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CN107096380B - Method and device for treating formaldehyde in air by catalytic oxidation - Google Patents

Method and device for treating formaldehyde in air by catalytic oxidation Download PDF

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CN107096380B
CN107096380B CN201710398616.2A CN201710398616A CN107096380B CN 107096380 B CN107096380 B CN 107096380B CN 201710398616 A CN201710398616 A CN 201710398616A CN 107096380 B CN107096380 B CN 107096380B
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formaldehyde
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based catalyst
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CN107096380A (en
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余皓
王坤
彭峰
王红娟
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South China University of Technology SCUT
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86Catalytic processes
    • B01D53/8668Removing organic compounds not provided for in B01D53/8603 - B01D53/8665
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86Catalytic processes
    • B01D53/8696Controlling the catalytic process
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/70Non-metallic catalysts, additives or dopants
    • B01D2255/702Carbon
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2259/00Type of treatment
    • B01D2259/45Gas separation or purification devices adapted for specific applications
    • B01D2259/4508Gas separation or purification devices adapted for specific applications for cleaning air in buildings
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2259/00Type of treatment
    • B01D2259/65Employing advanced heat integration, e.g. Pinch technology
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters

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Abstract

The invention discloses a catalystA method and a device for treating formaldehyde in air by chemical oxidation. The method uses the integral carbon material as a carrier of the formaldehyde oxidation catalyst, and uses the excellent Joule thermal property, mechanical property and electrothermal conversion efficiency of the catalyst, and uses the catalyst as a pure resistance heating element to directly heat the catalyst in an electrothermal mode, so that unnecessary energy consumption is not caused by using other heating elements in the reactor. The method combines Ag/Co 3 O 4 The catalyst is loaded on an integral porous carbon material, then the integral carbon-based catalyst is placed in a reactor, and both ends of the catalyst are connected with metal electrodes and applied with voltage, so that the temperature of the catalyst is raised to 20-300 ℃; when the air containing 10-500ppm formaldehyde is used in 15000-90000ml h ‑1 g ‑1 The conversion rate of formaldehyde can reach more than 95% when the space velocity of the catalyst flows through the reactor. The method has the advantages of good formaldehyde catalytic oxidation effect, high energy utilization efficiency, small pressure drop of the reactor and simple and convenient operation.

Description

一种催化氧化处理空气中甲醛的方法与装置Method and device for catalytic oxidation treatment of formaldehyde in air

技术领域technical field

本发明属于环保节能领域,具体涉及一种催化氧化处理空气中甲醛的方法与装置。The invention belongs to the field of environmental protection and energy saving, and in particular relates to a method and a device for catalytic oxidation treatment of formaldehyde in air.

背景技术Background technique

室内有害挥发性有机物(Volatile Organic Compounds,VOC)指的是挥发性的碳氢化合物及其衍生物。甲醛是VOC中最具代表性的污染物,主要来源是现在化学工业带来的各种胶类物质和各种粘合剂,长期生活在含有甲醛的环境中对人的眼睛、心脑血管、呼吸系统以及神经系统产生极大的危害。甲醛以其来源广泛、危害性大、持续时间长等特点,已成为我国普遍存在且较为严重的室内污染物之一,治理甲醛迫在眉睫。目前常用的甲醛处理方法主要有吸附法,生物法,催化氧化法,热氧化法,等离子法等。对于像甲醛这种不须回收的VOC,热氧化法与催化氧化法是较为彻底的处理方法。其中,甲醛的催化氧化法是成本最低、最容易实现广泛使用的方法,在工业上甲醛处理方面具有较好的应用前景。Indoor harmful volatile organic compounds (Volatile Organic Compounds, VOC) refer to volatile hydrocarbons and their derivatives. Formaldehyde is the most representative pollutant in VOC. The main source is various glues and various adhesives brought by the chemical industry. Living in an environment containing formaldehyde for a long time is harmful to human eyes, cardiovascular and cerebrovascular, Very harmful to the respiratory system and nervous system. Formaldehyde has become one of the ubiquitous and serious indoor pollutants in my country due to its wide sources, great harm and long duration, and it is imminent to control formaldehyde. At present, the commonly used formaldehyde treatment methods mainly include adsorption method, biological method, catalytic oxidation method, thermal oxidation method, plasma method and so on. For VOCs that do not need to be recovered, such as formaldehyde, thermal oxidation and catalytic oxidation are more thorough treatment methods. Among them, the catalytic oxidation of formaldehyde is the method with the lowest cost and the easiest way to be widely used, and has a good application prospect in industrial formaldehyde treatment.

我国规定居室空气中甲醛的最高容许浓度为0.08mg/m3。为保证在低浓度的甲醛环境下同样具有高转化率,对催化剂的活性有较高的要求。处理甲醛的催化剂可以大致分为两类:一类是贵金属催化剂,如Pt、Au、Pd、Rh等;一类是过渡金属氧化物,如MnO2、CeO2、Co3O4等。根据近年文献报道,具有复合活性组分的催化剂—如贵金属和过渡金属氧化物结合、多种过渡金属复合等可提高催化活性。Wu Jiang(Environ.Sci.Technol.2016,50,5370-5378)等人的研究以及Tan Hongyi(Environ.Sci.Technol.2015,49,8675-8682)等人的研究都证实这一观点。专利CN104353465提出了一种Co3O4/CeO2核壳结构的催化剂,其在室温下就对甲醛有良好的催化氧化活性。专利CN105013491报道了一种以镍盐、钴盐、表面活性剂为原料制备得到的NiCo2O4纳米片状催化剂,具有高效低成本等优点。专利CN104722299采用了CeO2纳米立方块为载体,负载纳米金属Pd颗粒作为活性组分,可以将大部分或者全部甲醛在室温条件下转化为二氧化碳和水,没有甲酸、一氧化碳等副产物。China stipulates that the maximum allowable concentration of formaldehyde in indoor air is 0.08mg/m 3 . In order to ensure a high conversion rate even in a low-concentration formaldehyde environment, higher requirements are placed on the activity of the catalyst. Catalysts for treating formaldehyde can be roughly divided into two categories: one is noble metal catalysts, such as Pt, Au, Pd, Rh, etc.; the other is transition metal oxides, such as MnO 2 , CeO 2 , Co 3 O 4 , etc. According to recent literature reports, catalysts with complex active components—such as the combination of noble metals and transition metal oxides, the combination of multiple transition metals, etc., can improve catalytic activity. The studies of Wu Jiang (Environ.Sci.Technol.2016, 50, 5370-5378) et al. and Tan Hongyi (Environ.Sci.Technol.2015, 49, 8675-8682) et al. have confirmed this point of view. Patent CN104353465 proposes a catalyst with a core-shell structure of Co 3 O 4 /CeO 2 , which has good catalytic oxidation activity for formaldehyde at room temperature. Patent CN105013491 reports a NiCo 2 O 4 nanosheet catalyst prepared from nickel salt, cobalt salt, and surfactant, which has the advantages of high efficiency and low cost. Patent CN104722299 uses CeO 2 nano cubes as the carrier, loaded with nano metal Pd particles as the active component, which can convert most or all formaldehyde into carbon dioxide and water at room temperature, without formic acid, carbon monoxide and other by-products.

在实际应用中,多数气固相反应装置需要加热元件的引入来对反应体系进行加热使其达到反应所需温度。本发明以电能作为能量输入方式,利用整体型碳材料的焦耳热性质加热催化剂。负载有活性组分的整体型催化剂在反应装置体系中,其自身作为一个纯电阻加热元件,将直流稳压电源通过两端对其输入的电能高效转化为热能,使整体型催化剂自身局部达到反应所需温度。在实现能量高效利用的同时,避免了向体系中引入额外的加热元件所造成的不必要的能量消耗。In practical applications, most gas-solid phase reaction devices require the introduction of heating elements to heat the reaction system to reach the required temperature for the reaction. The invention uses electric energy as the energy input mode, and utilizes the Joule heat property of the monolithic carbon material to heat the catalyst. In the reaction device system, the monolithic catalyst loaded with active components acts as a pure resistance heating element, which efficiently converts the electric energy input by the DC stabilized power supply through both ends into heat energy, so that the monolithic catalyst itself can achieve partial reaction. desired temperature. While achieving efficient energy utilization, unnecessary energy consumption caused by introducing additional heating elements into the system is avoided.

发明内容Contents of the invention

为了克服现有技术的不足,本发明的目的在于提供一种催化氧化处理空气中甲醛的方法与装置,可用于高效低能耗地清除室内空气或工厂尾气中的甲醛。In order to overcome the deficiencies of the prior art, the object of the present invention is to provide a method and device for catalytic oxidation treatment of formaldehyde in the air, which can be used to remove formaldehyde in indoor air or factory exhaust with high efficiency and low energy consumption.

本发明采用以下的技术方案。The present invention adopts the following technical solutions.

一种催化氧化处理空气中甲醛的方法,包括以下步骤:A method for catalytic oxidation treatment of formaldehyde in air, comprising the following steps:

将负载有活性组分的整体型碳基催化剂置于反应器内,所述整体型碳基催化剂两端用金属电极夹紧,并用导线与电源正负极相连,然后对所述整体型碳基催化剂输入电能,利用整体型碳基催化剂的焦耳热性质使整体型碳基催化剂达到所需反应温度;再向反应器内通入含有甲醛的空气,甲醛在通过被加热的整体型碳基催化剂的过程中发生催化氧化反应。The monolithic carbon-based catalyst loaded with active components is placed in the reactor, the two ends of the monolithic carbon-based catalyst are clamped by metal electrodes, and the positive and negative electrodes of the power supply are connected with wires, and then the monolithic carbon-based catalyst is The catalyst inputs electric energy, using the Joule heat property of the monolithic carbon-based catalyst to make the monolithic carbon-based catalyst reach the required reaction temperature; A catalytic oxidation reaction takes place.

优选的,所述的整体型碳基催化剂的载体(即整体型碳材料)为整体型介孔碳材料,整体型三维石墨烯、整体型碳基泡沫材料等整体型碳材料。Preferably, the carrier of the monolithic carbon-based catalyst (ie monolithic carbon material) is monolithic mesoporous carbon material, monolithic three-dimensional graphene, monolithic carbon-based foam material and other monolithic carbon materials.

进一步优选的,整体型介孔碳材料的制备方法为:将3.0g间苯二酚和1.25g F127混合,加入9ml水和11.4ml无水乙醇,搅拌溶解后加入0.078g 1,6-己二胺,继续搅拌30min后加入4.45g甲醛溶液(37%)至溶液呈乳白色,倒入模具中放入90℃烘箱中固化4h后取出干燥,在Ar气氛下以5℃/min的速率升温至800℃保持2h制得整体型介孔碳材料。Further preferably, the preparation method of the monolithic mesoporous carbon material is: mix 3.0g resorcinol and 1.25g F127, add 9ml water and 11.4ml absolute ethanol, stir and dissolve, add 0.078g 1,6-hexanedi Amine, continue to stir for 30 minutes, add 4.45g formaldehyde solution (37%) until the solution is milky white, pour it into a mold and put it in a 90°C oven to cure for 4h, take it out and dry it, and heat it up to 800°C at a rate of 5°C/min under Ar atmosphere ℃ for 2h to prepare monolithic mesoporous carbon materials.

进一步优选的,整体型三维石墨烯的制备方法为:将Hummers法制得的10mg/ml的氧化石墨烯溶液与5wt%的聚乙烯醇、蔗糖超声混合得到均匀的悬浊液,再与甲苯1:1混合形成稳定的乳浊液。将乳浊液倒入模具中在-70℃下冷冻后用冻干机干燥,之后在将95%Ar/5%H2气氛下900℃保持2h热还原得到整体型三维石墨烯。Further preferably, the preparation method of monolithic three-dimensional graphene is: the 10mg/ml graphene oxide solution that Hummers method is made is mixed with the polyvinyl alcohol of 5wt%, sucrose ultrasonically to obtain uniform suspension, then with toluene 1: 1 Mix to form a stable emulsion. Pour the emulsion into a mold, freeze it at -70°C and dry it with a lyophilizer, then keep it at 900°C for 2 hours under the atmosphere of 95% Ar/5% H 2 for thermal reduction to obtain monolithic three-dimensional graphene.

进一步优选的,整体型碳基泡沫材料的制备方法为:将剪裁成规整形状的三聚氰胺泡沫材料直接在Ar气氛下800℃保持2h碳化制得整体型碳基泡沫材料。Further preferably, the preparation method of the integral carbon-based foam material is as follows: the melamine foam material cut into a regular shape is directly carbonized at 800° C. for 2 hours under an Ar atmosphere to obtain the integral carbon-based foam material.

优选的,所述的活性组分为Ag和Co中的一种或两种。Preferably, the active component is one or both of Ag and Co.

优选的,所述整体型碳基催化剂的制备包括以下步骤:将所述的整体型碳基催化剂的载体置于含有Ag+和Co2+的浸渍液中浸渍1-20h,取出真空干燥后,在惰性气氛中300-800℃下保持1-8h,得整体型碳基催化剂。Preferably, the preparation of the monolithic carbon-based catalyst comprises the following steps: placing the carrier of the monolithic carbon-based catalyst in an impregnating solution containing Ag + and Co 2+ for 1-20 h, taking it out and drying it in vacuum, Keeping at 300-800° C. for 1-8 hours in an inert atmosphere to obtain a monolithic carbon-based catalyst.

进一步优选的,所述浸渍液为银盐和钴盐的水溶液,所述的钴盐为硝酸钴、氯化钴和硫酸钴中的一种以上;所述的银盐为硝酸银。Further preferably, the impregnation solution is an aqueous solution of silver salt and cobalt salt, and the cobalt salt is at least one of cobalt nitrate, cobalt chloride and cobalt sulfate; the silver salt is silver nitrate.

进一步优选的,所述浸渍液中Ag+的浓度为0~10wt%,Co2+的浓度为0~10wt%;所述整体型碳基催化剂的载体与浸渍液的质量比为1:(10~200)。Further preferably, the concentration of Ag + in the impregnating solution is 0-10wt%, and the concentration of Co2 + is 0-10wt%; the mass ratio of the carrier of the monolithic carbon-based catalyst to the impregnating solution is 1:(10 ~200).

优选的,所述金属电极为泡沫铜、泡沫镍、铜片等金属片状电极。Preferably, the metal electrode is a metal sheet electrode such as copper foam, nickel foam, or copper sheet.

优选的,所述输入电能时输入电压为0-10V,整体型碳基催化剂的核心温度为20-300℃。Preferably, when the electric energy is input, the input voltage is 0-10V, and the core temperature of the monolithic carbon-based catalyst is 20-300°C.

优选的,所述空气中甲醛的含量为10-500ppm,气体流速为50-300Ncm3/min,空速为15000-90000ml h-1g-1Preferably, the formaldehyde content in the air is 10-500ppm, the gas flow rate is 50-300Ncm 3 /min, and the space velocity is 15000-90000ml h -1 g -1 .

实现以上所述的一种催化氧化处理空气中甲醛的方法的装置,该装置包括整体型碳基催化剂、金属电极、反应管、电源、温度显示器、热电偶、导线、进气管、出气管和密封卡套;所述整体型碳基催化剂置于反应管内,金属电极夹在整体型碳基催化剂两端,金属电极两端通过导线与电源正负极连接;热电偶测量端插入整体型碳基催化剂中心位置,热电偶的另一端与温度显示器连接;反应管的一端与进气管连接,另一端与出气管连接;反应管、进气管和出气管通过密封卡套固定。A device for realizing the method for catalytic oxidation treatment of formaldehyde in air as described above, the device includes an integral carbon-based catalyst, a metal electrode, a reaction tube, a power supply, a temperature display, a thermocouple, a wire, an air inlet pipe, an air outlet pipe and a sealing ferrule; the integral carbon-based catalyst is placed in the reaction tube, the metal electrode is clamped at both ends of the integral carbon-based catalyst, and the two ends of the metal electrode are connected to the positive and negative electrodes of the power supply through wires; the thermocouple measurement end is inserted into the integral carbon-based catalyst At the center position, the other end of the thermocouple is connected to the temperature display; one end of the reaction tube is connected to the inlet tube, and the other end is connected to the outlet tube; the reaction tube, the inlet tube and the outlet tube are fixed by a sealed ferrule.

优选的,所述反应器为圆柱形玻璃反应管。Preferably, the reactor is a cylindrical glass reaction tube.

本发明与现有技术相比,具有如下优点:Compared with the prior art, the present invention has the following advantages:

(1)本发明的整体型碳材料作为催化剂的载体,不仅可通过模具的尺寸大小来调控整体型催化剂的尺寸大小,且制得的催化剂力学强度好,比表面积高,气体透过性好,床层压降低,有利于活性组分的负载及活性组分与反应物之间的接触。(1) As the carrier of the catalyst, the monolithic carbon material of the present invention can not only regulate the size of the monolithic catalyst through the size of the mold, but also the prepared catalyst has good mechanical strength, high specific surface area, and good gas permeability. The bed pressure is reduced, which is beneficial to the loading of the active components and the contact between the active components and the reactants.

(2)本发明采用了一种基于整体型碳材料焦耳热性质的能量输入方式,区别于传统固定床反应器对整个反应器加热使催化剂达到预设反应温度的方式,本发明利用整体型碳材料的焦耳热性质,其自身作为一个纯电阻加热元件,将输入的电能高效转化为热能,使催化剂自身被加热达到反应所需温度,而无需对不参与反应的反应器其他部分加热,实现了能量的高效利用。(2) The present invention adopts an energy input method based on the Joule heat property of the monolithic carbon material, which is different from the way in which the traditional fixed bed reactor heats the entire reactor to make the catalyst reach the preset reaction temperature. The Joule heat property of the material, as a pure resistance heating element, converts the input electric energy into heat energy efficiently, so that the catalyst itself is heated to the temperature required for the reaction without heating other parts of the reactor that do not participate in the reaction, realizing Efficient use of energy.

附图说明Description of drawings

图1为实施例12中整体型介孔碳催化剂的SEM图像。FIG. 1 is an SEM image of the monolithic mesoporous carbon catalyst in Example 12.

图2为实施例12中整体型介孔碳催化剂的TEM图像。FIG. 2 is a TEM image of the monolithic mesoporous carbon catalyst in Example 12.

图3为实施例12中整体型介孔碳催化剂的X射线衍射图。3 is an X-ray diffraction pattern of the monolithic mesoporous carbon catalyst in Example 12.

图4a为实施例9-14中不同负载量的整体型介孔碳催化剂的甲醛转化率与核心温度的对应关系曲线图。Fig. 4a is a graph showing the relationship between formaldehyde conversion and core temperature of monolithic mesoporous carbon catalysts with different loads in Examples 9-14.

图4b为实施例9-14中不同负载量的整体型介孔碳催化剂的甲醛转化率与输入功率密度的对应关系曲线图。Fig. 4b is a graph showing the relationship between formaldehyde conversion and input power density of monolithic mesoporous carbon catalysts with different loads in Examples 9-14.

图5为本发明催化氧化处理空气中甲醛的装置示意图。Fig. 5 is a schematic diagram of a device for catalytic oxidation treatment of formaldehyde in air according to the present invention.

图6为实施例12中整体型介孔碳催化剂的实物图。FIG. 6 is a physical diagram of the monolithic mesoporous carbon catalyst in Example 12.

具体实施方式Detailed ways

以下结合附图和实施例对本发明的具体实施作进一步的说明,但本发明不局限于以下实施例。The specific implementation of the present invention will be further described below in conjunction with the accompanying drawings and examples, but the present invention is not limited to the following examples.

下列实施例中的甲醛转化率是通过酚试剂分光光度法(国家标准号GB/T18204.2-2014)分析测得。The formaldehyde conversion rate in the following examples is measured by phenol reagent spectrophotometry (National Standard No. GB/T18204.2-2014).

整体型介孔碳材料的制备方法:将3.0g间苯二酚和1.25g F127(泊洛沙姆)混合,加入9ml去离子水和11.4ml无水乙醇,搅拌溶解后加入0.078g 1,6-己二胺,继续搅拌30min后加入4.45g甲醛溶液(浓度为37wt%)至溶液呈乳白色,倒入模具中放入90℃烘箱中固化4h后取出干燥,在Ar气氛下以5℃/min的速率升温至800℃保持2h制得整体型介孔碳材料。The preparation method of monolithic mesoporous carbon material: mix 3.0g resorcinol and 1.25g F127 (poloxamer), add 9ml deionized water and 11.4ml absolute ethanol, stir to dissolve and add 0.078g 1,6 - Hexamethylenediamine, after continuing to stir for 30min, add 4.45g formaldehyde solution (concentration is 37wt%) until the solution is milky white, pour it into a mold and put it in a 90°C oven to solidify for 4h, then take it out and dry it. The temperature was raised to 800°C for 2 hours to obtain monolithic mesoporous carbon materials.

整体型三维石墨烯的制备方法:将Hummers法制得的10mg/ml氧化石墨烯溶液5ml与2.5mg聚乙烯醇、2.5mg蔗糖超声混合得到均匀的悬浊液,再与甲苯以体积比为1:1混合形成稳定的乳浊液。将乳浊液倒入模具中在-70℃下冷冻后用冻干机干燥,之后在95vol%Ar/5vol%H2气氛下900℃保持2h热还原得到整体型三维石墨烯。The preparation method of monolithic three-dimensional graphene: 5ml of 10mg/ml graphene oxide solution prepared by Hummers method is mixed with 2.5mg polyvinyl alcohol and 2.5mg sucrose ultrasonically to obtain a uniform suspension, and then with toluene in a volume ratio of 1: 1 Mix to form a stable emulsion. Pour the emulsion into a mold, freeze it at -70°C and dry it with a lyophilizer, then keep it at 900°C for 2 hours under an atmosphere of 95vol%Ar/5vol% H2 for thermal reduction to obtain monolithic three-dimensional graphene.

整体型碳基泡沫材料的制备方法:将剪裁成规整形状的三聚氰胺泡沫材料直接在Ar气氛下800℃保持2h碳化制得整体型碳基泡沫材料。The preparation method of the integral carbon-based foam material: the melamine foam material cut into a regular shape is directly carbonized at 800° C. for 2 hours under an Ar atmosphere to obtain the integral carbon-based foam material.

以下实施例中的反应装置使用本发明催化氧化处理空气中甲醛的装置,示意图如图5所示。该装置包括整体型碳基催化剂1、金属电极2、反应管3、电源4、温度显示器5、热电偶6、导线7、进气管8、出气管9和密封卡套10;所述整体型碳基催化剂置于反应管内,金属电极夹在整体型碳基催化剂两端,金属电极两端通过导线与电源正负极连接;热电偶测量端插入整体型碳基催化剂中心位置,热电偶的另一端与温度显示器连接;反应管的一端与进气管连接,另一端与出气管连接;反应管、进气管和出气管通过密封卡套固定。The reaction device in the following examples uses the device for catalytic oxidation treatment of formaldehyde in air according to the present invention, and the schematic diagram is shown in FIG. 5 . The device includes an integral carbon-based catalyst 1, a metal electrode 2, a reaction tube 3, a power supply 4, a temperature display 5, a thermocouple 6, a wire 7, an air inlet pipe 8, an air outlet pipe 9 and a sealing ferrule 10; The base catalyst is placed in the reaction tube, and the metal electrodes are sandwiched between the two ends of the integral carbon-based catalyst. The two ends of the metal electrode are connected to the positive and negative electrodes of the power supply through wires; It is connected with the temperature display; one end of the reaction tube is connected with the inlet tube, and the other end is connected with the outlet tube; the reaction tube, the inlet tube and the outlet tube are fixed by a sealed ferrule.

该装置工作过程如下:将整体型碳基催化剂置于反应管内,所述整体型碳基催化剂两端用金属电极夹紧,并用导线使金属电极两端与电源正负极相连,用密封卡套将反应管、进气管、出气管固定,然后打开电源,对所述整体型碳基催化剂输入电能,利用整体型碳基催化剂的焦耳热性质使整体型碳基催化剂达到所需反应温度,当装置达到恒温稳态后,无需再调节电源电压,即可使催化氧化反应一直维持在特定温度下进行;整体型碳基催化剂的温度通过插入整体型碳基催化剂中心位置的热电偶测量,显示在温度显示器上,调节电源的电压可以调节碳基催化剂的温度;向进气管内通入含有甲醛的空气,甲醛在通过被加热的整体型碳基催化剂的过程中发生催化氧化反应,反应后的气体经出气管排出。The working process of the device is as follows: the integral carbon-based catalyst is placed in the reaction tube, the two ends of the integral carbon-based catalyst are clamped by metal electrodes, and the two ends of the metal electrodes are connected to the positive and negative electrodes of the power supply with wires, and the sealed ferrule Fix the reaction tube, inlet pipe, and outlet pipe, then turn on the power, input electric energy to the monolithic carbon-based catalyst, use the Joule heat property of the monolithic carbon-based catalyst to make the monolithic carbon-based catalyst reach the required reaction temperature, when the device After reaching a constant temperature and steady state, the catalytic oxidation reaction can be maintained at a specific temperature without adjusting the power supply voltage; the temperature of the monolithic carbon-based catalyst is measured by a thermocouple inserted into the center of the monolithic carbon-based catalyst, and displayed on the temperature On the display, adjusting the voltage of the power supply can adjust the temperature of the carbon-based catalyst; the air containing formaldehyde is introduced into the intake pipe, and the formaldehyde undergoes a catalytic oxidation reaction in the process of passing through the heated integral carbon-based catalyst, and the reacted gas passes through The outlet pipe is discharged.

实施例1-8Examples 1-8

将直径为15mm,厚度为10mm的整体型介孔碳材料置于盛有30ml AgNO3溶液的烧杯中,随后进行真空处理使孔道中的气体排出。整体型介孔碳材料与浸渍液的质量比为1:150,溶剂为去离子水,溶液中Ag+含量如表1所示,之后置于摇床中以200rpm的转速浸渍处理10h,取出真空干燥后,在Ar气氛下以5℃/min的速率升温至450℃保持5h制得整体型介孔碳催化剂。将所得整体型介孔碳催化剂放入直径为15mm的圆柱形玻璃反应管中,用泡沫铜圆片形电极压紧两端,并与直流稳压电源的正负极相连。整体型介孔碳催化剂核心位置温度为90℃,反应气为空气中含100ppm甲醛的混合气体,气体流速为100Ncm3/min,空速为30000ml h-1g-1,甲醛的转化率见表1。A monolithic mesoporous carbon material with a diameter of 15 mm and a thickness of 10 mm was placed in a beaker containing 30 ml of AgNO 3 solution, and then vacuum treatment was performed to discharge the gas in the channel. The mass ratio of the monolithic mesoporous carbon material to the impregnating solution is 1:150, the solvent is deionized water, the Ag + content in the solution is shown in Table 1, and then placed in a shaker at a speed of 200rpm for 10 hours, and the vacuum After drying, the temperature was raised to 450°C at a rate of 5°C/min and kept for 5h under an Ar atmosphere to prepare a monolithic mesoporous carbon catalyst. The obtained monolithic mesoporous carbon catalyst was put into a cylindrical glass reaction tube with a diameter of 15 mm, and the two ends were pressed tightly with foam copper disc electrodes, and connected to the positive and negative electrodes of a DC stabilized voltage power supply. The core position temperature of the monolithic mesoporous carbon catalyst is 90°C, the reaction gas is a mixed gas containing 100ppm formaldehyde in air, the gas flow rate is 100Ncm 3 /min, and the space velocity is 30000ml h -1 g -1 , the conversion rate of formaldehyde is shown in the table 1.

表1Table 1

Figure BDA0001309154790000051
Figure BDA0001309154790000051

从表1可知,甲醛转化率先随Ag+离子浓度和Ag负载量增大而上升,后趋于稳定无明显变化。当Ag+离子浓度为2.5wt%时,甲醛转化率最高。It can be seen from Table 1 that the formaldehyde conversion first increases with the increase of Ag + ion concentration and Ag loading, and then tends to be stable without significant change. When the concentration of Ag + ions was 2.5wt%, the conversion of formaldehyde was the highest.

实施例9-16Examples 9-16

将整体型介孔碳材料置于盛有30ml AgNO3/Co(NO3)2浸渍液的烧杯中,溶剂为去离子水,溶液中Ag+和Co2+的浓度与所得整体型介孔碳催化剂在90℃下甲醛的转化率如表2所示,其余条件与实施例1-8一致。Place the monolithic mesoporous carbon material in a beaker filled with 30ml AgNO 3 /Co(NO 3 ) 2 impregnating solution, the solvent is deionized water, the concentration of Ag + and Co 2+ in the solution is the same as the obtained monolithic mesoporous carbon The conversion rate of formaldehyde of the catalyst at 90° C. is shown in Table 2, and the other conditions are consistent with those in Examples 1-8.

表2Table 2

Figure BDA0001309154790000052
Figure BDA0001309154790000052

从表2可知,浸渍液中Co2+的引入使所制得的催化剂从单一的Ag活性组分变为Ag/Co3O4双组分催化剂,大大提高了甲醛的催化氧化活性。其中实施例12中的样品表现出了最优的活性,对其进一步的表征如图1-3所示。从图1整体型介孔碳催化剂的SEM图像可知其具有大孔蓬松结构,从图2中TEM图像可观察到介孔及催化剂颗粒的均匀分布。图3的XRD图像进一步说明了活性成分Ag和Co3O4的存在。图6为该整体型催化剂的实物图,可观察到其具有规整的宏观几何结构以及表面肉眼可见的孔道结构。规整的宏观几何结构为其提供了较好的力学性能,宏观孔道、大孔、介孔所构成的多级孔结构为该整体型催化剂提供了较大的比表面积(565m2/g)、较好的气体通过性以及较低的床层压降。实施例9-14中不同负载量的整体型介孔碳催化剂的甲醛转化率与核心温度、输入功率密度的对应关系曲线图分别如图4a、图4b所示。It can be seen from Table 2 that the introduction of Co 2+ in the impregnation solution changed the prepared catalyst from a single Ag active component to an Ag/Co 3 O 4 two-component catalyst, which greatly improved the catalytic oxidation activity of formaldehyde. The sample in Example 12 showed the best activity, and its further characterization is shown in Figures 1-3. From the SEM image of the monolithic mesoporous carbon catalyst in Figure 1, it can be seen that it has a macroporous fluffy structure, and from the TEM image in Figure 2, the uniform distribution of mesoporous and catalyst particles can be observed. The XRD images of Fig. 3 further illustrate the presence of active components Ag and Co3O4 . Fig. 6 is a physical picture of the monolithic catalyst, and it can be observed that it has a regular macroscopic geometric structure and a pore structure visible to the naked eye on the surface. The regular macroscopic geometric structure provides it with good mechanical properties, and the hierarchical pore structure composed of macroscopic channels, macropores and mesopores provides the monolithic catalyst with a large specific surface area (565m 2 /g), relatively Good gas permeability and low bed pressure drop. Figure 4a and Figure 4b show the corresponding relation curves of formaldehyde conversion rate, core temperature and input power density of monolithic mesoporous carbon catalysts with different loads in Examples 9-14.

实施例17,18Examples 17,18

将表3中三种不同碳载体的整体型介孔碳材料置于盛有30ml AgNO3/Co(NO3)2浸渍液的烧杯中,随后进行真空处理使孔道中的气体排出。整体型碳材料为圆柱形,直径为15mm,厚度为10mm,与浸渍液的质量比为1:150,浸渍液中Ag+浓度为1wt%,Co2+浓度为1wt%,之后分别置于摇床中以200rpm的转速浸渍处理10h,取出真空干燥后,在Ar气氛下以5℃/min的速率升温至450℃保持5h制得整体型碳基催化剂。将所得3种整体型碳基催化剂分别放入内径为15mm的圆柱形玻璃反应管中,用泡沫铜圆片形电极压紧两端,并与直流稳压电源的正负极相连。调节输入电功率使整体型催化剂核心位置温度为90℃,反应气为空气中含100ppm甲醛的混合气体,气体流速为100sccm,空速为30000ml h-1g-1。不同碳载体的整体型碳材料与对应的甲醛转化率如表3所示。The monolithic mesoporous carbon materials with three different carbon supports listed in Table 3 were placed in a beaker filled with 30ml AgNO 3 /Co(NO 3 ) 2 impregnation solution, and then vacuum treatment was performed to discharge the gas in the channels. The monolithic carbon material is cylindrical, with a diameter of 15 mm and a thickness of 10 mm. The mass ratio of the impregnated solution to the impregnated solution is 1:150. The Ag + concentration in the impregnated solution is 1wt%, and the Co2 + concentration is 1wt%. The bed was impregnated at a speed of 200 rpm for 10 h, taken out for vacuum drying, and then heated to 450 °C at a rate of 5 °C/min for 5 h under an Ar atmosphere to prepare a monolithic carbon-based catalyst. The obtained three monolithic carbon-based catalysts were put into cylindrical glass reaction tubes with an inner diameter of 15 mm, and the two ends were pressed tightly with foam copper disc electrodes, and connected to the positive and negative electrodes of a DC stabilized voltage power supply. Adjust the input electric power so that the core temperature of the integral catalyst is 90°C, the reaction gas is a mixed gas containing 100ppm formaldehyde in air, the gas flow rate is 100 sccm, and the space velocity is 30000ml h -1 g -1 . The monolithic carbon materials and corresponding formaldehyde conversion rates of different carbon supports are shown in Table 3.

表3table 3

Figure BDA0001309154790000061
Figure BDA0001309154790000061

实施例19-28Examples 19-28

将整体型介孔碳材料置于盛有AgNO3/Co(NO3)2浸渍液的烧杯中,随后进行真空处理使孔道中的气体排出。整体型介孔碳材料与浸渍液的质量比为1:10-200。浸渍液中Ag+浓度为1wt%,Co2+浓度为1wt%,之后置于摇床中以50-300rpm的转速浸渍处理1-20h,碳材料与浸渍液不同的质量比、浸渍时间、摇床转速与所制得的催化剂对应的甲醛转化率如表4所示,其余条件与实施例1一致。The monolithic mesoporous carbon material was placed in a beaker filled with AgNO 3 /Co(NO 3 ) 2 impregnation solution, and then vacuum treatment was performed to discharge the gas in the pores. The mass ratio of the monolithic mesoporous carbon material to the impregnating liquid is 1:10-200. The concentration of Ag + in the impregnation solution is 1wt%, and the concentration of Co 2+ is 1wt%. The bed rotation speed and the formaldehyde conversion rate corresponding to the prepared catalyst are shown in Table 4, and the rest of the conditions are consistent with Example 1.

表4Table 4

Figure BDA0001309154790000071
Figure BDA0001309154790000071

实施例29-33Examples 29-33

将整体型介孔碳材料浸渍处理,取出真空干燥后,在Ar气氛下以5℃/min的速率升温至300℃~800℃保持1~8h制得整体型介孔碳基催化剂。该催化剂不同的退火温度和时间与对应的甲醛转化率如表5所示,其他条件与实施例1一致。The monolithic mesoporous carbon material was impregnated, taken out and vacuum-dried, then heated to 300-800°C at a rate of 5°C/min under Ar atmosphere and kept for 1-8 hours to prepare the monolithic mesoporous carbon-based catalyst. The different annealing temperatures and times of the catalyst and the corresponding formaldehyde conversion are shown in Table 5, and other conditions are consistent with Example 1.

表5table 5

Figure BDA0001309154790000072
Figure BDA0001309154790000072

实施例34-40Examples 34-40

将实施例11中制得的整体型碳基催化剂放入直径为15mm的圆柱形玻璃反应管中,用金属圆片形电极压紧两端,并与电源的正负极相连,输入的电压为0-10V,整体型催化剂核心位置温度为20-300℃,反应气为空气中含100ppm甲醛的混合气体,气体流速为100Ncm3/min,空速为30000Ncm3h-1g-1。不同的金属电极、输入电压以及催化剂核心温度与对应的甲醛转化率如表6所示。Put the monolithic carbon-based catalyst prepared in Example 11 into a cylindrical glass reaction tube with a diameter of 15 mm, press the two ends with metal disc electrodes, and connect them to the positive and negative poles of the power supply. The input voltage is 0-10V, the core position temperature of the integral catalyst is 20-300°C, the reaction gas is a mixed gas containing 100ppm formaldehyde in the air, the gas flow rate is 100Ncm 3 /min, and the space velocity is 30000Ncm 3 h -1 g -1 . Table 6 shows the corresponding formaldehyde conversion rates for different metal electrodes, input voltages, and catalyst core temperatures.

表6Table 6

Figure BDA0001309154790000081
Figure BDA0001309154790000081

实施例41-47Examples 41-47

将实施例12中制得的整体型碳基催化剂放入直径为15mm的圆柱形玻璃反应管中,用泡沫铜圆片形电极压紧两端,并与电源的正负极相连,输入的电压为2.81V,整体型催化剂核心位置温度为90℃,反应气为空气中含10-500ppm甲醛的混合气体,气体流速为50-300Ncm3/min,空速为15-90L h-1g-1。混合气体中不同的甲醛浓度、气体流速以及空速与对应的甲醛转化率如表7所示。Put the monolithic carbon-based catalyst prepared in Example 12 into a cylindrical glass reaction tube with a diameter of 15 mm, press the two ends tightly with a foam copper disk electrode, and connect with the positive and negative poles of the power supply, and the input voltage 2.81V, the core temperature of the integral catalyst is 90°C, the reaction gas is a mixed gas containing 10-500ppm formaldehyde in the air, the gas flow rate is 50-300Ncm 3 /min, and the space velocity is 15-90L h -1 g -1 . The different formaldehyde concentrations, gas flow rates and space velocities in the mixed gas and the corresponding formaldehyde conversion rates are shown in Table 7.

表7Table 7

Figure BDA0001309154790000082
Figure BDA0001309154790000082

实施例48Example 48

本发明的催化氧化处理空气中甲醛的装置与传统加热反应装置的对比实验。采用传统加热模式的对比实验步骤与实施例12相类似,不同之处为:不通过直流稳压电源输入能量,而是通过缠绕在反应管外壁的电加热带对反应装置进行加热,使催化剂床层中心达到90℃。其他条件与实施例12一致。A comparative experiment between the device of the present invention for catalytic oxidation treatment of formaldehyde in air and the traditional heating reaction device. The comparative experimental procedure using the traditional heating mode is similar to that of Example 12, the difference is that instead of inputting energy through a DC stabilized power supply, the reaction device is heated by an electric heating belt wound on the outer wall of the reaction tube, so that the catalyst bed The center of the layer reaches 90°C. Other conditions are consistent with Example 12.

表8Table 8

Figure BDA0001309154790000091
Figure BDA0001309154790000091

由表8可知本发明反应装置在相同反应温度下甲醛的转化率略高于传统加热方式,但本发明的能耗较传统加热反应装置相比大大降低。It can be seen from Table 8 that the conversion rate of formaldehyde in the reaction device of the present invention is slightly higher than that of the traditional heating method at the same reaction temperature, but the energy consumption of the present invention is greatly lower than that of the traditional heating reaction device.

上述实施例仅仅是为了清楚地说明本发明所做的举例,而并非对实施方式的完全限定。所属领域的普通技术人员在上述说明的基础上还可以做出其它不同形式的变动,这里无法也无需对所有的实施方式给出实施例,但由此所引申出的显而易见的变动仍处于本发明的保护范围内。The above-mentioned embodiments are only examples for clearly illustrating the present invention, rather than fully limiting the implementation. Those of ordinary skill in the art can also make other changes in different forms on the basis of the above description. It is impossible and unnecessary to give examples for all implementation modes here, but the obvious changes derived from this are still within the scope of the present invention. within the scope of protection.

Claims (8)

1. A method for treating formaldehyde in air by catalytic oxidation, which is characterized by comprising the following steps:
placing an integral carbon-based catalyst (1) loaded with an active component in a reaction tube (3), clamping two ends of the integral carbon-based catalyst by using metal electrodes (2), connecting the two ends of the integral carbon-based catalyst with the positive electrode and the negative electrode of a power supply (4) by using a lead (7), inputting electric energy into the integral carbon-based catalyst, and enabling the integral carbon-based catalyst to reach a required reaction temperature by utilizing the Joule heat property of the integral carbon-based catalyst; introducing air containing formaldehyde into the reactor, carrying out catalytic oxidation reaction on the formaldehyde in the process of passing through the heated integral carbon-based catalyst, wherein the core temperature of the integral carbon-based catalyst is 90-300 ℃, the carrier of the integral carbon-based catalyst is an integral mesoporous carbon material,
the preparation method of the integral mesoporous carbon material comprises the following steps:
mixing resorcinol, polypropylene glycol and addition polymer of ethylene oxide, adding water and ethanol, stirring for dissolving, adding 1, 6-hexamethylenediamine, continuously stirring, adding formaldehyde solution until the solution is milky white, solidifying, taking out for drying, and heating to obtain the integral mesoporous carbon material.
2. The method for treating formaldehyde in air by catalytic oxidation according to claim 1, wherein the active component is one or both of Ag and Co.
3. The method for catalytic oxidation treatment of formaldehyde in air according to claim 1, characterized in that the preparation of the monolithic carbon-based catalyst comprises the following steps: placing a carrier of an integrated carbon-based catalyst in a catalyst containing Ag + And Co 2+ Soaking in the soaking solution for 1-20h, taking out, vacuum drying, and maintaining at 300-800 ℃ for 1-8h in inert atmosphere to obtain the monolithic carbon-based catalyst.
4. The method for treating formaldehyde in air by catalytic oxidation according to claim 3, wherein the impregnating solution is an aqueous solution of silver salt and cobalt salt, and the cobalt salt is one or more of cobalt nitrate, cobalt chloride and cobalt sulfate; the silver salt is silver nitrate.
5. A method for treating formaldehyde in air by catalytic oxidation according to claim 3, characterized in that Ag in the impregnation liquid + The concentration of (C) is 0-10wt%, co 2+ The concentration of (2) is 0-10wt%; the mass ratio of the carrier of the integral carbon-based catalyst to the impregnating solution is 1 (10-200).
6. The method for treating formaldehyde in air by catalytic oxidation according to claim 1, wherein the metal electrode is copper foam, nickel foam or copper sheet.
7. The method for catalytic oxidation treatment of formaldehyde in air according to claim 1, wherein the input voltage is 0-10V when the electric energy is input.
8. The method for catalytic oxidation treatment of formaldehyde in air according to any one of claims 1 to 7, characterized in that the formaldehyde content in the air is 10 to 500ppm and the gas flow rate is 50 to 300Ncm 3 Per minute, space velocity of 15000-90000ml h -1 g -1
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CN108483424B (en) * 2018-04-28 2019-11-19 厦门福纳新材料科技有限公司 A kind of fullerene electric heating synthesis device
CN108816040B (en) * 2018-06-29 2023-04-21 中国科学技术大学 A device and method for in-situ Joule thermocatalytic degradation of formaldehyde
CN109999658A (en) * 2019-05-08 2019-07-12 中国科学院宁波材料技术与工程研究所 Electric drive catalyst reaction device and its application
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