CN103757399A - Leaching method of lithium cobaltate waste battery positive electrode material - Google Patents
Leaching method of lithium cobaltate waste battery positive electrode material Download PDFInfo
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Abstract
本发明介绍的钴酸锂废电池正极材料的浸出方法是将从钴酸锂废电池中分离出的并经焙烧预处理得到的正极材料和木屑加入耐压、耐硫酸和硝酸腐蚀的反应釜中,加入硫酸和硝酸的混合溶液,并在密闭条件下进行搅拌浸出。The method for leaching the anode material of lithium cobalt oxide waste battery introduced in the present invention is to add the anode material and sawdust separated from the waste lithium cobalt oxide battery and obtained through roasting pretreatment into a pressure-resistant, sulfuric acid and nitric acid corrosion-resistant reaction kettle , adding a mixed solution of sulfuric acid and nitric acid, and stirring and leaching under airtight conditions.
Description
技术领域 technical field
本发明涉及钴酸锂废电池正极材料的一种浸出方法。 The invention relates to a method for leaching the positive electrode material of lithium cobalt oxide waste batteries.
背景技术 Background technique
钴酸锂电池是一类广泛使用的电池,该电池使用报废后将产生大量废电池。由于这类电池含有大量重金属,若弃入环境,将对环境产生很大的直接和潜在危害。钴酸锂废电池正极材料主要含钴、锂、铜和铝,其中钴、锂和铜三者的总含量大于60%,很具回收价值。目前从钴酸锂废电池正极材料中回收钴、锂和铜的工艺主要有火法工艺和湿法工艺。火法工艺得到的产品为合金材料,很难获得较纯的钴、锂和铜。湿法工艺比较容易得到较纯的钴、锂和铜。浸出是湿法工艺中必不可少的一个过程。目前钴酸锂废电池正极材料的浸出方法主要有盐酸浸出法、硫酸浸出法、硝酸浸出法和混酸(硫酸加硝酸)浸出法。盐酸浸出法,设备腐蚀大,酸雾产生量大而污染环境。硫酸浸出法消耗较昂贵的还原剂(如双氧水等)。硝酸浸出法的硝酸消耗量大,而且会产生大量氮氧化物,污染环境。所有的湿法工艺都存在如何经济地提高浸出速度、提高金属浸出率、降低酸耗和其它辅料消耗的问题。虽然硝酸加工业纯氧浸出法和混酸加工业纯氧浸出法较好地解决了上述问题,但浸出设备较复杂,而且废电池浸出所需工业纯氧量不大,废电池处理企业就地生产工业纯氧自用不经济,工业纯氧的储存、运输和使用比较麻烦。开发设备腐蚀小、浸出速度快、浸出率高、酸耗和其它辅料消耗低、使用方便、基本无环境污染的钴酸锂废电池正极材料的浸出方法具有较大实用价值。 Lithium cobalt oxide battery is a type of battery widely used, and a large amount of waste batteries will be generated after the battery is scrapped. Because this type of battery contains a large amount of heavy metals, if it is discarded into the environment, it will cause great direct and potential harm to the environment. The positive electrode material of lithium cobalt oxide waste batteries mainly contains cobalt, lithium, copper and aluminum, and the total content of cobalt, lithium and copper is more than 60%, which is very valuable for recycling. At present, the processes for recovering cobalt, lithium and copper from the positive electrode materials of lithium cobalt oxide waste batteries mainly include fire process and wet process. The products obtained by the fire process are alloy materials, and it is difficult to obtain relatively pure cobalt, lithium and copper. The wet process is relatively easy to obtain relatively pure cobalt, lithium and copper. Leaching is an essential process in the wet process. At present, the leaching methods of lithium cobalt oxide waste battery positive electrode materials mainly include hydrochloric acid leaching method, sulfuric acid leaching method, nitric acid leaching method and mixed acid (sulfuric acid plus nitric acid) leaching method. In the hydrochloric acid leaching method, the equipment is corroded, and the acid mist is produced in large quantities, which pollutes the environment. Sulfuric acid leaching consumes more expensive reducing agents (such as hydrogen peroxide, etc.). The consumption of nitric acid in the nitric acid leaching method is large, and a large amount of nitrogen oxides will be produced, which will pollute the environment. All wet processes have the problem of how to economically increase the leaching speed, increase the metal leaching rate, and reduce the consumption of acid and other auxiliary materials. Although the pure oxygen leaching method in the nitric acid processing industry and the pure oxygen leaching method in the mixed acid processing industry have solved the above problems, the leaching equipment is more complicated, and the amount of industrial pure oxygen required for the leaching of waste batteries is not large, and waste battery treatment enterprises produce on-site Industrial pure oxygen is not economical for personal use, and the storage, transportation and use of industrial pure oxygen are troublesome. The development of a leaching method for lithium cobalt oxide waste battery cathode materials with low equipment corrosion, fast leaching speed, high leaching rate, low acid consumption and other auxiliary material consumption, convenient use, and basically no environmental pollution has great practical value.
发明内容 Contents of the invention
针对目前钴酸锂废电池正极材料浸出的问题,本发明的目的是寻找一种金属浸出率高,浸出速度快,浸出率高,酸耗和其它辅料消耗低,使用方便,不用昂贵还原剂,基本无环境污染的钴酸锂废电池正极材料的浸出方法,其特征在于将从钴酸锂废电池中分离出的并经焙烧预处理得到的正极材料和≤1.5mm的木屑加入耐压、耐硫酸和硝酸腐蚀的反应釜中,加入硫酸和硝酸的混合溶液,并在密闭条件下进行搅拌浸出。浸出结束后 进行液固分离,得到所需浸出溶液。反应温度为60℃~80℃, 浸出的硫酸初始浓度为1mol/L~4mol/L, 硝酸的初始浓度为5g/L~10g/L 浸出时间为2h~4h,浸出过程进行搅拌,搅拌速度为30r/min~120r/min。硫酸加入量为加入反应容器的正极材料中全部金属浸出的硫酸理论消耗量的110%~140%。木屑的加入量以干基计为正极材料中LiCoO2质量的90%~120%。 Aiming at the problem of leaching the positive electrode material of the lithium cobalt oxide waste battery at present, the purpose of the present invention is to find a metal leaching rate high, the leaching speed is fast, the leaching rate is high, the consumption of acid and other auxiliary materials is low, the use is convenient, and no expensive reducing agent is used. The method for leaching the anode material of lithium cobaltate waste battery which is basically non-environmentally polluting is characterized in that the positive electrode material separated from the waste lithium cobaltate battery and obtained through roasting pretreatment and sawdust of ≤1.5mm are added to withstand voltage and withstand pressure. Add the mixed solution of sulfuric acid and nitric acid into the reaction kettle corroded by sulfuric acid and nitric acid, and carry out stirring and leaching under airtight conditions. After leaching, liquid-solid separation is carried out to obtain the desired leaching solution. The reaction temperature is 60℃~80℃, the initial concentration of leached sulfuric acid is 1mol/L~4mol/L, the initial concentration of nitric acid is 5g/L~10g/L, the leaching time is 2h~4h, the leaching process is stirred, and the stirring speed is 30r/min~120r/min. The amount of sulfuric acid added is 110% to 140% of the theoretical consumption of sulfuric acid for the leaching of all metals in the positive electrode material added to the reaction vessel. The amount of sawdust added is 90% to 120% of the mass of LiCoO 2 in the cathode material on a dry basis.
本发明的目的是这样实现的:在密闭并有木屑和硝酸存在的条件下,硫酸浸出经焙烧预处理后的钴酸锂废电池正极材料(材料中的钴和锂以钴酸锂形式存在,铜和铝主要呈金属氧化物形态)时,浸出过程发生如下主要化学反应: The object of the present invention is achieved like this: under the condition that airtight and have sawdust and nitric acid to exist, sulfuric acid leaches the waste lithium cobaltate battery anode material (cobalt and lithium in the material exist in the form of lithium cobaltate after roasting pretreatment, When copper and aluminum are mainly in the form of metal oxides), the following main chemical reactions occur during the leaching process:
CuO + H2SO4 = CuSO4 + H2O CuO + H2SO4 = CuSO4 + H2O
Al2O3 + 3H2SO4 = 3Al2(SO4)3 + 3H2O Al 2 O 3 + 3H 2 SO 4 = 3Al 2 (SO 4 ) 3 + 3H 2 O
nC6H10O5 + nH2SO4 =n(C5H11O5)HSO4 nC 6 H 10 O 5 + nH 2 SO 4 =n(C 5 H 11 O 5 )HSO 4
n(C5H11O5)HSO4 + nH2O = nC6H12O6 + nH2SO4 n(C 5 H 11 O 5 )HSO 4 + nH 2 O = nC 6 H 12 O 6 + nH 2 SO 4
C6H12O6 + 8HNO3 = 8NO + 6CO2 + 10H2O C 6 H 12 O 6 + 8HNO 3 = 8NO + 6CO 2 + 10H 2 O
nC6H10O5 + 8nHNO3 = 8nNO + 6nCO2 + 9nH2O nC 6 H 10 O 5 + 8nHNO 3 = 8nNO + 6nCO 2 + 9nH 2 O
6LiCoO2 + 9H2SO4 + 2NO = 6CoSO4 + 3Li2SO4 + 2HNO3 + 8H2O 6LiCoO 2 + 9H 2 SO 4 + 2NO = 6CoSO 4 + 3Li 2 SO 4 + 2HNO 3 + 8H 2 O
钴酸锂的总反应为: The overall reaction of lithium cobaltate is:
24nLiCoO2 + nC6H10O5 + 36nH2SO4 = 24nCoSO4 + 12nLi2SO4 + 6nCO2 + 41nH2O 24nLiCoO 2 + nC 6 H 10 O 5 + 36nH 2 SO 4 = 24nCoSO 4 + 12nLi 2 SO 4 + 6nCO 2 + 41nH 2 O
木屑中的其它有机物也与硝酸反应生成NO、CO2和H2O,生成的NO与LiCoO2和H2SO4按前述反应生成CoSO4 、Li2SO4、HNO3和H2O。 Other organic matter in sawdust also reacts with nitric acid to generate NO, CO 2 and H 2 O, and the generated NO reacts with LiCoO 2 and H 2 SO 4 to generate CoSO 4 , Li 2 SO 4 , HNO 3 and H 2 O.
由于硝酸与木屑的反应速度较快,产生的NO与LiCoO2的反应也较快,由此加快整个浸出过程,并实现LiCoO2较完全浸出。NO可以彻底破坏正极材料中高价氧化物的层状结构,提高有价金属的浸出率。 Since the reaction speed of nitric acid and wood chips is faster, the reaction of NO produced with LiCoO 2 is also faster, thereby speeding up the entire leaching process and achieving a more complete leaching of LiCoO 2 . NO can completely destroy the layered structure of high-valent oxides in positive electrode materials and improve the leaching rate of valuable metals.
相对于现有方法,本发明的突出优点是采用木屑作还原剂,硝酸作浸出加速剂浸出钴酸锂废电池正极材料,反应速度快,反应酸度较低,硫酸和还原剂的消耗量小,并且木屑便宜;正极材料中高价氧化物的层状结构破坏彻底,可提高金属浸出率;浸出液后续处理中不需要中和大量的酸,成本较低;浸出液后续处理中产生的废弃物量少,降低了污染治理费用,具有明显的经济效益和环境效益;过程在密闭条件下进行,避免了NO逸出产生的环境污染。 Compared with the existing method, the present invention has the outstanding advantages of using sawdust as the reducing agent and nitric acid as the leaching accelerator to leach the positive electrode material of the lithium cobalt oxide waste battery. The reaction speed is fast, the reaction acidity is low, and the consumption of sulfuric acid and reducing agent is small. And the wood chips are cheap; the layered structure of the high-valent oxide in the positive electrode material is completely destroyed, which can increase the metal leaching rate; the subsequent treatment of the leachate does not need to neutralize a large amount of acid, and the cost is low; the amount of waste generated in the subsequent treatment of the leachate is small. The cost of pollution control is reduced, and it has obvious economic and environmental benefits; the process is carried out under airtight conditions, which avoids environmental pollution caused by NO escape.
具体实施方法Specific implementation method
实施例1:将100g钴酸锂废电池正极材料(含钴53.6%,锂5.3%、铜8.2%、铝3.4%)和≤1.5mm木屑30g加入容积为2L的衬钛压力反应釜中,加入硫酸浓度为1.5mol/L、硝酸浓度为5g/L的混酸溶液1180ml,在60℃~70℃下密闭搅拌(搅拌速度80r/min)浸出4.0h,浸出结束后进行液固分离,得到1160ml浸出溶液(不含浸出渣洗涤水)。钴、锂、铜和铝的浸出率分别为99.0%、99.3%、98.5%和98.8%(按进入浸出溶液和浸出渣洗涤液中的钴、锂、铜和铝计算)。 Example 1: Add 100g of lithium cobalt oxide waste battery cathode material (containing 53.6% cobalt, 5.3% lithium, 8.2% copper, 3.4% aluminum) and 30g of sawdust ≤ 1.5mm into a titanium-lined pressure reactor with a volume of 2L, and add 1180ml of mixed acid solution with a concentration of sulfuric acid of 1.5mol/L and a concentration of nitric acid of 5g/L was leached at 60°C to 70°C with airtight stirring (stirring speed 80r/min) for 4.0h, and liquid-solid separation was carried out after leaching to obtain 1160ml of leaching solution (without leaching slag washing water). The leaching rates of cobalt, lithium, copper and aluminum are 99.0%, 99.3%, 98.5% and 98.8% respectively (calculated based on cobalt, lithium, copper and aluminum entering the leaching solution and leaching slag washing solution).
实施例2:将500g钴酸锂废电池正极材料(含钴53.6%,锂5.3%、铜8.2%、铝3.4%)≤1.5mm木屑190g加入容积为5L的衬钛压力反应釜中,加入硫酸浓度为3.0mol/L、硝酸浓度为10g/L的混酸溶液3500ml,在70℃~80℃下密闭搅拌(搅拌速度70r/min)浸出2h,浸出结束后进行液固分离,得到3300ml浸出溶液(不含浸出渣洗涤水),钴、锂、铜和铝的浸出率分别为99.3%、99.5%、99.0%和98.7%(按进入浸出溶液和浸出渣洗涤液中的钴、锂、铜和铝计算)。 Example 2: Add 500g of lithium cobalt oxide waste battery positive electrode material (containing 53.6% cobalt, 5.3% lithium, 8.2% copper, 3.4% aluminum)≤1.5mm sawdust 190g into a titanium-lined pressure reactor with a volume of 5L, and add sulfuric acid Concentration of 3.0mol/L, nitric acid concentration of 10g/L mixed acid solution 3500ml, at 70 ℃ ~ 80 ℃ closed stirring (stirring speed 70r/min) leaching 2h, liquid-solid separation after leaching, to obtain 3300ml leaching solution ( does not contain leaching slag washing water), the leaching rates of cobalt, lithium, copper and aluminum are 99.3%, 99.5%, 99.0% and 98.7% respectively (according to the cobalt, lithium, copper and aluminum in the leaching solution and leaching slag washing solution calculate).
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Publication number | Priority date | Publication date | Assignee | Title |
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CN115652098A (en) * | 2022-11-29 | 2023-01-31 | 湘潭大学 | Green reduction leaching method for waste lithium ion battery electrode powder mixed material |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101928831A (en) * | 2009-06-23 | 2010-12-29 | 四川师范大学 | Leaching method of lithium cobalt oxide waste battery cathode material |
CN102030375A (en) * | 2010-10-29 | 2011-04-27 | 北京矿冶研究总院 | Method for preparing lithium cobaltate by directly using failed lithium ion battery |
-
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Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101928831A (en) * | 2009-06-23 | 2010-12-29 | 四川师范大学 | Leaching method of lithium cobalt oxide waste battery cathode material |
CN102030375A (en) * | 2010-10-29 | 2011-04-27 | 北京矿冶研究总院 | Method for preparing lithium cobaltate by directly using failed lithium ion battery |
Non-Patent Citations (1)
Title |
---|
李进中等: "氧化锰矿还原浸出工艺技术研究进展", 《中国锰业》, vol. 29, no. 4, 30 November 2011 (2011-11-30), pages 1 - 7 * |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN115652098A (en) * | 2022-11-29 | 2023-01-31 | 湘潭大学 | Green reduction leaching method for waste lithium ion battery electrode powder mixed material |
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