CN107834052A - A kind of method and its material that lithium ion battery silicon cathode material is prepared using flyash solid waste - Google Patents
A kind of method and its material that lithium ion battery silicon cathode material is prepared using flyash solid waste Download PDFInfo
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- 239000010881 fly ash Substances 0.000 title claims abstract description 57
- HBBGRARXTFLTSG-UHFFFAOYSA-N Lithium ion Chemical compound [Li+] HBBGRARXTFLTSG-UHFFFAOYSA-N 0.000 title claims abstract description 37
- 229910001416 lithium ion Inorganic materials 0.000 title claims abstract description 37
- XUIMIQQOPSSXEZ-UHFFFAOYSA-N Silicon Chemical compound [Si] XUIMIQQOPSSXEZ-UHFFFAOYSA-N 0.000 title claims abstract description 29
- 229910052710 silicon Inorganic materials 0.000 title claims abstract description 28
- 239000010703 silicon Substances 0.000 title claims abstract description 28
- 239000000463 material Substances 0.000 title claims abstract description 24
- 239000002910 solid waste Substances 0.000 title claims abstract description 21
- 238000000034 method Methods 0.000 title claims abstract description 19
- 239000010406 cathode material Substances 0.000 title claims 11
- 239000003513 alkali Substances 0.000 claims abstract description 19
- 239000011230 binding agent Substances 0.000 claims abstract description 9
- WHXSMMKQMYFTQS-UHFFFAOYSA-N Lithium Chemical group [Li] WHXSMMKQMYFTQS-UHFFFAOYSA-N 0.000 claims abstract description 7
- 229910052744 lithium Inorganic materials 0.000 claims abstract description 7
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 claims abstract description 4
- 239000011889 copper foil Substances 0.000 claims abstract description 4
- 239000002994 raw material Substances 0.000 claims abstract description 4
- 229910052751 metal Inorganic materials 0.000 claims description 12
- 239000002184 metal Substances 0.000 claims description 12
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 6
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims description 6
- 238000002156 mixing Methods 0.000 claims description 5
- IXPNQXFRVYWDDI-UHFFFAOYSA-N 1-methyl-2,4-dioxo-1,3-diazinane-5-carboximidamide Chemical compound CN1CC(C(N)=N)C(=O)NC1=O IXPNQXFRVYWDDI-UHFFFAOYSA-N 0.000 claims description 4
- KWYUFKZDYYNOTN-UHFFFAOYSA-M Potassium hydroxide Chemical compound [OH-].[K+] KWYUFKZDYYNOTN-UHFFFAOYSA-M 0.000 claims description 4
- 239000000203 mixture Substances 0.000 claims description 4
- 239000011734 sodium Substances 0.000 claims description 4
- 235000010413 sodium alginate Nutrition 0.000 claims description 4
- 239000000661 sodium alginate Substances 0.000 claims description 4
- 229940005550 sodium alginate Drugs 0.000 claims description 4
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 claims description 3
- 229910052782 aluminium Inorganic materials 0.000 claims description 3
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 claims description 3
- 229910052799 carbon Inorganic materials 0.000 claims description 3
- 239000011777 magnesium Substances 0.000 claims description 3
- 229910052749 magnesium Inorganic materials 0.000 claims description 3
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 claims description 2
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 claims description 2
- 239000007864 aqueous solution Substances 0.000 claims description 2
- 238000001816 cooling Methods 0.000 claims description 2
- 229910052700 potassium Inorganic materials 0.000 claims description 2
- 239000011591 potassium Substances 0.000 claims description 2
- 229910052708 sodium Inorganic materials 0.000 claims description 2
- 238000007499 fusion processing Methods 0.000 claims 4
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 claims 2
- 239000004411 aluminium Substances 0.000 claims 1
- 239000010883 coal ash Substances 0.000 claims 1
- 238000005470 impregnation Methods 0.000 claims 1
- 238000002360 preparation method Methods 0.000 claims 1
- 229910000029 sodium carbonate Inorganic materials 0.000 claims 1
- 239000010405 anode material Substances 0.000 abstract description 14
- 239000007773 negative electrode material Substances 0.000 abstract description 14
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 abstract description 9
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 abstract description 7
- 230000004927 fusion Effects 0.000 abstract description 7
- 229910002804 graphite Inorganic materials 0.000 abstract description 7
- 239000010439 graphite Substances 0.000 abstract description 7
- 230000008901 benefit Effects 0.000 abstract description 4
- 235000012239 silicon dioxide Nutrition 0.000 abstract description 4
- 239000000377 silicon dioxide Substances 0.000 abstract description 2
- 150000002500 ions Chemical class 0.000 abstract 1
- 239000000243 solution Substances 0.000 description 6
- 238000002844 melting Methods 0.000 description 4
- 230000008018 melting Effects 0.000 description 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 3
- XKRFYHLGVUSROY-UHFFFAOYSA-N Argon Chemical compound [Ar] XKRFYHLGVUSROY-UHFFFAOYSA-N 0.000 description 2
- KMTRUDSVKNLOMY-UHFFFAOYSA-N Ethylene carbonate Chemical compound O=C1OCCO1 KMTRUDSVKNLOMY-UHFFFAOYSA-N 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 2
- 229910021419 crystalline silicon Inorganic materials 0.000 description 2
- 239000008367 deionised water Substances 0.000 description 2
- 229910021641 deionized water Inorganic materials 0.000 description 2
- IEJIGPNLZYLLBP-UHFFFAOYSA-N dimethyl carbonate Chemical compound COC(=O)OC IEJIGPNLZYLLBP-UHFFFAOYSA-N 0.000 description 2
- KZHJGOXRZJKJNY-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Si]=O.O=[Al]O[Al]=O.O=[Al]O[Al]=O.O=[Al]O[Al]=O KZHJGOXRZJKJNY-UHFFFAOYSA-N 0.000 description 2
- 238000003912 environmental pollution Methods 0.000 description 2
- JBTWLSYIZRCDFO-UHFFFAOYSA-N ethyl methyl carbonate Chemical compound CCOC(=O)OC JBTWLSYIZRCDFO-UHFFFAOYSA-N 0.000 description 2
- 239000012535 impurity Substances 0.000 description 2
- 239000002440 industrial waste Substances 0.000 description 2
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 2
- 229910052863 mullite Inorganic materials 0.000 description 2
- 230000007935 neutral effect Effects 0.000 description 2
- 239000010453 quartz Substances 0.000 description 2
- 238000011160 research Methods 0.000 description 2
- 239000002210 silicon-based material Substances 0.000 description 2
- 239000002699 waste material Substances 0.000 description 2
- 229910018072 Al 2 O 3 Inorganic materials 0.000 description 1
- 229910021536 Zeolite Inorganic materials 0.000 description 1
- 229910052786 argon Inorganic materials 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 239000006229 carbon black Substances 0.000 description 1
- 239000004568 cement Substances 0.000 description 1
- 239000003153 chemical reaction reagent Substances 0.000 description 1
- 239000011248 coating agent Substances 0.000 description 1
- 238000000576 coating method Methods 0.000 description 1
- 239000006258 conductive agent Substances 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 230000007123 defense Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 description 1
- 239000003792 electrolyte Substances 0.000 description 1
- 238000011049 filling Methods 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 230000002687 intercalation Effects 0.000 description 1
- 238000009830 intercalation Methods 0.000 description 1
- 230000002427 irreversible effect Effects 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000002808 molecular sieve Substances 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 239000012686 silicon precursor Substances 0.000 description 1
- 239000002002 slurry Substances 0.000 description 1
- URGAHOPLAPQHLN-UHFFFAOYSA-N sodium aluminosilicate Chemical compound [Na+].[Al+3].[O-][Si]([O-])=O.[O-][Si]([O-])=O URGAHOPLAPQHLN-UHFFFAOYSA-N 0.000 description 1
- 239000007784 solid electrolyte Substances 0.000 description 1
- 238000001228 spectrum Methods 0.000 description 1
- 238000001291 vacuum drying Methods 0.000 description 1
- 239000010457 zeolite Substances 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
- H01M4/00—Electrodes
- H01M4/02—Electrodes composed of, or comprising, active material
- H01M4/36—Selection of substances as active materials, active masses, active liquids
- H01M4/362—Composites
- H01M4/364—Composites as mixtures
-
- 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
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E60/00—Enabling technologies; Technologies with a potential or indirect contribution to GHG emissions mitigation
- Y02E60/10—Energy storage using batteries
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- Chemical & Material Sciences (AREA)
- Composite Materials (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Electrochemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Silicon Compounds (AREA)
- Battery Electrode And Active Subsutance (AREA)
Abstract
本发明公开了一种利用粉煤灰固体废弃物制备锂离子电池硅负极材料的方法,包括如下步骤:1)以粉煤灰为原材料进行碱熔融处理;2)将经步骤1)处理后的材料进行金属热还原处理;3)将经步骤2)处理后的材料在粘结剂中分散均匀;4)将经步骤3)处理后的材料涂布在铜箔上,进一步真空干燥得锂离子电池硅负极材料。本发明充分利用了粉煤灰中二氧化硅含量高的特点,通过对粉煤灰进行改性和加工,开发出高性能以及高性价比的锂离子电池硅负极材料,其与传统的二次锂离子电池负极材料石墨相比明显表现出了更优异的倍率性能。这样不但可以大幅度提升粉煤灰的商业价值,同时减少了粉煤灰固体废弃物对环境的污染,具有较大的社会效益和经济效益。
The invention discloses a method for preparing a silicon negative electrode material of a lithium ion battery by using fly ash solid waste, which comprises the following steps: 1) using fly ash as a raw material for alkali fusion treatment; The material is subjected to metallothermic reduction treatment; 3) the material treated in step 2) is uniformly dispersed in the binder; 4) the material treated in step 3) is coated on the copper foil, and further vacuum-dried to obtain lithium ion Battery silicon anode material. The present invention makes full use of the characteristics of high silicon dioxide content in fly ash, and develops a high-performance and cost-effective silicon negative electrode material for lithium-ion batteries by modifying and processing fly ash, which is different from traditional secondary lithium Compared with graphite, the negative electrode material of ion battery, it obviously shows better rate performance. This can not only greatly increase the commercial value of fly ash, but also reduce the pollution of fly ash solid waste to the environment, which has great social and economic benefits.
Description
技术领域technical field
本发明属于粉煤灰固体废弃物回收利用领域,具体涉及一种利用粉煤灰固体废弃物制备锂离子电池硅负极材料的方法及其材料。The invention belongs to the field of recovery and utilization of fly ash solid waste, and in particular relates to a method for preparing a silicon negative electrode material of a lithium ion battery by using fly ash solid waste and the material thereof.
背景技术Background technique
随着社会的飞速发展,环境污染和能源危机的挑战日益严峻,绿色能源成为世界各国的研究热点。锂离子电池作为一种新型清洁的可充电电源,具有质量轻、体积小、能量密度大、使用寿命长以及环境污染小等优点,在国防、电动车和电子领域展示了广阔的应用前景。目前,商品化的二次锂离子电池主要以石墨类碳作为负极材料,其优点是循环性能和倍率性能较好。然而,传统石墨负极的理论比容量仅为372mAh g-1,而且其嵌锂电位平台接近金属锂,快速充电或低温充电易发生“析锂”现象引发安全隐患。在便携式电子设备和混合电动汽车迅猛发展的当下,石墨类负极材料已经难以满足锂离子二次电池发展的迫切需要。硅材料作为一种有望替代商业化石墨的最具潜力的锂离子电池负极材料,具有高的理论容量(4200mAh g-1)和适宜的电压平台,在新一代二次锂离子电池负极材料领域的应用备受瞩目。With the rapid development of society, the challenges of environmental pollution and energy crisis are becoming increasingly severe, and green energy has become a research hotspot in countries all over the world. As a new type of clean rechargeable power source, lithium-ion batteries have the advantages of light weight, small size, high energy density, long service life and low environmental pollution. They have shown broad application prospects in the fields of national defense, electric vehicles and electronics. At present, commercialized secondary lithium-ion batteries mainly use graphite-like carbon as the negative electrode material, which has the advantage of better cycle performance and rate performance. However, the theoretical specific capacity of the traditional graphite anode is only 372mAh g -1 , and its lithium intercalation potential platform is close to that of metal lithium, so fast charging or low-temperature charging is prone to "lithium precipitation" phenomenon and cause safety hazards. With the rapid development of portable electronic devices and hybrid electric vehicles, graphite-based anode materials have been difficult to meet the urgent needs of the development of lithium-ion secondary batteries. As the most potential lithium-ion battery anode material that is expected to replace commercial graphite, silicon material has a high theoretical capacity (4200mAh g -1 ) and a suitable voltage platform. Apps get a lot of attention.
粉煤灰是火力发电厂燃煤粉锅炉排出的一种工业废渣,是目前世界上排放量最大的工业废物之一。目前我国对粉煤灰的利用,基本停留在初级利用阶段,即作为水泥的掺混料、混凝土的搅拌料、筑路填路等。研究解决粉煤灰的综合利用,变废为宝,使其变为高附加值产品,成为摆在我们面前的一项意义重大的任务。Fly ash is a kind of industrial waste discharged from coal-fired boilers in thermal power plants, and it is one of the largest industrial wastes in the world. At present, the utilization of fly ash in our country basically stays in the primary utilization stage, that is, as admixture of cement, mixing material of concrete, road construction and filling, etc. To study and solve the comprehensive utilization of fly ash, turn waste into treasure, and turn it into high value-added products has become a significant task before us.
目前关于粉煤灰处理用作锂离子电池硅负极材料的文章及专利还鲜有报道,现阶段仍主要集中在粉煤灰的精细利用方面,主要针对粉煤灰中的Al2O3和SiO2,制备高纯聚合铝、白炭黑、沸石分子筛等产品。而粉煤灰处理用作锂离子电池负极材料的文章和相关专利主要是用作碳负极材料。At present, there are few reports and patents on the use of fly ash as a silicon negative electrode material for lithium-ion batteries. At this stage, it is still mainly focused on the fine utilization of fly ash, mainly for Al 2 O 3 and SiO in fly ash 2. Prepare high-purity polymeric aluminum, white carbon black, zeolite molecular sieve and other products. However, the articles and related patents on the use of fly ash as a negative electrode material for lithium-ion batteries are mainly used as carbon negative electrode materials.
发明内容Contents of the invention
本发明的目的在于提供一种利用粉煤灰固体废弃物制备锂离子电池硅负极材料的方法及其材料。The object of the present invention is to provide a method and material for preparing silicon negative electrode material of lithium ion battery by using fly ash solid waste.
为实现上述发明目的,本发明具体提供了如下的技术方案:In order to realize the above-mentioned purpose of the invention, the present invention specifically provides the following technical solutions:
1、一种利用粉煤灰固体废弃物制备锂离子电池硅负极材料的方法,包括如下步骤:1, a kind of method utilizing fly ash solid waste to prepare lithium-ion battery silicon negative electrode material, comprises the steps:
1)以粉煤灰为原材料进行碱熔融处理;1) Carry out alkali fusion treatment with fly ash as raw material;
2)将经步骤1)处理后的材料进行金属热还原处理;2) performing metal thermal reduction treatment on the material treated in step 1);
3)将经步骤2)处理后的材料在粘结剂中分散均匀;3) uniformly dispersing the material treated in step 2) in the binder;
4)将经步骤3)处理后的材料涂布在铜箔上,进一步真空干燥得锂离子电池硅负极材料。4) coating the material treated in step 3) on a copper foil, and further vacuum drying to obtain a silicon negative electrode material for a lithium ion battery.
进一步,步骤3)中包括加入导电炭黑。Further, step 3) includes adding conductive carbon black.
进一步,步骤1)所述碱熔融处理包括如下步骤:将粉煤灰原料与碱按质量比1:1混合后在箱式电阻炉中焙烧,所述碱为Na2CO3、NaOH或KOHFurther, the alkali fusion treatment in step 1) includes the following steps: mixing the fly ash raw material and alkali in a mass ratio of 1:1 and roasting in a box-type resistance furnace, the alkali being Na 2 CO 3 , NaOH or KOH
进一步,步骤1)碱熔融处理的温度为600℃~1200℃,时间为4~12h。Further, the temperature of the step 1) alkali melting treatment is 600°C-1200°C, and the time is 4-12h.
进一步,步骤2)所述金属热还原处理包括如下步骤:将步骤1)中碱熔融处理后的材料与金属按照质量比1:1混合后置于管式炉中;在H2和Ar混合气保护下,温度为600℃~1200℃,焙烧5~12h后,将焙烧后的材料冷却后经2~5M的盐酸浸渍处理6~18h,再用去离子水洗至中性。Further, the metallothermic reduction treatment in step 2) includes the following steps: mixing the material after the alkali melting treatment in step 1) with the metal according to a mass ratio of 1: 1 and then placing it in a tube furnace; Under protection, the temperature is 600°C-1200°C, after roasting for 5-12 hours, the calcined material is cooled, impregnated with 2-5M hydrochloric acid for 6-18 hours, and then washed with deionized water until neutral.
进一步,所述金属为镁、铝、钠、钾或锂的一种或几种。Further, the metal is one or more of magnesium, aluminum, sodium, potassium or lithium.
进一步,步骤3)所述粘结剂为海藻酸钠的水溶液Further, in step 3) the binder is an aqueous solution of sodium alginate
进一步,所述粘结剂的质量分数为20%~50%。Further, the mass fraction of the binder is 20%-50%.
进一步,步骤3)中经步骤2)处理后的材料添加质量百分含量为60~90%。Further, in step 3), the added mass percentage of the material treated in step 2) is 60-90%.
2、根据任一项所述方法制得的锂离子电池负极材料。2. The lithium ion battery negative electrode material prepared according to any one of the methods.
本发明的有益效果在于:本发明充分利用了燃煤电厂产生的固体废弃物粉煤灰,研究解决固体废弃物粉煤灰的合理利用,变废为宝,使其由传统的低附加值应用变为高附加值的锂离子电池硅负极材料,通过对粉煤灰进行改性和加工,开发出高性能以及高性价比的锂离子电池硅负极材料,其与传统的二次锂离子电池负极材料石墨相比明显表现出了更优异的倍率性能。这样不但可以大幅度提升粉煤灰的商业价值,同时减少粉煤灰固体废弃物对环境的污染,具有较大的社会效益和经济效益。另外该工艺方法简单,高效节能并且易于工业化生产且整个工艺过程不需要使用价格昂贵的硅前驱物或者化学试剂。The beneficial effect of the present invention is that: the present invention makes full use of the solid waste fly ash produced by coal-fired power plants, researches and solves the rational utilization of solid waste fly ash, turns waste into wealth, and makes it be used by traditional low-value-added It has become a high-value-added silicon anode material for lithium-ion batteries. By modifying and processing fly ash, a high-performance and cost-effective silicon anode material for lithium-ion batteries has been developed, which is different from traditional secondary lithium-ion battery anode materials. Compared with graphite, it obviously exhibits better rate capability. This will not only greatly increase the commercial value of fly ash, but also reduce the pollution of fly ash solid waste to the environment, which has great social and economic benefits. In addition, the process method is simple, highly efficient and energy-saving, and easy to industrialized production, and the whole process does not need to use expensive silicon precursors or chemical reagents.
附图说明Description of drawings
图1为原始粉煤灰的XRD图谱;Fig. 1 is the XRD collection of illustrative plates of original fly ash;
图2是粉煤灰经碱熔融和金属热还原处理的XRD谱图;Fig. 2 is the XRD spectrogram of fly ash treated by alkali fusion and metal thermal reduction;
图3是粉煤灰制备的锂离子电池硅负极材料在1C下循环性能曲线;Fig. 3 is the cycle performance curve at 1C of the lithium-ion battery silicon anode material prepared by fly ash;
图4是粉煤灰制备的锂离子电池硅负极材料在0.5C、1C、2C和4C不同倍率下充放电曲线。Figure 4 is the charge and discharge curves of silicon anode materials for lithium ion batteries prepared from fly ash at different rates of 0.5C, 1C, 2C and 4C.
具体实施方式Detailed ways
为了进一步理解本发明及体现本发明的有益效果,下面将结合具体实施例对本发明提供的技术方案进行详细说明。In order to further understand the present invention and realize the beneficial effects of the present invention, the technical solutions provided by the present invention will be described in detail below in conjunction with specific embodiments.
实施例1 粉煤灰的预处理Example 1 The pretreatment of fly ash
将粉煤灰、Na2CO3按质量比1:1进行混合,放入箱式电阻炉中,在800℃温度条件下焙烧2小时,然后按照质量比1:1和还原金属镁混合后置于管式炉中,在H2/Ar混合气保护下650℃焙烧6小时,冷却后用3M盐酸溶液浸渍处理,然后用去离子水洗至中性。粉煤灰固体废弃物处理前后的物相结构见图1和图2。图1为原始粉煤灰XRD图,由曲线可以看出,原始粉煤灰中的物相主要是石英和莫来石,说明粉煤灰中杂质含量种类较多;图2为原始粉煤灰经碱熔融和金属热还原处理后的物相结构,对比原始粉煤灰XRD谱图,曲线的峰较少,且比较尖锐,由此可知经碱熔融和金属热还原处理后,粉煤灰中的杂质明显减少且呈现出明显的晶体硅的特征衍射峰,说明原始粉煤灰经碱熔融和金属热还原处理后,粉煤灰中的石英和莫来石已经完全转变为单一的晶体硅物相。Mix fly ash and Na 2 CO 3 at a mass ratio of 1:1, put them into a box-type resistance furnace, and bake them at 800°C for 2 hours, then mix them with reduced metal magnesium at a mass ratio of 1:1 and place In a tube furnace, it was baked at 650°C for 6 hours under the protection of H 2 /Ar mixed gas. After cooling, it was impregnated with 3M hydrochloric acid solution, and then washed with deionized water until neutral. The phase structure of fly ash solid waste before and after treatment is shown in Figure 1 and Figure 2. Figure 1 is the XRD diagram of the original fly ash. It can be seen from the curve that the phases in the original fly ash are mainly quartz and mullite, indicating that there are many types of impurities in the fly ash; Figure 2 is the original fly ash Compared with the original fly ash XRD spectrum of the phase structure after alkali fusion and metal thermal reduction treatment, the peaks of the curve are less and sharper, so it can be seen that after alkali fusion and metal thermal reduction treatment, the The impurities in the fly ash are significantly reduced and the characteristic diffraction peaks of crystalline silicon are obvious, indicating that the quartz and mullite in the fly ash have been completely transformed into a single crystalline silicon after the original fly ash has been processed by alkali melting and metal thermal reduction. Mutually.
应用实施例 处理后的粉煤灰作为电负极材料的应用Application example Application of treated fly ash as electric negative electrode material
将碱熔融和金属热还原处理后的粉煤灰材料添加10%的导电剂Super-p(导电炭黑)后与粘结剂海藻酸钠按照质量比80:10:10混合均匀调成浆料(粘结剂海藻酸钠使用前预先溶解在水中,配置成质量分数50%的溶液),并均匀涂布在铜箔上,然后在70℃真空环境中干燥24小时,制得锂离子电池用硅负极极片。以锂片为对电极、1mol/LLiPF6的EC(乙烯碳酸酯)+DMC(碳酸二甲酯)+EMC(碳酸甲乙酯)(体积比为1:1:1)溶液作为电解液,型号为Celgard 2400的电池隔膜,在充满氩气的手套箱中组装成扣式电池。Add 10% conductive agent Super-p (conductive carbon black) to the fly ash material after alkali fusion and metal thermal reduction treatment, and then mix it with the binder sodium alginate according to the mass ratio of 80:10:10 to make a slurry (the binder sodium alginate is pre-dissolved in water before use, and is configured as a solution with a mass fraction of 50%), and is evenly coated on the copper foil, and then dried in a vacuum environment at 70°C for 24 hours to obtain a lithium-ion battery. Silicon negative pole piece. Lithium sheet as the counter electrode, 1mol/LLiPF 6 EC (ethylene carbonate) + DMC (dimethyl carbonate) + EMC (ethyl methyl carbonate) (volume ratio 1:1:1) solution as the electrolyte, model Cell separators for Celgard 2400 were assembled into coin cells in an argon-filled glove box.
图3是粉煤灰制备的锂离子电池硅负极材料在1C下循环性能曲线。由图3可以看出,粉煤灰固体废弃物经碱熔融和金属热还原处理后制备获得的硅负极材料的循环容量和库伦效率,在0.1(1C=1000mAh g-1)的电流密度下,制备获得的硅负极材料的首循环的放电容量达到3995.7mAh g-1;首次库伦效率高达80%,不可逆容量主要是由于Si材料表面固体电解质界面(SEI)膜的形成;而且库伦效率在第一次循环之后逐渐提高,第三次循环之后,库伦效率高达97%以上。首次循环之后将电流密度提高到1C,经过100次充放电循环,放电容量仍保持在大约1000mAh g-1,表现出很好的循环性能。Figure 3 is the cycle performance curve of the lithium-ion battery silicon anode material prepared from fly ash at 1C. It can be seen from Fig. 3 that the cycle capacity and coulombic efficiency of the silicon anode material prepared after the fly ash solid waste is processed by alkali melting and metallothermic reduction, at a current density of 0.1 (1C=1000mAh g -1 ), The first-cycle discharge capacity of the prepared silicon anode material reaches 3995.7mAh g -1 ; the first coulombic efficiency is as high as 80%, and the irreversible capacity is mainly due to the formation of the solid electrolyte interface (SEI) film on the surface of the Si material; and the coulombic efficiency is the first After the second cycle, it gradually increases, and after the third cycle, the Coulombic efficiency is as high as 97%. After the first cycle, the current density was increased to 1C, and after 100 charge-discharge cycles, the discharge capacity remained at about 1000mAh g -1 , showing good cycle performance.
图4是粉煤灰制备的锂离子电池硅负极材料在0.5C、1C、2C和4C不同倍率下充放电曲线。由图四可看出,其放电容量分别达到2792.5mAh g-1(0.5C)、2112.0mAh g-1(1C)、1571.6mAh g-1(2C)和1450.3mAh g-1(4C),分别超过传统二次锂离子电池负极材料石墨理论容量(372mAh g-1)的7.5、5.7、5.0和4.2倍,表现出优异的倍率性能。Figure 4 is the charge and discharge curves of silicon anode materials for lithium ion batteries prepared from fly ash at different rates of 0.5C, 1C, 2C and 4C. It can be seen from Figure 4 that the discharge capacity reaches 2792.5mAh g -1 (0.5C), 2112.0mAh g -1 (1C), 1571.6mAh g -1 (2C) and 1450.3mAh g -1 (4C), respectively. Exceeding 7.5, 5.7, 5.0 and 4.2 times of the theoretical capacity (372mAh g -1 ) of graphite as the negative electrode material of the traditional secondary lithium ion battery, it exhibits excellent rate performance.
由以上实施例及应用实施例可说明本发明通过对粉煤灰进行改性和加工,充分利用粉煤灰中二氧化硅含量高的特点,将其作为廉价硅源,回收其中的硅材料并将其应用于锂离子电池负极材料体现出高性能以及高性价比,其与传统的二次锂离子电池负极材料石墨相比明显表现出了更优异的倍率性能。It can be illustrated from the above examples and application examples that the present invention makes full use of the high silicon dioxide content in the fly ash by modifying and processing the fly ash, uses it as a cheap silicon source, reclaims the silicon material therein and The application of it to lithium-ion battery anode materials shows high performance and high cost performance, and it obviously shows better rate performance compared with graphite, the traditional secondary lithium-ion battery anode material.
最后说明的是,以上优选实施例仅用以说明本发明的技术方案而非限制,尽管通过上述优选实施例已经对本发明进行了详细的描述,但本领域技术人员应当理解,可以在形式上和细节上对其作出各种各样的改变,而不偏离本发明权利要求书所限定的范围。Finally, it should be noted that the above preferred embodiments are only used to illustrate the technical solutions of the present invention and not to limit them. Although the present invention has been described in detail through the above preferred embodiments, those skilled in the art should understand that it can be described in terms of form and Various changes may be made in the details without departing from the scope of the invention defined by the claims.
Claims (10)
- A kind of 1. method that lithium ion battery silicon cathode material is prepared using flyash solid waste, it is characterised in that including Following steps:1) alkali fusion processing is carried out by raw material of flyash;2) metallothermic reduction processing will be carried out through the material after step 1) processing;3) material after step 2) processing is uniformly dispersed in a binder;4) material after step 3) processing is coated on copper foil, is further dried in vacuo to obtain lithium ion battery silicium cathode material Material.
- A kind of 2. side that lithium ion battery silicon cathode material is prepared using flyash solid waste according to claim 1 Method, it is characterised in that step 3) includes adding conductive black.
- A kind of 3. side that lithium ion battery silicon cathode material is prepared using flyash solid waste according to claim 1 Method, it is characterised in that step 1) the alkali fusion processing comprises the following steps:By powdered coal ash and alkali in mass ratio 1:1 is mixed It is calcined after conjunction in chamber type electric resistance furnace, the alkali is Na2CO3, NaOH or KOH.
- A kind of 4. side that lithium ion battery silicon cathode material is prepared using flyash solid waste according to claim 1 Method, it is characterised in that the temperature of step 1) alkali fusion processing is 600 DEG C~1200 DEG C, and the time is 4~12h.
- A kind of 5. side that lithium ion battery silicon cathode material is prepared using flyash solid waste according to claim 1 Method, it is characterised in that step 2) the metallothermic reduction processing comprises the following steps:By the material after alkali fusion processing in step 1) Material is with metal according to mass ratio 1:It is placed in after 1 mixing in tube furnace;In H2Under Ar mixing gas shieldeds, temperature be 600 DEG C~ 1200 DEG C, be calcined 5~12h after, by after roasting material cooling after hydrochloric acid 6~18h of impregnation through 2~5M, then spend from Son is washed to neutrality.
- 6. a kind of prepare lithium ion battery silicon cathode material using flyash solid waste according to claim 1 or 5 is described Method, it is characterised in that the metal is the one or more of magnesium, aluminium, sodium, potassium or lithium.
- A kind of 7. side that lithium ion battery silicon cathode material is prepared using flyash solid waste according to claim 1 Method, it is characterised in that the step 3) binding agent is the aqueous solution of sodium alginate.
- A kind of 8. side that lithium ion battery silicon cathode material is prepared using flyash solid waste according to claim 7 Method, it is characterised in that the mass fraction of the binding agent is 20~50%.
- A kind of 9. side that lithium ion battery silicon cathode material is prepared using flyash solid waste according to claim 1 Method, it is characterised in that the material addition weight/mass percentage composition in step 3) after step 2) processing is 60~90%.
- 10. according to lithium ion battery negative material made from the preparation method of any one of claim 1 to 9.
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