TWI535479B - Valuable metals recovering method - Google Patents
Valuable metals recovering method Download PDFInfo
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- TWI535479B TWI535479B TW103132318A TW103132318A TWI535479B TW I535479 B TWI535479 B TW I535479B TW 103132318 A TW103132318 A TW 103132318A TW 103132318 A TW103132318 A TW 103132318A TW I535479 B TWI535479 B TW I535479B
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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
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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
- 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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Description
下列敘述是有關於一種回收有價金屬之方法,特別是,有關於利用過氧化氫及超音波輔助,從廢棄之鋰電池回收並分離純化鈷、錳、鎳或鋰之方法。 The following description relates to a method for recovering valuable metals, and more particularly to a method for recovering and separating and purifying cobalt, manganese, nickel or lithium from a spent lithium battery using hydrogen peroxide and ultrasonic assist.
二次電池可藉充電過程將電能轉換成化學能再次使用,因可充電功能具重覆使用之環保概念,使二次電池普及全球市場。在商業上,一般將二次鋰電池依正極材料不同,分為鈷酸鋰(氧化鋰鈷,LiCoO2)、鎳酸鋰(氧化鋰鎳,LiNiO2)、錳酸鋰(氧化鋰錳,LiMn2O4)、三元系鈷鎳錳酸鋰(氧化鋰鈷鎳錳,LiCoO2/LiNiO2/LiMn2O4)、磷酸鐵鋰(鋰鐵磷,LiFePO4)。 The secondary battery can be converted into chemical energy by the charging process, and the secondary battery is popularized in the global market due to the environmentally-friendly concept of the rechargeable function. Commercially, secondary lithium batteries are generally classified into lithium cobalt oxide (lithium oxide, LiCoO 2 ), lithium nickelate (lithium nickel oxide, LiNiO 2 ), lithium manganate (lithium manganese oxide, LiMn) depending on the cathode material. 2 O 4 ), ternary cobalt lithium nickel manganese oxide (lithium oxide cobalt nickel manganese, LiCoO 2 /LiNiO 2 /LiMn 2 O 4 ), lithium iron phosphate (lithium iron phosphorus, LiFePO 4 ).
一般而言,鈷酸鋰電池以應用於手持式裝置電子產品為主;鎳酸鋰電池因為安全性尚未克服,所以生產者以及使用者較少;而錳酸鋰電池因為安全性高,讓其目前廣泛應用在手工具當中。二次鋰電池的正極材料評估結果顯示,以鈷酸鋰為正極材料之二次鋰電池,其正極材料所佔成本約40%,但以錳酸鋰為正極材料之二次鋰電池,其正極材料所佔成本約20%,以錳酸鋰為正極材料可降低二次鋰電池之價格,且錳元素對環境之相容性較高。因此,三元系(LiCoO2/LiNiO2/LiMn2O4)正極材料,透過增加鎳元素提高電容量,及增加錳元素達到安全性與低成本要求。因為三元系正極材料可降低成本,其體積小及重量輕,具發展進步空間,逐漸於市場崛起,成為二次鋰電池中最具競爭力的正 極材料,並於2012年開始陸續出貨。 In general, lithium cobalt oxide batteries are mainly used in handheld device electronic products; lithium nickel acid batteries have not been overcome because of safety, so producers and users are less; and lithium manganate batteries are safe because of their high safety. Currently widely used in hand tools. The evaluation results of the positive electrode material of the secondary lithium battery show that the secondary lithium battery with lithium cobaltate as the positive electrode material accounts for about 40% of the cost of the positive electrode material, but the secondary lithium battery with lithium manganate as the positive electrode material has its positive electrode. The cost of the material is about 20%. The use of lithium manganate as the positive electrode material can lower the price of the secondary lithium battery, and the compatibility of the manganese element with the environment is high. Therefore, the ternary system (LiCoO 2 /LiNiO 2 /LiMn 2 O 4 ) cathode material increases the capacitance by increasing the nickel element and increases the manganese element to meet safety and low cost requirements. Because the ternary cathode material can reduce the cost, its small size and light weight, with room for development and progress, gradually emerged in the market, becoming the most competitive cathode material in secondary lithium batteries, and began to ship in 2012.
然而,當三元系正極材料鋰電池在二至五年後廢棄,卻會影響到現行回收技術在未來的可適用性。二次鋰電池內含多種金屬元素(鋰、鈷、鎳、錳、銅、鋁等),多屬有價物,在有限資源之使用,如不加以回收再生,資源將會耗盡。其中,鈷金屬在自然界中只佔25ppm,蘊藏量相當稀少。當鋰電池漸漸投入使用時,其原料來源勢必將受產地的開採量所限制,所以基於資源有限且使用量逐年上升的考量,電池材料的回收處理將是未來各國必須面臨的重要課題。 However, when the ternary cathode material lithium battery is discarded after two to five years, it will affect the applicability of the current recycling technology in the future. Secondary lithium batteries contain a variety of metal elements (lithium, cobalt, nickel, manganese, copper, aluminum, etc.), which are mostly valuable materials. If they are used in limited resources, if they are not recycled, the resources will be exhausted. Among them, cobalt metal accounts for only 25ppm in nature, and the reserves are quite rare. When lithium batteries are gradually put into use, the source of raw materials is bound to be limited by the amount of production. Therefore, based on the limited resources and increasing usage, the recycling of battery materials will be an important issue for all countries in the future.
本發明實施例之態樣係針對一種回收有價金屬之方法,能夠從廢棄之鋰電池中提升回收鈷、錳、鎳及鋰等有價金屬之純度。 The aspect of the embodiment of the present invention is directed to a method for recovering valuable metals, which can improve the purity of valuable metals such as cobalt, manganese, nickel and lithium from waste lithium batteries.
基於上述目的,本發明係提供一種回收有價金屬之方法,其適用於一廢二次鋰電池。回收有價金屬之方法可包含下列步驟:利用放電程序與切割剝離程序去除廢二次鋰電池之外殼,接著進行一粉碎分選程序以產生含有鈷、錳、鎳、鋁及鋰之正極材料粉體。利用鹼溶程序以沉澱去除粉體中之鋁金屬。利用含有硫酸但不含有過氧化氫之酸液混合粉體以浸漬出酸浸漬液,酸液與粉體的比例介於1g/100ml至4g/100ml之間,且酸液及粉體係放置於超音波增幅器中,酸液中硫酸的濃度介於3N至4N之間,酸液與粉體混合之溫度介於攝氏45度至55度之間,以上條件可使酸浸漬液中含有1%以下的錳。利用萃取劑對酸浸漬液進行錳、鈷鎳及鋰之萃取,經預萃取去除銅、鐵等微量雜金屬。除雜後的酸浸漬液再經溶劑萃取,以生成含有錳之第一油相溶液以及含有鈷、鎳及鋰之第一水相萃餘液,再對第一水相萃餘液萃取以生成含有鈷之第二油相溶液以及含有鎳及鋰之第二水相萃餘液。以及利用回收程序以分別自第一油相溶液之反萃液、第二油相溶液之反萃液及第二水相萃餘液分別回收純化之錳、鈷、鎳 以及鋰,其中回收程序可包含化學沉澱反應或電解反應。 Based on the above object, the present invention provides a method of recovering valuable metals suitable for use in a waste secondary lithium battery. The method of recovering the valuable metal may include the steps of removing the outer casing of the waste secondary lithium battery by a discharge program and a cutting and stripping procedure, followed by a pulverization sorting process to produce a positive electrode material powder containing cobalt, manganese, nickel, aluminum, and lithium. The aluminum metal in the powder is removed by precipitation using an alkali dissolution procedure. The acid immersion liquid is mixed by using an acid liquid containing sulfuric acid but not containing hydrogen peroxide, and the ratio of the acid liquid to the powder is between 1 g/100 ml and 4 g/100 ml, and the acid liquid and the powder system are placed in the super In the sonic amplifier, the concentration of sulfuric acid in the acid solution is between 3N and 4N, and the temperature at which the acid solution and the powder are mixed is between 45 and 55 degrees Celsius, and the above conditions can make the acid immersion liquid contain 1% or less. Manganese. The acid immersion liquid is extracted with manganese, cobalt nickel and lithium by an extracting agent, and pre-extracted to remove trace metals such as copper and iron. The impurity-containing acid immersion liquid is further subjected to solvent extraction to form a first oil phase solution containing manganese and a first aqueous phase raffinate containing cobalt, nickel and lithium, and then extracting the first aqueous phase raffinate to generate a second oil phase solution containing cobalt and a second aqueous phase raffinate containing nickel and lithium. And recovering the purified manganese, cobalt and nickel by using a recovery program to separately extract the stripping solution of the first oil phase solution, the stripping solution of the second oil phase solution and the second aqueous phase raffinate respectively And lithium, wherein the recovery procedure can comprise a chemical precipitation reaction or an electrolytic reaction.
較佳地,化學沉澱反應係利用一氧化還原反應將金屬離子沉澱,電解反應可將金屬離子還原成金屬元素。 Preferably, the chemical precipitation reaction utilizes a redox reaction to precipitate metal ions, and the electrolytic reaction reduces metal ions to metal elements.
較佳地,氧化還原反應包含藉由對第一油相溶液之反萃液或第二油相溶液之反萃液或第二水相萃餘液,進行不同之一pH值之調整,使鈷、錳、鎳或鋰沉澱,並藉由過濾使鈷、錳、鎳或鋰各以固態鹽之形態來加以回收,pH值之範圍介於2.0~11.0。 Preferably, the redox reaction comprises adjusting the pH of the stripping solution of the first oil phase solution or the stripping solution of the second oil phase solution or the second aqueous phase raffinate to make the cobalt , manganese, nickel or lithium is precipitated, and cobalt, manganese, nickel or lithium is recovered by filtration in the form of a solid salt, and the pH ranges from 2.0 to 11.0.
較佳地,pH調整劑包括氫氧化鈉、碳酸鈉、硫化鈉、草酸氨。 Preferably, the pH adjusting agent comprises sodium hydroxide, sodium carbonate, sodium sulfide, and ammonium oxalate.
較佳地,本發明之回收有價金屬之方法更包含將固態鹽溶解於一酸液以進行電解提煉鈷、錳或鎳。 Preferably, the method for recovering valuable metals of the present invention further comprises dissolving a solid salt in an acid solution for electrolytically refining cobalt, manganese or nickel.
較佳地,萃取劑包含D2EHPA或Cyanex272。 Preferably, the extractant comprises D2EHPA or Cyanex272.
較佳地,放置酸液及粉體的超音波增幅器,其頻率介於20KHz~28KHz。 Preferably, the ultrasonic amplifier for placing acid and powder has a frequency between 20 kHz and 28 kHz.
基於上述目的,本發明再提供一種回收有價金屬之方法,適用於一廢二次鋰電池之正極材料,回收有價金屬之方法可包含以下步驟:利用一放電程序與一粉碎分選程序使正極材料形成含有錳、鈷、鎳、鋁及鋰之粉體。利用一鹼溶程序以沉澱去除粉體中之鋁金屬。利用含有硫酸之一酸液混合粉體以浸漬出含錳、鈷、鎳及鋰之一酸浸漬液,其中酸液與粉體的比例介於1g/100ml至4g/100ml之間,且酸液及粉體係放置於一超音波裝置中進行混和並於每隔一小時加入0.25ml至2.5ml、濃度為35%之過氧化氫,酸液中硫酸的濃度介於3N至4N之間,酸液與粉體混合時的溫度介於45℃至55℃之間。利用一萃取劑對酸浸漬液進行錳、鈷、鎳及鋰之萃取,以生成含有錳之一第一油相溶液以及含有鈷、鎳及鋰之一第一水相萃餘液。對第一水相萃餘液中的鈷進行萃取,以分 別生成含有鈷之第二油相溶液以及含有鎳及鋰之第二水相萃餘液。以及,利用一回收程序以分別自第一油相溶液之反萃液、第二油相溶液之反萃液,及第二水相萃餘液回收錳、鈷、鎳以及鋰,其中回收程序係包含一化學沉澱反應或一電解反應。 Based on the above object, the present invention further provides a method for recovering valuable metals, which is suitable for a positive electrode material of a waste secondary lithium battery. The method for recovering valuable metals may include the following steps: forming a positive electrode material by a discharge process and a pulverization sorting process A powder containing manganese, cobalt, nickel, aluminum and lithium. The alkali metal in the powder is removed by precipitation using an alkali dissolution procedure. Mixing powder containing one of sulfuric acid to impregnate an acid impregnation solution containing manganese, cobalt, nickel and lithium, wherein the ratio of acid to powder is between 1g/100ml and 4g/100ml, and the acid solution And the powder system is placed in an ultrasonic device for mixing and 0.25ml to 2.5ml, 35% hydrogen peroxide is added every hour, the concentration of sulfuric acid in the acid solution is between 3N and 4N, the acid solution The temperature when mixed with the powder is between 45 ° C and 55 ° C. The acid immersion liquid is extracted with manganese, cobalt, nickel and lithium by an extracting agent to form a first oil phase solution containing manganese and a first aqueous phase raffinate containing one of cobalt, nickel and lithium. Extracting cobalt in the first aqueous phase raffinate to divide Do not form a second oil phase solution containing cobalt and a second aqueous phase raffinate containing nickel and lithium. And recovering manganese, cobalt, nickel, and lithium by using a recovery procedure to recover manganese, cobalt, nickel, and lithium from the stripping solution of the first oil phase solution, the stripping solution of the second oil phase solution, and the second aqueous phase raffinate, respectively. Contains a chemical precipitation reaction or an electrolytic reaction.
較佳地,超音波裝置可包含一超音波震盪槽或一超音波。 Preferably, the ultrasonic device may comprise an ultrasonic oscillating groove or an ultrasonic wave.
較佳地,超音波震盪槽之頻率介於28KHz~200KHz,超音波增幅器之頻率介於20KHz~28KHz。 Preferably, the frequency of the ultrasonic oscillation tank is between 28KHz and 200KHz, and the frequency of the ultrasonic amplifier is between 20KHz and 28KHz.
較佳地,過氧化氫之溶出反應式為2LiCoO2+3H2SO4+H2O2=Li2SO4+2CoSO4+O2↑+4H2O(l) Preferably, the dissolution reaction formula of hydrogen peroxide is 2LiCoO 2 +3H 2 SO 4 +H 2 O 2 =Li 2 SO 4 +2CoSO 4 +O 2 ↑+4H 2 O (l)
S1~S6‧‧‧步驟 S1~S6‧‧‧Steps
本發明之上述及其他特徵及優勢將藉由參照附圖詳細說明其例示性實施例而變得更顯而易知,其中: The above and other features and advantages of the present invention will become more apparent from the detailed description of the exemplary embodiments thereof
第1圖係為根據本發明實施例之回收有價金屬之方法之步驟流程圖。 BRIEF DESCRIPTION OF THE DRAWINGS Figure 1 is a flow chart showing the steps of a method for recovering valuable metals according to an embodiment of the present invention.
第2A圖係為根據本發明之另一實施例之酸溶提取金屬濃度之第一示意圖。 Fig. 2A is a first schematic view showing the concentration of acid-soluble extracted metal according to another embodiment of the present invention.
第2B圖係為根據本發明之另一實施例之酸溶提取金屬濃度之第二示意圖。 Figure 2B is a second schematic diagram of the acid-extracted metal concentration in accordance with another embodiment of the present invention.
第2C圖係為根據本發明之另一實施例之酸溶提取金屬濃度之第三示意圖。 Figure 2C is a third schematic diagram of the acid-extracted metal concentration in accordance with another embodiment of the present invention.
第3A圖係為根據本發明之第二實施例之溶劑萃取及反萃之第一示意圖。 Figure 3A is a first schematic view of solvent extraction and stripping in accordance with a second embodiment of the present invention.
第3B圖係為根據本發明之第二實施例之溶劑萃取及反萃之第二示意圖。 Figure 3B is a second schematic view of solvent extraction and stripping in accordance with a second embodiment of the present invention.
第3C圖係為根據本發明之第二實施例之溶劑萃取及反萃之第三示意圖。 Figure 3C is a third schematic view of solvent extraction and stripping in accordance with a second embodiment of the present invention.
第4圖係為根據本發明之萃取各個金屬離子之萃取率之示意圖。 Figure 4 is a schematic illustration of the extraction rate of various metal ions extracted in accordance with the present invention.
第5A圖係為根據本發明之第一次反萃所得金屬濃度與反萃液當量濃度之示意圖。 Fig. 5A is a schematic diagram showing the metal concentration obtained in the first stripping according to the present invention and the equivalent concentration of the stripping solution.
第5B圖係為根據本發明之第二次反萃時所得金屬濃度與反萃液當量濃度之示意圖。 Figure 5B is a graphical representation of the concentration of metal obtained and the equivalent concentration of the stripping solution in the second stripping according to the present invention.
為利 貴審查員瞭解本發明之特徵、內容與優點及其所能達成之功效,茲將本發明配合附圖,並以實施例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,未必為本發明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、侷限本發明於實際實施上的權利範圍。 The features, the contents and advantages of the present invention, and the advantages thereof, will be understood by the present invention. The present invention will be described in detail with reference to the accompanying drawings, The use of the present invention is not intended to be a limitation of the scope of the present invention, and the scope of the present invention is not limited by the scope and configuration of the accompanying drawings.
本發明之優點、特徵以及達到之技術方法將參照例示性實施例及所附圖式進行更詳細地描述而更容易理解,且本發明或可以不同形式來實現,故不應被理解僅限於此處所陳述的實施例,相反地,對所屬技術領域具有通常知識者而言,所提供的實施例將使本揭露更加透徹與全面且完整地傳達本發明的範疇,且本發明將僅為所附加的申請專利範圍所定義。 The advantages and features of the present invention, as well as the technical methods of the present invention, are described in more detail with reference to the exemplary embodiments and the accompanying drawings, and the present invention may be implemented in various forms and should not be construed as limited thereby. The embodiments of the present invention, and the embodiments of the present invention are intended to provide a more complete and complete and complete disclosure of the scope of the present invention, and The scope of the patent application is defined.
請參閱第1圖,請參閱第1圖,其係根據本發明實施例之回收有價金屬之步驟流程圖。如第1圖所示,此回收有價金屬之方法適用於一廢二次 鋰電池,回收有價金屬之方法可包含下列步驟。步驟S1利用一放電程序與一粉碎分選程序,去除廢二次鋰電池之外殼以取得含有鈷、錳、鎳、鋁及鋰之一正極材料粉體。步驟S2利用一鹼溶程序以沉澱去除粉體中之鋁金屬。步驟S3利用含有過氧化氫與硫酸之一酸液將粉體浸漬出含錳、鈷、鎳及鋰之一酸浸漬液,其中酸液及粉體係放置於一超音波裝置中。步驟S4利用一萃取劑對酸浸漬液進行錳、鈷、鎳及鋰之萃取,以分別生成含有錳之一第一油相溶液以及含有鈷、鎳及鋰之一第一水相萃餘液。步驟S5對第一水相萃餘液進行溶劑萃取,以分別生成含有鈷之一第二油相溶液以及含有鎳及鋰之一第二水相萃餘液。步驟S6利用一回收程序以分別自第一油相溶液之反萃液、第二油相溶液之反萃液及第二水相萃餘液回收錳、鈷、鎳以及鋰,其中回收程序可包含一化學沉澱反應或一電解反應,此化學沉澱反應係利用一氧化還原反應將金屬離子沉澱,而電解反應可將金屬離子還原成金屬元素。 Please refer to FIG. 1, which is a first flow chart showing the steps of recovering valuable metals according to an embodiment of the present invention. As shown in Figure 1, this method of recovering valuable metals is applicable to one waste twice. A lithium battery, the method of recovering a valuable metal may include the following steps. Step S1 uses a discharge process and a pulverization sorting process to remove the outer casing of the waste secondary lithium battery to obtain a positive electrode material powder containing cobalt, manganese, nickel, aluminum and lithium. Step S2 uses an alkali dissolution procedure to precipitate to remove aluminum metal in the powder. In step S3, the powder is impregnated with an acid immersion liquid containing manganese, cobalt, nickel and lithium by using an acid liquid containing hydrogen peroxide and sulfuric acid, wherein the acid liquid and the powder system are placed in an ultrasonic device. Step S4 extracts manganese, cobalt, nickel and lithium from the acid immersion liquid by using an extracting agent to respectively form a first oil phase solution containing manganese and a first aqueous phase raffinate containing one of cobalt, nickel and lithium. In step S5, the first aqueous phase raffinate is subjected to solvent extraction to respectively form a second oil phase solution containing cobalt and a second aqueous phase raffinate containing nickel and lithium. Step S6 uses a recovery procedure to recover manganese, cobalt, nickel, and lithium from the stripping solution of the first oil phase solution, the stripping solution of the second oil phase solution, and the second aqueous phase raffinate, respectively, wherein the recovery procedure may include A chemical precipitation reaction or an electrolytic reaction which precipitates metal ions by a redox reaction, and the electrolytic reaction reduces metal ions to metal elements.
值得一提的是,粉體與酸液之比例範圍為1g/100ml~4g/100ml,浸漬時間之範圍為0.5~3.0小時,酸液包含3.0~4.0N之硫酸,酸浸漬之溫度介於攝氏45度~55度,並每隔一時間間距加入2.5ml、濃度為35%之過氧化氫。 It is worth mentioning that the ratio of powder to acid is in the range of 1g/100ml~4g/100ml, the immersion time ranges from 0.5 to 3.0 hours, the acid solution contains 3.0~4.0N sulfuric acid, and the acid impregnation temperature is between Celsius. 45 degrees to 55 degrees, and 2.5 ml of 35% hydrogen peroxide at intervals.
其中,步驟S3中之過氧化氫之溶出反應式為2LiCoO2+3H2SO4+H2O2=Li2SO4+2CoSO4+O2↑+4H2O(l),且超音波裝置包含一超音波震盪槽或一超音波增幅器,當酸液及粉體置於超音波震盪槽中,每隔一時間間距係加入0.25~2.5ml、濃度為35%之過氧化氫。 Wherein, the dissolution reaction formula of hydrogen peroxide in step S3 is 2LiCoO 2 +3H 2 SO 4 +H 2 O 2 =Li 2 SO 4 +2CoSO 4 +O 2 ↑+4H 2 O (l) , and the ultrasonic device It includes an ultrasonic oscillating groove or an ultrasonic amplifier. When the acid and powder are placed in the ultrasonic oscillating tank, 0.25~2.5ml of hydrogen peroxide with a concentration of 35% is added at intervals.
更進一步的說明,超音波震盪槽之頻率介於28KHz~200KHz,超音波增幅器之頻率介於20KHz~28KHz。 Furthermore, the frequency of the ultrasonic oscillation tank is between 28KHz and 200KHz, and the frequency of the ultrasonic amplifier is between 20KHz and 28KHz.
在進行從廢二次鋰電池進行回收有價金屬前,須先經過一前處理流程,其主要包含一放電程序以及剝離/破碎程序,前者係為了避免後續處理過程產生燃燒或爆炸現象,須利用放電程序直至電池完全放電。後者主要以切割 與剝離等方法將廢二次鋰電池的外殼去除,並粉碎分選或刮取得正極材料粉體,避免正極材料粉體含過量雜金屬及不純物。一方面,剝除的外殼可先透過分選程序進行回收金屬碎片或粉料以及塑膠碎片或粉料,另一方面,則從正極材料粉體進行後續之酸溶程序,其中此正極材料粉體包含錳、鈷、鎳、鋰以及少量鋁、鐵、銅、鈣或鎂。 Before carrying out the recovery of valuable metals from waste secondary lithium batteries, it is necessary to go through a pre-treatment process, which mainly includes a discharge program and a stripping/crushing procedure. The former is to avoid the burning or explosion phenomenon in the subsequent processing, and the discharge must be utilized. Program until the battery is fully discharged. The latter mainly cuts The outer casing of the waste secondary lithium battery is removed by a method such as stripping, and the powder of the positive electrode material is pulverized by sorting or scraping to prevent the positive electrode material powder from containing excessive amounts of impurities and impurities. On the one hand, the stripped outer shell can be first subjected to a sorting process for recovering metal fragments or powders, as well as plastic chips or powders, and on the other hand, a subsequent acid dissolution procedure is performed from the positive material powder, wherein the positive electrode material powder Contains manganese, cobalt, nickel, lithium and a small amount of aluminum, iron, copper, calcium or magnesium.
詳細地說,超音波裝置可包含一超音波震盪槽或一超音波增幅器。表1包含利用一超音波增幅器及一超音波震盪槽對一三元系正極材料粉體中鈷、錳、鎳、鋰的溶出率的實驗結果,其中此超音波增幅器之功率為800W,頻率為20000Hz,其為單點振動,振幅桿為1/2吋,超音波震盪槽之功率為200W,頻率為53000Hz,其為水浴震盪,此鈷、錳、鎳、鋰之比率為2:3:5:10。 In detail, the ultrasonic device may include an ultrasonic oscillating groove or an ultrasonic amplifier. Table 1 contains experimental results of the dissolution rate of cobalt, manganese, nickel and lithium in a ternary positive electrode material powder using an ultrasonic amplifier and an ultrasonic oscillating groove, wherein the power of the ultrasonic amplifier is 800 W. The frequency is 20,000 Hz, which is a single point vibration, the amplitude rod is 1/2 吋, the power of the ultrasonic oscillating groove is 200 W, the frequency is 53000 Hz, which is a water bath oscillation. The ratio of cobalt, manganese, nickel and lithium is 2:3. :5:10.
實驗0係配置濃度3.6N的硫酸溶液200ml,放置於250ml燒杯中,加入5克三元系正極材料粉體。每小時加入2.5ml的過氧化氫的條件下,使用磁石攪拌機,以溫度55℃、攪拌速度400轉/min進行酸溶4小時,最後使用火焰式原子吸收光譜儀測定溶出濃度,計算溶出率。 Experiment 0 was set up with 200 ml of a sulfuric acid solution having a concentration of 3.6 N, placed in a 250 ml beaker, and 5 g of a ternary positive electrode material powder was added. After adding 2.5 ml of hydrogen peroxide per hour, the solution was acid-dissolved for 4 hours at a temperature of 55 ° C and a stirring speed of 400 rpm using a magnet mixer. Finally, the dissolution concentration was measured by a flame atomic absorption spectrometer to calculate the dissolution rate.
實驗1及實驗2之設定同於實驗0,其相異點在於實驗1係觀察不加入過氧化氫以進行酸溶之溶出率,實驗2係觀察利用超音波增幅器且不加入過氧化氫以進行酸溶之溶出率,此超音波振幅器之設定功率為50%,每振動5秒鐘停止5秒的間斷工作方式連續進行酸溶4小時,實驗3係實驗2中剩餘含鈷、錳、鎳或鋰粉末之百分比含量。 The settings of Experiment 1 and Experiment 2 are the same as those of Experiment 0. The difference is that Experiment 1 observes that no hydrogen peroxide is added for acid dissolution, and Experiment 2 observes the use of ultrasonic amplifier without hydrogen peroxide. The acid dissolution rate was 50%, and the ultrasonic power was continuously dissolved for 4 hours in a discontinuous operation mode of 5 seconds per 5 seconds of vibration. In experiment 3, the remaining cobalt and manganese in the experiment 2 were contained. Percentage of nickel or lithium powder.
由實驗3可得知,依據此處理條件,酸浸漬液僅溶出鈷、鎳及1%以下之錳,意即,超音波增幅器幾乎無法溶出錳,換句話說,利用超音波增幅器可直接酸浸溶出鈷及鎳,此產生之功效可省略一般習知技藝中須先將錳、鈷、鎳萃取分離為一錳溶液以及一鈷與鎳溶液,再萃取分離為一鈷溶液以及一鎳溶液的兩階段萃取流程。超音波增幅器酸溶即分離出錳,酸浸漬液僅需萃取 分離為一鈷溶液以及一鎳溶液的一階段萃取流程,可大幅減少萃取時的溶劑操作量。 According to Experiment 3, according to the treatment conditions, the acid immersion liquid only dissolves cobalt, nickel and manganese below 1%, that is, the ultrasonic amplifier can hardly dissolve manganese, in other words, the ultrasonic amplifier can be directly used. Acid leaching of cobalt and nickel, the effect of this can be omitted. In the prior art, manganese, cobalt, nickel should be extracted and separated into a manganese solution and a cobalt and nickel solution, and then extracted and separated into a cobalt solution and a nickel solution. Two-stage extraction process. Ultrasonic amplifier is acid soluble to separate manganese, acid immersion liquid only needs extraction The one-stage extraction process, which is separated into a cobalt solution and a nickel solution, can greatly reduce the amount of solvent operation during extraction.
在實驗4~實驗8中,分別利用超音波震盪槽以及磁石攪拌機以進行酸溶之溶出率,並在實驗5、6、7、8係每小時加入0.25ml、0.5ml、1.25ml以及0.5ml之過氧化氫,此超音波震盪槽之設定溫度為攝氏55度且進行酸溶4小時,最後使用火焰式原子吸收光譜儀測定溶出濃度,計算溶出率。 In Experiments 4 to 8, ultrasonic wave oscillating tanks and magnet mixers were used to separate the acid dissolution rate, and 0.25 ml, 0.5 ml, 1.25 ml, and 0.5 ml were added per hour in experiments 5, 6, 7, and 8. The hydrogen peroxide was set at a temperature of 55 degrees Celsius and acid-dissolved for 4 hours. Finally, the dissolution concentration was measured by a flame atomic absorption spectrometer to calculate the dissolution rate.
由實驗結果可得知,當使用超音波震盪槽輔助溶出正極材料時,只需原20%的過氧化氫即可將錳、鈷、鎳及鋰溶出,可大幅減少雙氧水之使用量。 It can be seen from the experimental results that when the ultrasonic oscillating tank is used to assist in the dissolution of the positive electrode material, only the original 20% hydrogen peroxide can be used to dissolve manganese, cobalt, nickel and lithium, which can greatly reduce the amount of hydrogen peroxide used.
請參閱第2A圖~第2C圖,其係根據本發明之另一實施例之酸溶提取金屬濃度之第一示意圖、第二示意圖以及第三示意圖。其相同的實驗方式均為將10g之正極材料浸入4.0N之H2SO4中,不同點在於第2A圖更加入10ml 鹽酸並加熱至65度C(正負5度之間)並攪拌8小時,第2B圖不加入10ml鹽酸並加熱至65度C(正負5度之間)並攪拌8小時,同時在第1小時加入2.5ml的過氧化氫(濃度為35%),第2C圖亦不加入10ml鹽酸,並加熱至50度C(正負5度之間)並攪拌3小時,同時每一小時加入2.5ml的過氧化氫(濃度為35%)。 Please refer to FIG. 2A to FIG. 2C , which are a first schematic diagram, a second schematic diagram and a third schematic diagram of an acid-soluble extraction metal concentration according to another embodiment of the present invention. The same experimental method was carried out by immersing 10 g of the positive electrode material in 4.0 N of H 2 SO 4 , except that in FIG. 2A, 10 ml of hydrochloric acid was further added and heated to 65° C. (between plus and minus 5 degrees) and stirred for 8 hours. Figure 2B does not add 10ml of hydrochloric acid and heated to 65 degrees C (between plus and minus 5 degrees) and stirred for 8 hours, while adding 2.5ml of hydrogen peroxide (concentration of 35%) in the first hour, the second C chart is not added 10 ml of hydrochloric acid was heated to 50 ° C (between plus and minus 5 degrees) and stirred for 3 hours while 2.5 ml of hydrogen peroxide (concentration 35%) was added every hour.
第2A圖代表習知所使用之有價金屬溶出方式,第2B圖為結合過氧化氫與習知之溶出方式,第2C圖為拼棄習知加入鹽酸以進行酸溶之步驟,利用逐次加入35%濃度之過氧化氫,且此過氧化氫與硫酸之體積比為1:100,在此時所溶出之有價金屬濃度為最高,而利用習知技術所溶出之有價金屬濃度為最低。故由此可知,過氧化氫協同硫酸對金屬氧化物中金屬的溶出有極大之幫助,且當提高溫度時可促進硫酸對金屬氧化物中金屬的溶出,且鹽酸對硫酸亦可產生些微的協同作用。 Fig. 2A represents a method of eluting a valuable metal used in the prior art, Fig. 2B is a combination of hydrogen peroxide and a conventional dissolution method, and Fig. 2C is a step of abandoning the conventional addition of hydrochloric acid for acid dissolution, using a sequential addition of 35%. The concentration of hydrogen peroxide, and the volume ratio of hydrogen peroxide to sulfuric acid is 1:100, at which the concentration of the valuable metal eluted is the highest, and the concentration of the valuable metal eluted by the prior art is the lowest. Therefore, it can be seen that hydrogen peroxide and sulfuric acid greatly contribute to the dissolution of metal in metal oxides, and when the temperature is raised, the dissolution of metal in metal oxides by sulfuric acid can be promoted, and hydrochloric acid can also produce slight synergy with sulfuric acid. effect.
請參閱第3A圖~第3C圖,其係根據本發明之第二實施例之溶劑萃取及反萃之第一示意圖、第二示意圖及第三示意圖。正極材料經酸溶程序將錳、鈷、鎳及鋰自氧化物固體中溶出後,接著進行溶劑萃取以分離錳、鈷、鎳及鋰。其中,在分離錳時可利用D2EHPA進行萃取以及酸反萃,實驗的條件為將D2EHPA(圖中之P204即表示D2EHPA)與煤油以3:7體積比混合作為萃取劑,油水比(O/A)為1,調整不同的pH 2.5~3.8,分別進行30min振盪萃取平衡後,檢測萃餘液的主要金屬離子濃度。如第3A圖所示,相對於鈷、鎳及鋰,錳極易被D2EHPA萃取劑抓取,且pH越高(故以pH2.5為最佳),錳的萃取率越高,但伴隨著鈷、鎳、鋰的萃取率也會增高。因此,萃取平衡欲回收高純度物質需操作於低萃取率(A區),而高萃取率則伴隨著低純度回收物(B區)。要同時於操作於高萃取率,且回收高純度物質,則需要採用錯流萃取、逆向串級萃取或批次循環萃取及反萃。 Please refer to FIG. 3A to FIG. 3C , which are a first schematic diagram, a second schematic diagram and a third schematic diagram of solvent extraction and stripping according to a second embodiment of the present invention. The positive electrode material is dissolved in the oxide solid by an acid solution procedure, followed by solvent extraction to separate manganese, cobalt, nickel and lithium. Among them, when separating manganese, D2EHPA can be used for extraction and acid stripping. The experimental conditions are as follows: D2EHPA (P204 in the figure means D2EHPA) and kerosene mixed in a volume ratio of 3:7 as extractant, oil-water ratio (O/A) ), the different pH values of 2.5 to 3.8 were adjusted, and the main metal ion concentration of the raffinate was detected after 30 min oscillation extraction equilibrium. As shown in Figure 3A, manganese is easily captured by D2EHPA extractant relative to cobalt, nickel and lithium, and the higher the pH (so the best pH2.5), the higher the extraction rate of manganese, but accompanied by The extraction rate of cobalt, nickel and lithium will also increase. Therefore, the extraction equilibrium is required to operate at a low extraction rate (zone A), while the high extraction rate is accompanied by a low purity recovery (zone B). To operate at high extraction rates simultaneously and to recover high purity materials, cross-flow extraction, reverse cascade extraction or batch cycle extraction and stripping are required.
第3B圖係將D2EHPA萃取所得之高量錳油相液,以不同當量濃 度0.1、0.4、0.7、1.0、1.5、2.0N的硫酸進行反萃取。實驗的油水比(O/A)為5,使用不同當量的硫酸持續進行反萃取,並分別檢測每個當量反萃液的主要金屬離子濃度。在1.0N的硫酸反萃液中已足以將D2EHPA萃取油相液中的高量錳反萃至水相,以供後續資源化為金屬錳或錳鹽。反萃液當量濃度須適當選擇,當量濃度過低,錳的反萃率低;當量濃度過高,會造成D2EHPA萃取劑pH值過低,後續循環萃取,需再大幅調整pH值。 Figure 3B shows the high amount of manganese oil phase liquid obtained by extracting D2EHPA with different equivalents. The sulfuric acid of degree 0.1, 0.4, 0.7, 1.0, 1.5, 2.0 N was subjected to back extraction. The oil-water ratio (O/A) of the experiment was 5, and back extraction was continued using different equivalents of sulfuric acid, and the main metal ion concentration of each equivalent stripping solution was separately measured. In the 1.0 N sulfuric acid stripping solution, it is sufficient to strip the high amount of manganese in the D2EHPA extracted oil phase liquid to the aqueous phase for subsequent resource conversion to the metal manganese or manganese salt. The equivalent concentration of the stripping solution should be appropriately selected, the equivalent concentration is too low, and the stripping rate of manganese is low; if the equivalent concentration is too high, the pH value of the D2EHPA extracting agent is too low, and the subsequent cyclic extraction requires a large adjustment of the pH value.
如第3C圖所示,其實驗的條件是將D2EHPA與煤油以3:7體積比混合作為萃取劑,油水比(O/A)為1,調整至pH 5,分別進行30min振盪萃取平衡後,檢測萃餘液的主要金屬離子濃度。萃取劑經2.0N硫酸反萃後,循環再次萃取原萃餘液,總計循環萃取及反萃三次。由含有錳、鈷及鎳之溶液每次被萃取前後的各個金屬離子的濃度差,計算得各個金屬離子的萃取率。 As shown in Fig. 3C, the experimental conditions were as follows: D2EHPA and kerosene were mixed at a volume ratio of 3:7 as an extractant, and the oil-water ratio (O/A) was 1, adjusted to pH 5, and after 30 min of shaking extraction and equilibration, respectively. The main metal ion concentration of the raffinate is detected. After the extractant is back-extracted with 2.0 N sulfuric acid, the original raffinate is extracted again by circulation, and the total extraction and back extraction are performed three times. The extraction ratio of each metal ion was calculated from the difference in concentration of each metal ion before and after the extraction of the solution containing manganese, cobalt, and nickel.
含有錳、鈷及鎳之溶液在D2EHPA萃取劑中,經批次循環萃取後,原含有錳、鈷及鎳之溶液的錳萃取率,經三次循環萃取及反萃,由40.84%逐次提升至71.75%及89.00%,而其他金屬的萃取率則維持在變化不大的低水準狀態。因此三次循環萃取及反萃,可有效提升錳的萃取率,且可將所萃取的錳溶液中的其他雜金屬維持在低含量水準。此時再利用一氧化還原反應對此溶液進行一pH值之調整,使錳沉澱,並藉由過濾錳使其成為一固態鹽之形態來加以回收。 The solution containing manganese, cobalt and nickel in the D2EHPA extractant, after batch batch extraction, the manganese extraction rate of the solution containing manganese, cobalt and nickel, after three cycles of extraction and stripping, from 40.84% to 71.75 % and 89.00%, while the extraction rate of other metals is maintained at a low level of change. Therefore, the three-cycle extraction and stripping can effectively increase the extraction rate of manganese, and maintain the other impurities in the extracted manganese solution at a low level. At this time, the pH of the solution is adjusted by a redox reaction to precipitate manganese and recovered by filtering manganese into a solid salt form.
承上,利用類似的作法可對鈷進行回收,利用HEHEHP與煤油以2:8體積比混合作為含有鈷、鎳及鋰溶液的萃取劑,油水比(O/A)為1,調整pH至5,經三次循環萃取及反萃。再以1.5N的硫酸反萃液,油水比(O/A)為1,足以將HEHEHP萃取油相液中的高量鈷反萃至水相。再將水相反萃溶液電解回收鈷,陽極使用不溶性陽極,陰極使用不銹鋼,電極有效電解面積36cm2,電解液pH 4.5,槽液溫度50℃,電流密度為1.5A/dm2,電解時間為48小時,可得 純度97.7%金屬鈷。第4圖係顯示含鈷、鎳及鋰溶液每次被萃取前後的各個金屬離子的濃度差,並顯示萃取各個金屬離子之萃取率。第5A圖及第5B圖則分別顯示第一次反萃及第二次反萃時所得金屬濃度與反萃液當量濃度之示意圖。 Cobalt can be recovered by a similar method. HEHEHP and kerosene are mixed in a 2:8 volume ratio as an extractant containing cobalt, nickel and lithium solutions. The oil-water ratio (O/A) is 1, and the pH is adjusted to 5. , after three cycles of extraction and stripping. The 1.5N sulfuric acid stripping solution has an oil to water ratio (O/A) of 1, which is sufficient to strip the high amount of cobalt in the HEHEHP extracted oil phase liquid to the aqueous phase. The water is reversely extracted and the solution is electrolyzed to recover cobalt. The anode is made of insoluble anode, the cathode is made of stainless steel, the effective electrolytic area of the electrode is 36 cm 2 , the electrolyte pH is 4.5, the bath temperature is 50 ° C, the current density is 1.5 A/dm 2 , and the electrolysis time is 48. In an hour, a purity of 97.7% metallic cobalt can be obtained. Figure 4 shows the difference in concentration of each metal ion before and after each extraction of the cobalt, nickel and lithium solutions, and shows the extraction rate of each metal ion. Fig. 5A and Fig. 5B are schematic diagrams showing the concentration of the metal obtained in the first stripping and the second stripping, respectively, and the equivalent concentration of the stripping solution.
不同於習知技術利用硫酸或鹽酸進行酸溶,本發明揭露一種新的酸液以提升鈷、錳及鎳等有價金屬之溶出率,經多次試驗後,本發明人發現從廢二次鋰電池回收有價金屬時,在酸溶程序中加入過氧化氫至硫酸中可提升之有價金屬之溶出率,其特徵在於將過氧化氫混合硫酸溶液,實驗例為35%過氧化氫與硫酸之體積比設定為1:100,配合電解或化學沉澱反應,即可從廢二次鋰電池中回收高濃度之錳、鈷或鎳等有價金屬。 Different from the conventional techniques for acid dissolution using sulfuric acid or hydrochloric acid, the present invention discloses a new acid solution for increasing the dissolution rate of valuable metals such as cobalt, manganese and nickel. After repeated tests, the inventors discovered that secondary lithium batteries are discarded. When the pool recovers the valuable metal, the dissolution rate of the valuable metal can be increased by adding hydrogen peroxide to the sulfuric acid in the acid solution process, which is characterized in that the hydrogen peroxide is mixed with the sulfuric acid solution, and the experimental example is the volume of 35% hydrogen peroxide and sulfuric acid. The ratio is set to 1:100, and combined with electrolysis or chemical precipitation reaction, high-concentration metals such as manganese, cobalt or nickel can be recovered from the waste secondary lithium battery.
雖然本發明已參照其例示性實施例而特別地顯示及描述,將為所屬技術領域具通常知識者所理解的是,於不脫離以下申請專利範圍及其等效物所定義之本發明之精神與範疇下可對其進行形式與細節上之各種變更。 The present invention has been particularly shown and described with reference to the exemplary embodiments thereof, and it is understood by those of ordinary skill in the art Various changes in form and detail can be made in the context of the category.
以上所述之實施例僅係為說明本發明之技術思想及特點,其目的在使熟習此項技藝之人士能夠瞭解本發明之內容並據以實施,當不能以之限定本發明之專利範圍,即大凡依本發明所揭示之精神所作之均等變化或修飾,仍應涵蓋在本發明之專利範圍內。 The embodiments described above are merely illustrative of the technical spirit and the features of the present invention, and the objects of the present invention can be understood by those skilled in the art, and the scope of the present invention cannot be limited thereto. That is, the equivalent variations or modifications made by the spirit of the present invention should still be included in the scope of the present invention.
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