and advantages of this creation and the effects it can achieve, the expression form of this creation together with the accompanying drawings is described in detail below. The purpose of the drawings used therein is only to illustrate and assist the instructions. The purpose is not necessarily the true proportion and precise configuration of this creation after its implementation. Therefore, the proportion and configuration relationship of the attached drawings should not be interpreted to limit the scope of rights in the actual implementation of this creation, which is stated in advance.

請參閱圖1,本創作之鋰離子電池中有價金屬之回收方法依序包含材料檢測步驟S00、鹼浸步驟S10、酸浸步驟S20、金屬置換步驟S30、除鐵步驟S40、回收鎳及錳步驟S50、回收鈷步驟S60及回收鋰步驟S70。其中,材料檢測步驟S00、鹼浸步驟S10、酸浸步驟S20、金屬置換步驟S30及除鐵步驟S40合稱為去除雜質金屬步驟,回收鎳及錳步驟S50、回收鈷步驟S60及回收鋰步驟S70則合稱為分離有價金屬步驟。Please refer to Figure 1. The method for recovering valuable metals in lithium-ion batteries of this invention sequentially includes a material detection step S00, an alkali leaching step S10, an acid leaching step S20, a metal replacement step S30, an iron removal step S40, and a nickel and manganese recovery step. S50, cobalt recovery step S60 and lithium recovery step S70. Among them, the material detection step S00, the alkali leaching step S10, the acid leaching step S20, the metal replacement step S30 and the iron removal step S40 are collectively referred to as the impurity metal removal step, the nickel and manganese recovery step S50, the cobalt recovery step S60 and the lithium recovery step S70. It is collectively called the step of separating valuable metals.

材料檢測步驟S00:將取自廢棄的鋰離子電池中的正極材料之碳墨粉末進行碳墨粉末中的金屬含量分析,以取得其中的鋰、鎳、鈷、錳、鋁、銅及鐵的含量數值,碳墨粉末中還包含有碳。鋰離子電池拆解過程可參考前述文獻1至4,因此不在此贅述,本創作係自廢棄的鋰離子電池中的正極材料之碳墨粉末依序分離出雜質金屬及有價金屬。於本創作中,材料檢測步驟係指在得到碳墨粉末之後會先進行原子吸收光譜(Atomic absorption spectroscopy,AAS)分析,例如在一實施例中測得碳墨粉末中的鋰、鎳、鈷及錳的含量(重量百分比)分別為2.92%、4.04%、15.97%及5.12%;其餘則包含鋁、銅、鐵、鉛、鋅、鉻、鈣、鈉及鎂的含量分別為30320 ppm、15710 ppm、23940 ppm、436 ppm、3504 ppm、804 ppm、622 ppm、2641 ppm及496 ppm。因此,於本創作中,有價金屬係指鋰、鎳、鈷及錳;雜質金屬則係指鋁、銅及鐵;其餘金屬如鉛、鋅、鉻、鈣、鈉及鎂由於含量小而忽略之。換言之,材料檢測步驟係指在得到碳墨粉末之後會先進行碳墨粉末中的金屬含量分析,以取得其中的鋰、鎳、鈷、錳、鋁、銅及鐵的含量數值。當然,碳墨粉末中還包含有碳。Material testing step S00: Analyze the metal content in the carbon ink powder taken from the cathode material of the discarded lithium-ion battery to obtain the content of lithium, nickel, cobalt, manganese, aluminum, copper and iron. Numerical value, carbon ink powder also contains carbon. The lithium-ion battery disassembly process can be referred to the aforementioned documents 1 to 4, so it will not be described in detail here. This invention is to sequentially separate impurity metals and valuable metals from the carbon ink powder of the cathode material in the discarded lithium-ion battery. In this invention, the material detection step means that after obtaining the carbon ink powder, atomic absorption spectroscopy (AAS) analysis is first performed. For example, in one embodiment, lithium, nickel, cobalt and lithium in the carbon ink powder are measured. The contents of manganese (weight percentage) are 2.92%, 4.04%, 15.97% and 5.12% respectively; the remaining contents include aluminum, copper, iron, lead, zinc, chromium, calcium, sodium and magnesium, which are 30320 ppm and 15710 ppm respectively. , 23940 ppm, 436 ppm, 3504 ppm, 804 ppm, 622 ppm, 2641 ppm and 496 ppm. Therefore, in this work, valuable metals refer to lithium, nickel, cobalt and manganese; impurity metals refer to aluminum, copper and iron; other metals such as lead, zinc, chromium, calcium, sodium and magnesium are ignored due to their small content. . In other words, the material testing step means that after obtaining the carbon ink powder, the metal content in the carbon ink powder will be analyzed to obtain the content values of lithium, nickel, cobalt, manganese, aluminum, copper and iron. Of course, carbon ink powder also contains carbon.

鹼浸步驟S10:或稱為除鋁步驟,將鹼性水溶液(例如氫氧化鈉水溶液)與碳墨粉末混合後於一第一預定溫度下攪拌一第一預定時間,使碳墨粉末中的鋰、鎳、鈷、錳、銅、鐵及碳沉澱為第一濾渣,鋁溶於鹼性水溶液而為第一水溶液,去除第一水溶液而保留第一濾渣。於本創作中,鹼浸步驟係指使用鹼性物質調整溶液之pH值至大於12;較佳地,pH值為13。鹼性物質包括氫氧化鈉及氨水,較佳為氫氧化鈉,更佳地,使用濃度為重量百分比是5%、10%、15%、20%、25%、30% 的氫氧化鈉水溶液。鹼浸步驟的條件,包含使用之鹼性物質、pH值、加熱溫度、加熱時間、固體液體比例,可依碳墨粉末及/或其中各金屬之含量調整,不受理論拘束。鹼浸步驟的方程式可為Al 2O 3+ 2NaOH →2NaAlO 2+ H 2O,例如碳墨粉末中主要含有鋰、鎳、鈷、錳、鋁、銅、鐵及碳而其餘物質忽略不計,基本上為了反應完全起見,鹼性水溶液的鹼的當量數(例如氫氧根離子的莫耳數)大於鋁的當量數。於一實施例中,鹼浸步驟是使用重量為碳墨粉末的10倍且濃度為10%的氫氧化鈉水溶液與碳墨粉末混合後於預定溫度下攪拌預定時間,則碳墨粉末其中的Al 2O 3會形成NaAlO 2並溶於氫氧化鈉水溶液而為第一水溶液,其餘含有鋰、鎳、鈷、錳、銅、鐵及碳則會不溶於氫氧化鈉水溶液中而沉澱為第一濾渣。換言之,鹼浸步驟使碳墨粉末中的鋁形成鋁鹽而溶於水,而鋰、鎳、鈷、錳、銅、鐵及碳則是形成含金屬的碳粉而沉澱為第一濾渣。並且,去除第一水溶液而保留第一濾渣。 Alkali leaching step S10: Also known as the aluminum removal step, an alkaline aqueous solution (such as sodium hydroxide aqueous solution) and carbon ink powder are mixed and then stirred at a first predetermined temperature for a first predetermined time to remove lithium from the carbon ink powder. , nickel, cobalt, manganese, copper, iron and carbon precipitate as the first filter residue, aluminum dissolves in the alkaline aqueous solution and becomes the first aqueous solution, the first aqueous solution is removed and the first filter residue is retained. In this invention, the alkali leaching step refers to using alkaline substances to adjust the pH value of the solution to greater than 12; preferably, the pH value is 13. The alkaline substance includes sodium hydroxide and ammonia, preferably sodium hydroxide. More preferably, the concentration used is 5%, 10%, 15%, 20%, 25%, or 30% sodium hydroxide aqueous solution by weight. The conditions of the alkali leaching step, including the alkaline substance used, pH value, heating temperature, heating time, and solid-to-liquid ratio, can be adjusted according to the content of the carbon ink powder and/or each metal in it, and are not bound by theory. The equation of the alkali leaching step can be Al 2 O 3 + 2NaOH → 2NaAlO 2 + H 2 O. For example, the carbon ink powder mainly contains lithium, nickel, cobalt, manganese, aluminum, copper, iron and carbon and the other substances are ignored. Basically In order to complete the reaction, the equivalent number of the base of the alkaline aqueous solution (for example, the molar number of hydroxide ions) is greater than the equivalent number of aluminum. In one embodiment, the alkali leaching step is to use a sodium hydroxide aqueous solution whose weight is 10 times that of the carbon ink powder and whose concentration is 10%, and the carbon ink powder is mixed with the carbon ink powder and then stirred at a predetermined temperature for a predetermined time, then the Al in the carbon ink powder 2 O 3 will form NaAlO 2 and dissolve in the sodium hydroxide aqueous solution to become the first aqueous solution. The rest containing lithium, nickel, cobalt, manganese, copper, iron and carbon will be insoluble in the sodium hydroxide aqueous solution and precipitate into the first filter residue. . In other words, the alkali leaching step causes the aluminum in the carbon ink powder to form aluminum salts and dissolve in water, while lithium, nickel, cobalt, manganese, copper, iron and carbon form metal-containing carbon powder and precipitate as the first filter residue. And, the first aqueous solution is removed and the first filter residue is retained.

酸浸步驟S20:或稱為除碳步驟,將酸性水溶液(例如硫酸水溶液)與第一濾渣混合後於一第二預定溫度下攪拌一第二預定時間,使第一濾渣中的鋰、鎳、鈷、錳、銅及鐵溶於酸性水溶液而為第二水溶液,第一濾渣中的碳則沉澱為第二濾渣,去除第二濾渣而保留第二水溶液。於本創作中,酸浸步驟係指使用酸性物質調整溶液之pH值至小於4,較佳地,pH值為0.5。酸性物質包括硫酸、硝酸或鹽酸,較佳為硫酸,更佳為5%、10%、15%、20%、25%、30%硫酸。酸浸步驟的條件,包含使用之酸性物質、pH值、加熱溫度、加熱時間、固體液體比例,可依碳墨粉末及/或其中各金屬之含量調整,不受理論拘束。酸浸步驟的方程式可為Co/Ni/Mn/Li/Fe/Cu/C + H 2SO 4→ CoSO 4/NiSO 4/MnSO 4/Li 2SO 4/Fe 2(SO 4) 3/CuSO 4+ C,例如前述鹼浸步驟所產生的第一濾渣含有鋰、鎳、鈷、錳、銅、鐵及碳,基本上為了反應完全起見,酸性水溶液的硫酸根的當量數大於鋰、鎳、鈷、錳、銅及鐵的當量數總和。於一實施例中,酸浸步驟是使用重量為碳墨粉末的10倍且濃度為20%的硫酸水溶液與第一濾渣混合後於第二預定溫度下攪拌第二預定時間。特別說明的是,為了計量上的便利且避免第一濾渣含水而造成計量上的誤失,因此酸浸步驟是使用重量為碳墨粉末的10倍且濃度為20%的硫酸水溶液,而不是使用重量為第一濾渣的10倍且濃度為20%的硫酸水溶液。由上述鹼浸步驟的方程式可得知,原來在第一濾渣中的鋰、鎳、鈷、錳、銅及鐵,分別形成硫酸鋰、硫酸鎳、硫酸鈷、硫酸錳、硫酸銅及硫酸鐵而溶於酸性水溶液而為第二水溶液,而原來在第一濾渣中的碳則不會與硫酸反應成硫酸鹽,因而沉澱為不含鋰、鎳、鈷、錳、銅及鐵的第二濾渣,或者稱為碳渣、石墨渣。並且,去除第二濾渣而保留第二水溶液。 Acid leaching step S20: also known as the carbon removal step, the acidic aqueous solution (such as sulfuric acid aqueous solution) is mixed with the first filter residue and then stirred at a second predetermined temperature for a second predetermined time to remove lithium, nickel, Cobalt, manganese, copper and iron are dissolved in the acidic aqueous solution to form a second aqueous solution, and the carbon in the first filter residue is precipitated to become a second filter residue. The second filter residue is removed and the second aqueous solution is retained. In this invention, the acid leaching step refers to using acidic substances to adjust the pH value of the solution to less than 4, preferably, the pH value is 0.5. The acidic substance includes sulfuric acid, nitric acid or hydrochloric acid, preferably sulfuric acid, more preferably 5%, 10%, 15%, 20%, 25% or 30% sulfuric acid. The conditions of the acid leaching step, including the acidic substance used, pH value, heating temperature, heating time, and solid-to-liquid ratio, can be adjusted according to the content of the carbon ink powder and/or the metals in it, and are not bound by theory. The equation for the acid leaching step can be Co/Ni/Mn/Li/Fe/Cu/C + H 2 SO 4 → CoSO 4 /NiSO 4 /MnSO 4 /Li 2 SO 4 /Fe 2 (SO 4 ) 3 /CuSO 4 + C, for example, the first filter residue produced in the aforementioned alkali leaching step contains lithium, nickel, cobalt, manganese, copper, iron and carbon. Basically, for the sake of complete reaction, the equivalent number of sulfate in the acidic aqueous solution is greater than that of lithium, nickel, The sum of the equivalents of cobalt, manganese, copper and iron. In one embodiment, the acid leaching step involves mixing a sulfuric acid aqueous solution with a weight 10 times that of the carbon ink powder and a concentration of 20% with the first filter residue and then stirring at a second predetermined temperature for a second predetermined time. In particular, for the convenience of measurement and to avoid measurement errors caused by the water content of the first filter residue, the acid leaching step is to use a sulfuric acid aqueous solution that is 10 times the weight of the carbon ink powder and has a concentration of 20%, instead of using A sulfuric acid aqueous solution whose weight is 10 times that of the first filter residue and whose concentration is 20%. It can be known from the equation of the above alkali leaching step that the lithium, nickel, cobalt, manganese, copper and iron originally in the first filter residue form lithium sulfate, nickel sulfate, cobalt sulfate, manganese sulfate, copper sulfate and iron sulfate respectively. It dissolves in the acidic aqueous solution and becomes the second aqueous solution. The carbon originally in the first filter residue will not react with sulfuric acid to form sulfate, so it precipitates into the second filter residue that does not contain lithium, nickel, cobalt, manganese, copper and iron. It is also called carbon slag and graphite slag. And, the second filter residue is removed and the second aqueous solution is retained.

前述固體液體比例係指固體的重量與液體的重量比,固體液體比例可以為5、10、15、20其分別是指液體重量是固體重量的5倍、10倍、15倍、20倍;前述及後述加熱溫度或預定溫度可以為室溫25℃(未加熱)、60℃、70℃、80℃或90℃;前述及後述加熱時間或預定時間可以為2小時、4小時、6小時、8小時或10小時。The aforementioned solid-liquid ratio refers to the weight ratio of solid to liquid. The solid-liquid ratio can be 5, 10, 15, and 20, which means that the weight of the liquid is 5 times, 10 times, 15 times, and 20 times the weight of the solid respectively; the aforementioned The heating temperature or predetermined temperature mentioned later can be room temperature 25°C (unheated), 60°C, 70°C, 80°C or 90°C; the heating time or predetermined time mentioned later can be 2 hours, 4 hours, 6 hours, 8 hours. hours or 10 hours.

有關於前述金屬置換步驟,於本創作中,金屬置換步驟係指加入過量的其他金屬,使過量的其他金屬置換出欲得到或除去的金屬。過量的比例是指其他金屬當量數是欲得到或除去的金屬當量數的1.05倍、1.1倍、1.15倍、1.2倍、1.25倍或1.3倍。金屬置換發生反應的條件為金屬的活性序,本創作中金屬置換步驟的方程式可為3CuSO 4+ 2Fe → Fe 2(SO 4) 3+ 3Cu。 Regarding the aforementioned metal replacement step, in this invention, the metal replacement step refers to adding excess other metals so that the excess other metals replace the metal to be obtained or removed. The excess ratio means that the number of other metal equivalents is 1.05 times, 1.1 times, 1.15 times, 1.2 times, 1.25 times or 1.3 times the number of metal equivalents to be obtained or removed. The condition for the metal replacement reaction to occur is the active order of the metal. The equation of the metal replacement step in this creation can be 3CuSO 4 + 2Fe → Fe 2 (SO 4 ) 3 + 3Cu.

金屬置換步驟S30:或稱為除銅步驟,係將第二水溶液與外加含鐵物質(例如鐵粉)混合後於一第三預定溫度下攪拌一第三預定時間,該外加含鐵物質(鐵粉)中鐵的當量數大於第二水溶液中銅的當量數或碳墨粉末中銅的當量數,使第二水溶液中的硫酸銅的銅被置換成鐵而成為硫酸鐵並析出銅金屬而使第二水溶液轉而成為第三水溶液,所析出的銅金屬則沉澱為第三濾渣,去除第三濾渣而保留第三水溶液。於本創作中,金屬置換步驟係指使第二水溶液之pH值小於4(例如添加酸性物質硫酸)並將第二水溶液與外加含鐵物質(例如鐵粉)混合。金屬置換步驟的方程式可為3CuSO 4+ 2Fe → Fe 2(SO 4) 3+ 3Cu,於一實施例中,金屬置換步驟是將第二水溶液與鐵粉混合,其中鐵粉中鐵的當量數是第二水溶液中銅的當量數或碳墨粉末中銅的當量數的1.2倍。由上述金屬置換步驟的方程式可得知,在pH值小於4的條件下,原來在第二水溶液中的硫酸銅的銅被置換成鐵而成為硫酸鐵並析出銅金屬而成為第三水溶液,所析出的銅金屬則沉澱為第三濾渣。接著去除第三濾渣而保留第三水溶液,因此第三水溶液中包含硫酸鋰、硫酸鎳、硫酸鈷、硫酸錳及硫酸鐵,而原來在第二水溶液中的硫酸銅的銅則被析出為第三濾渣。 Metal replacement step S30: also known as the copper removal step, the second aqueous solution is mixed with an additional iron-containing substance (such as iron powder) and then stirred at a third predetermined temperature for a third predetermined time. The additional iron-containing substance (iron powder) The equivalent number of iron in the second aqueous solution or the carbon ink powder is greater than the equivalent number of copper in the second aqueous solution or the equivalent number of copper in the carbon ink powder, so that the copper in the copper sulfate in the second aqueous solution is replaced with iron to become iron sulfate and copper metal is precipitated. The second aqueous solution turns into the third aqueous solution, and the precipitated copper metal precipitates into the third filter residue. The third filter residue is removed and the third aqueous solution is retained. In this invention, the metal replacement step refers to making the pH value of the second aqueous solution less than 4 (for example, adding an acidic substance such as sulfuric acid) and mixing the second aqueous solution with an additional iron-containing substance (for example, iron powder). The equation of the metal replacement step can be 3CuSO 4 + 2Fe → Fe 2 (SO 4 ) 3 + 3Cu. In one embodiment, the metal replacement step is to mix the second aqueous solution and iron powder, where the equivalent number of iron in the iron powder is The equivalent number of copper in the second aqueous solution or the equivalent number of copper in the carbon ink powder is 1.2 times. It can be known from the equation of the above metal replacement step that under the condition that the pH value is less than 4, the copper in the copper sulfate originally in the second aqueous solution is replaced with iron to become iron sulfate and copper metal precipitates to become the third aqueous solution, so The precipitated copper metal precipitates as the third filter residue. Then the third filter residue is removed and the third aqueous solution is retained. Therefore, the third aqueous solution contains lithium sulfate, nickel sulfate, cobalt sulfate, manganese sulfate and iron sulfate, and the copper of copper sulfate originally in the second aqueous solution is precipitated as the third aqueous solution. Filter residue.

有關於前述除鐵步驟、回收鎳及錳步驟、回收鈷步驟,於本創作中係指調整pH值後,金屬在不同pH值環境下沉澱。本創作包含除鐵步驟、回收鎳及錳步驟及回收鈷步驟,除鐵步驟、回收鎳及錳步驟、回收鈷步驟的方程式分別可為Fe 2(SO 4) 3+ 6NaOH → 2Fe(OH) 3+ 3Na 2SO 4、NiSO 4+ Na 2CO 3→ NiCO 3+ Na 2SO 4、MnSO 4+ Na 2CO 3→ MnCO 3+ Na 2SO 4及CoSO 4 +NaOH → Co(OH) 2+ Na 2SO 4Regarding the aforementioned iron removal step, nickel and manganese recovery step, and cobalt recovery step, in this creation, it refers to the precipitation of metals in environments with different pH values after adjusting the pH value. This creation includes an iron removal step, a nickel and manganese recovery step, and a cobalt recovery step. The equations of the iron removal step, the nickel and manganese recovery step, and the cobalt recovery step can respectively be Fe 2 (SO 4 ) 3 + 6NaOH → 2Fe(OH) 3 + 3Na 2 SO 4 , NiSO 4 + Na 2 CO 3 → NiCO 3 + Na 2 SO 4 , MnSO 4 + Na 2 CO 3 → MnCO 3 + Na 2 SO 4 and CoSO 4 + NaOH → Co(OH) 2 + Na 2 SO 4 .

除鐵步驟S40:係將第三水溶液以第一鹼性物質(例如氫氧化鈉)調整使pH值為介於4至5之間(較佳地,pH值為4.5)後於一第四預定溫度下攪拌一第四預定時間,使第三水溶液中的硫酸鐵的鐵與第一鹼性物質形成第一鹼性化合物(例如氫氧化鐵)並析出第一鹼性化合物(例如氫氧化鐵)而使第三水溶液轉而成為第四水溶液,所析出的第一鹼性化合物為鐵的化合物(例如氫氧化鐵)則沉澱為第四濾渣,去除第四濾渣而保留第四水溶液。除鐵步驟的方程式可為Fe 2(SO 4) 3+ 6NaOH → 2Fe(OH) 3+ 3Na 2SO 4。由上述除鐵步驟的方程式可得知,在pH值為介於4至5之間的條件下,於一實施例中,第一鹼性物質是氫氧化鈉,原來在第三水溶液中的硫酸鐵的鐵與氫氧根離子形成氫氧化鐵並析出氫氧化鐵沉澱物(第四濾渣),而使第三水溶液轉而成為第四水溶液,去除第四濾渣而保留第四水溶液,因此第四水溶液中包含硫酸鋰、硫酸鎳、硫酸鈷及硫酸錳,而原來在第三水溶液中的硫酸鐵的鐵則被析出為氫氧化鐵沉澱物(第四濾渣)。 Iron removal step S40: The third aqueous solution is adjusted with a first alkaline substance (such as sodium hydroxide) so that the pH value is between 4 and 5 (preferably, the pH value is 4.5), and then a fourth predetermined step is performed. Stirring for a fourth predetermined time at high temperature, so that the iron of ferric sulfate in the third aqueous solution and the first alkaline substance form a first alkaline compound (such as iron hydroxide) and precipitate the first alkaline compound (such as iron hydroxide) The third aqueous solution is turned into the fourth aqueous solution, and the precipitated first basic compound is an iron compound (such as ferric hydroxide), which precipitates into the fourth filter residue. The fourth filter residue is removed and the fourth aqueous solution is retained. The equation for the iron removal step may be Fe 2 (SO 4 ) 3 + 6NaOH → 2Fe(OH) 3 + 3Na 2 SO 4 . It can be known from the equation of the above iron removal step that under the condition that the pH value is between 4 and 5, in one embodiment, the first alkaline substance is sodium hydroxide, and the original sulfuric acid in the third aqueous solution The iron and hydroxide ions of the iron form iron hydroxide and precipitate the iron hydroxide precipitate (the fourth filter residue), so that the third aqueous solution turns into the fourth aqueous solution, the fourth filter residue is removed and the fourth aqueous solution is retained, so the fourth aqueous solution is The aqueous solution contains lithium sulfate, nickel sulfate, cobalt sulfate and manganese sulfate, and the iron of ferric sulfate originally in the third aqueous solution is precipitated as iron hydroxide precipitate (the fourth filter residue).

回收鎳及錳步驟S50:係將第四水溶液以第二鹼性物質(例如氫氧化鈉)調整使pH值為介於6至8之間(較佳地,pH值為7)並加入碳酸鹽(例如碳酸鈉)後於一第五預定溫度下攪拌一第五預定時間,使第四水溶液中的硫酸鎳的鎳及硫酸錳的錳與碳酸鹽形成碳酸鎳及碳酸錳,並析出碳酸鎳及碳酸錳而使第四水溶液轉而成為第五水溶液,所析出的碳酸鎳及碳酸錳則沉澱為第五濾渣,分離出第五濾渣並保留第五水溶液。回收鎳及錳步驟的方程式可為NiSO 4+ Na 2CO 3→ NiCO 3+ Na 2SO 4、MnSO 4+ Na 2CO 3→ MnCO 3+ Na 2SO 4。由上述回收鎳及錳步驟的方程式可得知,在pH值為介於6至8之間的條件下,於一實施例中,碳酸鹽是碳酸鈉,原來在第四水溶液中的硫酸鎳的鎳及硫酸錳的錳與碳酸鹽形成碳酸鎳及碳酸錳,並析出碳酸鎳及碳酸錳而使第四水溶液轉而成為第五水溶液,所析出的碳酸鎳及碳酸錳則沉澱為第五濾渣,分離出第五濾渣並保留第五水溶液,因此第五水溶液中包含硫酸鋰及硫酸鈷。 Recovering nickel and manganese step S50: adjust the fourth aqueous solution with a second alkaline substance (such as sodium hydroxide) to make the pH value between 6 and 8 (preferably, the pH value is 7) and add carbonate (such as sodium carbonate) and then stirred at a fifth predetermined temperature for a fifth predetermined time, so that the nickel of nickel sulfate and the manganese of manganese sulfate in the fourth aqueous solution form nickel carbonate and manganese carbonate, and nickel carbonate and manganese carbonate are precipitated. Manganese carbonate turns the fourth aqueous solution into the fifth aqueous solution, and the precipitated nickel carbonate and manganese carbonate precipitate into the fifth filter residue. The fifth filter residue is separated and the fifth aqueous solution is retained. The equations of the nickel and manganese recovery steps can be NiSO 4 + Na 2 CO 3 → NiCO 3 + Na 2 SO 4 , MnSO 4 + Na 2 CO 3 → MnCO 3 + Na 2 SO 4 . It can be known from the equation of the above step of recovering nickel and manganese that under the condition that the pH value is between 6 and 8, in one embodiment, the carbonate is sodium carbonate, and the original nickel sulfate in the fourth aqueous solution is The manganese and carbonate of nickel and manganese sulfate form nickel carbonate and manganese carbonate, and nickel carbonate and manganese carbonate are precipitated, turning the fourth aqueous solution into the fifth aqueous solution, and the precipitated nickel carbonate and manganese carbonate are precipitated into the fifth filter residue. The fifth filter residue is separated and the fifth aqueous solution is retained, so the fifth aqueous solution contains lithium sulfate and cobalt sulfate.

回收鈷步驟S60:係將第五水溶液以鹼性物質(例如氫氧化鈉)調整使pH值為介於11至13之間(較佳地,pH值為12)後於一第六預定溫度下攪拌一第六預定時間,使第五水溶液中的硫酸鈷的鈷與鹼性物質形成形成鹼性化合物(例如氫氧化鈷)並析出鹼性化合物(例如氫氧化鈷)而使第五水溶液轉而成為第六水溶液,所析出的鹼性化合物為鈷的化合物(例如氫氧化鈷)並沉澱為第六濾渣,分離出第六濾渣並保留第六水溶液。回收鈷步驟的方程式可為CoSO 4 +NaOH → Co(OH) 2+ Na 2SO 4。由上述回收鈷步驟的方程式可得知,在pH值為介於11至13之間的條件下,於一實施例中,鹼性物質是氫氧化鈉,原來在第五水溶液中的硫酸鈷的鈷與氫氧根離子形成氫氧化鈷並析出氫氧化鈷沉澱物(第六濾渣),而使第五水溶液轉而成為第六水溶液,分離出第六濾渣並保留第六水溶液,因此第六水溶液包含中包含硫酸鋰,而原來在第五水溶液中的硫酸鈷的鈷則被析出為氫氧化鈷沉澱物(第六濾渣)。當然,也可以將氫氧化鈷沉澱物(第六濾渣)加熱烘乾而轉變成氧化鈷。 Cobalt recovery step S60: The fifth aqueous solution is adjusted with an alkaline substance (such as sodium hydroxide) so that the pH value is between 11 and 13 (preferably, the pH value is 12) and then heated at a sixth predetermined temperature. Stir for a sixth predetermined time, so that the cobalt of cobalt sulfate in the fifth aqueous solution and the alkaline substance form an alkaline compound (such as cobalt hydroxide) and precipitate the alkaline compound (such as cobalt hydroxide), so that the fifth aqueous solution is turned It becomes the sixth aqueous solution, and the precipitated basic compound is a cobalt compound (such as cobalt hydroxide) and precipitates into the sixth filter residue. The sixth filter residue is separated and the sixth aqueous solution is retained. The equation for the cobalt recovery step can be CoSO 4 + NaOH → Co(OH) 2 + Na 2 SO 4 . It can be known from the equation of the above cobalt recovery step that under the condition that the pH value is between 11 and 13, in one embodiment, the alkaline substance is sodium hydroxide, and the original cobalt sulfate in the fifth aqueous solution is Cobalt and hydroxide ions form cobalt hydroxide and precipitate cobalt hydroxide precipitate (sixth filter residue), turning the fifth aqueous solution into the sixth aqueous solution, separating the sixth filter residue and retaining the sixth aqueous solution, so the sixth aqueous solution The content contains lithium sulfate, and the cobalt sulfate originally in the fifth aqueous solution is precipitated as cobalt hydroxide precipitate (sixth filter residue). Of course, the cobalt hydroxide precipitate (sixth filter residue) can also be heated and dried to transform into cobalt oxide.

回收鋰步驟S70:係將第六水溶液與磷酸鹽(例如磷酸鈉)混合後於一第七預定溫度下攪拌一第七預定時間,該磷酸鹽(例如磷酸鈉)中磷酸根離子的當量數大於第六水溶液中鋰的當量數或碳墨粉末中鋰的當量數,磷酸鹽與該第六水溶液中的硫酸鋰進行復分解反應,使第六水溶液中的硫酸鋰的鋰因復分解反應而被交換成磷酸鹽(例如磷酸鈉)中的金屬(例如鈉)而成為可溶於水的硫酸鹽(例如硫酸鈉)並析出磷酸鋰而使第六水溶液轉而成為第七水溶液,所析出的磷酸鋰則沉澱為第七濾渣,去除第七水溶液而保留第七濾渣。於本創作中,回收鋰步驟係指將第六水溶液與磷酸鹽(例如磷酸鈉)混合。回收鋰步驟的方程式可為3Li 2SO 4+ 2Na 3PO 4→ 2Li 3PO 4+ 3Na 2SO 4,於一實施例中,回收鋰步驟是將第六水溶液與磷酸鈉混合,其中磷酸鈉中磷酸根離子的當量數是第六水溶液中鋰的當量數或碳墨粉末中鋰的當量數的1.2倍。由上述回收鋰步驟的方程式可得知,原來第六水溶液中的硫酸鋰的鋰被交換成磷酸鈉中的鈉而成為可溶於水的硫酸鈉並析出磷酸鋰而使第六水溶液轉而成為第七水溶液,所析出的磷酸鋰則沉澱為第七濾渣,去除第七水溶液而保留第七濾渣。 Lithium recovery step S70: The sixth aqueous solution is mixed with a phosphate (such as sodium phosphate) and then stirred at a seventh predetermined temperature for a seventh predetermined time. The equivalent number of phosphate ions in the phosphate (such as sodium phosphate) is greater than The equivalent number of lithium in the sixth aqueous solution or the equivalent number of lithium in the carbon ink powder, the phosphate carries out a metathesis reaction with the lithium sulfate in the sixth aqueous solution, so that the lithium of the lithium sulfate in the sixth aqueous solution is decomposed due to the metathesis reaction. Exchange the metal (such as sodium) in the phosphate (such as sodium phosphate) to become a water-soluble sulfate (such as sodium sulfate) and precipitate lithium phosphate, turning the sixth aqueous solution into the seventh aqueous solution, and the precipitated phosphoric acid Lithium is precipitated as the seventh filter residue, and the seventh aqueous solution is removed while the seventh filter residue is retained. In this invention, the step of recovering lithium refers to mixing the sixth aqueous solution with phosphate (such as sodium phosphate). The equation of the lithium recovery step can be 3Li 2 SO 4 + 2Na 3 PO 4 → 2Li 3 PO 4 + 3Na 2 SO 4 . In one embodiment, the lithium recovery step is to mix the sixth aqueous solution with sodium phosphate, wherein sodium phosphate is The equivalent number of phosphate ions is 1.2 times the equivalent number of lithium in the sixth aqueous solution or the equivalent number of lithium in the carbon ink powder. It can be known from the above equation of the lithium recovery step that the lithium of the lithium sulfate in the sixth aqueous solution is exchanged for the sodium in the sodium phosphate to become water-soluble sodium sulfate and lithium phosphate is precipitated, causing the sixth aqueous solution to become In the seventh aqueous solution, the precipitated lithium phosphate is precipitated as the seventh filter residue. The seventh aqueous solution is removed and the seventh filter residue is retained.

因此,本創作先去除碳墨粉末中的鋁、銅、鐵等雜質金屬及碳,然後接著藉由收集第五濾渣的碳酸鎳及碳酸錳、第六濾渣的氫氧化鈷或氧化鈷、第七濾渣的磷酸鋰,而達到分離及回收有價金屬鋰、鎳、鈷及錳的目的。Therefore, this invention first removes aluminum, copper, iron and other impurity metals and carbon in the carbon ink powder, and then collects the nickel carbonate and manganese carbonate of the fifth filter residue, the cobalt hydroxide or cobalt oxide of the sixth filter residue, and the seventh filter residue. Lithium phosphate in the filter residue is used to separate and recover valuable metals lithium, nickel, cobalt and manganese.

本創作還提供一種鋰離子電池中有價金屬之回收設備,用以執行前述鋰離子電池中有價金屬之回收方法。This invention also provides a device for recycling valuable metals in lithium-ion batteries, which is used to perform the aforementioned method of recycling valuable metals in lithium-ion batteries.

請一併參閱圖2,鋰離子電池中有價金屬之回收設備100,其包含:鹼浸裝置1、酸浸裝置2、除銅裝置3、除鐵裝置4、鎳錳回收裝置5、鈷回收裝置6及鋰回收裝置7。Please refer to Figure 2 together, the valuable metal recovery equipment 100 in lithium-ion batteries includes: alkali leaching device 1, acid leaching device 2, copper removal device 3, iron removal device 4, nickel manganese recovery device 5, cobalt recovery device 6 and lithium recovery device 7.

鹼浸裝置1,包含鹼浸槽11、設置於鹼浸槽11內的第一攪拌裝置12、以管路系統P連通鹼浸槽11底部的第一過濾裝置13、以管路系統P連通第一過濾裝置13的鋁鹽槽14。鹼浸裝置1是用以實施鹼浸步驟S10,於鹼浸槽11內使用重量為碳墨粉末的10倍且濃度為10%的氫氧化鈉水溶液與碳墨粉末混合後,第一預定溫度為80℃下以第一攪拌裝置12進行攪拌第一預定時間為4小時以形成第一水溶液及第一濾渣,反應結束後打開鹼浸槽11底部的管路系統P將鹼浸槽11中的第一水溶液及第一濾渣輸送至第一過濾裝置13,第一過濾裝置13將第一水溶液及第一濾渣分離,並使第一水溶液儲存於鋁鹽槽14。其中,秤取碳墨粉末為1000Kg(公斤),並依前述材料檢測步驟S00中的原子吸收光譜分析結果換算得到碳墨粉末其中鋰為29.2Kg、鎳為40.4Kg、鈷為159.7Kg及錳為51.2Kg。The alkali leaching device 1 includes an alkali leaching tank 11, a first stirring device 12 disposed in the alkali leaching tank 11, a first filtering device 13 connected to the bottom of the alkali leaching tank 11 by a pipeline system P, and a first filtering device 13 connected to the bottom of the alkali leaching tank 11 by a pipeline system P. An aluminum salt tank 14 with a filtering device 13 . The alkali leaching device 1 is used to implement the alkali leaching step S10. After mixing the sodium hydroxide aqueous solution with a weight of 10 times that of the carbon ink powder and a concentration of 10% with the carbon ink powder in the alkali leaching tank 11, the first predetermined temperature is The first stirring device 12 is used to stir at 80° C. for a first predetermined time of 4 hours to form the first aqueous solution and the first filter residue. After the reaction is completed, the pipeline system P at the bottom of the alkali leaching tank 11 is opened and the first aqueous solution in the alkali leaching tank 11 is An aqueous solution and the first filter residue are transported to the first filtering device 13 . The first filtering device 13 separates the first aqueous solution and the first filter residue, and stores the first aqueous solution in the aluminum salt tank 14 . Among them, the carbon ink powder is weighed to be 1000Kg (kg), and converted according to the atomic absorption spectrometry analysis results in the aforementioned material testing step S00 to obtain the carbon ink powder, in which lithium is 29.2Kg, nickel is 40.4Kg, cobalt is 159.7Kg and manganese is 51.2Kg.

酸浸裝置2,包含以管路系統P連接第一過濾裝置13以承接第一濾渣的酸浸槽21、設置於酸浸槽21內的第二攪拌裝置22、以管路系統P連通酸浸槽21底部的第二過濾裝置23。酸浸裝置2是用以實施酸浸步驟S20,於酸浸槽21內使用重量為碳墨粉末的10倍且濃度為20%的硫酸水溶液與第一濾渣混合後,第二預定溫度為80℃下以第二攪拌裝置22進行攪拌第二預定時間為8小時以形成第二水溶液及第二濾渣,反應結束後打開酸浸槽21底部的管路系統P將酸浸槽21中的第二水溶液及第二濾渣輸送至第二過濾裝置23,第二過濾裝置23將第二水溶液及第二濾渣分離。The acid leaching device 2 includes an acid leaching tank 21 connected to the first filtering device 13 by a pipeline system P to receive the first filter residue, a second stirring device 22 disposed in the acid leaching tank 21, and an acid leaching tank 22 connected to the first filtering device 13 by the pipeline system P. The second filter device 23 at the bottom of the tank 21. The acid leaching device 2 is used to implement the acid leaching step S20. After using a sulfuric acid aqueous solution that is 10 times the weight of the carbon ink powder and has a concentration of 20% and the first filter residue in the acid leaching tank 21, the second predetermined temperature is 80°C. Next, the second stirring device 22 is used to stir for a second predetermined time of 8 hours to form the second aqueous solution and the second filter residue. After the reaction is completed, the pipeline system P at the bottom of the acid leaching tank 21 is opened and the second aqueous solution in the acid leaching tank 21 is and the second filter residue is transported to the second filtering device 23, and the second filter device 23 separates the second aqueous solution and the second filter residue.

除銅裝置3,包含以管路系統P連接第二過濾裝置23以承接第二水溶液的除銅槽31、設置於除銅槽31內的第三攪拌裝置32、以管路系統P連通除銅槽31底部的第三過濾裝置33。除銅裝置3是用以實施金屬置換步驟S30,在除銅槽31內使第二水溶液pH值小於4並與鐵粉混合,其中鐵粉中鐵的當量數是第二水溶液中銅的當量數或碳墨粉末中銅的當量數的1.2倍,第三預定溫度為室溫下以第三攪拌裝置32進行攪拌第三預定時間為4小時以形成第三水溶液及第三濾渣,反應結束後打開除銅槽31底部的管路系統P將除銅槽31中的第三水溶液及第三濾渣輸送至第三過濾裝置33,第三過濾裝置33將第三水溶液及第三濾渣分離。The copper removal device 3 includes a copper removal tank 31 connected to the second filtration device 23 via a piping system P to receive the second aqueous solution, a third stirring device 32 disposed in the copper removal tank 31, and a copper removal tank 32 connected to the piping system P. The third filter device 33 at the bottom of the tank 31. The copper removal device 3 is used to implement the metal replacement step S30, making the pH value of the second aqueous solution less than 4 in the copper removal tank 31 and mixing it with iron powder, where the equivalent number of iron in the iron powder is the equivalent number of copper in the second aqueous solution Or 1.2 times the equivalent number of copper in the carbon ink powder, the third predetermined temperature is room temperature and the third predetermined time is 4 hours for stirring with the third stirring device 32 to form the third aqueous solution and the third filter residue. After the reaction is completed, open The pipeline system P at the bottom of the copper removal tank 31 transports the third aqueous solution and the third filter residue in the copper removal tank 31 to the third filtering device 33, and the third filtering device 33 separates the third aqueous solution and the third filter residue.

除鐵裝置4,包含以管路系統P連接第三過濾裝置33以承接第三水溶液的除鐵槽41、設置於除鐵槽41內的第四攪拌裝置42、以管路系統P連通除鐵槽41底部的第四過濾裝置43。除鐵裝置4是用以實施除鐵步驟S40,在除鐵槽41內使用氫氧化鈉使第三水溶液pH值為4.5,第四預定溫度為室溫下以第四攪拌裝置42進行攪拌第四預定時間為4小時以形成第四水溶液及第四濾渣,反應結束後打開除鐵槽41底部的管路系統P將除鐵槽41中的第四水溶液及第四濾渣輸送至第四過濾裝置43,第四過濾裝置43將第四水溶液及第四濾渣分離。The iron removal device 4 includes an iron removal tank 41 connected to the third filtering device 33 via a pipeline system P to receive the third aqueous solution, a fourth stirring device 42 disposed in the iron removal tank 41, and a pipeline system P connected to the iron removal tank 41. The fourth filter device 43 at the bottom of the tank 41. The iron removal device 4 is used to implement the iron removal step S40. Sodium hydroxide is used in the iron removal tank 41 to make the pH value of the third aqueous solution 4.5. The fourth predetermined temperature is room temperature and the fourth stirring device 42 is used to stir the fourth step. The predetermined time is 4 hours to form the fourth aqueous solution and the fourth filter residue. After the reaction is completed, the pipeline system P at the bottom of the iron removal tank 41 is opened to transport the fourth aqueous solution and the fourth filter residue in the iron removal tank 41 to the fourth filtering device 43 , the fourth filtering device 43 separates the fourth aqueous solution and the fourth filter residue.

鎳錳回收裝置5,包含以管路系統P連接第四過濾裝置43以承接第四水溶液的鎳錳回收槽51、設置於鎳錳回收槽51內的第五攪拌裝置52、以管路系統P連通鎳錳回收槽51底部的第五過濾裝置53。鎳錳回收裝置5是用以實施回收鎳及錳步驟S50,在鎳錳回收槽51內使用氫氧化鈉使第四水溶液pH值為7,第五預定溫度為80℃下以第五攪拌裝置52進行攪拌第五預定時間為4小時以形成第五水溶液及第五濾渣,反應結束後打開鎳錳回收槽51底部的管路系統P將鎳錳回收槽51中的第五水溶液及第五濾渣輸送至第五過濾裝置53,第五過濾裝置53將第五水溶液及第五濾渣分離。第五濾渣為碳酸鎳及碳酸錳,其濾渣之重量為180.3Kg,經原子吸收光譜分析計算後得鎳為38.58Kg與錳為48.9Kg,再除以碳墨粉末的鎳與錳的含量(鎳為40.4Kg及錳為51.2Kg),得到鎳及錳的回收率為96%。The nickel-manganese recovery device 5 includes a nickel-manganese recovery tank 51 connected to the fourth filtering device 43 with a piping system P to receive the fourth aqueous solution, a fifth stirring device 52 disposed in the nickel-manganese recovery tank 51, and a nickel-manganese recovery tank 52 with a piping system P. It is connected to the fifth filtering device 53 at the bottom of the nickel-manganese recovery tank 51 . The nickel-manganese recovery device 5 is used to implement the step S50 of recovering nickel and manganese. Sodium hydroxide is used in the nickel-manganese recovery tank 51 to make the pH value of the fourth aqueous solution 7, and the fifth predetermined temperature is 80°C with the fifth stirring device 52 Stir for a fifth predetermined time of 4 hours to form a fifth aqueous solution and a fifth filter residue. After the reaction, open the pipeline system P at the bottom of the nickel-manganese recovery tank 51 to transport the fifth aqueous solution and the fifth filter residue in the nickel-manganese recovery tank 51 to the fifth filtering device 53, which separates the fifth aqueous solution and the fifth filter residue. The fifth filter residue is nickel carbonate and manganese carbonate. The weight of the filter residue is 180.3Kg. After calculation by atomic absorption spectrometry analysis, the nickel is 38.58Kg and the manganese is 48.9Kg. Then divided by the nickel and manganese content of the carbon ink powder (nickel (40.4Kg and 51.2Kg for manganese), and the recovery rate of nickel and manganese was 96%.

鈷回收裝置6,包含以管路系統P連接第五過濾裝置53以承接第五水溶液的鈷回收槽61、設置於鈷回收槽61內的第六攪拌裝置62、以管路系統P連通鈷回收槽61底部的第六過濾裝置63。鈷回收裝置6是用以實施回收鈷步驟S60,在鈷回收槽61內使用氫氧化鈉使第五水溶液pH值為12,第六預定溫度為80℃下以第六攪拌裝置62進行攪拌第六預定時間為8小時以形成第六水溶液及第六濾渣,反應結束後打開鈷回收槽61底部的管路系統P將鈷回收槽61中的第六水溶液及第六濾渣輸送至第六過濾裝置63,第六過濾裝置63將第六水溶液及第六濾渣分離。第六濾渣為氫氧化鈷,其濾渣之重量為240.55Kg,經原子吸收光譜分析計算鈷為152.5Kg,再除以碳墨粉末的鈷的含量159.7Kg,得到鈷的回收率為95%The cobalt recovery device 6 includes a cobalt recovery tank 61 connected to the fifth filtering device 53 via a pipeline system P to receive the fifth aqueous solution, a sixth stirring device 62 disposed in the cobalt recovery tank 61, and a cobalt recovery tank 62 connected to the fifth filtering device 53 via a pipeline system P. The sixth filter device 63 at the bottom of the tank 61. The cobalt recovery device 6 is used to implement the cobalt recovery step S60, using sodium hydroxide in the cobalt recovery tank 61 to make the pH value of the fifth aqueous solution 12, and stirring the sixth predetermined temperature with the sixth stirring device 62 at 80°C. The predetermined time is 8 hours to form the sixth aqueous solution and the sixth filter residue. After the reaction is completed, the pipeline system P at the bottom of the cobalt recovery tank 61 is opened to transport the sixth aqueous solution and the sixth filter residue in the cobalt recovery tank 61 to the sixth filtering device 63 , the sixth filtering device 63 separates the sixth aqueous solution and the sixth filter residue. The sixth filter residue is cobalt hydroxide. The weight of the filter residue is 240.55Kg. According to atomic absorption spectrometry analysis, the cobalt is 152.5Kg. Then divided by the cobalt content of the carbon ink powder, 159.7Kg, the recovery rate of cobalt is 95%.

鋰回收裝置7,包含以管路系統P連接第六過濾裝置63以承接第六水溶液的鋰回收槽71、設置於鋰回收槽71內的第七攪拌裝置72、以管路系統P連通鋰回收槽71底部的第七過濾裝置73。鋰回收裝置7是用以實施回收鋰步驟S70,在鋰回收槽71內使第六水溶液與磷酸鈉混合後,其中磷酸鈉中磷酸根離子的當量數是第六水溶液中鋰的當量數或碳墨粉末中鋰的當量數的1.2倍,第七預定溫度為70℃下以第七攪拌裝置72進行攪拌第七預定時間為4小時以形成第七水溶液及第七濾渣,反應結束後打開除鋰回收槽71底部的管路系統P將鋰回收槽71中的第七水溶液及第七濾渣輸送至第七過濾裝置73,第七過濾裝置73將第七水溶液及第七濾渣分離。第七濾渣為磷酸鋰,其濾渣之重量為155.1Kg,經原子吸收光譜分析計算鋰的含量為27.9Kg,再除以碳墨粉末的鋰的含量29.2Kg,得到鋰的回收率為96%The lithium recovery device 7 includes a lithium recovery tank 71 connected to the sixth filtering device 63 by a pipeline system P to receive the sixth aqueous solution, a seventh stirring device 72 disposed in the lithium recovery tank 71, and a lithium recovery tank 72 connected to the sixth filtering device 63 by the pipeline system P. The seventh filter device 73 at the bottom of the tank 71 . The lithium recovery device 7 is used to implement the lithium recovery step S70. After the sixth aqueous solution and sodium phosphate are mixed in the lithium recovery tank 71, the equivalent number of phosphate ions in the sodium phosphate is the equivalent number of lithium or carbon in the sixth aqueous solution. 1.2 times the equivalent number of lithium in the ink powder. The seventh predetermined temperature is 70°C and the seventh stirring device 72 is used to stir the seventh predetermined time for 4 hours to form the seventh aqueous solution and the seventh filter residue. After the reaction is completed, the lithium removal is opened. The pipeline system P at the bottom of the recovery tank 71 transports the seventh aqueous solution and the seventh filter residue in the lithium recovery tank 71 to the seventh filtering device 73, and the seventh filtering device 73 separates the seventh aqueous solution and the seventh filter residue. The seventh filter residue is lithium phosphate. The weight of the filter residue is 155.1Kg. The lithium content is calculated by atomic absorption spectrometry analysis to be 27.9Kg. Then divided by the lithium content of the carbon ink powder of 29.2Kg, the recovery rate of lithium is 96%.

特別說明的是,本創作之第一過濾裝置13、第二過濾裝置23、第三過濾裝置33、第四過濾裝置43、第五過濾裝置53、第六過濾裝置63及第七過濾裝置73可以為板框壓濾機,亦可稱板壓機。第一攪拌裝置12、第二攪拌裝置22、第三攪拌裝置32、第四攪拌裝置42、第五攪拌裝置52、第六攪拌裝置62及第七攪拌裝置72可以為葉片攪拌機。Specifically, the first filtering device 13, the second filtering device 23, the third filtering device 33, the fourth filtering device 43, the fifth filtering device 53, the sixth filtering device 63 and the seventh filtering device 73 of the present invention can be It is a plate and frame filter press, also known as a plate press. The first stirring device 12 , the second stirring device 22 , the third stirring device 32 , the fourth stirring device 42 , the fifth stirring device 52 , the sixth stirring device 62 and the seventh stirring device 72 may be blade mixers.

本創作鋰離子電池中有價金屬之回收方法及回收設備,可在不使用電解反應及不使用特別的萃取劑下有效分離有價金屬。再者,本創作先去除碳墨粉末中的鋁、銅、鐵等雜質金屬及碳,然後接著藉由收集第五濾渣的碳酸鎳及碳酸錳、第六濾渣的氫氧化鈷或氧化鈷、第七濾渣的磷酸鋰,而達到分離及回收有價金屬鋰、鎳、鈷及錳的目的。另外,本創作是先去除碳墨粉末中的鋁、銅、鐵等雜質金屬及碳,因此後續回收獲得的有價金屬其回收率可高達95%以上。The method and equipment for recycling valuable metals in lithium-ion batteries of this invention can effectively separate valuable metals without using electrolysis reaction and without using special extractants. Furthermore, this invention first removes aluminum, copper, iron and other impurity metals and carbon in the carbon ink powder, and then collects the nickel carbonate and manganese carbonate of the fifth filter residue, the cobalt hydroxide or cobalt oxide of the sixth filter residue, and the Seven filter residues of lithium phosphate to achieve the purpose of separating and recovering valuable metals lithium, nickel, cobalt and manganese. In addition, this creation first removes aluminum, copper, iron and other impurity metals and carbon from the carbon ink powder, so the recovery rate of valuable metals obtained from subsequent recycling can be as high as more than 95%.

以上所述之實施例僅係為說明本創作之技術思想及特點,其目的在使熟習此項技藝之人士能夠瞭解本創作之內容並據以實施,當不能以之限定本創作之專利範圍,即大凡依本創作所揭示之精神所作之均等變化或修飾,仍應涵蓋在本創作之專利範圍內。The above-mentioned embodiments are only for illustrating the technical ideas and characteristics of this invention. Their purpose is to enable those familiar with this art to understand the content of this invention and implement it accordingly. They should not be used to limit the patent scope of this invention. That is to say, all equivalent changes or modifications made in accordance with the spirit revealed by this creation should still be covered by the patent scope of this creation.

P:管路系統P:Pipeline system

S00:材料檢測步驟S00: Material testing steps

S10:鹼浸步驟S10: Alkali leaching step

S20:酸浸步驟S20: Acid leaching step

S30:金屬置換步驟S30: Metal replacement step

S40:除鐵步驟S40: Iron removal step

S50:回收鎳及錳步驟S50: Steps to recover nickel and manganese

S60:回收鈷步驟S60: Cobalt recovery step

S70:回收鋰步驟S70: Lithium recovery step

100:鋰離子電池中有價金屬之回收設備100: Recovery equipment for valuable metals in lithium-ion batteries

1:鹼浸裝置1:Alkali leaching device

11:鹼浸槽11:Alkali soaking tank

12:第一攪拌裝置12: The first stirring device

13:第一過濾裝置13: First filtering device

14:鋁鹽槽14:Aluminum salt tank

2:酸浸裝置2: Acid leaching device

21:酸浸槽21:Acid soaking tank

22:第二攪拌裝置22: Second stirring device

23:第二過濾裝置23:Second filtering device

3:除銅裝置3: Copper removal device

31:除銅槽31: Copper removal tank

32:第三攪拌裝置32: The third stirring device

33:第三過濾裝置33:Third filtering device

4:除鐵裝置4: Iron removal device

41:除鐵槽41: Iron removal tank

42:第四攪拌裝置42: The fourth stirring device

43:第四過濾裝置43: The fourth filtering device

5:鎳錳回收裝置5: Nickel manganese recovery device

51:鎳錳回收槽51: Nickel manganese recovery tank

52:第五攪拌裝置52: The fifth stirring device

53:第五過濾裝置53:Fifth filter device

6:鈷回收裝置6: Cobalt recovery device

61:鈷回收槽61:Cobalt recovery tank

62:第六攪拌裝置62:Sixth stirring device

63:第六過濾裝置63:Sixth filter device

7:鋰回收裝置7: Lithium recovery device

71:鋰回收槽71:Lithium recovery tank

72:第七攪拌裝置72:Seventh stirring device

73:第七過濾裝置73:Seventh filtering device

圖1為本創作鋰離子電池中有價金屬之回收方法的流程圖。 圖2為本創作鋰離子電池中有價金屬之回收設備的示意圖。 Figure 1 is a flow chart of the recycling method of valuable metals in lithium-ion batteries of this invention. Figure 2 is a schematic diagram of the recycling equipment for valuable metals in lithium-ion batteries of this invention.

P:管路系統 P:Pipeline system

100:鋰離子電池中有價金屬之回收設備 100: Recovery equipment for valuable metals in lithium-ion batteries

1:鹼浸裝置 1:Alkali leaching device

11:鹼浸槽 11:Alkali soaking tank

12:第一攪拌裝置 12: The first stirring device

13:第一過濾裝置 13: First filtering device

14:鋁鹽槽 14:Aluminum salt tank

2:酸浸裝置 2: Acid leaching device

21:酸浸槽 21:Acid soaking tank

22:第二攪拌裝置 22: Second stirring device

23:第二過濾裝置 23:Second filtering device

3:除銅裝置 3: Copper removal device

31:除銅槽 31: Copper removal tank

32:第三攪拌裝置 32: The third stirring device

33:第三過濾裝置 33:Third filtering device

4:除鐵裝置 4: Iron removal device

41:除鐵槽 41: Iron removal tank

42:第四攪拌裝置 42: The fourth stirring device

43:第四過濾裝置 43: The fourth filtering device

5:鎳錳回收裝置 5: Nickel manganese recovery device

51:鎳錳回收槽 51: Nickel manganese recovery tank

52:第五攪拌裝置 52: The fifth stirring device

53:第五過濾裝置 53:Fifth filter device

6:鈷回收裝置 6: Cobalt recovery device

61:鈷回收槽 61:Cobalt recovery tank

62:第六攪拌裝置 62:Sixth stirring device

63:第六過濾裝置 63:Sixth filter device

7:鋰回收裝置 7: Lithium recovery device

71:鋰回收槽 71:Lithium recovery tank

72:第七攪拌裝置 72:Seventh stirring device

73:第七過濾裝置 73:Seventh filtering device

Claims (1)

一種鋰離子電池中有價金屬之回收設備,至少包含: 一鹼浸裝置(1),其包含混合一氫氧化鈉水溶液與一碳墨粉末及pH值至大於12的一鹼浸槽(11)、設置於該鹼浸槽(11)內的一第一攪拌裝置(12)、以一管路系統(P)連通該鹼浸槽(11)底部的一第一過濾裝置(13)及以該管路系統(P)連通該第一過濾裝置(13)的一鋁鹽槽(14),該鹼浸槽(11)底部的該管路系統(P)將該鹼浸槽(11)中的一第一水溶液及一第一濾渣輸送至該第一過濾裝置(13),該第一過濾裝置(13)將該第一水溶液及該第一濾渣分離,並使該第一水溶液儲存於該鋁鹽槽(14),其中該碳墨粉末包含鋰、鎳、鈷、錳、鋁、銅、鐵及碳,該第一水溶液為鋁鹽,該第一濾渣含有鋰、鎳、鈷、錳、銅、鐵及碳; 一酸浸裝置(2),其包含以該管路系統(P)連接該第一過濾裝置(13)以承接該第一濾渣並以一酸性水溶液混合使pH值小於4的一酸浸槽(21)、設置於該酸浸槽(21)內的一第二攪拌裝置(22)及以該管路系統(P)連通該酸浸槽(21)底部的一第二過濾裝置(23),該酸浸槽(21)底部的該管路系統(P)將該酸浸槽(21)中的一第二水溶液及一第二濾渣輸送至該第二過濾裝置(23),該第二過濾裝置(23)將該第二水溶液及該第二濾渣分離,該第二濾渣為碳渣; 一除銅裝置(3),其包含以該管路系統(P)連接該第二過濾裝置(23)以承接該第二水溶液並混合鐵粉且pH值小於4的一除銅槽(31)、設置於該除銅槽(31)內的一第三攪拌裝置(32)及以該管路系統(P)連通該除銅槽(31)底部的一第三過濾裝置(33),該除銅槽(31)底部的該管路系統(P)將該除銅槽(31)中的一第三水溶液及一第三濾渣輸送至該第三過濾裝置(33),該第三過濾裝置(33)將該第三水溶液及該第三濾渣分離,該第三濾渣為銅; 一除鐵裝置(4),其包含以該管路系統(P)連接該第三過濾裝置(33)以承接該第三水溶液並混合氫氧化鈉使pH值為介於4至5之間的一除鐵槽(41)、設置於該除鐵槽(41)內的一第四攪拌裝置(42)及以該管路系統(P)連通該除鐵槽(41)底部的一第四過濾裝置(43),該除鐵槽(41)底部的該管路系統(P)將該除鐵槽(41)中的一第四水溶液及一第四濾渣輸送至該第四過濾裝置(43),該第四過濾裝置(43)將該第四水溶液及該第四濾渣分離,該第四濾渣為氫氧化鐵; 一鎳錳回收裝置(5),其包含以該管路系統(P)連接該第四過濾裝置(43)以承接該第四水溶液並混合碳酸鈉及氫氧化鈉使pH值為介於6至8之間的一鎳錳回收槽(51)、設置於該鎳錳回收槽(51)內的一第五攪拌裝置(52)及以該管路系統(P)連通該鎳錳回收槽(51)底部的一第五過濾裝置(53),該鎳錳回收槽(51)底部的該管路系統(P)將該鎳錳回收槽(51)中的一第五水溶液及一第五濾渣輸送至該第五過濾裝置(53),該第五過濾裝置(53)將該第五水溶液及該第五濾渣分離,該第五濾渣為碳酸鎳及碳酸錳; 一鈷回收裝置(6),其包含以該管路系統(P)連接該第五過濾裝置(53)以承接該第五水溶液並混合氫氧化鈉使pH值為介於11至13之間的一鈷回收槽(61)、設置於該鈷回收槽(61)內的一第六攪拌裝置(62)及以該管路系統(P)連通該鈷回收槽(61)底部的一第六過濾裝置(63),該鈷回收槽(61)底部的該管路系統(P)將該鈷回收槽(61)中的一第六水溶液及一第六濾渣輸送至該第六過濾裝置(63),該第六過濾裝置(63)將該第六水溶液及該第六濾渣分離,該第六濾渣為氫氧化鈷;以及, 一鋰回收裝置(7),包含以該管路系統(P)連接該第六過濾裝置(63)以承接該第六水溶液並混合磷酸鈉的一鋰回收槽(71)、設置於該鋰回收槽(71)內的一第七攪拌裝置(72)及以該管路系統(P)連通該鋰回收槽(71)底部的一第七過濾裝置(73),該鋰回收槽(71)底部的該管路系統(P)將該鋰回收槽(71)中的一第七水溶液及一第七濾渣輸送至該第七過濾裝置(73),該第七過濾裝置(73)將該第七水溶液及該第七濾渣分離,該第七濾渣為磷酸鋰。 A recycling equipment for valuable metals in lithium-ion batteries, including at least: An alkali immersion device (1), which includes an alkali immersion tank (11) that mixes a sodium hydroxide aqueous solution and a carbon ink powder with a pH value greater than 12, and a first alkali immersion tank (11) disposed in the alkali immersion tank (11). The stirring device (12) is connected to a first filtering device (13) at the bottom of the alkali soaking tank (11) with a pipeline system (P), and the first filtering device (13) is connected with the pipeline system (P). An aluminum salt tank (14), the pipeline system (P) at the bottom of the alkali leaching tank (11) transports a first aqueous solution and a first filter residue in the alkali leaching tank (11) to the first filter Device (13), the first filtering device (13) separates the first aqueous solution and the first filter residue, and stores the first aqueous solution in the aluminum salt tank (14), wherein the carbon ink powder contains lithium, nickel , cobalt, manganese, aluminum, copper, iron and carbon, the first aqueous solution is aluminum salt, the first filter residue contains lithium, nickel, cobalt, manganese, copper, iron and carbon; An acid leaching device (2), which includes an acid leaching tank (2) connected to the first filtering device (13) with the pipeline system (P) to receive the first filter residue and mix it with an acidic aqueous solution to make the pH value less than 4. 21), a second stirring device (22) provided in the acid leaching tank (21) and a second filtering device (23) connected to the bottom of the acid leaching tank (21) with the piping system (P), The pipeline system (P) at the bottom of the acid leaching tank (21) transports a second aqueous solution and a second filter residue in the acid leaching tank (21) to the second filtering device (23). The device (23) separates the second aqueous solution and the second filter residue, and the second filter residue is carbon residue; A copper removal device (3), which includes a copper removal tank (31) connected to the second filtering device (23) with the piping system (P) to receive the second aqueous solution and mix iron powder with a pH value less than 4 , a third stirring device (32) installed in the copper removal tank (31) and a third filtering device (33) connected to the bottom of the copper removal tank (31) with the piping system (P). The pipeline system (P) at the bottom of the copper tank (31) transports a third aqueous solution and a third filter residue in the copper removal tank (31) to the third filtering device (33), and the third filtering device (33) 33) Separate the third aqueous solution and the third filter residue, and the third filter residue is copper; An iron removal device (4), which includes connecting the third filtering device (33) with the pipeline system (P) to receive the third aqueous solution and mix sodium hydroxide to make the pH value between 4 and 5. An iron removal tank (41), a fourth stirring device (42) provided in the iron removal tank (41), and a fourth filter connected to the bottom of the iron removal tank (41) with the pipeline system (P) Device (43), the pipeline system (P) at the bottom of the iron removal tank (41) transports a fourth aqueous solution and a fourth filter residue in the iron removal tank (41) to the fourth filtering device (43) , the fourth filtering device (43) separates the fourth aqueous solution and the fourth filter residue, and the fourth filter residue is ferric hydroxide; A nickel-manganese recovery device (5), which includes connecting the fourth filtering device (43) with the pipeline system (P) to receive the fourth aqueous solution and mixing sodium carbonate and sodium hydroxide to make the pH value between 6 and A nickel-manganese recovery tank (51) between 8, a fifth stirring device (52) provided in the nickel-manganese recovery tank (51), and the pipeline system (P) connected to the nickel-manganese recovery tank (51) ), a fifth filtering device (53) at the bottom of the nickel-manganese recovery tank (51), and the pipeline system (P) at the bottom of the nickel-manganese recovery tank (51) transports a fifth aqueous solution and a fifth filter residue in the nickel-manganese recovery tank (51) To the fifth filtering device (53), the fifth filtering device (53) separates the fifth aqueous solution and the fifth filter residue, and the fifth filter residue is nickel carbonate and manganese carbonate; A cobalt recovery device (6), which includes connecting the fifth filtration device (53) with the pipeline system (P) to receive the fifth aqueous solution and mix sodium hydroxide to make the pH value between 11 and 13 A cobalt recovery tank (61), a sixth stirring device (62) provided in the cobalt recovery tank (61), and a sixth filter connected to the bottom of the cobalt recovery tank (61) with the pipeline system (P) Device (63), the pipeline system (P) at the bottom of the cobalt recovery tank (61) transports a sixth aqueous solution and a sixth filter residue in the cobalt recovery tank (61) to the sixth filtering device (63) , the sixth filtering device (63) separates the sixth aqueous solution and the sixth filter residue, the sixth filter residue is cobalt hydroxide; and, A lithium recovery device (7), including a lithium recovery tank (71) connected to the sixth filtering device (63) with the pipeline system (P) to receive the sixth aqueous solution and mix sodium phosphate, and is provided in the lithium recovery device A seventh stirring device (72) in the tank (71) and a seventh filtering device (73) connected to the bottom of the lithium recovery tank (71) by the pipeline system (P), and the bottom of the lithium recovery tank (71) The pipeline system (P) transports a seventh aqueous solution and a seventh filter residue in the lithium recovery tank (71) to the seventh filtering device (73), and the seventh filtering device (73) The aqueous solution and the seventh filter residue are separated, and the seventh filter residue is lithium phosphate.
TW112208652U 2023-08-15 2023-08-15 Recycling equipment for valuable metal in lithium-ion battery TWM650076U (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
TWI863507B (en) * 2023-08-15 2024-11-21 三旺科技股份有限公司 Method for recovering valuable metals in lithium-ion batteries

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
TWI863507B (en) * 2023-08-15 2024-11-21 三旺科技股份有限公司 Method for recovering valuable metals in lithium-ion batteries

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