CN106299526A - Recycling method of strong alkali solution in waste lithium battery recycling industry - Google Patents
Recycling method of strong alkali solution in waste lithium battery recycling industry Download PDFInfo
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Abstract
本发明涉及一种废旧锂电池回收行业强碱溶液的回收利用方法。本发明属于废旧锂离子电池回收技术领域。废旧锂电池回收行业强碱溶液的回收利用方法:(1)含铝物料分离:将废旧锂电池进行机械破碎,加入水进行搅拌,浆料过筛,筛上物为含铝物料;(2)铝的溶解:含铝物料加入到3‑25mol/L的氢氧化钠溶液中,搅拌反应过筛子,滤液为含铝强碱溶液;(3)铝强碱溶液离子比例的调整:添加氢氧化钠或水调整溶液中钠离子浓度为6‑25mol/L,铝离子浓度为0.001‑1mol/L;(4)含铝强碱溶液的利用:所得强碱溶液为沉淀剂,与目标盐溶液反应,制得磷酸铁锂、三元材料正极材料的前躯体,进而制得磷酸铁锂、三元材料目标正极材料。本发明具有工艺简单,操作方便,绿色、环保,低成本,高附加值等优点。
The invention relates to a method for recycling strong alkali solution in the waste lithium battery recycling industry. The invention belongs to the technical field of recycling waste lithium ion batteries. Recycling and utilization methods of strong alkaline solutions in the waste lithium battery recycling industry: (1) Separation of aluminum-containing materials: mechanically crush the waste lithium batteries, add water for stirring, slurry is screened, and the material on the screen is aluminum-containing materials; (2) Dissolution of aluminum: Add aluminum-containing materials to 3-25mol/L sodium hydroxide solution, stir the reaction and pass through a sieve. The filtrate is an aluminum-containing strong alkali solution; (3) Adjustment of the ion ratio of the aluminum strong alkali solution: add sodium hydroxide Or water to adjust the sodium ion concentration in the solution to 6-25mol/L and the aluminum ion concentration to 0.001-1mol/L; (4) Utilization of aluminum-containing strong alkali solution: the obtained strong alkali solution is used as a precipitant and reacts with the target salt solution. Precursors of lithium iron phosphate and ternary material cathode materials are prepared, and then lithium iron phosphate and ternary material target cathode materials are prepared. The invention has the advantages of simple process, convenient operation, green, environmental protection, low cost, high added value and so on.
Description
技术领域technical field
本发明属于废旧锂离子电池回收技术领域,特别是涉及一种废旧锂电池回收行业强碱溶液的回收利用方法。The invention belongs to the technical field of waste lithium ion battery recycling, in particular to a method for recycling strong alkali solution in the waste lithium battery recycling industry.
背景技术Background technique
目前,随着电动汽车产业快速增长,到2020年,仅我国电动汽车动力电池累计报废量将达到12万-17万吨的规模。如果不能进行妥善的回收处理,将会对环境造成巨大的破坏。At present, with the rapid growth of the electric vehicle industry, by 2020, the cumulative scrap of electric vehicle power batteries in my country alone will reach a scale of 120,000-170,000 tons. If it cannot be properly recycled, it will cause huge damage to the environment.
专利CN101921917B公开了一种从废旧锂电池回收有价金属的方法。该方法将放电后的废旧锂电池机械粉碎,高温350℃~400℃煅烧,得到含钴、铝、铜的物料,再加入含量为5%~10%的氢氧化钠溶液,反应2-3h,对碱液过滤,洗涤,干燥得到含钴、铜的物料。其中的碱液中含有大量的铝,经进一步的酸处理及过滤洗涤等技术得到氢氧化铝晶体。该专利中铝箔回收方法是目前锂离子电池回收行业中铝箔的主要回收方法,专利CN101217206A、CN104157926A等采用同样的方法达到将铝箔回收再利用的目的。该法在酸处理时需加入大量硫酸,来中和碱液中的碱,达到调节pH值进而实现氢氧化铝沉淀的目的。此时,滤液中含有大量硫酸钠而无法循环利用,产生的废液需进行处理以避免对环境的二次污染,废水处理量大,并且酸处理时消耗大量硫酸,成本较高。Patent CN101921917B discloses a method for recovering valuable metals from waste lithium batteries. In this method, the discharged waste lithium battery is mechanically crushed, calcined at a high temperature of 350°C to 400°C to obtain a material containing cobalt, aluminum, and copper, and then a sodium hydroxide solution with a content of 5% to 10% is added to react for 2-3 hours. The lye is filtered, washed, and dried to obtain materials containing cobalt and copper. The lye contains a large amount of aluminum, and aluminum hydroxide crystals are obtained through further acid treatment, filtration and washing. The aluminum foil recycling method in this patent is currently the main recycling method for aluminum foil in the lithium ion battery recycling industry. Patents CN101217206A, CN104157926A, etc. use the same method to achieve the purpose of recycling aluminum foil. In this method, a large amount of sulfuric acid needs to be added during the acid treatment to neutralize the alkali in the lye, so as to adjust the pH value and realize the purpose of aluminum hydroxide precipitation. At this time, the filtrate contains a large amount of sodium sulfate and cannot be recycled, and the waste liquid generated needs to be treated to avoid secondary pollution to the environment. The amount of waste water to be treated is large, and a large amount of sulfuric acid is consumed during acid treatment, resulting in high cost.
专利CN102285738B公开了一种废旧锂电池回收行业高盐废水的处理方法。该法通过反渗透工艺得到净化水和浓水,浓水通过自然蒸发或低温结晶或多级闪蒸的方法,得到盐产品。所用反渗透膜成本较高,处理效率有限,而且存以后期盐分结晶过程能耗较大或处理时间极长等技术问题。Patent CN102285738B discloses a treatment method for high-salt wastewater in the waste lithium battery recycling industry. This method obtains purified water and concentrated water through reverse osmosis technology, and the concentrated water obtains salt products through natural evaporation or low-temperature crystallization or multi-stage flash evaporation. The cost of the reverse osmosis membrane used is high, the treatment efficiency is limited, and there are technical problems such as high energy consumption or extremely long treatment time in the later salt crystallization process.
发明内容Contents of the invention
本发明为解决公知技术中存在的技术问题而提供一种废旧锂电池回收行业强碱溶液的回收利用方法。In order to solve the technical problems existing in the known technology, the invention provides a method for recycling strong alkali solution in the waste lithium battery recycling industry.
本发明的目的是提供一种具有工艺简单,操作方便,只需微调离子比例既可用于锂离子电池正极材料磷酸铁锂、三元材料等前躯体的生产过程,绿色、环保,低成本,高附加值等特点的废旧锂电池回收行业强碱溶液的回收利用方法。The purpose of the present invention is to provide a production process with simple process and convenient operation, which can be used in the production process of precursors such as lithium iron phosphate and ternary materials, which are green, environmentally friendly, low-cost, and high-efficiency. The recycling method of the strong alkali solution in the waste lithium battery recycling industry with the characteristics of added value and so on.
本发明废旧锂电池回收行业强碱溶液的回收利用方法,包括工艺过程:The recycling method of the strong alkali solution in the waste lithium battery recycling industry of the present invention comprises a process:
⑴含铝物料的分离:将完全放电的废旧锂电池进行机械破碎,加入水进行搅拌加速极片物料与集流体的分离;将搅拌后的浆料通过60目的筛子,筛上物即为含铝物料;⑴Separation of aluminum-containing materials: mechanically crush the fully discharged waste lithium batteries, add water for stirring to accelerate the separation of the electrode material and the current collector; pass the stirred slurry through a 60-mesh sieve, and the sieve is aluminum-containing materials;
⑵铝的溶解:将(1)中所得含铝物料加入到3-25mol/L的氢氧化钠溶液中,搅拌反应1-2h后浆料通过筛子,将滤渣加入到同浓度的氢氧化钠溶液中,同样的工艺进行二次碱浸后过滤,滤渣进行后续处理,滤液并入第一次滤液中,滤液经多次过滤除渣后即为含铝强碱溶液;(2) Dissolution of aluminum: Add the aluminum-containing material obtained in (1) into a 3-25mol/L sodium hydroxide solution, stir and react for 1-2 hours, then pass the slurry through a sieve, and add the filter residue to a sodium hydroxide solution of the same concentration In the same process, filter after secondary alkali leaching, the filter residue is subjected to subsequent treatment, the filtrate is merged into the first filtrate, and the filtrate is a strong alkali solution containing aluminum after repeated filtration to remove residue;
⑶含铝强碱溶液离子比例的调整:用电感耦合等离子体发射光谱仪(ICP)对(2)中钠离子、铝离子浓度进行测试,根据目标产物成分,添加氢氧化钠或水调整溶液中钠离子浓度为6-25mol/L,铝离子浓度为0.001-1mol/L;(3) Adjustment of the ion ratio of the aluminum-containing strong alkali solution: use an inductively coupled plasma emission spectrometer (ICP) to test the concentration of sodium ions and aluminum ions in (2), and add sodium hydroxide or water to adjust the concentration of the solution according to the target product composition. The sodium ion concentration is 6-25mol/L, and the aluminum ion concentration is 0.001-1mol/L;
(4)含铝强碱溶液的回收利用:以(3)所得强碱溶液为沉淀剂,与目标盐溶液进行液相沉淀反应,制得磷酸铁锂、三元材料等正极材料的前躯体,进而制得磷酸铁锂、三元材料等目标正极材料成品。(4) Recycling of aluminum-containing strong alkali solution: use the strong alkali solution obtained in (3) as a precipitating agent, carry out liquid phase precipitation reaction with the target salt solution, and prepare precursors of positive electrode materials such as lithium iron phosphate and ternary materials, Then, target positive electrode materials such as lithium iron phosphate and ternary materials are produced.
本发明废旧锂电池回收行业强碱溶液的回收利用方法所采取的技术方案是:The technical scheme adopted by the recycling method of the strong alkali solution in the waste lithium battery recycling industry of the present invention is:
一种废旧锂电池回收行业强碱溶液的回收利用方法,其特点是:废旧锂电池回收行业强碱溶液的回收利用方法包括以下工艺过程:A method for recycling a strong alkali solution in the waste lithium battery recycling industry is characterized in that: the method for recycling a strong alkali solution in the waste lithium battery recycling industry includes the following process:
(1)含铝物料的分离(1) Separation of aluminum-containing materials
将完全放电的废旧锂电池进行机械破碎,加入水进行搅拌加速极片物料与集流体的分离;将搅拌后的浆料过筛子,筛上物即为含铝物料;The fully discharged waste lithium battery is mechanically crushed, and water is added for stirring to accelerate the separation of the electrode material and the current collector; the stirred slurry is passed through a sieve, and the material on the sieve is the aluminum-containing material;
(2)铝的溶解(2) Dissolution of aluminum
将(1)中所得含铝物料加入到3-25mol/L的氢氧化钠溶液中,搅拌反应1-2h后浆料通过60目筛子,滤液为含铝强碱溶液;Add the aluminum-containing material obtained in (1) to a 3-25mol/L sodium hydroxide solution, stir and react for 1-2h, and then pass the slurry through a 60-mesh sieve, and the filtrate is a strong alkali solution containing aluminum;
(3)铝强碱溶液离子比例的调整(3) Adjustment of ion ratio of aluminum strong alkali solution
根据目标产物成分,添加氢氧化钠或水调整溶液中钠离子浓度为6-25mol/L,铝离子浓度为0.001-1mol/L;According to the target product composition, add sodium hydroxide or water to adjust the sodium ion concentration in the solution to 6-25mol/L, and the aluminum ion concentration to 0.001-1mol/L;
(4)含铝强碱溶液的利用(4) Utilization of aluminum-containing strong alkali solution
以(3)所得强碱溶液为沉淀剂,与目标盐溶液进行液相沉淀反应,制得磷酸铁锂、三元材料正极材料的前躯体,进而制得磷酸铁锂、三元材料目标正极材料成品。Using the strong base solution obtained in (3) as a precipitating agent, carry out a liquid phase precipitation reaction with the target salt solution to prepare the precursor of lithium iron phosphate and ternary material positive electrode materials, and then prepare lithium iron phosphate and ternary material target positive electrode materials finished product.
本发明废旧锂电池回收行业强碱溶液的回收利用方法还可以采用如下技术方案:The recycling method of the strong alkali solution in the waste lithium battery recycling industry of the present invention can also adopt the following technical scheme:
所述的废旧锂电池回收行业强碱溶液的回收利用方法,其特点是:铝的溶解过程中,将(1)中所得含铝物料加入到3-25mol/L的氢氧化钠溶液中搅拌反应1-2h后浆料通过筛子后,将滤渣加入到同浓度的氢氧化钠溶液中,同样的工艺进行二次碱浸后过滤,滤渣进行后续处理,滤液并入第一次滤液中,滤液经2-6次过滤除渣后即为含铝强碱溶液。The method for recycling the strong alkali solution in the waste lithium battery recycling industry is characterized in that during the dissolving process of aluminum, the aluminum-containing material obtained in (1) is added to a 3-25mol/L sodium hydroxide solution and stirred for reaction After 1-2 hours, after the slurry passes through the sieve, the filter residue is added to the sodium hydroxide solution of the same concentration, and the same process is carried out for the second alkali leaching and then filtered, and the filter residue is subjected to subsequent treatment, and the filtrate is incorporated into the first filtrate, and the filtrate is passed through After 2-6 times of filtering to remove slag, it is an aluminum-containing strong alkali solution.
所述的废旧锂电池回收行业强碱溶液的回收利用方法,其特点是:铝强碱溶液离子比例的调整过程中,用电感耦合等离子体发射光谱仪(ICP)对(2)中钠离子、铝离子浓度进行测试,然后根据目标产物成分添加氢氧化钠或水调整溶液中钠离子浓度。The method for recycling the strong alkali solution in the waste lithium battery recycling industry is characterized in that: in the process of adjusting the ion ratio of the aluminum strong alkali solution, the sodium ion, The concentration of aluminum ions is tested, and then sodium hydroxide or water is added according to the target product composition to adjust the concentration of sodium ions in the solution.
所述的废旧锂电池回收行业强碱溶液的回收利用方法,其特点是:含铝强碱溶液的利用过程中,三元材料包括氧化镍钴锰锂、氧化镍钴铝锂以及相应的掺杂改性材料。The method for recycling the strong alkali solution in the waste lithium battery recycling industry is characterized in that during the utilization of the aluminum-containing strong alkali solution, the ternary materials include nickel-cobalt-manganese-lithium oxide, nickel-cobalt-aluminum-lithium oxide and corresponding doped modified material.
所述的废旧锂电池回收行业强碱溶液的回收利用方法,其特点是:磷酸铁锂的前躯体包括磷酸铁及相应的掺杂组分,三元材料的前躯体包括氢氧化镍钴锰或氢氧化镍钴铝以及相应的掺杂组分。The method for recycling strong alkali solution in the waste lithium battery recycling industry is characterized in that: the precursor of lithium iron phosphate includes iron phosphate and corresponding doping components, and the precursor of ternary materials includes nickel hydroxide cobalt manganese or Nickel cobalt aluminum hydroxide and corresponding doping components.
所述的废旧锂电池回收行业强碱溶液的回收利用方法,其特点是:磷酸铁制备时盐溶液包括含铁溶液、含磷溶液或二者的混合溶液;三元材料制备时盐溶液包括含镍溶液、含钴溶液、含锰溶液或者任意几种的混合溶液。The method for recycling the strong alkali solution in the waste lithium battery recycling industry is characterized in that: when ferric phosphate is prepared, the salt solution includes iron-containing solution, phosphorus-containing solution or a mixed solution of the two; when the ternary material is prepared, the salt solution includes Nickel solution, cobalt-containing solution, manganese-containing solution or any mixed solution of several kinds.
本发明具有的优点和积极效果是:The advantages and positive effects that the present invention has are:
废旧锂电池回收行业强碱溶液的回收利用方法由于采用了本发明全新的技术方案,与现有技术相比,本发明具有如下特点:The recycling method of the strong alkali solution in the waste lithium battery recycling industry has adopted the brand-new technical solution of the present invention. Compared with the prior art, the present invention has the following characteristics:
⑴工艺简单:将废旧锂电池中的铝箔用碱溶液溶解后即可用作新的生产原料,无需现有技术中后续的沉淀、洗涤、分离及再生产等工序,使整个回收工艺简化;(1) The process is simple: the aluminum foil in the waste lithium battery can be used as a new production raw material after being dissolved in an alkaline solution, without the subsequent processes of precipitation, washing, separation and reproduction in the prior art, which simplifies the entire recycling process;
⑵绿色环保:无需加入大量硫酸进行酸处理,避免了大量副产物和废水的产生,既降低了强碱溶液回收利用的成本又避免了副产物带来的二次污染;(2) Environmental protection: no need to add a large amount of sulfuric acid for acid treatment, avoiding the generation of a large number of by-products and waste water, which not only reduces the cost of recycling strong alkali solution but also avoids secondary pollution caused by by-products;
⑶高附加值:将回收的强碱溶液用于锂离子电池正极材料前躯体的制备过程,既节约了现有回收技术在碱液回收中的投入,又省去了前躯体制备时所需氢氧化钠与铝盐的成本,提高了整个回收利用工艺的附加值。(3) High added value: The recovered strong alkali solution is used in the preparation process of the precursor of the cathode material of lithium-ion batteries, which not only saves the investment in the recovery of lye in the existing recovery technology, but also saves the hydrogen required for the preparation of the precursor The cost of sodium oxide and aluminum salt increases the added value of the entire recycling process.
附图说明Description of drawings
图1为本发明强碱溶液回收利用工艺图;Fig. 1 is the process figure of strong alkali solution recycling of the present invention;
图2为实施例1所得三元材料前躯体SEM图(Ni1/3Co1/3Mn1/3(OH)2,含Al 1200ppm);Fig. 2 is the SEM image of the ternary material precursor obtained in Example 1 (Ni 1/3 Co 1/3 Mn 1/3 (OH) 2 , containing Al 1200ppm);
图3为实施例2所得三元材料前躯体SEM图(Ni0.5Co0.2Mn0.3(OH)2,含Al 1500ppm);Fig. 3 is the SEM image of the precursor of the ternary material obtained in Example 2 (Ni 0.5 Co 0.2 Mn 0.3 (OH) 2 , containing 1500 ppm of Al);
图4为实施例3三元材料前躯体SEM图(Ni0.6Co0.2Mn0.2(OH)2,含Al 2000ppm);Fig. 4 is the SEM image of the precursor of the ternary material of Example 3 (Ni 0.6 Co 0.2 Mn 0.2 (OH) 2 , containing Al 2000ppm);
图5为实施例4三元材料前躯体SEM图(Ni0.8Co0.15Al0.05(OH)2)。Fig. 5 is an SEM image of the precursor of the ternary material of Example 4 (Ni 0.8 Co 0.15 Al 0.05 (OH) 2 ).
具体实施方式detailed description
为能进一步了解本发明的发明内容、特点及功效,兹例举以下实施例,并配合附图详细说明如下:In order to further understand the invention content, characteristics and effects of the present invention, the following examples are given, and detailed descriptions are as follows in conjunction with the accompanying drawings:
参阅附图1至图5。Refer to accompanying drawing 1 to Fig. 5.
实施例1Example 1
一种废旧锂电池回收行业强碱溶液的回收利用方法,包括以下工艺过程:A method for recycling a strong alkali solution in the waste lithium battery recycling industry, comprising the following process:
1.含铝物料的分离:将完全放电的废旧锂电池进行机械破碎,加入水进行搅拌加速极片物料与集流体的分离;将搅拌后的浆料通过60目的筛子,筛上物即为含铝物料;1. Separation of aluminum-containing materials: Mechanically crush the fully discharged waste lithium batteries, add water for stirring to accelerate the separation of the electrode material and the current collector; pass the stirred slurry through a 60-mesh sieve, and the sieve is the containing aluminum material;
2.铝的溶解:将(1)中所得含铝物料加入到12mol/L的氢氧化钠溶液中,搅拌反应2h后浆料通过60目筛子,将滤渣加入到同浓度的氢氧化钠溶液中,同样的工艺进行二次碱浸后过滤,滤渣进行后续处理,滤液并入第一次滤液中,滤液经多次过滤除渣后即为含铝强碱溶液;2. Dissolution of aluminum: Add the aluminum-containing material obtained in (1) into a 12mol/L sodium hydroxide solution, stir and react for 2 hours, then pass the slurry through a 60-mesh sieve, and add the filter residue into a sodium hydroxide solution of the same concentration , the same process is filtered after secondary alkali leaching, the filter residue is subjected to subsequent treatment, the filtrate is incorporated into the first filtrate, and the filtrate is a strong alkali solution containing aluminum after repeated filtration to remove residue;
3.含铝强碱溶液离子比例的调整:用电感耦合等离子体发射光谱仪(ICP)对(2)所得碱液进行测试,钠离子浓度为11.5mol/L,铝离子浓度为0.1mol/L,根据目标产物成分,添加氢氧化钠与水调整溶液中钠离子浓度为6mol/L,铝离子浓度为0.01mol/L;3. Adjustment of the ion ratio of the aluminum-containing strong alkali solution: the lye obtained in (2) is tested with an inductively coupled plasma emission spectrometer (ICP), and the sodium ion concentration is 11.5mol/L, and the aluminum ion concentration is 0.1mol/L , according to the target product composition, add sodium hydroxide and water to adjust the sodium ion concentration in the solution to 6mol/L, and the aluminum ion concentration to 0.01mol/L;
4.含铝强碱溶液的回收利用:以(3)所得强碱溶液为沉淀剂,与镍离子浓度为0.8mol/L,钴离子浓度为0.8mol/L,锰离子浓度为0.8mol/L的混合盐溶液进行液相沉淀反应,制得111型三元材料前躯体。4. Recycling of aluminum-containing strong alkali solution: with the strong alkali solution obtained in (3) as a precipitant, the concentration of nickel ions is 0.8mol/L, the concentration of cobalt ions is 0.8mol/L, and the concentration of manganese ions is 0.8mol/L The mixed salt solution was subjected to liquid-phase precipitation reaction to obtain the precursor of the 111-type ternary material.
实施例2Example 2
一种废旧锂电池回收行业强碱溶液的回收利用方法,包括以下工艺过程:A method for recycling a strong alkali solution in the waste lithium battery recycling industry, comprising the following process:
1.含铝物料的分离:将完全放电的废旧锂电池进行机械破碎,加入水进行搅拌加速极片物料与集流体的分离;将搅拌后的浆料通过60目的筛子,筛上物即为含铝物料;1. Separation of aluminum-containing materials: Mechanically crush the fully discharged waste lithium batteries, add water for stirring to accelerate the separation of the electrode material and the current collector; pass the stirred slurry through a 60-mesh sieve, and the sieve is the containing aluminum material;
2.铝的溶解:将(1)中所得含铝物料加入到16mol/L的氢氧化钠溶液中,搅拌反应1.5h后浆料通过60目筛子,将滤渣加入到同浓度的氢氧化钠溶液中,同样的工艺进行二次碱浸后过滤,滤渣进行后续处理,滤液并入第一次滤液中,滤液经多次过滤除渣后即为含铝强碱溶液;2. Dissolution of aluminum: Add the aluminum-containing material obtained in (1) to a 16mol/L sodium hydroxide solution, stir and react for 1.5 hours, and then pass the slurry through a 60-mesh sieve, and add the filter residue to a sodium hydroxide solution of the same concentration In the same process, filter after secondary alkali leaching, the filter residue is subjected to subsequent treatment, the filtrate is merged into the first filtrate, and the filtrate is a strong alkali solution containing aluminum after repeated filtration to remove residue;
3.含铝强碱溶液离子比例的调整:用电感耦合等离子体发射光谱仪(ICP)对(2)所得碱液进行测试,钠离子浓度为15mol/L,铝离子浓度为0.2mol/L,根据目标产物成分,添加氢氧化钠与水调整溶液中钠离子浓度为8mol/L,铝离子浓度为0.02mol/L;3. The adjustment of the ion ratio of aluminum-containing strong alkali solution: test the lye obtained in (2) with an inductively coupled plasma emission spectrometer (ICP), the sodium ion concentration is 15mol/L, and the aluminum ion concentration is 0.2mol/L. According to the target product composition, add sodium hydroxide and water to adjust the sodium ion concentration in the solution to be 8mol/L, and the aluminum ion concentration to be 0.02mol/L;
4.含铝强碱溶液的回收利用:以(3)所得强碱溶液为沉淀剂,与镍离子浓度为1.2mol/L,钴离子浓度为0.48mol/L,锰离子浓度为0.72mol/L的混合盐溶液进行液相沉淀反应,制得523型三元材料前躯体。4. Recycling of aluminum-containing strong alkali solution: with the strong alkali solution obtained in (3) as a precipitant, the concentration of nickel ions is 1.2mol/L, the concentration of cobalt ions is 0.48mol/L, and the concentration of manganese ions is 0.72mol/L The mixed salt solution was subjected to liquid-phase precipitation reaction to obtain the precursor of the 523-type ternary material.
实施例3Example 3
一种废旧锂电池回收行业强碱溶液的回收利用方法,包括以下工艺过程:A method for recycling a strong alkali solution in the waste lithium battery recycling industry, comprising the following process:
1.含铝物料的分离:将完全放电的废旧锂电池进行机械破碎,加入水进行搅拌加速极片物料与集流体的分离;将搅拌后的浆料通过60目的筛子,筛上物即为含铝物料;1. Separation of aluminum-containing materials: Mechanically crush the fully discharged waste lithium batteries, add water for stirring to accelerate the separation of the electrode material and the current collector; pass the stirred slurry through a 60-mesh sieve, and the sieve is the containing aluminum material;
2.铝的溶解:将(1)中所得含铝物料加入到20mol/L的氢氧化钠溶液中,搅拌反应1h后浆料通过60目筛子,将滤渣加入到同浓度的氢氧化钠溶液中,同样的工艺进行二次碱浸后过滤,滤渣进行后续处理,滤液并入第一次滤液中,滤液经多次过滤除渣后即为含铝强碱溶液;2. Dissolution of aluminum: Add the aluminum-containing material obtained in (1) into a 20mol/L sodium hydroxide solution, stir and react for 1 hour, and then pass the slurry through a 60-mesh sieve, and add the filter residue into a sodium hydroxide solution of the same concentration , the same process is filtered after secondary alkali leaching, the filter residue is subjected to subsequent treatment, the filtrate is incorporated into the first filtrate, and the filtrate is a strong alkali solution containing aluminum after repeated filtration to remove residue;
3.含铝强碱溶液离子比例的调整:用电感耦合等离子体发射光谱仪(ICP)对(2)所得碱液进行测试,钠离子浓度为19mol/L,铝离子浓度为0.4mol/L,根据目标产物成分,添加氢氧化钠与水调整溶液中钠离子浓度为10mol/L,铝离子浓度为0.04mol/L;3. The adjustment of ion ratio of aluminum-containing strong alkali solution: test (2) gained lye with inductively coupled plasma emission spectrometer (ICP), sodium ion concentration is 19mol/L, and aluminum ion concentration is 0.4mol/L, According to the target product composition, add sodium hydroxide and water to adjust the sodium ion concentration in the solution to 10mol/L, and the aluminum ion concentration to 0.04mol/L;
4.含铝强碱溶液的回收利用:以(3)所得强碱溶液为沉淀剂,与镍离子浓度为1.44mol/L,钴离子浓度为0.48mol/L,锰离子浓度为0.48mol/L的混合盐溶液进行液相沉淀反应,制得622型三元材料前躯体。4. Recycling of aluminum-containing strong alkali solution: with (3) gained strong alkali solution as a precipitant, the nickel ion concentration is 1.44mol/L, the cobalt ion concentration is 0.48mol/L, and the manganese ion concentration is 0.48mol/L The mixed salt solution was subjected to liquid-phase precipitation reaction to obtain the precursor of the 622-type ternary material.
实施例4Example 4
一种废旧锂电池回收行业强碱溶液的回收利用方法,包括以下工艺过程:A method for recycling a strong alkali solution in the waste lithium battery recycling industry, comprising the following process:
1.含铝物料的分离:将完全放电的废旧锂电池进行机械破碎,加入水进行搅拌加速极片物料与集流体的分离;将搅拌后的浆料通过60目的筛子,筛上物即为含铝物料;1. Separation of aluminum-containing materials: Mechanically crush the fully discharged waste lithium batteries, add water for stirring to accelerate the separation of the electrode material and the current collector; pass the stirred slurry through a 60-mesh sieve, and the sieve is the containing aluminum material;
2.铝的溶解:将(1)中所得含铝物料加入到24mol/L的氢氧化钠溶液中,搅拌反应0.5h后浆料通过60目筛子,将滤渣加入到同浓度的氢氧化钠溶液中,同样的工艺进行二次碱浸后过滤,滤渣进行后续处理,滤液并入第一次滤液中,滤液经多次过滤除渣后即为含铝强碱溶液;2. Dissolution of aluminum: Add the aluminum-containing material obtained in (1) into a 24mol/L sodium hydroxide solution, stir and react for 0.5h, and then pass the slurry through a 60-mesh sieve, and add the filter residue to a sodium hydroxide solution of the same concentration In the same process, filter after secondary alkali leaching, the filter residue is subjected to subsequent treatment, the filtrate is merged into the first filtrate, and the filtrate is a strong alkali solution containing aluminum after repeated filtration to remove residue;
3.含铝强碱溶液离子比例的调整:用电感耦合等离子体发射光谱仪(ICP)对(2)所得碱液进行测试,钠离子浓度为22mol/L,铝离子浓度为3mol/L,根据目标产物成分,添加氢氧化钠与水调整溶液中钠离子浓度为12mol/L,铝离子浓度为0.3mol/L;3. The adjustment of the ion ratio of aluminum-containing strong alkali solution: test the lye obtained in (2) with an inductively coupled plasma emission spectrometer (ICP), the sodium ion concentration is 22mol/L, and the aluminum ion concentration is 3mol/L, according to Target product composition, adding sodium hydroxide and water to adjust the sodium ion concentration in the solution to 12mol/L, and the aluminum ion concentration to 0.3mol/L;
4.含铝强碱溶液的回收利用:以(3)所得强碱溶液为沉淀剂,与镍离子浓度为1.92mol/L,钴离子浓度为0.36mol/L,锰离子浓度为0.12mol/L的混合盐溶液进行液相沉淀反应,制得NCA型三元材料前躯体。4. Recycling of aluminum-containing strong alkali solution: with the strong alkali solution obtained in (3) as a precipitant, the concentration of nickel ions is 1.92mol/L, the concentration of cobalt ions is 0.36mol/L, and the concentration of manganese ions is 0.12mol/L The mixed salt solution was subjected to liquid phase precipitation reaction to prepare the NCA type ternary material precursor.
表1各实施例所得前躯体中元素含量Element content in the precursor obtained by each embodiment of table 1
本实施例具有所述的工艺简单,操作方便,只需微调离子比例既可用于锂离子电池正极材料磷酸铁锂、三元材料等前躯体的生产过程,绿色、环保,低成本,高附加值等积极效果。This embodiment has the advantages of simple process and convenient operation, and only needs to fine-tune the ion ratio, which can be used in the production process of precursors such as lithium iron phosphate and ternary materials for lithium ion batteries. It is green, environmentally friendly, low cost, and high added value. and other positive effects.
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Cited By (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN108899604A (en) * | 2018-06-28 | 2018-11-27 | 郑州中科新兴产业技术研究院 | Utilize the method for waste lithium cell anode pole piece preparation ternary anode material precursor |
| CN109193059A (en) * | 2018-09-26 | 2019-01-11 | 王书珍 | A kind of regeneration treating method of LiFePO4 waste material |
| CN109742472A (en) * | 2018-12-12 | 2019-05-10 | 江西赣锋循环科技有限公司 | A method of aluminium foil and ternary powder in recycling ternary pole piece |
| CN109786753A (en) * | 2018-12-11 | 2019-05-21 | 广东工业大学 | A kind of bipolarity sodium-ion battery assembly and its assembling, recovery method |
| CN110010990A (en) * | 2019-03-27 | 2019-07-12 | 欣旺达电子股份有限公司 | There is the method for the nickel-cobalt-manganese ternary material of alumina-coated layer using retired lithium ion battery as raw material preparation |
| CN110277552A (en) * | 2018-03-16 | 2019-09-24 | 荆门市格林美新材料有限公司 | The reparative regeneration method of nickel-cobalt-manganternary ternary anode material in old and useless battery |
| CN110862110A (en) * | 2019-11-26 | 2020-03-06 | 宁夏百川新材料有限公司 | Method for preparing ternary positive electrode material precursor by using waste lithium ion battery |
| EP4362169A4 (en) * | 2021-06-24 | 2025-07-09 | Dowa Eco System Co Ltd | Recycled positive electrode material precursor, recycled positive electrode material, method for producing the same, and recycled lithium-ion secondary battery |
Citations (10)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| KR20050112487A (en) * | 2004-05-25 | 2005-11-30 | (주)지케이엠 | High-rate recovery of valuable metals such as cobalt and lithium from waste lithium secondary batteries |
| US7078122B1 (en) * | 1999-07-26 | 2006-07-18 | Ariel Rosenberg | High efficiency process for treating mixed metal waste |
| CN102676827A (en) * | 2012-06-01 | 2012-09-19 | 奇瑞汽车股份有限公司 | Method for recovering valuable metal from nickel cobalt lithium manganate batteries and positive pole materials |
| CN103199320A (en) * | 2013-03-28 | 2013-07-10 | 四川天齐锂业股份有限公司 | Method for recycling nickel-cobalt-manganese ternary anode material |
| CN103259010A (en) * | 2013-04-23 | 2013-08-21 | 宁夏东方钽业股份有限公司 | Preparation method of amphoteric metal element doped lithium-ion cathode material precursor |
| US20130302226A1 (en) * | 2012-04-04 | 2013-11-14 | Yan Wang | Method and apparatus for recycling lithium-ion batteries |
| CN103943911A (en) * | 2014-03-26 | 2014-07-23 | 四川长虹电器股份有限公司 | Method for comprehensively recycling waste lithium ion batteries |
| CN104282961A (en) * | 2013-07-02 | 2015-01-14 | 浙江万向亿能动力电池有限公司 | A kind of treatment method of waste lithium iron phosphate power battery |
| GB2522860A (en) * | 2014-02-05 | 2015-08-12 | Frank Riedewald | Process for the recycling of waste batteries and waste printed circuit boards in molten salts or molten metals |
| CN105098277A (en) * | 2015-07-21 | 2015-11-25 | 河南科技学院 | Method for researching aluminum foil dissolution conditions in spent lithium ion battery |
-
2016
- 2016-09-19 CN CN201610832665.8A patent/CN106299526B/en active Active
Patent Citations (10)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US7078122B1 (en) * | 1999-07-26 | 2006-07-18 | Ariel Rosenberg | High efficiency process for treating mixed metal waste |
| KR20050112487A (en) * | 2004-05-25 | 2005-11-30 | (주)지케이엠 | High-rate recovery of valuable metals such as cobalt and lithium from waste lithium secondary batteries |
| US20130302226A1 (en) * | 2012-04-04 | 2013-11-14 | Yan Wang | Method and apparatus for recycling lithium-ion batteries |
| CN102676827A (en) * | 2012-06-01 | 2012-09-19 | 奇瑞汽车股份有限公司 | Method for recovering valuable metal from nickel cobalt lithium manganate batteries and positive pole materials |
| CN103199320A (en) * | 2013-03-28 | 2013-07-10 | 四川天齐锂业股份有限公司 | Method for recycling nickel-cobalt-manganese ternary anode material |
| CN103259010A (en) * | 2013-04-23 | 2013-08-21 | 宁夏东方钽业股份有限公司 | Preparation method of amphoteric metal element doped lithium-ion cathode material precursor |
| CN104282961A (en) * | 2013-07-02 | 2015-01-14 | 浙江万向亿能动力电池有限公司 | A kind of treatment method of waste lithium iron phosphate power battery |
| GB2522860A (en) * | 2014-02-05 | 2015-08-12 | Frank Riedewald | Process for the recycling of waste batteries and waste printed circuit boards in molten salts or molten metals |
| CN103943911A (en) * | 2014-03-26 | 2014-07-23 | 四川长虹电器股份有限公司 | Method for comprehensively recycling waste lithium ion batteries |
| CN105098277A (en) * | 2015-07-21 | 2015-11-25 | 河南科技学院 | Method for researching aluminum foil dissolution conditions in spent lithium ion battery |
Cited By (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN110277552A (en) * | 2018-03-16 | 2019-09-24 | 荆门市格林美新材料有限公司 | The reparative regeneration method of nickel-cobalt-manganternary ternary anode material in old and useless battery |
| CN108899604A (en) * | 2018-06-28 | 2018-11-27 | 郑州中科新兴产业技术研究院 | Utilize the method for waste lithium cell anode pole piece preparation ternary anode material precursor |
| CN109193059A (en) * | 2018-09-26 | 2019-01-11 | 王书珍 | A kind of regeneration treating method of LiFePO4 waste material |
| CN109786753A (en) * | 2018-12-11 | 2019-05-21 | 广东工业大学 | A kind of bipolarity sodium-ion battery assembly and its assembling, recovery method |
| CN109742472A (en) * | 2018-12-12 | 2019-05-10 | 江西赣锋循环科技有限公司 | A method of aluminium foil and ternary powder in recycling ternary pole piece |
| CN110010990A (en) * | 2019-03-27 | 2019-07-12 | 欣旺达电子股份有限公司 | There is the method for the nickel-cobalt-manganese ternary material of alumina-coated layer using retired lithium ion battery as raw material preparation |
| CN110862110A (en) * | 2019-11-26 | 2020-03-06 | 宁夏百川新材料有限公司 | Method for preparing ternary positive electrode material precursor by using waste lithium ion battery |
| EP4362169A4 (en) * | 2021-06-24 | 2025-07-09 | Dowa Eco System Co Ltd | Recycled positive electrode material precursor, recycled positive electrode material, method for producing the same, and recycled lithium-ion secondary battery |
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