CN111900415A - Method for preparing metal-nitrogen co-doped oxygen reduction catalyst using electroplating sludge - Google Patents

Method for preparing metal-nitrogen co-doped oxygen reduction catalyst using electroplating sludge Download PDF

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CN111900415A
CN111900415A CN202010663359.2A CN202010663359A CN111900415A CN 111900415 A CN111900415 A CN 111900415A CN 202010663359 A CN202010663359 A CN 202010663359A CN 111900415 A CN111900415 A CN 111900415A
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nitrogen
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oxygen reduction
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electroplating sludge
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杨超
魏萍
刘强
曹为民
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SHANGHAI UNIVERSITY
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    • HELECTRICITY
    • H01ELECTRIC ELEMENTS
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    • HELECTRICITY
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    • HELECTRICITY
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    • H01MPROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
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Abstract

本发明公开了一种利用电镀污泥制备金属‑氮共掺杂氧还原催化剂的方法,将电镀污泥、三聚氰胺和玉米秸秆生物质粉末按一定比例混合溶于超纯水中,室温下磁力搅拌4h,搅拌后在50~70℃下干燥,干燥后研磨成粉末;随后取适量粉末,在950℃、N2保护下热解2h,冷却至100℃以下取出;将所得物置于1mol/L的盐酸中进行浸泡震荡、洗涤、干燥,得到基于电镀污泥的金属‑氮共掺杂氧还原催化剂。该催化剂测试时具有与商业Pt/C相媲美的氧还原催化活性,且具有优良的稳定性、抗甲醇性好、制备简单,是一项“变废为宝”的良好举措,为燃料电池的阴极催化剂提供了一个选择。

Figure 202010663359

The invention discloses a method for preparing a metal-nitrogen co-doped oxygen reduction catalyst by using electroplating sludge. Electroplating sludge, melamine and corn stalk biomass powder are mixed and dissolved in ultrapure water in a certain proportion, and magnetically stirred at room temperature. After stirring, it was dried at 50-70 °C for 4 h, and then ground into powder after drying; then an appropriate amount of powder was taken, pyrolyzed at 950 °C under the protection of N 2 for 2 h, cooled to below 100 °C and taken out; Soak and shake in hydrochloric acid, wash and dry to obtain a metal-nitrogen co-doped oxygen reduction catalyst based on electroplating sludge. The catalyst has an oxygen reduction catalytic activity comparable to that of commercial Pt/C, and has excellent stability, good methanol resistance, and simple preparation. Cathode catalysts offer an option.

Figure 202010663359

Description

利用电镀污泥制备金属-氮共掺杂氧还原催化剂的方法Method for preparing metal-nitrogen co-doped oxygen reduction catalyst using electroplating sludge

技术领域technical field

本发明涉及一种利用电镀污泥制备金属-氮共掺杂氧还原催化剂的方法,属于电催化和废弃物资源化技术领域。The invention relates to a method for preparing a metal-nitrogen co-doped oxygen reduction catalyst by using electroplating sludge, and belongs to the technical field of electrocatalysis and waste recycling.

背景技术Background technique

燃料电池是一种效率高、噪音小的环境友好型能源装置,但其阴极氧还原反应过电位高,抗甲醇性差,需要有合适的催化剂才能让其具有良好的性能,发挥出其优点。当前商业化的Pt类催化剂价格昂贵且Pt的储量有限,需要开发出催化性能好、价格低、储量大的非贵金属类催化剂来替代Pt类催化剂。非贵金属类氧还原催化剂为燃料电池带来了新的希望,尤其是金属-氮/碳型催化剂。Fuel cell is an environment-friendly energy device with high efficiency and low noise, but its cathode oxygen reduction reaction overpotential is high, and its resistance to methanol is poor. The current commercialized Pt-based catalysts are expensive and the reserves of Pt are limited. It is necessary to develop non-precious metal-based catalysts with good catalytic performance, low price and large reserves to replace Pt-based catalysts. Non-precious metal-based oxygen reduction catalysts have brought new hope for fuel cells, especially metal-nitrogen/carbon-based catalysts.

金属源是金属-氮/碳型催化剂中的重要成分。作为电镀行业废水处理的“终态物”的电镀污泥,含有大量含有不同含量的铜、镍、铬、铁、锌等重要金属,如果得不到合适的处理,会对环境造成污染与破坏,但也具有成为金属源的潜力。将电镀污泥作为金属-氮/碳类催化剂的金属源,都将会是一个废物利用和环境保护的两全举措,但至今未见文献报道。Metal sources are important components in metal-nitrogen/carbon type catalysts. Electroplating sludge, which is the "final state" of wastewater treatment in the electroplating industry, contains a large amount of important metals such as copper, nickel, chromium, iron, and zinc with different contents. If it is not properly treated, it will cause pollution and damage to the environment. , but also has the potential to be a metal source. Using electroplating sludge as a metal source for metal-nitrogen/carbon catalysts will be a combination of waste utilization and environmental protection, but it has not been reported in the literature so far.

发明内容SUMMARY OF THE INVENTION

为了解决现有技术问题,本发明的目的在于克服已有技术存在的不足,提供一种利用电镀污泥制备金属-氮共掺杂氧还原催化剂的方法,操作简便、制备所需时间短、所用的金属来源为电镀工业废弃物,且制备出的催化剂氧还原催化性能好,可媲美当前的商业Pt/C,还具有良好的抗甲醇性及耐久性。In order to solve the problems of the prior art, the object of the present invention is to overcome the deficiencies of the prior art, and to provide a method for preparing a metal-nitrogen co-doped oxygen reduction catalyst by utilizing electroplating sludge, which is easy to operate, requires a short preparation time, and uses The source of the metal is electroplating industrial waste, and the prepared catalyst has good oxygen reduction catalytic performance, which is comparable to the current commercial Pt/C, and also has good methanol resistance and durability.

为达到上述发明创造目的,本发明采用如下技术方案:In order to achieve the above-mentioned purpose of invention and creation, the present invention adopts the following technical solutions:

一种利用电镀污泥制备金属-氮共掺杂氧还原催化剂的方法,包括如下步骤:A method for preparing a metal-nitrogen co-doped oxygen reduction catalyst by utilizing electroplating sludge, comprising the following steps:

a.将玉米秸秆烘干并磨碎,然后将磨碎后的秸秆粉末过100目筛后收集,得到秸秆粉末;a. Dry and grind the corn stalks, and then pass the ground stalk powder through a 100-mesh sieve and collect it to obtain the stalk powder;

b.将电镀污泥、三聚氰胺和在所述步骤a中进行过筛后的秸秆粉末进行混合,然后溶于超纯水中,在室温下磁力搅拌至少4h,在搅拌后过滤分离获得固形物,并在50~70℃下进行干燥,然后将干燥后的固形物进行研磨成混合物粉末;b. Mix the electroplating sludge, melamine and the sieved straw powder in step a, then dissolve in ultrapure water, stir magnetically for at least 4 hours at room temperature, and filter and separate to obtain solids after stirring, And dry at 50~70℃, and then grind the dried solids into powder mixture;

c.取在所述步骤b得到的混合物粉末,置于石英舟中,在不低于950℃下,并在N2保护下对混合物进行热解至少2h,然后将裂解产区冷却至不高于100℃,将裂解产物取出,得到热解金属-氮改性生物炭;c. Take the mixture powder obtained in the step b, put it in a quartz boat, and pyrolyze the mixture under the protection of N 2 at a temperature of not lower than 950 ° C for at least 2 hours, and then cool the cracking production area to not high At 100°C, the pyrolysis product is taken out to obtain pyrolysis metal-nitrogen modified biochar;

d.将在所述步骤c得到的生物炭置于浓度不低于1mol/L的盐酸中,进行浸泡震荡洗涤至少12h,然后用超纯水抽滤洗涤至pH为7,将洗涤后的产物分出出来并进行收集,然后在50~70℃下进行干燥,得到金属-氮共掺杂氧还原催化剂。d. The biochar obtained in the step c is placed in hydrochloric acid with a concentration of not less than 1 mol/L, soaked and shaken for washing for at least 12 hours, and then washed with ultrapure water suction filtration until the pH is 7, and the washed product It is separated out and collected, and then dried at 50-70° C. to obtain a metal-nitrogen co-doped oxygen reduction catalyst.

作为本发明优选的技术方案,在所述步骤b中,将电镀污泥、三聚氰胺和在所述步骤a中进行过筛后的秸秆粉末按照原料质量配比为1:20:4的比例进行混合。As a preferred technical solution of the present invention, in the step b, the electroplating sludge, melamine and the sieved straw powder in the step a are mixed according to the ratio of raw material mass ratio of 1:20:4 .

作为本发明优选的技术方案,在所述步骤c中,取步骤b得到的混合物粉末,置于石英舟中,在真空管式炉中,通入非氧化还原保护气体流量不低于200mL/min,从室温程序升温至不低于100℃,升温速率不低于10℃/min,恒温保持至少20min,以此操作来维持管式炉内氧气排尽,且生物质处于干燥状态;然后以不低于10℃/min的升温速率,加热至不低于950℃,恒温碳化处理至少2h;然后将恒温碳化处理后获得的裂解产物冷却至不高于100℃,将裂解产物取出,得到热解金属-氮改性生物炭。As a preferred technical solution of the present invention, in the step c, the mixture powder obtained in the step b is taken, placed in a quartz boat, and in a vacuum tube furnace, the flow rate of the non-redox protective gas is not less than 200mL/min, Program the temperature from room temperature to not less than 100 °C, the heating rate is not less than 10 °C/min, and the constant temperature is maintained for at least 20 minutes. This operation is used to maintain the oxygen exhaust in the tube furnace and the biomass is in a dry state; At a heating rate of 10°C/min, heat to not lower than 950°C, and carbonize at a constant temperature for at least 2 hours; then cool the pyrolysis product obtained after the constant temperature carbonization treatment to not higher than 100°C, and take out the pyrolysis product to obtain pyrolysis metal. - Nitrogen-modified biochar.

作为本发明优选的技术方案,在所述步骤d中,所制备的金属-氮共掺杂氧还原催化剂中含有金属的质量百分比不少于0.65wt.%,含有氮的质量百分比不少于4.76wt.%。As a preferred technical solution of the present invention, in the step d, the prepared metal-nitrogen co-doped oxygen reduction catalyst contains a mass percentage of metal not less than 0.65 wt.%, and a mass percentage of nitrogen not less than 4.76 wt.%.

作为本发明进一步优选的技术方案,在所述步骤d中,所制备的金属-氮共掺杂氧还原催化剂中含有金属的质量百分比不少于0.65wt.%,含有氮的质量百分比不少于4.76wt.%,含有硅的质量百分比不少于2.13wt.%,含有氧的质量百分比不少于14.35wt.%,余量为碳和杂质。As a further preferred technical solution of the present invention, in the step d, the prepared metal-nitrogen co-doped oxygen reduction catalyst contains a mass percentage of metal not less than 0.65 wt.%, and a mass percentage of nitrogen not less than 4.76wt.%, the mass percentage containing silicon is not less than 2.13wt.%, the mass percentage containing oxygen is not less than 14.35wt.%, and the balance is carbon and impurities.

一种金属-氮共掺杂氧还原催化剂,通过本发明利用电镀污泥制备金属-氮共掺杂氧还原催化剂的方法制备而成。A metal-nitrogen co-doped oxygen reduction catalyst is prepared by the method of the present invention using electroplating sludge to prepare a metal-nitrogen co-doped oxygen reduction catalyst.

本发明与现有技术相比较,具有如下显而易见的突出实质性特点和显著优点:Compared with the prior art, the present invention has the following obvious outstanding substantive features and significant advantages:

1.本发明方法能基于电镀污泥制备一种金属-氮共掺杂氧还原催化剂,该催化剂测试时具有与商业Pt/C相媲美的氧还原催化活性,且具有优良的稳定性、抗甲醇性好、制备简单,是一项“变废为宝”的良好举措,为燃料电池的阴极催化剂提供了一个选择;1. The method of the present invention can prepare a metal-nitrogen co-doped oxygen reduction catalyst based on electroplating sludge. The catalyst has an oxygen reduction catalytic activity comparable to that of commercial Pt/C during testing, and has excellent stability and methanol resistance. Good performance and simple preparation, it is a good measure to "turn waste into treasure", and provides a choice for the cathode catalyst of fuel cells;

2.本发明方法简单易行,成本低,适合推广使用。2. The method of the present invention is simple and easy to implement, low in cost, and suitable for popularization and use.

附图说明Description of drawings

图1是本发明优选实施例制备方法的SEM、TEM测试图。Fig. 1 is the SEM and TEM test charts of the preparation method of the preferred embodiment of the present invention.

图2是本发明优选实施例所制备金属-氮共掺杂氧还原催化剂和商业Pt/C的LSV图对比。FIG. 2 is a comparison of the LSV diagrams of the metal-nitrogen co-doped oxygen reduction catalyst prepared in the preferred embodiment of the present invention and commercial Pt/C.

图3是现有技术的商业Pt/C氧还原催化剂的抗甲醇测试图。Figure 3 is a graph of methanol resistance test of a prior art commercial Pt/C oxygen reduction catalyst.

图4是本发明优选实施例所制备金属-氮共掺杂氧还原催化剂的抗甲醇测试图。FIG. 4 is a test chart of methanol resistance of the metal-nitrogen co-doped oxygen reduction catalyst prepared in the preferred embodiment of the present invention.

具体实施方式Detailed ways

以下结合具体的实施例子对上述方案做进一步说明,本发明的优选实施例详述如下:The above scheme will be further described below in conjunction with specific embodiments, and preferred embodiments of the present invention are described in detail as follows:

在本实施例中,一种利用电镀污泥制备金属-氮共掺杂氧还原催化剂的方法,步骤如下:In this embodiment, a method for preparing a metal-nitrogen co-doped oxygen reduction catalyst using electroplating sludge, the steps are as follows:

a.将玉米秸秆烘干并磨碎,然后将磨碎后的秸秆粉末过100目筛后收集,得到秸秆粉末;a. Dry and grind the corn stalks, and then pass the ground stalk powder through a 100-mesh sieve and collect it to obtain the stalk powder;

b.将电镀污泥、三聚氰胺和在所述步骤a中进行过筛后的秸秆粉末按质量比1:20:4的比例进行混合,然后溶于超纯水中,在室温下磁力搅拌4h,在搅拌后过滤分离获得固形物,并在50~70℃下进行干燥,然后将干燥后的固形物进行研磨成混合物粉末;b. The electroplating sludge, melamine and the sieved straw powder in the step a are mixed in a mass ratio of 1:20:4, then dissolved in ultrapure water, and magnetically stirred at room temperature for 4h, After stirring, the solid matter is obtained by filtration and separation, and dried at 50-70° C., and then the dried solid matter is ground into a mixture powder;

c.取步骤b得到的混合物粉末,置于石英舟中,在真空管式炉中,通入非氧化还原保护气体流量为200mL/min,从室温程序升温至100℃,升温速率为10℃/min,恒温保持20min,以此操作来维持管式炉内氧气排尽,且生物质处于干燥状态;然后以10℃/min的升温速率,加热至950℃,恒温碳化处理2h;然后将恒温碳化处理后获得的裂解产物冷却至100℃,将裂解产物取出,得到热解金属-氮改性生物炭;c. Take the mixture powder obtained in step b and place it in a quartz boat. In a vacuum tube furnace, the flow rate of the non-redox protective gas is 200mL/min, and the temperature is programmed from room temperature to 100°C, and the heating rate is 10°C/min. , the constant temperature is maintained for 20min, and this operation is used to maintain the oxygen exhaust in the tube furnace, and the biomass is in a dry state; then, at a heating rate of 10℃/min, heated to 950℃, constant temperature carbonization treatment for 2h; then constant temperature carbonization treatment The obtained pyrolysis product is cooled to 100°C, and the pyrolysis product is taken out to obtain pyrolysis metal-nitrogen modified biochar;

d.将在所述步骤c得到的生物炭置于浓度为1mol/L的盐酸中,进行浸泡震荡洗涤12h,然后用超纯水抽滤洗涤至pH为7,将洗涤后的产物分出出来并进行收集,然后在50~70℃下进行干燥,得到金属-氮共掺杂氧还原催化剂。d. The biochar obtained in the step c is placed in hydrochloric acid with a concentration of 1 mol/L, soaked and shaken for 12 hours, and then washed with ultrapure water by suction filtration until the pH is 7, and the washed product is separated out and collected, and then dried at 50-70° C. to obtain a metal-nitrogen co-doped oxygen reduction catalyst.

实验测试分析:Experimental test analysis:

将本实施例制备的金属-氮共掺杂氧还原催化剂作为试验样品,进行性质检验。The metal-nitrogen co-doped oxygen reduction catalyst prepared in this example was used as a test sample for property inspection.

在本实施例中,电镀污泥的成分如表1所示。In this example, the composition of the electroplating sludge is shown in Table 1.

表1.电镀污泥成分表Table 1. Electroplating sludge composition table

Figure BDA0002579439880000031
Figure BDA0002579439880000031

本实施例中所用电镀污泥的成分分析,结果显示,该电镀污泥以Fe为主,并含有少量其他金属的混合物。The composition analysis of the electroplating sludge used in this example shows that the electroplating sludge is mainly Fe and contains a small amount of mixture of other metals.

在本实施例中,所制备的金属-氮共掺杂氧还原催化剂的成分如表2所示。In this example, the composition of the prepared metal-nitrogen co-doped oxygen reduction catalyst is shown in Table 2.

表2.ES-N/BC样品XPS成分分析表Table 2. XPS composition analysis table of ES-N/BC samples

Figure BDA0002579439880000032
Figure BDA0002579439880000032

表2为本实施例中制备的催化剂的XPS成分分析表,金属及氮都已经成功掺杂到材料中。Table 2 is the XPS composition analysis table of the catalyst prepared in this example, and both metal and nitrogen have been successfully doped into the material.

图1是本实施例制备方法的SEM、TEM测试图,其中图1(a)为SEM,图1(b)为TEM测试图。由图1可知,本实施例制备出的材料是具有多孔的絮状结构,并具有丰富的边缘结构。图2是本实施例所制备金属-氮共掺杂氧还原催化剂和商业Pt/C的LSV图对比。在-0.80V处,ES-N/BC的极限电流密度绝对值分别达到5.094mA cm-2,达到并超过了商业Pt/C的5.048mAcm-2,实施例制备的催化剂的催化活性与商业Pt/C相当了。图3是现有技术的商业Pt/C氧还原催化剂的抗甲醇测试图。图4是本发明实施例一所制备金属-氮共掺杂氧还原催化剂的抗甲醇测试图。由图3和图4可见,商业Pt/C在加入甲醇后,出现了明显的甲醇反应峰,其抗甲醇性能不佳。而实施例制备出的材料,在加入甲醇后曲线基本没有变化,具有良好的抗甲醇性能。Fig. 1 is the SEM and TEM test charts of the preparation method of this embodiment, wherein Fig. 1(a) is the SEM, and Fig. 1(b) is the TEM test chart. It can be seen from FIG. 1 that the material prepared in this example has a porous floc structure and has abundant edge structures. FIG. 2 is a comparison of the LSV diagrams of the metal-nitrogen co-doped oxygen reduction catalyst prepared in this example and commercial Pt/C. At -0.80V, the absolute value of the limiting current density of ES-N/BC reaches 5.094mA cm -2 respectively, which reaches and exceeds the 5.048mAcm -2 of commercial Pt/C. The catalytic activity of the catalyst prepared in the example is comparable to that of commercial Pt/C. /C is equivalent. Figure 3 is a graph of methanol resistance test of a prior art commercial Pt/C oxygen reduction catalyst. 4 is a test chart of methanol resistance of the metal-nitrogen co-doped oxygen reduction catalyst prepared in Example 1 of the present invention. It can be seen from Figure 3 and Figure 4 that commercial Pt/C has an obvious methanol reaction peak after adding methanol, and its anti-methanol performance is not good. However, the materials prepared in the examples have basically no change in the curve after the addition of methanol, and have good methanol resistance.

本实施例利用电镀污泥制备金属-氮共掺杂氧还原催化剂的方法,将电镀污泥、三聚氰胺和玉米秸秆生物质粉末按一定比例混合溶于超纯水中,室温下磁力搅拌4h,搅拌后在50~70℃下干燥,干燥后研磨成粉末;随后取适量粉末,在950℃、N2保护下热解2h,冷却至100℃以下取出;将所得物置于1mol/L的盐酸中进行浸泡震荡、洗涤、干燥,得到基于电镀污泥的金属-氮共掺杂氧还原催化剂。该催化剂测试时具有与商业Pt/C相媲美的氧还原催化活性,且具有优良的稳定性、抗甲醇性好、制备简单,是一项“变废为宝”的良好举措,为燃料电池的阴极催化剂提供了一个选择。In this example, the method for preparing a metal-nitrogen co-doped oxygen reduction catalyst by using electroplating sludge, the electroplating sludge, melamine and corn stover biomass powder are mixed in a certain proportion and dissolved in ultrapure water, and the magnetic stirring is carried out at room temperature for 4 hours. After drying, it was dried at 50-70 °C, and ground into powder after drying; then an appropriate amount of powder was taken, pyrolyzed at 950 °C under the protection of N 2 for 2 h, cooled to below 100 °C and taken out; the resultant was placed in 1 mol/L hydrochloric acid for Soaking and shaking, washing and drying to obtain a metal-nitrogen co-doped oxygen reduction catalyst based on electroplating sludge. The catalyst has an oxygen reduction catalytic activity comparable to that of commercial Pt/C, and has excellent stability, good methanol resistance, and simple preparation. Cathode catalysts offer an option.

上面对本发明实施例结合附图进行了说明,但本发明不限于上述实施例,还可以根据本发明的发明创造的目的做出多种变化,凡依据本发明技术方案的精神实质和原理下做的改变、修饰、替代、组合或简化,均应为等效的置换方式,只要符合本发明的发明目的,只要不背离本发明的技术原理和发明构思,都属于本发明的保护范围。The embodiments of the present invention have been described above in conjunction with the accompanying drawings, but the present invention is not limited to the above-mentioned embodiments, and various changes can also be made according to the purpose of the invention and creation of the present invention. Changes, modifications, substitutions, combinations or simplifications should be equivalent substitution methods, as long as they meet the purpose of the present invention, as long as they do not deviate from the technical principles and inventive concepts of the present invention, all belong to the protection scope of the present invention.

Claims (6)

1. A method for preparing a metal-nitrogen codoped oxygen reduction catalyst by using electroplating sludge is characterized by comprising the following steps:
a. drying and grinding corn straws, and then sieving the ground straw powder with a 100-mesh sieve and collecting to obtain straw powder;
b. mixing electroplating sludge, melamine and the straw powder sieved in the step a, dissolving the mixture in ultrapure water, magnetically stirring the mixture at room temperature for at least 4 hours, filtering and separating the mixture after stirring to obtain solid matters, drying the solid matters at 50-70 ℃, and grinding the dried solid matters into mixture powder;
c. putting the mixture powder obtained in the step b into a quartz boat, and carrying out reaction at the temperature of not less than 950 ℃ and in N2Pyrolyzing the mixture for at least 2 hours under protection, then cooling the pyrolysis product to be not higher than 100 ℃, and taking out the pyrolysis product to obtain pyrolytic metal-nitrogen modified biochar;
d. and c, placing the biochar obtained in the step c in hydrochloric acid with the concentration not lower than 1mol/L, soaking, shaking and washing for at least 12 hours, then performing suction filtration and washing with ultrapure water until the pH value is 7, separating and collecting washed products, and then drying at 50-70 ℃ to obtain the metal-nitrogen co-doped oxygen reduction catalyst.
2. The method for preparing the metal-nitrogen co-doped oxygen reduction catalyst by using electroplating sludge according to claim 1, wherein in the step b, the electroplating sludge, the melamine and the straw powder sieved in the step a are mixed according to a raw material mass ratio of 1:20: 4.
3. The method for preparing a metal-nitrogen co-doped oxygen reduction catalyst by using electroplating sludge according to claim 1, wherein in the step c, the mixture powder obtained in the step b is taken and placed in a quartz boat, a non-redox protection gas is introduced into a vacuum tube furnace, the flow rate is not lower than 200mL/min, the temperature is programmed to be not lower than 100 ℃ from room temperature, the heating rate is not lower than 10 ℃/min, the temperature is kept for at least 20min at constant temperature, so that the oxygen in the tube furnace is exhausted, and the biomass is in a dry state; then heating to be not less than 950 ℃ at the heating rate of not less than 10 ℃/min, and carrying out constant-temperature carbonization treatment for at least 2 h; and then cooling the pyrolysis product obtained after the constant-temperature carbonization treatment to be not higher than 100 ℃, and taking out the pyrolysis product to obtain the pyrolytic metal-nitrogen modified biochar.
4. The method for preparing a metal-nitrogen co-doped oxygen reduction catalyst by using electroplating sludge as claimed in claim 1, wherein in the step d, the prepared metal-nitrogen co-doped oxygen reduction catalyst contains not less than 0.65 wt.% of metal and not less than 4.76 wt.% of nitrogen.
5. The method for preparing a metal-nitrogen co-doped oxygen reduction catalyst by using electroplating sludge as claimed in claim 4, wherein in the step d, the prepared metal-nitrogen co-doped oxygen reduction catalyst contains not less than 0.65 wt.% of metal, not less than 4.76 wt.% of nitrogen, not less than 2.13 wt.% of silicon, not less than 14.35 wt.% of oxygen, and the balance of carbon and impurities.
6. A metal-nitrogen co-doped oxygen reduction catalyst, which is prepared by the method for preparing a metal-nitrogen co-doped oxygen reduction catalyst by using electroplating sludge according to claim 1.
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