CN116443875A - Preparation method and application of a nitrogen-doped porous carbon material - Google Patents

Preparation method and application of a nitrogen-doped porous carbon material Download PDF

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CN116443875A
CN116443875A CN202310380657.4A CN202310380657A CN116443875A CN 116443875 A CN116443875 A CN 116443875A CN 202310380657 A CN202310380657 A CN 202310380657A CN 116443875 A CN116443875 A CN 116443875A
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nitrogen
porous carbon
doped porous
carbon material
washing
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董庆
朱林
耿瑞鹏
孙振杰
龚上焜
李松林
时号
陈筱晓
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Huaiyin Institute of Technology
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Abstract

The invention discloses a preparation method and application of a nitrogen-doped porous carbon material, which specifically comprises the following steps: crushing waste corn stalks, washing the crushed waste corn stalks with deionized water, and drying the washed waste corn stalks; sterilizing the dried corn stalk powder; uniformly mixing sterilized corn stalk powder and fungus spore liquid, performing constant temperature treatment, filtering, washing and drying to obtain a carbonized precursor; carbonizing the carbonized precursor; dissolving corn stalk carbide, urea and KOH in deionized water, magnetically stirring, drying and sieving to obtain an activated precursor; the activation precursor is added in N 2 Performing activation treatment in atmosphere, washing the activated product with hydrochloric acid, washing with deionized water to neutrality, washing with absolute ethanol, drying, grinding, and sieving to obtain nitrogen-doped porous carbon material. The preparation method has the advantages of low cost, simple steps, high nitrogen doping efficiency, high specific capacity of the electrode material and good cycle stability when being applied to the preparation of the electrode material.

Description

一种氮掺杂多孔炭材料的制备方法及应用Preparation method and application of a nitrogen-doped porous carbon material

技术领域technical field

本发明属于生物质炭材料制备技术领域,涉及一种氮掺杂多孔炭材料的制备,具体涉及一种氮掺杂多孔炭材料的制备方法及其在制备高性能电极材料中的应用。The invention belongs to the technical field of preparation of biomass carbon materials, and relates to the preparation of a nitrogen-doped porous carbon material, in particular to a preparation method of a nitrogen-doped porous carbon material and its application in the preparation of high-performance electrode materials.

背景技术Background technique

随着能源需求的不断增长和环境问题的日益突出,发展先进的储能设备和管理系统已成为能源行业的趋势。超级电容器又称超级电容或电化学双层电容器。因其功率密度高、充放电速度快、使用寿命长和工作温度宽等优点,已成为最受关注且大有前途的储能装置之一。With the continuous growth of energy demand and the increasingly prominent environmental problems, the development of advanced energy storage equipment and management systems has become a trend in the energy industry. Supercapacitors are also called supercapacitors or electrochemical double layer capacitors. Due to the advantages of high power density, fast charging and discharging speed, long service life and wide operating temperature, it has become one of the most concerned and promising energy storage devices.

目前,限制超级电容器大规模应用的关键问题在于超级电容器的能量密度低。通过提高比电容可以提高超级电容器的能量密度,而比电容主要取决于电极材料的性能。At present, the key problem limiting the large-scale application of supercapacitors is the low energy density of supercapacitors. The energy density of supercapacitors can be improved by increasing the specific capacitance, which mainly depends on the performance of the electrode materials.

生物质炭材料具有来源广泛、杂原子丰富和天然孔道等特点,成为超级电容器电极材料的研究热点之一。生物质炭材料的结构特征与超级电容器的电化学性能密切相关,如比表面积、表面性质、导电性和孔径大小等。传统工艺制备的生物质炭材料中、大孔结构数量少,氮掺杂率低,导致电解液离子传输困难,制备的超级电容器电化学性能较低。 传统的物理、化学预处理方法虽然能够通过改变生物质组成及结构实现对生物质炭材料的调控,但预处理后的生物质部分原生骨架会发生塌陷,会导致生物质内部孔隙的堵塞,使得氮源难以与生物质基材充分掺杂,后续处理过程中氮源容易流失,最终对碳材料的电化学性能产生不利影响。Biomass carbon materials have the characteristics of wide sources, rich heteroatoms and natural pores, and have become one of the research hotspots of supercapacitor electrode materials. The structural characteristics of biochar materials are closely related to the electrochemical performance of supercapacitors, such as specific surface area, surface properties, electrical conductivity, and pore size. The biochar material prepared by the traditional process has a small number of macroporous structures and a low nitrogen doping rate, which leads to difficulty in ion transport in the electrolyte and low electrochemical performance of the prepared supercapacitor. Although traditional physical and chemical pretreatment methods can regulate the biochar material by changing the composition and structure of biomass, part of the primary skeleton of the pretreated biomass will collapse, which will lead to the blockage of the internal pores of the biomass, making It is difficult for the nitrogen source to be fully doped with the biomass substrate, and the nitrogen source is easily lost in the subsequent treatment process, which will eventually have an adverse effect on the electrochemical performance of the carbon material.

因此,亟需开发一种新的氮掺杂多孔炭材料的制备方法,实现氮源与生物质基材的充分掺杂,从而得到具有比容量高、循环稳定性好的高性能电极材料。Therefore, it is urgent to develop a new preparation method of nitrogen-doped porous carbon materials to achieve sufficient doping of nitrogen sources and biomass substrates, so as to obtain high-performance electrode materials with high specific capacity and good cycle stability.

发明内容Contents of the invention

针对现有技术的不足,本发明的目的在于提供一种氮掺杂多孔炭材料的的制备方法,本发明制备方法成本低、步骤简单,掺氮效率高,应用于制备电极材料时,电极材料比容量高,循环稳定性好。Aiming at the deficiencies of the prior art, the purpose of the present invention is to provide a preparation method of nitrogen-doped porous carbon material. The preparation method of the present invention has low cost, simple steps and high nitrogen doping efficiency. When applied to the preparation of electrode materials, electrode materials High specific capacity and good cycle stability.

本发明是通过以下技术方案实现的:The present invention is achieved through the following technical solutions:

一种高性能超级电容器电极材料的制备方法,包括以下步骤:A preparation method of a high-performance supercapacitor electrode material, comprising the following steps:

1) 将废弃玉米秸秆进行粉碎,粉碎后用去离子水洗涤,除去玉米秸秆粉表面的杂质,洗涤后干燥;1) Grinding the waste corn stalks, washing with deionized water after crushing, removing impurities on the surface of the corn stalk powder, washing and drying;

2)将干燥的玉米秸秆粉与去离子水混合均匀,进行灭菌处理,得到灭菌玉米秸秆粉;2) Mix the dried corn stalk powder with deionized water evenly, and perform sterilization treatment to obtain sterilized corn stalk powder;

3)将灭菌的玉米秸秆粉与真菌孢子液混合均匀,恒温处理,过滤,洗涤,干燥,得到炭化前驱体;3) Mix the sterilized corn stalk powder and the fungal spore liquid evenly, treat at a constant temperature, filter, wash, and dry to obtain a carbonized precursor;

4)将炭化前驱体进行炭化处理,获得玉米秸秆炭化物;4) Carbonize the carbonization precursor to obtain carbonized corn stalks;

5)将玉米秸秆炭化物、尿素以及 KOH 溶于去离子水中,磁力搅拌,干燥 ,过筛,获得活化前体物;5) Dissolve corn stalk charcoal, urea and KOH in deionized water, stir magnetically, dry, and sieve to obtain activated precursors;

6)将活化前体物在 N2氛围下进行活化处理,将活化处理的产物先用盐酸洗涤,再用去离子水洗涤至中性,再经无水乙醇洗涤,干燥,研磨,过筛,获得氮掺杂多孔炭材料。6) The activated precursor is activated under N2 atmosphere, the activated product is first washed with hydrochloric acid, then washed with deionized water until neutral, then washed with absolute ethanol, dried, ground, and sieved to obtain Nitrogen-doped porous carbon materials.

本发明的进一步改进方案为:A further improvement of the present invention is:

步骤1)中干燥的温度为100~110℃,时间为10~14h;粉碎后的玉米秸秆粉的粒径为40~60目;玉米秸秆粉和去离子水质量比为1﹕2~5。The drying temperature in step 1) is 100-110° C., and the drying time is 10-14 hours; the particle size of the crushed corn stalk powder is 40-60 mesh; the mass ratio of corn stalk powder to deionized water is 1:2-5.

进一步的,步骤3)中真菌孢子液是将黄孢原毛平革菌(Phanerochaetechrysosporium SHBCC D22643) 接种至培养基上进行培养、水洗、过滤获得;恒温处理的温度为25~32℃,时间为1-3周。Further, the fungal spore liquid in step 3) is obtained by inoculating Phanerochaetechrysosporium SHBCC D22643 on the medium, culturing, washing with water, and filtering; the temperature of the constant temperature treatment is 25-32°C, and the time is 1- 3 weeks.

进一步的,步骤4)中炭化处理的温度为480~520℃,炭化时间为8~15min。Further, the temperature of the carbonization treatment in step 4) is 480-520° C., and the carbonization time is 8-15 minutes.

进一步的,步骤5)中玉米秸秆炭化物,尿素以及KOH 质量比为 1﹕0.8~1.2﹕0.8~1.2。Further, in step 5), the mass ratio of corn stalk charcoal, urea and KOH is 1:0.8~1.2:0.8~1.2.

进一步的,步骤6)中活化处理的温度为750℃~850℃,时间为80~100 min.Further, the temperature of the activation treatment in step 6) is 750°C~850°C, and the time is 80~100 min.

进一步的,步骤6)中所述盐酸的摩尔浓度为 0.8~1.2 mol/L,过200目筛。Further, the molar concentration of the hydrochloric acid described in step 6) is 0.8-1.2 mol/L, passing through a 200-mesh sieve.

本发明的更进一步改进方案为:A further improvement of the present invention is:

上述方法制备的氮掺杂多孔炭材料在制备高性能电极材料中的应用。Application of the nitrogen-doped porous carbon material prepared by the above method in the preparation of high-performance electrode materials.

进一步的,应用的具体过程为:将氮掺杂多孔炭作为活性材料,乙炔黑作为导电剂,聚四氟乙烯乳液为粘结剂,按照质量比 8:0.8~1.2﹕0.8~1.2 的比例混合于研钵中,加乙醇,充分研磨使其混合均匀,得到浆料,将浆料涂抹于1 cm×1 cm 的泡沫镍上,烘干后压片,得到生物质炭电极。Further, the specific process of application is: nitrogen-doped porous carbon is used as the active material, acetylene black is used as the conductive agent, and polytetrafluoroethylene emulsion is used as the binder, and they are mixed according to the mass ratio of 8:0.8~1.2:0.8~1.2 In a mortar, add ethanol, fully grind to mix evenly to obtain a slurry, smear the slurry on a 1 cm×1 cm foamed nickel, dry it and press it into a tablet to obtain a biochar electrode.

与现有技术相比,本发明的有益效果为:Compared with prior art, the beneficial effect of the present invention is:

第一、本发明的利用真菌预处理玉米秸秆制备高性能超级电容器电极材料及其制备方法,得到了具有掺氮率高、储能比容量高、循环稳定性好的高性能电极材料。为生物质资源的综合利用提供了一种新的途径。First, the present invention uses fungi to pretreat corn stalks to prepare high-performance supercapacitor electrode materials and its preparation method, and obtains high-performance electrode materials with high nitrogen doping rate, high specific energy storage capacity, and good cycle stability. It provides a new way for the comprehensive utilization of biomass resources.

第二、本发明的利用真菌预处理玉米秸秆制备高性能超级电容器电极材料及其制备方法,本发明以玉米秸秆作为原料,为废弃生物质,来源丰富,实现资源再生利用。Second, the present invention uses fungi to pretreat corn stalks to prepare high-performance supercapacitor electrode materials and its preparation method. The present invention uses corn stalks as raw materials, which are waste biomass with abundant sources, and realize resource regeneration and utilization.

第三、本发明的利用真菌预处理玉米秸秆制备高性能超级电容器电极材料及其制备方法,本发明利用真菌产生的木质纤维素降解酶,破坏生物质表面的蜡质层,拓宽生物质表面孔隙结构,使得尿素分子渗入到材料内部,进一步提高炭材料氮掺杂量。Third, the present invention uses fungi to pretreat corn stalks to prepare high-performance supercapacitor electrode materials and its preparation method. The present invention uses lignocellulose-degrading enzymes produced by fungi to destroy the waxy layer on the surface of biomass and widen the pores on the surface of biomass The structure allows urea molecules to penetrate into the interior of the material, further increasing the nitrogen doping amount of the carbon material.

第四、本发明的利用真菌预处理玉米秸秆制备高性能超级电容器电极材料及其制备方法,本发明利用真菌产生的木质纤维素降解酶,破坏生物质使真菌菌丝直接进入生物质内部,拓宽孔隙,使得电解质可以进入到材料内部,提高电化学性能。Fourth, the present invention uses fungi to pretreat corn stalks to prepare high-performance supercapacitor electrode materials and its preparation method. The present invention uses lignocellulose-degrading enzymes produced by fungi to destroy biomass so that fungal hyphae directly enter the interior of the biomass, broadening the The pores allow the electrolyte to enter the interior of the material and improve the electrochemical performance.

第五、本发明的利用真菌预处理玉米秸秆制备高性能超级电容器电极材料及其制备方法,制备的电极材料表现出高的比电容,高倍率性能和良好的循环稳定性。Fifth, the present invention uses fungi to pretreat corn stalks to prepare high-performance supercapacitor electrode materials and its preparation method. The prepared electrode materials exhibit high specific capacitance, high rate performance and good cycle stability.

附图说明Description of drawings

图1为实施例1所得玉米秸秆炭化物SEM图;Fig. 1 is the SEM figure of the corn stalk carbonized product obtained in embodiment 1;

图2为实施例3所得玉米秸秆炭化物SEM图;Fig. 2 is the SEM figure of the obtained corn stalk charcoal of embodiment 3;

图3为实施例4所得的生物质炭电极片不同扫描速率下的CV曲线图;Fig. 3 is the CV graph under the different scanning speeds of the biochar electrode sheet gained in embodiment 4;

图4为实施例4所得的生物质炭电极片在不同电流密度下的GCD曲线图;Fig. 4 is the GCD graph of the biochar electrode sheet obtained in Example 4 under different current densities;

图5为实施例5所得的生物质炭电极片不同扫描速率下的CV曲线图;Fig. 5 is the CV graph under the different scanning speeds of the biochar electrode sheet gained in embodiment 5;

图6为实施例5所得的生物质炭电极片在不同电流密度下的GCD曲线图;Fig. 6 is the GCD graph of the biochar electrode sheet obtained in Example 5 under different current densities;

图7为实施例4所得的生物质电极片在电流密度为 10 A/g下的循环稳定性图。Fig. 7 is the cycle stability diagram of the biomass electrode sheet obtained in Example 4 at a current density of 10 A/g.

具体实施方式Detailed ways

下面结合具体实施例对本发明进行详细的介绍。The present invention will be described in detail below in conjunction with specific embodiments.

实施例1:制备真菌孢子液Embodiment 1: prepare fungal spore liquid

将黄孢原毛平革菌Phanerochaete chrysosporium 冻干粉活化后,转接到综合PDA平板中,于培养箱中27℃培养7-9天。带菌丝长满平板后,将灭菌水滴入平板中,用灭菌后的接种环轻轻刮下真菌菌丝,并用纱布过滤,倒入250 mL锥形瓶中,并用灭菌去离子水定容,获得Phanerochaete chrysosporium真菌孢子液。After the freeze-dried powder of Phanerochaete chrysosporium is activated, it is transferred to a comprehensive PDA plate and cultured in an incubator at 27°C for 7-9 days. After the plate is covered with hyphae, drop sterilized water into the plate, gently scrape off the fungal mycelium with a sterilized inoculation loop, filter it with gauze, pour it into a 250 mL Erlenmeyer flask, and rinse with sterilized deionized water Constant volume, obtain Phanerochaete chrysosporium fungal spore liquid.

实施例2:制备氮掺杂多孔炭材料Example 2: Preparation of nitrogen-doped porous carbon material

1) 将废弃玉米秸秆进行粉碎,粉碎后的颗粒粒径为40~60目,粉碎后用2~5倍重量的去离子水不断洗涤,直至洗涤液无浑浊则视为原料表面杂质已经去除,洗涤后在100~110℃下干燥10~14h;1) The waste corn stalks are crushed, and the particle size after crushing is 40-60 mesh. After crushing, it is continuously washed with 2-5 times the weight of deionized water until the washing liquid is not turbid, it is considered that the impurities on the surface of the raw material have been removed. After washing, dry at 100~110℃ for 10~14h;

2)将干燥的玉米秸秆粉与去离子水混合均匀,进行灭菌处理,得到灭菌玉米秸秆粉;2) Mix the dried corn stalk powder with deionized water evenly, and perform sterilization treatment to obtain sterilized corn stalk powder;

3)将灭菌的玉米秸秆粉与真菌孢子液按照质量体积比为30 g:10 mL混合均匀,25~32℃下恒温处理1周,过滤,洗涤,干燥,得到炭化前驱体;3) The sterilized corn stalk powder and the fungal spore liquid were mixed evenly according to the mass volume ratio of 30 g: 10 mL, treated at a constant temperature of 25-32 °C for 1 week, filtered, washed, and dried to obtain a carbonized precursor;

4)将炭化前驱体在480~520℃下进行炭化处理8~15min,获得玉米秸秆炭化物;使用电子扫描显微镜(SEM)观察玉米秸秆炭化物,结果如图1所示,真菌处理后,炭化物表面具有较为发达的孔隙结构,有利于氮源和活化剂的渗入;4) The carbonization precursor was carbonized at 480-520°C for 8-15 minutes to obtain carbonized corn stalks; the carbonized corn stalks were observed with a scanning electron microscope (SEM). More developed pore structure is conducive to the infiltration of nitrogen source and activator;

5)将玉米秸秆炭化物、尿素以及 KOH 按质量比 1﹕0.8~1.2﹕0.8~1.2的比列溶于去离子水中,磁力搅拌,干燥 ,过60目筛,获得活化前体物;5) Dissolve corn stalk charcoal, urea and KOH in deionized water at a mass ratio of 1:0.8~1.2:0.8~1.2, magnetically stir, dry, and pass through a 60-mesh sieve to obtain an activated precursor;

6)将活化前体物在 N2氛围下、750℃~850℃进行活化处理80~100 min,将活化处理的产物先用0.8~1.2 mol/L盐酸洗涤,再用去离子水洗涤至中性,再经无水乙醇洗涤,干燥,研磨,过筛,获得氮掺杂多孔炭材料。6) The activated precursor is activated under N2 atmosphere at 750°C~850°C for 80~100 min, and the activated product is first washed with 0.8~1.2 mol/L hydrochloric acid, and then washed with deionized water until neutral , and then washed with absolute ethanol, dried, ground, and sieved to obtain a nitrogen-doped porous carbon material.

实施例3:制备氮掺杂多孔炭材料Example 3: Preparation of nitrogen-doped porous carbon material

步骤3)恒温处理时间为3周,其他操作通实施例2,真菌处理3周、碳化处理所得玉米秸秆炭化物使用电子扫描显微镜(SEM)观察玉米秸秆炭化物,结果如图2所示。Step 3) The constant temperature treatment time was 3 weeks, and other operations were the same as in Example 2. The carbonized corn stalks obtained from fungal treatment for 3 weeks and carbonization were observed with a scanning electron microscope (SEM), and the results are shown in Figure 2.

实施例4:制备生物质炭电极Example 4: Preparation of Biomass Charcoal Electrode

将实施例2制得的氮掺杂多孔炭材料作为活性材料,乙炔黑作为导电剂,聚四氟乙烯乳液为粘结剂,按照质量比8:1:1的比例混合于研钵中,加乙醇,充分研磨使其混合均匀,得到浆料,将约5 mg浆料涂抹于1 cm×1 cm 的泡沫镍上,烘干后在 10 MPa 的压强下压片2分钟,得到生物质炭电极。The nitrogen-doped porous carbon material obtained in Example 2 is used as an active material, acetylene black is used as a conductive agent, and polytetrafluoroethylene emulsion is used as a binder, mixed in a mortar according to a mass ratio of 8:1:1, and added Ethanol, fully ground to make it evenly mixed to obtain a slurry, smear about 5 mg of the slurry on a nickel foam of 1 cm×1 cm, dry it and press it under a pressure of 10 MPa for 2 minutes to obtain a biochar electrode .

实施例5:制备生物质炭电极Embodiment 5: preparation biochar electrode

将实施例3制得的氮掺杂多孔炭材料作为活性材料,其他操作通实施例4。The nitrogen-doped porous carbon material prepared in Example 3 was used as the active material, and the other operations were the same as in Example 4.

实施例6:性能测试Embodiment 6: performance test

将实施例4、5制备的生物质炭电极使用CS310M电化学工作站,在三电极体系下进行电化学测试,以制备的生物质炭电极为工作电极,铂片电极 (2 cm×2 cm)为对电极,Hg/HgO电极为参比电极,在6M KOH溶液中进行电化学测试。电势窗口范围在 -0.8-0.2 V ,在不同电流密度下的恒电流放电,根据比电容计算公式 Cs= IΔt/(m*ΔV) 。其中Cs为样品的质量比电容,单位为F/g;I为放电电流,单位为A;Δt为放电时间,单位为s;m为电极片上活性物质质量,单位为g;ΔV为电势差,单位为V。The biomass charcoal electrode prepared in Examples 4 and 5 was used in a CS310M electrochemical workstation to carry out electrochemical tests in a three-electrode system. The prepared biomass charcoal electrode was used as the working electrode, and the platinum sheet electrode (2 cm × 2 cm) was The counter electrode, the Hg/HgO electrode is the reference electrode, and the electrochemical test is carried out in 6M KOH solution. The potential window range is -0.8-0.2 V, constant current discharge at different current densities, according to the specific capacitance calculation formula Cs=IΔt/(m*ΔV). Among them, Cs is the mass specific capacitance of the sample, the unit is F/g; I is the discharge current, the unit is A; Δt is the discharge time, the unit is s; m is the mass of the active material on the electrode sheet, the unit is g; ΔV is the potential difference, the unit is for V.

所得结果如下:The results obtained are as follows:

图3为实施例4所得的生物质炭电极片不同扫描速率下的CV曲线图,CV曲线表现出良好的矩形,在 2-100 mV·s-1的扫描速率下没有明显的变形,所制备电极材料比电容主要源于双电层电容;Fig. 3 is the CV curve diagram of the biochar electrode sheet obtained in Example 4 at different scan rates, the CV curve shows a good rectangle, and there is no obvious deformation at the scan rate of 2-100 mV s-1, the prepared The specific capacitance of the electrode material is mainly derived from the electric double layer capacitance;

图4为实施例4所得的生物质炭电极片在不同电流密度下的GCD曲线图,通过计算在0.5A/g,1A/g,2A/g,5A/g,10A/g电流密度下比电容分别为 303.9 F/g,286.1 F/g,273.8F/g,260.0 F/g,252.4 F/g;Fig. 4 is the GCD graph of the biochar electrode sheet obtained in Example 4 at different current densities, by calculation at 0.5A/g, 1A/g, 2A/g, 5A/g, 10A/g current density ratio The capacitance is 303.9 F/g, 286.1 F/g, 273.8 F/g, 260.0 F/g, 252.4 F/g;

图5为实施例5所得的生物质炭电极片不同扫描速率下的CV曲线图, CV曲线表现出良好的矩形,在 2-100 mV·s-1的扫描速率下没有明显的变形,所制备电极材料比电容主要源于双电层电容;Fig. 5 is the CV curve diagram of the biochar electrode sheet obtained in Example 5 at different scan rates, the CV curve shows a good rectangle, and there is no obvious deformation at the scan rate of 2-100 mV s-1, the prepared The specific capacitance of the electrode material is mainly derived from the electric double layer capacitance;

图6为实施例5所得的生物质炭电极片在不同电流密度下的GCD曲线图,通过计算在0.5A/g,1A/g,2A/g,5A/g,10A/g电流密度下比电容分别为408.7 F/g,377.2 F/g, 356.8F/g,335.8 F/g, 320.4 F/g;Fig. 6 is the GCD graph of the biochar electrode sheet obtained in Example 5 at different current densities, by calculation at 0.5A/g, 1A/g, 2A/g, 5A/g, 10A/g current density ratio The capacitances are 408.7 F/g, 377.2 F/g, 356.8 F/g, 335.8 F/g, 320.4 F/g;

图7为实施例4所得的生物质电极片在电流密度为 10 A/g下的循环稳定性图,通过恒定电流充放电循环对电极材料进行测试并评估其循环寿命,在10 A/g下循环10000次后,电容保持率为89.5%,具有良好的循环稳定性。Figure 7 is the cycle stability diagram of the biomass electrode sheet obtained in Example 4 at a current density of 10 A/g. The electrode material is tested and evaluated for its cycle life through a constant current charge and discharge cycle. Under 10 A/g After 10,000 cycles, the capacitance retention rate is 89.5%, showing good cycle stability.

上述实施方式只为说明本发明的技术构思及特点,其目的在于让熟悉此项技术的人能够了解本发明的内容并据以实施,并不能以此限制本发明的保护范围。凡根据本发明精神实质所做的等效变换或修饰,都应涵盖在本发明的保护范围之内。The above-mentioned embodiments are only for illustrating the technical concept and characteristics of the present invention, and its purpose is to enable those skilled in the art to understand the content of the present invention and implement it accordingly, and not to limit the scope of protection of the present invention. All equivalent changes or modifications made according to the spirit of the present invention shall fall within the protection scope of the present invention.

Claims (9)

1. The preparation method of the nitrogen-doped porous carbon material is characterized by comprising the following steps of:
1) Crushing waste corn stalks, washing the crushed waste corn stalks with deionized water to remove impurities on the surfaces of corn stalk powder, and drying the washed waste corn stalk powder;
2) Uniformly mixing the dried corn stalk powder with deionized water, and performing sterilization treatment to obtain sterilized corn stalk powder;
3) Uniformly mixing sterilized corn stalk powder and fungus spore liquid, performing constant temperature treatment, filtering, washing and drying to obtain a carbonized precursor;
4) Carbonizing the carbonized precursor to obtain corn stalk carbonized matter;
5) Dissolving corn stalk carbide, urea and KOH in deionized water, magnetically stirring, drying and sieving to obtain an activated precursor;
6) The activation precursor is added in N 2 And (3) performing activation treatment in an atmosphere, washing the activated product with hydrochloric acid, washing with deionized water to be neutral, washing with absolute ethyl alcohol, drying, grinding and sieving to obtain the nitrogen-doped porous carbon material.
2. The method for preparing the nitrogen-doped porous carbon material according to claim 1, wherein the method comprises the following steps: the drying temperature in the step 1) is 100-110 ℃ and the drying time is 10-14 h; the grain diameter of the crushed corn stalk powder is 40-60 meshes; the mass ratio of the corn stalk powder to the deionized water is 1:2-5.
3. The method for preparing the nitrogen-doped porous carbon material according to claim 1, wherein the method comprises the following steps: the fungus spore liquid in the step 3) is obtained by inoculating Phanerochaete chrysosporium to a culture medium for culturing, washing and filtering; the constant temperature treatment is carried out at 25-32 ℃ for 1-3 weeks.
4. The method for preparing the nitrogen-doped porous carbon material according to claim 1, wherein the method comprises the following steps: the carbonization treatment temperature in the step 4) is 480-520 ℃, and the carbonization time is 8-15 min.
5. The method for preparing the nitrogen-doped porous carbon material according to claim 1, wherein the method comprises the following steps: in the step 5), the mass ratio of the corn stalk carbide to the urea to the KOH is 1:0.8-1.2:0.8-1.2.
6. The method for preparing the nitrogen-doped porous carbon material according to claim 1, wherein the method comprises the following steps: the temperature of the activation treatment in the step 6) is 750-850 ℃ and the time is 80-100 min.
7. The method for preparing the nitrogen-doped porous carbon material according to claim 1, wherein the method comprises the following steps: and 6) the molar concentration of the hydrochloric acid in the step 6) is 0.8-1.2 mol/L, and the hydrochloric acid is sieved by a 200-mesh sieve.
8. Use of a nitrogen-doped porous carbon material prepared by the method of any one of claims 1-7 in the preparation of a high performance electrode material.
9. The use of the nitrogen-doped porous carbon material according to claim 8 for preparing high-performance electrode materials, wherein the specific process is: mixing nitrogen-doped porous carbon serving as an active material, acetylene black serving as a conductive agent and polytetrafluoroethylene emulsion serving as a binder in a mass ratio of 8:0.8-1.2:0.8-1.2 in a mortar, adding ethanol, fully grinding and uniformly mixing to obtain slurry, smearing the slurry on foamed nickel of 1 cm multiplied by 1 cm, drying and tabletting to obtain the biomass carbon electrode.
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