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CN104307473B - A kind of preparation method of the absorption visible light catalytic material for air pollution treatment - Google Patents

A kind of preparation method of the absorption visible light catalytic material for air pollution treatment Download PDF

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CN104307473B
CN104307473B CN201410558124.1A CN201410558124A CN104307473B CN 104307473 B CN104307473 B CN 104307473B CN 201410558124 A CN201410558124 A CN 201410558124A CN 104307473 B CN104307473 B CN 104307473B
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visible light
adsorption
air
mix
light catalytic
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CN104307473A (en
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王学江
尹大强
赵建夫
宋靖柯
张晶
马荣荣
夏鹏
王鑫
黄嘉瑜
陈杰
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Tongji University
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Abstract

本发明涉及一种用于空气治理的吸附可见光催化复合功能材料的制备方法,具体地说是利用煤矸石、沥青粉和电气石为原料,制备带永久负电荷的活性炭-沸石复合物,作为WO3/TiO2催化剂的载体合成吸附-可见光催化材料。该复合材料中,电气石自然带永久负电荷,能持续高效地吸附空气中带正电荷的PM2.5,煤矸石生成的活性炭-沸石复合物具有超大的比表面积,同时具备沸石的亲水性和活性炭的疏水特性,对空气中的极性污染物和疏水性的VOCs等物质具有良好的特异吸附性,在太阳光照下,上述被吸附的污染物可被WO3/TiO2催化剂降解去除。本发明产品可以用在外墙涂料技术领域,在雨水冲洗后保持自净,从而实现对污染空气的持续高效净化。The invention relates to a method for preparing an adsorption visible light catalytic composite functional material for air treatment. Specifically, coal gangue, asphalt powder and tourmaline are used as raw materials to prepare activated carbon-zeolite composites with permanent negative charges. As WO 3 /TiO 2 Catalyst Support Synthesis of Adsorption-Visible Light Catalytic Materials. In this composite material, tourmaline naturally has a permanent negative charge, which can continuously and efficiently absorb positively charged PM2.5 in the air. The activated carbon-zeolite composite produced by coal gangue has a large specific surface area and has the hydrophilicity of zeolite. And the hydrophobic characteristics of activated carbon, it has good specific adsorption for polar pollutants and hydrophobic VOCs in the air. Under sunlight, the above-mentioned adsorbed pollutants can be degraded and removed by WO 3 /TiO 2 catalyst. The product of the invention can be used in the technical field of exterior wall coatings, and can maintain self-cleaning after being washed by rainwater, so as to realize continuous and efficient purification of polluted air.

Description

一种用于空气污染治理的吸附可见光催化材料的制备方法A preparation method of adsorption visible light catalytic material for air pollution control

技术领域technical field

本发明属大气污染治理技术领域,具体涉及一种用于空气治理的吸附-可见光催化复合功能材料的制备方法。The invention belongs to the technical field of air pollution control, and in particular relates to a preparation method of an adsorption-visible light catalysis composite functional material used for air control.

背景技术Background technique

随着我国经济的高速发展、城市化进程的加快和工业规模的扩大,区域性大气污染日益严重。近年来在我国多个地区接连出现以细颗粒物为特征污染物的雾霾天气,对能见度、公众健康和城市景观构成巨大威胁。With the rapid development of my country's economy, the acceleration of urbanization and the expansion of industrial scale, regional air pollution is becoming more and more serious. In recent years, smog weather characterized by fine particulate matter has appeared successively in many regions of my country, posing a huge threat to visibility, public health and urban landscape.

在现有的空气污染治理技术中,光催化材料因其具有显著的空气净化效能,成为解决城市空气污染的有效途径之一。光催化技术的原理是利用的光催化材料,把太阳能转化为化学能,对有毒有害的物质进行氧化降解,达到了无害化处理。光催化反应对于空气中的挥发性有机物(VOCs)具有普遍较好的降解效果,同时,其对空气中的无机污染物(NOx、CO、H2S等)也有氧化去除作用,并对暴露于空气中的细菌和病毒同样具有良好的灭杀作用。在诸多光催化/敏化半导体材料中,二氧化钛(TiO2)因其洁净、安全、环境友好等特点受到人们的广泛关注。Among the existing air pollution control technologies, photocatalytic materials have become one of the effective ways to solve urban air pollution because of their remarkable air purification efficiency. The principle of photocatalytic technology is to use photocatalytic materials to convert solar energy into chemical energy, oxidize and degrade toxic and harmful substances, and achieve harmless treatment. The photocatalytic reaction has a generally good degradation effect on volatile organic compounds (VOCs) in the air. At the same time, it can also oxidize and remove inorganic pollutants (NOx, CO, H 2 S, etc.) Bacteria and viruses in the air also have a good killing effect. Among many photocatalytic/sensitizing semiconductor materials, titanium dioxide (TiO 2 ) has attracted widespread attention due to its cleanliness, safety, and environmental friendliness.

近年来,国内外在光催化环境净化涂料的研究和工业化应用方面取得了一定成果。如专利CN101629031B公开了一种具有杀菌和分解有毒物质的光催化功能涂料的制备方法,可以用在内墙涂料、纺织织物等技术领域。专利CN102776993A公开了一种具有防污自洁功能的光触媒建筑物外壁,通过在建筑物的基材表面喷涂TiO2光触媒,从而使外壁有防污自洁功能的具有防污自洁功能。实践表明,在城市的道路、建筑立面的表面涂布光催化剂材料,通过光线作用催化降解功能,能有效降解空气中的NOX、VOCs和硫氧化物等污染物,从而间接消除PM2.5,对净化城市空气污染物和改善空气质量有较好效果,同时不影响建筑物的使用功能,也不影响建筑物的外观。In recent years, some achievements have been made in the research and industrial application of photocatalytic environmental purification coatings at home and abroad. For example, the patent CN101629031B discloses a preparation method of a photocatalytic functional coating capable of sterilizing and decomposing toxic substances, which can be used in technical fields such as interior wall coatings and textile fabrics. Patent CN102776993A discloses a photocatalyst building outer wall with anti-fouling and self-cleaning functions. By spraying TiO2 photocatalyst on the substrate surface of the building, the outer wall has anti-fouling and self-cleaning functions. Practice has shown that coating photocatalyst materials on the surface of urban roads and building facades can effectively degrade pollutants such as NOx , VOCs and sulfur oxides in the air through the catalytic degradation function of light, thereby indirectly eliminating PM2.5 , It has a good effect on purifying urban air pollutants and improving air quality, and at the same time does not affect the use function of the building, nor does it affect the appearance of the building.

尽管纳米TiO2在环境净化涂料中的应用取得了引人注目、卓有成效的成果,但依然存在有某些不利于实际推广的问题。(1)纳米TiO2在使用上对环境有一定的依赖性和局限性,其对紫外光源利用率极高,而对常见的可见光源(如:太阳光)利用不足,效率很低,但在太阳光照中,紫外光源的比例不到6%,这就大大局限了纳米TiO2环境净化涂料的使用范围。(2)在气相反应体系中,污染物预先在催化剂表面的吸附对提高光催化氧化速率是非常重要的,而现有TiO2复合光催化材料往往只注重自洁功能,其对VOCs和PM2.5等污染物的吸附性能较差,直接影响了其实际空气净化效果。Although the application of nano-TiO 2 in environmental purification coatings has achieved remarkable and fruitful results, there are still some problems that are not conducive to practical promotion. (1) The use of nano-TiO 2 has certain dependence and limitations on the environment, and its utilization rate of ultraviolet light source is extremely high, while the utilization of common visible light source (such as: sunlight) is insufficient, and the efficiency is very low, but in In sunlight, the proportion of ultraviolet light source is less than 6%, which greatly limits the scope of application of nano- TiO2 environmental purification coatings. (2) In the gas phase reaction system, the pre-adsorption of pollutants on the surface of the catalyst is very important to improve the photocatalytic oxidation rate, while the existing TiO 2 composite photocatalytic materials often only focus on the self-cleaning function, which is harmful to VOCs and PM2. The adsorption performance of pollutants such as 5 is poor, which directly affects its actual air purification effect.

发明内容Contents of the invention

本发明旨在克服现有技术缺点,提供一种用于空气治理的吸附可见光催化复合功能材料的制备方法。具体是利用煤矸石、沥青粉和电气石为原料,制备高质量的活性炭-沸石复合物,以此为载体负载WO3/TiO2合成吸附-可见光催化剂,用于对空气中PM2.5和VOCs等污染物的高效吸附-光催化去除。The invention aims to overcome the disadvantages of the prior art, and provides a method for preparing an adsorbed visible light catalytic composite functional material for air treatment. Specifically, coal gangue, asphalt powder and tourmaline are used as raw materials to prepare high-quality activated carbon-zeolite composites, which are used as carriers to support WO 3 /TiO 2 to synthesize adsorption-visible light catalysts for PM2.5 and VOCs in the air. Efficient adsorption-photocatalytic removal of pollutants such as

本发明提出的一种用于空气污染治理的吸附可见光催化材料的制备方法,所述吸附可见光催化材料为负载有WO3/TiO2的活性炭-沸石材料,具体步骤如下:The present invention proposes a method for preparing an adsorbed visible light catalytic material for air pollution control, wherein the adsorbed visible light catalytic material is an activated carbon - zeolite material loaded with WO3/ TiO2 , and the specific steps are as follows:

(1)将粒度为200目以下煤矸石、电气石和沥青粉,按煤矸石:电气石:沥青粉为(0.5~0.9):(0.05~0.15):(0.1~0.3)的重量比进行配比,并充分混合,制得物料A;(1) Mix coal gangue, tourmaline and asphalt powder with a particle size below 200 meshes according to the weight ratio of coal gangue: tourmaline: asphalt powder (0.5~0.9): (0.05~0.15): (0.1~0.3) , and fully mixed to obtain material A;

(2)在室温下,将钛酸四正丁酯与无水乙醇按1:1的体积比混合,搅拌0.5~2h,得到均匀透明的黄色溶液B;(2) At room temperature, mix tetra-n-butyl titanate and absolute ethanol at a volume ratio of 1:1, and stir for 0.5~2 hours to obtain a uniform and transparent yellow solution B;

(3)将步骤(1)得到的物料A和步骤(2)得到的黄色溶液B按质量体积比1:1~5的比例混合,陈化24~48h,在流速为200mL/min的二氧化碳气体条件下,升温至500~800℃炭化6~12h,冷却至室温后,制得物料C;(3) Mix the material A obtained in step (1) and the yellow solution B obtained in step (2) according to the mass volume ratio of 1:1~5, age for 24~48h, in the carbon dioxide gas with a flow rate of 200mL/min Under the same conditions, the temperature was raised to 500~800°C for 6~12 hours of carbonization, and after cooling to room temperature, material C was obtained;

(4)将步骤(3)得到的物料C和钨酸钠水溶液按照质量体积比(w/v)10%充分混合,超声振荡4~8h,然后洗涤干燥,氮气气氛400~550℃下活化2~4h,冷却室温后粉碎至150目以下,即制得成品。(4) Mix the material C obtained in step (3) and sodium tungstate aqueous solution according to the mass volume ratio (w/v) of 10%, ultrasonically oscillate for 4~8h, then wash and dry, and activate at 400~550°C in a nitrogen atmosphere for 2 ~4h, after cooling to room temperature, crush to below 150 mesh to obtain the finished product.

本发明中,所述的物料C和钨酸钠的重量比为(0.8~0.95):(0.05~0.2)。In the present invention, the weight ratio of the material C to sodium tungstate is (0.8~0.95): (0.05~0.2).

原理:利用煤矸石、沥青粉和电气石为原料,制备带永久负电荷的活性炭-沸石复合物,作为WO3/TiO2催化剂的载体合成吸附可见光催化复合材料。该复合材料中,电气石自然带永久负电荷,能持续高效地吸附空气中带正电荷的PM2.5,煤矸石生成的活性炭-沸石复合物具有超大的比表面积,同时具备沸石的亲水性和活性炭的疏水特性,对空气中的极性污染物和疏水性的VOCs等物质具有良好的特异吸附性,在太阳光照下,上述被吸附的污染物可被WO3/TiO2催化剂降解去除。本发明产品可以用在外墙涂料技术领域,在雨水冲洗后保持自净,从而实现对污染空气的持续高效净化。Principle: Coal gangue, asphalt powder and tourmaline are used as raw materials to prepare activated carbon-zeolite composites with permanent negative charges, which are used as the carrier of WO 3 /TiO 2 catalysts to synthesize adsorption visible light catalytic composite materials. In this composite material, tourmaline naturally has a permanent negative charge, which can continuously and efficiently absorb positively charged PM2.5 in the air. The activated carbon-zeolite composite produced by coal gangue has a large specific surface area and has the hydrophilicity of zeolite. And the hydrophobic characteristics of activated carbon, it has good specific adsorption for polar pollutants and hydrophobic VOCs in the air. Under sunlight, the above-mentioned adsorbed pollutants can be degraded and removed by WO 3 /TiO 2 catalyst. The product of the invention can be used in the technical field of exterior wall coatings, and can maintain self-cleaning after being washed by rainwater, so as to realize continuous and efficient purification of polluted air.

与已有的技术相比,本发明具有以下优点:Compared with the prior art, the present invention has the following advantages:

1.在吸附光催化材料的制备中,沥青粉的加入不仅可以作为粘结剂提高复合材料的机械强度,而且还可以起到补炭的作用,进而调节复合材料中活性炭/沸石的比例,所制备的复合材料同时具备沸石的亲水性和活性炭的疏水性,具有超大的比表面积和微孔吸附孔道,可实现对空气中污染物的高效吸附。1. In the preparation of adsorbed photocatalytic materials, the addition of asphalt powder can not only serve as a binder to improve the mechanical strength of the composite material, but also play a role in carbon supplementation, thereby adjusting the ratio of activated carbon/zeolite in the composite material. The prepared composite material has both the hydrophilicity of zeolite and the hydrophobicity of activated carbon, and has a large specific surface area and microporous adsorption channels, which can achieve efficient adsorption of pollutants in the air.

2.在吸附光催化材料中添加电气石,其表面的自然永久性负电荷与PM2.5的正电荷相互匹配,使其具有吸附PM2.5的独特功能。2. Adding tourmaline to the adsorption photocatalytic material, the natural permanent negative charge on its surface matches the positive charge of PM2.5, making it have the unique function of adsorbing PM2.5.

3.WO3/TiO2光催化剂具有良好的可见光催化性能,能充分利用太阳光能源,实现对吸附的空气污染物彻底降解去除。3. WO 3 /TiO 2 photocatalyst has good visible light catalytic performance, can make full use of sunlight energy, and realize the complete degradation and removal of adsorbed air pollutants.

4.该吸附光催化材料以廉价的煤矸石为主要原料,成本低,经济可行,在应用中通过雨水作用实现自净,无需另行维护。4. The adsorption photocatalytic material uses cheap coal gangue as the main raw material, which is low in cost and economically feasible, and realizes self-purification through the action of rainwater in application without additional maintenance.

具体实施方式detailed description

以下实施例将对本发明作进一步说明。The following examples will further illustrate the present invention.

实施例1Example 1

(1)将粒度为200目的煤矸石、电气石和沥青粉,按煤矸石:电气石:沥青粉=0.8:0.05:0.15的重量比进行配比,并充分混合,制得物料A。(1) Proportion coal gangue, tourmaline and asphalt powder with a particle size of 200 meshes according to the weight ratio of coal gangue: tourmaline: asphalt powder = 0.8:0.05:0.15, and fully mix them to obtain material A.

(2)在室温下,将钛酸四正丁酯与无水乙醇按体积比1:1混合,搅拌0.5h,得到均匀透明的黄色溶液B。(2) At room temperature, mix tetra-n-butyl titanate and absolute ethanol at a volume ratio of 1:1, and stir for 0.5 h to obtain a uniform and transparent yellow solution B.

(3)将物料A和黄色溶液B按质量体积比1:3的比例混合,陈化24h,在流速为200mL/min的二氧化碳气体条件下,升温至650℃炭化6h,冷却至室温后,制得物料C。(3) Mix the material A and the yellow solution B at a mass volume ratio of 1:3, age for 24 hours, heat up to 650°C for carbonization for 6 hours under the condition of carbon dioxide gas with a flow rate of 200mL/min, and cool to room temperature to prepare Get material C.

(4)将物料C和钨酸钠水溶液按照质量体积比(w/v)10%充分混合(物料C和钨酸钠的重量比为0.95:0.05),超声振荡4h,然后洗涤干燥,氮气气氛400℃下活化2h,冷却室温后粉碎至150目以下,即制得成品。(4) Mix material C and sodium tungstate aqueous solution according to the mass volume ratio (w/v) of 10% (the weight ratio of material C and sodium tungstate is 0.95:0.05), ultrasonically oscillate for 4 hours, then wash and dry, nitrogen atmosphere Activation at 400°C for 2 hours, cooling to room temperature and crushing to below 150 mesh to obtain the finished product.

采用《GBT23761-2009光催化空气净化材料性能测试方法》进行制备材料对空气净化能力测试,实验将0.5g上述制备的吸附可见光催化材料涂布在200mm×100mm片状玻璃片上,在甲苯初始浓度为6mg/L时,可见光光照8h,去除率达到96%,处理效果良好。The "GBT23761-2009 Photocatalytic Air Purification Material Performance Test Method" was used to test the air purification ability of the prepared material. In the experiment, 0.5g of the above-mentioned adsorbed visible light catalytic material prepared above was coated on a 200mm×100mm flake glass. The initial concentration of toluene was At 6mg/L, visible light irradiation for 8 hours, the removal rate reached 96%, and the treatment effect was good.

实施例2Example 2

(1)将粒度为200目的煤矸石、电气石和沥青粉,按煤矸石:电气石:沥青粉=0.85:0.03:0.12的重量比进行配比,并充分混合,制得物料A。(1) Proportion coal gangue, tourmaline and asphalt powder with a particle size of 200 meshes according to the weight ratio of gangue: tourmaline: asphalt powder = 0.85:0.03:0.12, and fully mix them to obtain material A.

(2)在室温下,将钛酸四正丁酯与无水乙醇按体积比1:1混合,搅拌0.5h,得到均匀透明的黄色溶液B。(2) At room temperature, mix tetra-n-butyl titanate and absolute ethanol at a volume ratio of 1:1, and stir for 0.5 h to obtain a uniform and transparent yellow solution B.

(3)将物料A和黄色溶液B按质量体积比1:3的比例混合,陈化12h,在流速为200mL/min的二氧化碳气体条件下,升温至550℃炭化6h,冷却至室温后,制得物料C。(3) Mix material A and yellow solution B at a mass volume ratio of 1:3, age for 12 hours, raise the temperature to 550°C for carbonization for 6 hours under the condition of carbon dioxide gas with a flow rate of 200mL/min, and cool to room temperature to prepare Get material C.

(4)将物料C和钨酸钠水溶液按照质量体积比(w/v)10%充分混合(物料C和钨酸钠的重量比为0.93:0.07),超声振荡4h,然后洗涤干燥,氮气气氛500℃下活化2h,冷却室温后粉碎至150目以下,即制得成品。(4) Fully mix material C and sodium tungstate aqueous solution according to the mass volume ratio (w/v) of 10% (the weight ratio of material C and sodium tungstate is 0.93:0.07), ultrasonically oscillate for 4 hours, then wash and dry, nitrogen atmosphere Activation at 500°C for 2 hours, cooling to room temperature and crushing to below 150 mesh to obtain the finished product.

采用《GBT23761-2009光催化空气净化材料性能测试方法》进行制备材料对空气净化能力测试,实验将0.5g上述制备的吸附可见光催化材料涂布在200mm×100mm片状玻璃片上,在甲醛初始浓度为10mg/L时,可见光光照11h,去除率达到94%,处理效果良好。The "GBT23761-2009 Photocatalytic Air Purification Material Performance Test Method" was used to test the air purification ability of the prepared material. In the experiment, 0.5g of the above-mentioned adsorbed visible light catalytic material was coated on a 200mm×100mm flake glass. The initial concentration of formaldehyde was When the concentration is 10mg/L, visible light is irradiated for 11 hours, and the removal rate reaches 94%, and the treatment effect is good.

实施例3Example 3

(1)将粒度为200目的煤矸石、电气石和沥青粉,按煤矸石:电气石:沥青粉=0.7:0.08:0.22的重量比进行配比,并充分混合,制得物料A。(1) Proportion coal gangue, tourmaline and asphalt powder with a particle size of 200 meshes according to the weight ratio of coal gangue: tourmaline: asphalt powder = 0.7:0.08:0.22, and fully mix them to obtain material A.

(2)在室温下,将钛酸四正丁酯与无水乙醇按体积比1:1混合,搅拌0.5h,得到均匀透明的黄色溶液B。(2) At room temperature, mix tetra-n-butyl titanate and absolute ethanol at a volume ratio of 1:1, and stir for 0.5 h to obtain a uniform and transparent yellow solution B.

(3)将物料A和黄色溶液B按质量体积比1:4的比例混合,陈化24h,在流速为200mL/min的二氧化碳气体条件下,升温至600℃炭化8h,冷却至室温后,制得物料C。(3) Mix the material A and the yellow solution B at a mass volume ratio of 1:4, age for 24 hours, heat up to 600°C for carbonization for 8 hours under the condition of carbon dioxide gas with a flow rate of 200mL/min, and cool to room temperature to prepare Get material C.

(4)将物料C和钨酸钠水溶液按照质量体积比(w/v)10%充分混合(物料C和钨酸钠的重量比为0.95:0.05),超声振荡4h,然后洗涤干燥,氮气气氛500℃下活化2h,冷却室温后粉碎至150目以下,即制得成品。(4) Fully mix material C and sodium tungstate aqueous solution according to the mass volume ratio (w/v) of 10% (the weight ratio of material C and sodium tungstate is 0.95:0.05), ultrasonically oscillate for 4 hours, then wash and dry, nitrogen atmosphere Activation at 500°C for 2 hours, cooling to room temperature and crushing to below 150 mesh to obtain the finished product.

采用PM2.5实验舱、PM2.5检测仪,检验待测产品能对PM2.5的吸附和光催化去除性能,实验将0.5g上述制备的吸附可见光催化材料涂布在200mm×100mm片状玻璃片上,在PM2.5浓度为73ug/m3,吸附时间为30min时,产品对PM2.5的吸附率达54%以上,在可见光光照条件下,PM2.5中的有机物污染可被彻底降解去除。Use the PM2.5 experimental cabin and PM2.5 detector to test the adsorption and photocatalytic removal performance of the product to be tested on PM2.5. In the experiment, 0.5g of the adsorption visible light catalytic material prepared above is coated on a 200mm×100mm flake glass. , when the PM2.5 concentration is 73ug/m 3 and the adsorption time is 30min, the adsorption rate of the product to PM2.5 is over 54%. Under the condition of visible light, the organic pollution in PM2.5 can be completely degraded and removed.

Claims (1)

1.一种用于空气污染治理的吸附-可见光催化材料的制备方法,其特征在于所述吸附可见光催化材料为负载有WO3/TiO2的活性炭-沸石材料,具体步骤如下:1. A method for preparing an adsorption-visible light catalytic material for air pollution control, characterized in that said adsorption visible light catalytic material is loaded with WO 3 /TiO 2 activated carbon-zeolite material, the specific steps are as follows: (1)将粒度为200目以下煤矸石、电气石和沥青粉,按煤矸石:电气石:沥青粉为(0.5~0.9):(0.05~0.15):(0.1~0.3)的重量比进行配比,并充分混合,制得物料A;(1) Mix coal gangue, tourmaline and asphalt powder with a particle size below 200 meshes according to the weight ratio of coal gangue: tourmaline: asphalt powder (0.5~0.9): (0.05~0.15): (0.1~0.3) , and fully mixed to obtain material A; (2)在室温下,将钛酸四正丁酯与无水乙醇按1:1的体积比混合,搅拌0.5~2h,得到均匀透明的黄色溶液B;(2) At room temperature, mix tetra-n-butyl titanate and absolute ethanol at a volume ratio of 1:1, and stir for 0.5~2 hours to obtain a uniform and transparent yellow solution B; (3)将步骤(1)得到的物料A和步骤(2)得到的黄色溶液B按质量体积比1:1~5的比例混合,陈化24~48h,在流速为200mL/min的二氧化碳气体条件下,升温至500~800℃炭化6~12h,冷却至室温后,制得物料C;(3) Mix the material A obtained in step (1) and the yellow solution B obtained in step (2) according to the mass volume ratio of 1:1~5, age for 24~48h, in the carbon dioxide gas with a flow rate of 200mL/min Under the same conditions, the temperature was raised to 500~800°C for 6~12 hours of carbonization, and after cooling to room temperature, material C was obtained; (4)将步骤(3)得到的物料C和钨酸钠水溶液按照质量体积比(w/v)10%充分混合,超声振荡4~8h,然后洗涤干燥,氮气气氛400~550℃下活化2~4h,冷却室温后粉碎至150目以下,即制得成品;所述的物料C和钨酸钠的重量比为(0.8~0.95):(0.05~0.2)。(4) Mix the material C obtained in step (3) and sodium tungstate aqueous solution according to the mass volume ratio (w/v) of 10%, ultrasonically oscillate for 4~8h, then wash and dry, and activate at 400~550°C in a nitrogen atmosphere for 2 ~4h, after cooling at room temperature, pulverize to below 150 mesh to obtain the finished product; the weight ratio of the material C to sodium tungstate is (0.8~0.95): (0.05~0.2).
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