CN108376789A - A method for recycling waste alkaline manganese batteries into primary zinc-air batteries - Google Patents
A method for recycling waste alkaline manganese batteries into primary zinc-air batteries Download PDFInfo
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- 238000000034 method Methods 0.000 title claims abstract description 29
- 239000002699 waste material Substances 0.000 title claims abstract description 20
- 238000004064 recycling Methods 0.000 title claims abstract description 13
- 229910052748 manganese Inorganic materials 0.000 title abstract description 8
- 239000011572 manganese Substances 0.000 title abstract description 8
- PWHULOQIROXLJO-UHFFFAOYSA-N Manganese Chemical compound [Mn] PWHULOQIROXLJO-UHFFFAOYSA-N 0.000 title abstract description 5
- WJZHMLNIAZSFDO-UHFFFAOYSA-N manganese zinc Chemical compound [Mn].[Zn] WJZHMLNIAZSFDO-UHFFFAOYSA-N 0.000 claims abstract description 22
- 239000012467 final product Substances 0.000 claims abstract description 13
- 239000000047 product Substances 0.000 claims abstract description 13
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims abstract description 10
- 229910052760 oxygen Inorganic materials 0.000 claims abstract description 10
- 239000001301 oxygen Substances 0.000 claims abstract description 10
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 claims description 16
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 13
- 239000003054 catalyst Substances 0.000 claims description 13
- KFZMGEQAYNKOFK-UHFFFAOYSA-N Isopropanol Chemical group CC(C)O KFZMGEQAYNKOFK-UHFFFAOYSA-N 0.000 claims description 12
- 229920001343 polytetrafluoroethylene Polymers 0.000 claims description 12
- 239000004810 polytetrafluoroethylene Substances 0.000 claims description 12
- 239000011230 binding agent Substances 0.000 claims description 11
- 230000003197 catalytic effect Effects 0.000 claims description 11
- 238000012360 testing method Methods 0.000 claims description 10
- 229910052799 carbon Inorganic materials 0.000 claims description 9
- 208000028659 discharge Diseases 0.000 claims description 9
- BASFCYQUMIYNBI-UHFFFAOYSA-N platinum Chemical compound [Pt] BASFCYQUMIYNBI-UHFFFAOYSA-N 0.000 claims description 9
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical group [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 claims description 8
- NUJOXMJBOLGQSY-UHFFFAOYSA-N manganese dioxide Chemical compound O=[Mn]=O NUJOXMJBOLGQSY-UHFFFAOYSA-N 0.000 claims description 8
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 7
- 238000009792 diffusion process Methods 0.000 claims description 7
- 239000010926 waste battery Substances 0.000 claims description 6
- 239000002482 conductive additive Substances 0.000 claims description 5
- 239000011701 zinc Substances 0.000 claims description 5
- 238000001354 calcination Methods 0.000 claims description 4
- 239000002270 dispersing agent Substances 0.000 claims description 4
- 239000006185 dispersion Substances 0.000 claims description 4
- 239000003792 electrolyte Substances 0.000 claims description 4
- 239000006260 foam Substances 0.000 claims description 4
- 239000010439 graphite Substances 0.000 claims description 4
- 229910002804 graphite Inorganic materials 0.000 claims description 4
- 239000000203 mixture Substances 0.000 claims description 4
- 229910052759 nickel Inorganic materials 0.000 claims description 4
- -1 polytetrafluoroethylene Polymers 0.000 claims description 4
- 239000002002 slurry Substances 0.000 claims description 4
- 239000002904 solvent Substances 0.000 claims description 4
- 238000003756 stirring Methods 0.000 claims description 4
- 229920000557 Nafion® Polymers 0.000 claims description 3
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 claims description 3
- 229910021642 ultra pure water Inorganic materials 0.000 claims description 3
- 239000012498 ultrapure water Substances 0.000 claims description 3
- 229910052725 zinc Inorganic materials 0.000 claims description 3
- RNWHGQJWIACOKP-UHFFFAOYSA-N zinc;oxygen(2-) Chemical group [O-2].[Zn+2] RNWHGQJWIACOKP-UHFFFAOYSA-N 0.000 claims description 3
- 239000002033 PVDF binder Substances 0.000 claims description 2
- 239000002131 composite material Substances 0.000 claims description 2
- ZOMNIUBKTOKEHS-UHFFFAOYSA-L dimercury dichloride Chemical class Cl[Hg][Hg]Cl ZOMNIUBKTOKEHS-UHFFFAOYSA-L 0.000 claims description 2
- 238000001035 drying Methods 0.000 claims description 2
- 239000011521 glass Substances 0.000 claims description 2
- 229910021397 glassy carbon Inorganic materials 0.000 claims description 2
- 239000000463 material Substances 0.000 claims description 2
- 239000004570 mortar (masonry) Substances 0.000 claims description 2
- 230000007935 neutral effect Effects 0.000 claims description 2
- 229910052697 platinum Inorganic materials 0.000 claims description 2
- 229920002981 polyvinylidene fluoride Polymers 0.000 claims description 2
- 239000007787 solid Substances 0.000 claims description 2
- 238000006555 catalytic reaction Methods 0.000 claims 1
- 238000005265 energy consumption Methods 0.000 abstract description 4
- 230000007613 environmental effect Effects 0.000 abstract description 4
- 238000011161 development Methods 0.000 abstract description 2
- 239000007774 positive electrode material Substances 0.000 abstract description 2
- 239000003513 alkali Substances 0.000 abstract 1
- 230000000694 effects Effects 0.000 abstract 1
- 238000010438 heat treatment Methods 0.000 abstract 1
- 231100000252 nontoxic Toxicity 0.000 abstract 1
- 230000003000 nontoxic effect Effects 0.000 abstract 1
- 238000005554 pickling Methods 0.000 abstract 1
- 238000006722 reduction reaction Methods 0.000 abstract 1
- AMWRITDGCCNYAT-UHFFFAOYSA-L hydroxy(oxo)manganese;manganese Chemical compound [Mn].O[Mn]=O.O[Mn]=O AMWRITDGCCNYAT-UHFFFAOYSA-L 0.000 description 4
- 239000007795 chemical reaction product Substances 0.000 description 3
- 230000010287 polarization Effects 0.000 description 3
- 238000011084 recovery Methods 0.000 description 3
- 239000010411 electrocatalyst Substances 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 229910052751 metal Inorganic materials 0.000 description 2
- 239000002184 metal Substances 0.000 description 2
- 150000002739 metals Chemical class 0.000 description 2
- 238000002336 sorption--desorption measurement Methods 0.000 description 2
- 235000008331 Pinus X rigitaeda Nutrition 0.000 description 1
- 235000011613 Pinus brutia Nutrition 0.000 description 1
- 241000018646 Pinus brutia Species 0.000 description 1
- 238000003723 Smelting Methods 0.000 description 1
- 238000002441 X-ray diffraction Methods 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 239000011149 active material Substances 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 238000000227 grinding Methods 0.000 description 1
- 238000009854 hydrometallurgy Methods 0.000 description 1
- 238000011068 loading method Methods 0.000 description 1
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 description 1
- 229910052753 mercury Inorganic materials 0.000 description 1
- 150000002736 metal compounds Chemical class 0.000 description 1
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 1
- 238000011056 performance test Methods 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 238000003672 processing method Methods 0.000 description 1
- 238000009853 pyrometallurgy Methods 0.000 description 1
- 238000005096 rolling process Methods 0.000 description 1
- 238000005070 sampling Methods 0.000 description 1
- 238000001878 scanning electron micrograph Methods 0.000 description 1
- 238000002525 ultrasonication Methods 0.000 description 1
Classifications
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- H—ELECTRICITY
- H01—ELECTRIC ELEMENTS
- H01M—PROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
- H01M6/00—Primary cells; Manufacture thereof
- H01M6/52—Reclaiming serviceable parts of waste cells or batteries, e.g. recycling
-
- H—ELECTRICITY
- H01—ELECTRIC ELEMENTS
- H01M—PROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
- H01M12/00—Hybrid cells; Manufacture thereof
- H01M12/04—Hybrid cells; Manufacture thereof composed of a half-cell of the fuel-cell type and of a half-cell of the primary-cell type
- H01M12/06—Hybrid cells; Manufacture thereof composed of a half-cell of the fuel-cell type and of a half-cell of the primary-cell type with one metallic and one gaseous electrode
-
- H—ELECTRICITY
- H01—ELECTRIC ELEMENTS
- H01M—PROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
- H01M4/00—Electrodes
- H01M4/86—Inert electrodes with catalytic activity, e.g. for fuel cells
- H01M4/90—Selection of catalytic material
- H01M4/9016—Oxides, hydroxides or oxygenated metallic salts
-
- 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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- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Electrochemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Manufacturing & Machinery (AREA)
- Materials Engineering (AREA)
- Life Sciences & Earth Sciences (AREA)
- Sustainable Development (AREA)
- Hybrid Cells (AREA)
Abstract
本发明公开了一种废旧碱性锌锰电池回收利用制作一次锌空气电池的新方法。该方法通过收集碱锰电池的正极放电产物,经过简单的酸洗和热处理步骤,得到的处理终产物能够直接用作空气电池正极活性材料。本发明的优点是:该回收方法操作简单,能耗低,绿色环保,产量高。所得放电产物无须复杂的处理过程,对氧还原反应具有良好的电催化活性,能成功应用于锌空气电池空气电极,所组装的锌空气电池具有较高的比容量和比能量,显著增加废弃碱性锌锰电池再利用附加值,有利于节约资源和可持续发展。
The invention discloses a new method for making primary zinc-air batteries by recycling waste alkaline zinc-manganese batteries. In the method, the positive electrode discharge product of the alkaline manganese battery is collected, and after simple pickling and heat treatment steps, the processed final product obtained can be directly used as the positive electrode active material of the air battery. The invention has the advantages of simple operation, low energy consumption, environmental protection and high output. The obtained discharge product does not require complex treatment process, has good electrocatalytic activity for oxygen reduction reaction, and can be successfully applied to the air electrode of zinc-air battery. The assembled zinc-air battery has high specific capacity and specific energy, which significantly increases the waste alkali The added value of reuse of non-toxic zinc-manganese batteries is conducive to resource conservation and sustainable development.
Description
技术领域technical field
本发明涉及资源回收利用和电池技术领域,特别是一种废旧碱性锌锰电池回收再利用为一次锌空气电池的方法。The invention relates to the field of resource recycling and battery technology, in particular to a method for recycling waste alkaline zinc-manganese batteries into primary zinc-air batteries.
背景技术Background technique
我国是电池生产和消耗大国,其中碱性锌锰电池的销量在2015年接近40亿只。根据国家政策要求,我国干电池已经基本实现了无汞化生产。2003年,原国家环境保护总局会同有关部门联合发布《废电池污染防治技术政策》,提出废电池污染控制的重点是废含汞电池、废铅蓄电池等;在缺乏有效回收的技术经济条件情况下,难以集中收集一次性电池。因此,每年大量的废旧碱锰电池被随意丢弃,除了引起环境问题外,还造成了巨大的资源浪费,如不加以回收利用,很难实现可持续发展。my country is a big country in battery production and consumption, among which the sales volume of alkaline zinc-manganese batteries was close to 4 billion in 2015. According to national policy requirements, my country's dry batteries have basically achieved mercury-free production. In 2003, the former State Environmental Protection Administration and relevant departments jointly issued the "Waste Battery Pollution Prevention and Control Technology Policy", which proposed that the focus of waste battery pollution control is waste mercury-containing batteries, waste lead-acid batteries, etc.; in the absence of technical and economic conditions for effective recycling , it is difficult to centrally collect disposable batteries. Therefore, a large number of waste alkaline manganese batteries are discarded randomly every year, which not only causes environmental problems, but also causes a huge waste of resources. If it is not recycled, it is difficult to achieve sustainable development.
针对废旧电池的回收,目前已有广泛研究和报道,主要是将电池破碎后,通过物理、化学反应将电池中的金属、化合物等分离回收,其中包括湿法冶金法、火法冶金法等。这些方法存在工艺复杂、成本高等问题,且在回收过程中需要高能耗,甚至造成二次污染。Aiming at the recycling of waste batteries, there have been extensive studies and reports, mainly after the batteries are broken, and the metals and compounds in the batteries are separated and recovered through physical and chemical reactions, including hydrometallurgy and pyrometallurgy. These methods have problems such as complex process and high cost, and require high energy consumption in the recycling process, and even cause secondary pollution.
金属空气电池具有高理论比容量和能量密度,应用前景突出。其中,锌空气电池是目前唯一规模商业化的金属空气电池体系,因较高的安全性和较低的成本越来越引人关注。碱性锌锰电池放电后的正极产物经过简单处理后主要为锰氧化物,测试表明,此锰氧化物具有良好的氧还原(ORR)催化活性,因此可以用作锌空气电池的空气电极催化剂。此种方法操作方式,附加值高,为废旧碱锰电池的回收再利用提供了新思路,也显示出潜在的应用价值。Metal-air batteries have high theoretical specific capacity and energy density, and their application prospects are outstanding. Among them, zinc-air battery is currently the only large-scale commercial metal-air battery system, and it has attracted more and more attention due to its high safety and low cost. After simple treatment, the positive electrode product of alkaline zinc-manganese battery is mainly manganese oxide. Tests show that this manganese oxide has good oxygen reduction (ORR) catalytic activity, so it can be used as an air electrode catalyst for zinc-air batteries. The operation mode of this method has high added value, which provides a new idea for the recycling and reuse of waste alkaline manganese batteries, and also shows potential application value.
发明内容Contents of the invention
本发明的目的是提供一种全新的电池回收思路,将废旧碱性锌锰电池中的正极放电产物经过简单收集处理,即可用作一次锌空气电池的正极催化剂,实现高附加值利用。该方法与传统回收方法相比,具有方法新颖、工艺简单、能耗较低等优点。The purpose of the present invention is to provide a brand-new idea of battery recycling. After simple collection and treatment, the positive electrode discharge product in the waste alkaline zinc-manganese battery can be used as the positive electrode catalyst of the primary zinc-air battery to realize high value-added utilization. Compared with the traditional recovery method, the method has the advantages of novel method, simple process and low energy consumption.
本发明的技术方案:Technical scheme of the present invention:
一种废旧碱性锌锰电池回收用作一次锌空气电池的方法,将放电完毕的碱性锌锰电池的正极经简单处理后的产物具有良好的氧还原(ORR)催化性能,可用作锌空气电池的正极催化剂。A method for recycling waste alkaline zinc-manganese batteries as primary zinc-air batteries, the product after simple treatment of the positive electrode of the discharged alkaline zinc-manganese batteries has good oxygen reduction (ORR) catalytic performance and can be used as zinc Catalysts for air batteries.
所述的废旧碱性锌锰电池回收用作一次锌空气电池的方法,包含以下步骤:The method for reclaiming the waste alkaline zinc-manganese battery as a primary zinc-air battery comprises the following steps:
(1)材料的获得和处理:将市售碱性锌锰电池经过放电处理后机械拆解,收集其正极放电产物并在稀盐酸中搅拌浸洗,过滤,再用超纯水清洗数次至中性,收集不溶物;将此不溶物在烘箱中干燥;随后在空气气氛中煅烧得到处理终产物;(1) Acquisition and treatment of materials: after discharge treatment, the commercially available alkaline zinc-manganese batteries were mechanically disassembled, and the positive electrode discharge products were collected, stirred and dipped in dilute hydrochloric acid, filtered, and washed several times with ultrapure water to Neutral, collect the insoluble matter; dry the insoluble matter in an oven; then calcinate in the air atmosphere to obtain the final product;
(2)测试氧还原(ORR)性能:取处理终产物与导电碳混合并研磨均匀,再滴加粘结剂和分散剂,超声30min得到均匀分散的浆液;移取9μL浆液滴于玻碳电极上,自然晾干作为工作电极,铂片作对电极,饱和甘汞电极为参比电极,组装成三电极体系测试其氧还原性能;(2) Test the oxygen reduction (ORR) performance: take the finished product and mix it with conductive carbon and grind it evenly, then add the binder and dispersant dropwise, and ultrasonicate for 30 minutes to obtain a uniformly dispersed slurry; pipette 9 μL of the slurry and drop it on the glassy carbon electrode As the working electrode, the platinum sheet was used as the counter electrode, and the saturated calomel electrode was used as the reference electrode, and a three-electrode system was assembled to test its oxygen reduction performance;
(3)制作电池正极:取处理终产物和导电碳混合并用研钵研磨均匀,再滴加粘结剂,加入乙醇,加热搅拌至溶液蒸干,得到具有粘性的固体团状物,将其用玻璃管滚压成薄片,此即为催化层;将催化层、集流体与空气扩散层用辊压机压为一体作为锌空气电池的正极;其中催化层和空气扩散层分别位于集流体的两侧;(3) Making the positive electrode of the battery: Mix the final product with conductive carbon and grind it evenly with a mortar, then add the binder dropwise, add ethanol, heat and stir until the solution is evaporated to dryness, and obtain a sticky solid mass, which is used The glass tube is rolled into a thin sheet, which is the catalytic layer; the catalytic layer, the current collector and the air diffusion layer are pressed together by a roller press as the positive electrode of the zinc-air battery; the catalytic layer and the air diffusion layer are respectively located on the two sides of the current collector. side;
(4)锌空气电池的组装和测试:以上述制得的复合电极为正极、KOH为电解液、锌为负极组装成锌空气电池并用Land系统对装配的锌空气电池进行电化学测试。(4) Assembly and testing of Zn-air batteries: Zn-air batteries were assembled with the composite electrode prepared above as the positive electrode, KOH as the electrolyte, and Zn as the negative electrode, and the assembled Zn-air batteries were electrochemically tested with the Land system.
步骤(1)所回收的电池为碱性锌锰电池,其形状包括但不限于圆柱形和长方体形,其大小包括但不限于5号、7号电池;盐酸浓度为0.5-3mol L-1,干燥温度为60-100℃;煅烧温度为200-300℃,煅烧时间为2-6h。The battery recovered in step (1) is an alkaline zinc-manganese battery, its shape includes but not limited to cylindrical and cuboid, and its size includes but not limited to No. 5 and No. 7 batteries; the concentration of hydrochloric acid is 0.5-3mol L -1 , The drying temperature is 60-100°C; the calcination temperature is 200-300°C, and the calcination time is 2-6h.
所述步骤(2)中的导电添加剂为Vulcan XC-72或super P或石墨;粘结剂为Nafion或PTFE或PVDF,分散溶剂为异丙醇,且催化剂与导电添加剂的质量比范围为2:8到5:5,5wt%的粘结剂分散液与异丙醇的体积比范围为1:10至1:30。Conductive additive in described step (2) is Vulcan XC-72 or super P or graphite; Binding agent is Nafion or PTFE or PVDF, and dispersion solvent is Virahol, and the mass ratio range of catalyst and conductive additive is 2: 8 to 5:5, the volume ratio of 5 wt% binder dispersion to isopropanol ranges from 1:10 to 1:30.
所述步骤(3)中的导电碳为Vulcan XC-72,super P和石墨,粘结剂为聚四氟乙烯即PTFE溶液,溶剂为乙醇,分散剂为异丙醇;二氧化锰、导电碳和PTFE的质量比为6:13:1-19:19:2;活性物质载量为5-10mg cm-2;所述的集流体为泡沫镍。Conductive carbon in described step (3) is Vulcan XC-72, super P and graphite, binder is polytetrafluoroethylene i.e. PTFE solution, solvent is ethanol, and dispersant is Virahol; Manganese dioxide, conductive carbon The mass ratio to PTFE is 6:13:1-19:19:2; the active material load is 5-10 mg cm -2 ; the current collector is nickel foam.
所述步骤(4)中的KOH浓度为6mol/L,并添加0.2mol/LZnO;所述的锌负极为锌膏;所组装的锌空气电池包括但不限于2032型,A675型或自制的磨具电池。The KOH concentration in the step (4) is 6mol/L, and 0.2mol/LZnO is added; the zinc negative electrode is zinc paste; the assembled zinc-air battery includes but is not limited to 2032 type, A675 type or self-made grinding with battery.
本发明的优点:针对传统废旧电池回收方法将电池中的不同金属或金属化合物分离冶炼回收过程中的工艺复杂、设备要求高、能耗高等问题,本发明提出一种全新的回收思路,将已放电的碱性锌锰电池的正极产物经过简单处理后即可用于锌空气电池的正极催化剂,因此工艺比较简单,成本低廉且节能环保,在碱锰废旧电池处理领域具有重要实用价值。Advantages of the present invention: Aiming at the problems of complex process, high equipment requirements and high energy consumption in the process of separating and smelting different metals or metal compounds in the battery in the traditional waste battery recycling method, the present invention proposes a brand new recycling idea, which will The positive electrode product of the discharged alkaline zinc-manganese battery can be used as the positive electrode catalyst of the zinc-air battery after simple treatment, so the process is relatively simple, the cost is low, energy saving and environmental protection, and it has important practical value in the field of alkaline manganese waste battery treatment.
附图说明Description of drawings
图1是本发明的废旧锌锰电池回收流程图。Fig. 1 is the recovery flow chart of waste zinc-manganese battery of the present invention.
图2实施例1的是处理终产物的XRD图。What Fig. 2 embodiment 1 is to process the XRD figure of final product.
图3实施例1的是处理终产物的SEM图。What Fig. 3 embodiment 1 is the SEM figure of processing final product.
图4实施例1的是处理终产物的N2吸脱附曲线。What Fig. 4 embodiment 1 is to process the N2 adsorption-desorption curve of final product.
图5实施例1的处理终产物与Pt/C催化剂在0.1mol L-1KOH中在1600rpm下的线性扫描极化曲线。Fig. 5 is the linear scanning polarization curve of the treated end product of Example 1 and the Pt/C catalyst in 0.1 mol L -1 KOH at 1600 rpm.
图6实施例1的处理终产物与Pt/C催化剂由极化曲线拟合出的塔菲尔斜率曲线。Fig. 6 is the Tafel slope curve fitted from the polarization curve between the treated end product of Example 1 and the Pt/C catalyst.
图7是实施例1所组装的锌空气电池的放电曲线。7 is the discharge curve of the zinc-air battery assembled in Example 1.
具体实施方式Detailed ways
实施例1:Example 1:
本发明流程图如图1所示,本发明废旧锌锰电池的回收处理方法,其包括以下步骤:Flow chart of the present invention is as shown in Figure 1, and the recovery processing method of waste zinc-manganese battery of the present invention, it comprises the following steps:
(一)取市售AA型电池以20mA电流放电至0.8V,随后对其进行机械拆解,收集正极放电产物。将所收集的产物在0.5mol L-1稀盐酸中搅拌浸洗3分钟,过滤,再用超纯水清洗数次至中性,随后在80℃烘箱中干燥,然后于250℃空气气氛中煅烧4小时。所得处理终产物的XRD图如图2所示,其主要成分为epsilon相的二氧化锰(ε-MnO2)。扫描电镜图如图3所示,是较为松散的块状结构。N2吸脱附曲线如图4,比表面积约为46m2g-1。(1) A commercially available AA battery was discharged to 0.8V with a current of 20mA, and then mechanically disassembled to collect the positive discharge product. The collected product was stirred and soaked in 0.5mol L -1 dilute hydrochloric acid for 3 minutes, filtered, and washed several times with ultrapure water to neutrality, then dried in an oven at 80°C, and then calcined in an air atmosphere at 250°C 4 hours. The XRD pattern of the obtained treated final product is shown in FIG. 2 , and its main component is manganese dioxide (ε-MnO 2 ) in epsilon phase. The scanning electron micrograph is shown in Figure 3, which is a relatively loose block structure. The N 2 adsorption-desorption curve is shown in Figure 4, and the specific surface area is about 46m 2 g -1 .
(二)测试氧还原(ORR)性能:取处理终产物与Vulcan XC-72以质量比4:6研磨均匀,并滴加50μLNafion和950μL异丙醇,超声30min分散均匀后移取9μL滴于玻碳电极上,在乙醇气氛下自然晾干。催化剂的性能测试采用三电极体系,电解液为0.1mol L-1KOH溶液,所用仪器为双恒电位电化学工作站(AFCBP1,Pine Instrument),图5为处理终产物作为电催化剂在1600rpm,5mV s-1下的线性扫描极化曲线,并与商业化Pt/C进行对比。图中显示:该处理终产物表现出与Pt/C近似的氧还原性能。(2) Test the oxygen reduction (ORR) performance: Take the final product and Vulcan XC-72 and grind it evenly at a mass ratio of 4:6, add 50 μL Nafion and 950 μL isopropanol dropwise, and disperse evenly by ultrasonication for 30 minutes. Carbon electrodes were dried naturally in an ethanol atmosphere. The performance test of the catalyst adopts a three-electrode system, the electrolyte is 0.1mol L -1 KOH solution, and the instrument used is a double constant potential electrochemical workstation (AFCBP1, Pine Instrument). Figure 5 shows the treatment of the final product as an electrocatalyst at 1600rpm, 5mV s Linear scanning polarization curves at -1 and compared with commercial Pt/C. The figure shows that the final product of this treatment exhibits an oxygen reduction performance similar to that of Pt/C.
图6为处理终产物作为电催化剂的塔菲尔斜率曲线。图中显示:该催化剂在低电位和高电位下均具有与Pt/C相近的塔菲尔斜率,证明其催化动力学优异。Figure 6 is a Tafel slope curve for treating the final product as an electrocatalyst. The figure shows that the catalyst has a Tafel slope similar to that of Pt/C at both low and high potentials, proving its excellent catalytic kinetics.
(三)制作电池正极和锌空气电池的组装及测试:以3:7的质量比取导电添加剂和聚四氟乙烯(PTFE)粘结剂,并分散于乙醇中,搅拌加热至乙醇蒸干,将所得的团状物擀压成片即为空气扩散层。以导电碳:处理终产物:聚四氟乙烯(PTFE)为12:7:1的质量比取样,加入2mL乙醇,搅拌加热至溶液蒸干后,将所得团状物擀压成片作为催化层(载量约为10mgcm-2)。取上述催化层1cm×1cm与泡沫镍、空气扩散层用辊压机滚压在一起,作为锌空气电池的正极。其中二氧化锰催化层和空气扩散层分别位于泡沫镍的两侧。(3) Assembling and testing of battery cathode and zinc-air battery: take conductive additive and polytetrafluoroethylene (PTFE) binder with a mass ratio of 3:7, and disperse them in ethanol, stir and heat until ethanol evaporates to dryness, Rolling the obtained dough into sheets is the air diffusion layer. Take conductive carbon: end product of treatment: polytetrafluoroethylene (PTFE) as a mass ratio of 12:7:1 for sampling, add 2mL of ethanol, stir and heat until the solution is evaporated to dryness, and roll the resulting dough into sheets as a catalytic layer (Loading capacity is about 10 mgcm -2 ). Take the above catalyst layer 1cm×1cm, foam nickel and air diffusion layer and roll them together with a roller press, as the positive electrode of the zinc-air battery. Wherein the manganese dioxide catalyst layer and the air diffusion layer are respectively located on both sides of the nickel foam.
(四)锌空气电池的组装及测试:以催化层为正极、添加0.2mol L-1ZnO的6mol L- 1KOH为电解液、滤纸为隔膜、锌膏为负极组装2032型扣式锌空气电池,其正极壳预先用电钻均匀钻好17个半径约1mm的孔。图7是所组装的锌空气电池的放电曲线。如图中显示,此空气电池开路电压约为1.40V,在电流密度为10mAcm-2时,放电电压保持稳定,可放出675mAh的容量和810mWh的能量。通常一节5号碱锰电池中的正极活性物质的质量约为10g,则一节废旧碱锰电池可转化为1000块扣式锌空气电池,由此估算可获得675Ah的总容量和810Wh的总能量。因此,这种将废旧碱锰电池转化为锌空气电池的方法附加值高,应用前景广阔。(4) Assembly and testing of zinc-air battery: 2032-type button-type zinc-air battery was assembled with the catalytic layer as the positive electrode, 6mol L - 1 KOH added with 0.2mol L - 1 ZnO as the electrolyte, filter paper as the diaphragm, and zinc paste as the negative electrode 17 holes with a radius of about 1 mm are uniformly drilled in the positive electrode shell with an electric drill in advance. Figure 7 is the discharge curve of the assembled zinc-air battery. As shown in the figure, the open circuit voltage of this air battery is about 1.40V, and when the current density is 10mAcm -2 , the discharge voltage remains stable, and the capacity of 675mAh and the energy of 810mWh can be released. Usually, the mass of the positive electrode active material in a No. 5 alkaline-manganese battery is about 10g, and a spent alkaline-manganese battery can be converted into 1000 button-type zinc-air batteries, and it is estimated that the total capacity of 675Ah and the total capacity of 810Wh can be obtained. energy. Therefore, this method of converting waste alkaline-manganese batteries into zinc-air batteries has high added value and broad application prospects.
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| CN113611876A (en) * | 2021-08-05 | 2021-11-05 | 哈尔滨工业大学 | Method for recycling waste lithium-ion battery cathode material for use as electrocatalyst |
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| Publication number | Priority date | Publication date | Assignee | Title |
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| CN110820018A (en) * | 2019-11-13 | 2020-02-21 | 刘伟春 | Reduction, regeneration and cyclic utilization method for zinc electrode of zinc-air battery |
| CN113611876A (en) * | 2021-08-05 | 2021-11-05 | 哈尔滨工业大学 | Method for recycling waste lithium-ion battery cathode material for use as electrocatalyst |
| CN113707893A (en) * | 2021-08-16 | 2021-11-26 | 广西师范大学 | Carbon-based electrocatalyst prepared from waste lithium iron phosphate battery positive electrode material and preparation method and application thereof |
| CN113707893B (en) * | 2021-08-16 | 2022-08-12 | 广西师范大学 | A carbon-based electrocatalyst prepared by using waste lithium iron phosphate battery cathode material, and preparation method and application thereof |
| CN114583190A (en) * | 2022-03-14 | 2022-06-03 | 清华大学深圳国际研究生院 | Recovery and conversion of metal in waste lithium ion battery and application of metal in zinc-air battery |
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