CN107824212B - Nitrogen-doped carbon-cerium oxide composite material and preparation and application thereof - Google Patents

Nitrogen-doped carbon-cerium oxide composite material and preparation and application thereof Download PDF

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CN107824212B
CN107824212B CN201711043909.5A CN201711043909A CN107824212B CN 107824212 B CN107824212 B CN 107824212B CN 201711043909 A CN201711043909 A CN 201711043909A CN 107824212 B CN107824212 B CN 107824212B
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cerium oxide
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dopamine
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李星运
刘早锦
罗栋
赵修松
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Qingdao University
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Abstract

The invention belongs to the technical field of catalysts, and particularly relates to a nitrogen-doped carbon-cerium oxide composite material and preparation and application thereof. The method takes dopamine as a precursor and polymethyl methacrylate (PMMA) as a template, and introduces ammonium ceric nitrate in the dopamine polymerization process to carry out in-situ complexation on cerium species. The PMMA can be decomposed and removed through high-temperature treatment, polydopamine is converted into nitrogen-doped porous carbon at high temperature, and ammonium ceric nitrate is converted into small-size cerium oxide quantum dots, so that the porous nitrogen-doped carbon-cerium oxide quantum dot composite material with a three-dimensional structure is obtained. When used in formaldehyde catalytic oxidation reaction, the composite material shows far superior to pure nanometer CeO2The catalytic performance of the material has higher potential industrial application value.

Description

Nitrogen-doped carbon-cerium oxide composite material and preparation and application thereof
Technical Field
The invention belongs to the technical field of catalysts, and particularly relates to a nitrogen-doped carbon-cerium oxide composite material and preparation and application thereof.
Background
Formaldehyde (HCHO) is a major indoor pollution source, and long-term exposure to inhaled formaldehyde gas can irritate eyes, throat, nerves and respiratory tract systems, and formaldehyde has carcinogenicity, thereby posing a great threat to human health (s.wang et al.j. mater.chem.a,2014,2,6598-. Along with the enhancement of environmental awareness of people, the removal of formaldehyde has attracted extensive social attention. At present, the traditional physical adsorption method is a formaldehyde treatment method which is generally adopted, but because the adsorption method adopts an adsorbent such as activated carbon, the adsorption capacity is limited, and when the adsorbed formaldehyde reaches saturation, the adsorbent can slowly release the formaldehyde so as to become a new pollution source (J.Hazard.Mater.331(2017) 161-170). In contrast, catalytic oxidation of formaldehyde to carbon dioxide using a catalyst is a more effective treatment. The supported noble metal Pt catalyst (Ma C.Y.et. environ. Sci. Tchnol.2011,45,3628-3634) shows excellent formaldehyde catalytic oxidation activity. However, the noble metal is expensive, the resource is scarce, and the noble metal is easy to be poisoned and inactivated, so that the replacement of the noble metal has important significance.
In the research of non-noble metal catalysts, transition metal oxides have active lattice oxygen and surface defects, and are the current research hotspots. In 2002, Sekine compared a series of metal oxides to find MnO2Has excellent activity (Y.sekine, Atmos. environ, 2002,36, 5543). Most researchers are working on optimally designing MnO2Material to improve its catalytic performance. Wang et al synthesized partially crystalline MnOxThe catalyst, coated on cordierite honeycomb ceramics, exhibits extremely high catalytic activity at low formaldehyde concentrations (1ppm) (Wang et al chem. Eng. J,2017,320: 667-one 676). In order to increase the mass transfer and adsorption of reaction molecules, the construction of a three-dimensional macroporous-mesoporous structure is an effective means. Rong et al uses MnO2Nanowire and MnO2The nanosheets synthesize three-dimensional MnO2Nanomaterial, which can sufficiently expose active sites to promote formaldehyde catalytic activity (Rong et al. Acs Catal.2017,7(2): 1067-. Although MnO2Exhibit some potential for replacing precious metals, but the synthesis is relatively complex and the activity remains to be improved. Relative to MnO2,CeO2Is a multifunctional rare metal oxide, has excellent physical and chemical properties, and has industrial application in the fields of electrochemistry, photochemistry and heterogeneous catalysis. CeO (CeO)2Is of fluorite crystal structure and simultaneously has Ce4+And Ce3+And has a large number of oxygen vacancies and active surface oxygen. For increasing CeO2The key point of the catalytic oxidation activity of (2) is to improve the surface oxygen concentration and the exposure of active sites. Huang et al used Eu vs. CeO2Doping is performed to increase the defect sites and oxygen hole concentration, thereby greatly increasing the activity of catalyzing formaldehyde oxidation (Huang Y.C.et al.appl.Catal.B: Environ,181(2016), 779-787). Lin and the like design and synthesize CeO2-MnO2The research shows that the material has more oxygen vacancies and surface oxygen species (Lin Z. et. appl. Catal. B: environ.211(2017) 212-221). The preparation of small-size and even single-atom catalysts is an effective means for promoting the activity of the catalysts, and the construction of a three-dimensional hierarchical pore structure is expected to promote reaction mass transfer and further improve the catalytic performance. The invention aims to synthesize small-size cluster CeO with a three-dimensional framework structure2Based on composite materials to add CeO2The number of defect sites and the exposure of active sites. Dopamine is a biological material of mussel-like secretion, can be adhered and polymerized on the surface of any material, and can be converted into a nitrogen-doped porous carbon material by high-temperature roasting polymerization. By utilizing the characteristics of dopamine, the nitrogen-doped porous carbon material with a three-dimensional structure can be synthesized by adopting a template method. Meanwhile, dopamine has an o-diphenol functional group and has a certain complexing function with metal. When the cerium nitrate amine is introduced in the dopamine polymerization process, Ce is hopeful to be complexed in the polydopamine framework so as to synthesize the highly dispersed cerium cluster. In the process, PMMA is added as a hard template, and dopamine of the complex cerium species can be polymerized on the surface of the template. After high-temperature roasting, PMMA can be decomposed and removed, dopamine can be converted into three-dimensional nitrogen-doped porous carbon, and high-dispersion cerium oxide can be obtained, so that the nitrogen-doped porous carbon-cerium oxide quantum dot composite material with a three-dimensional structure is prepared, and the composite material and the catalytic application in synthesis and formaldehyde oxidation reaction are not reported.
Disclosure of Invention
The invention mainly aims to provide a nitrogen-doped carbon-cerium oxide composite catalyst suitable for catalytic oxidation reaction and a preparation method thereof, and a three-dimensional nitrogen-doped carbon-cerium oxide composite catalyst and a preparation method thereof.
In order to achieve the purpose, the invention adopts the following technical scheme:
a nitrogen-doped carbon-cerium oxide composite catalyst:
the cerium oxide is dispersed on the surface of the nitrogen-doped carbon, and the weight content of the cerium oxide is 0.05-40%.
Further, the specific surface area of the nitrogen-doped carbon is 5-2000 m2The pore diameter is 0.2-50 nm; n atoms are doped in the porous carbon structure, and the doping amount of the N atoms is 1-15% of the mass of the porous carbon; the cerium oxide is quantum dots in a high dispersion state, and the average particle size is 0.1-3 nm.
A three-dimensional nitrogen-doped carbon-cerium oxide composite catalyst:
a) the nitrogen-doped carbon is a three-dimensional cross-linked porous carbon material with a honeycomb structure;
b) the cerium oxide is dispersed on the surface of the nitrogen-doped carbon, and the weight content of the cerium oxide is 0.05-40%.
Further, the nitrogen-doped carbon is macroporous-mesoporous grade porous carbon with a three-dimensional structure, the pore diameter of the macropores is 20-500 nm, the pore diameter of the mesopores is 2-10 nm, and the specific surface area is 30-3000 m2(ii)/g; n atoms are doped in the porous carbon structure, and the doping amount of the N atoms is 1-15% of the mass of the porous carbon; the cerium oxide is quantum dots in a high dispersion state, and the average particle size is 0.1-3 nm.
A preparation method of a nitrogen-doped carbon-cerium oxide composite material catalyst comprises the following steps:
dissolving dopamine in a mixed solution of distilled water and alcohol, adding a cerium ammonium nitrate solution while stirring, stirring until the mixture is uniformly mixed, adding an alkaline substance to adjust the pH value of the solution to be alkaline, and stirring at room temperature; and carrying out suction filtration, washing, drying and roasting in an inert atmosphere to obtain the nitrogen-doped carbon-cerium oxide composite material.
Further, the alcohol is methanol, ethanol, propanol, butanol or ethylene glycol, and the volume ratio of the alcohol to the water is 0.1-10; the concentration of the solution obtained after dissolving the dopamine is 0.01-100 g/L; the concentration of the ammonium ceric nitrate solution is 0.01-100 g/L, and the mass ratio of dopamine to ammonium ceric nitrate is 10-0.1; the alkaline substance used for adjusting the pH value of the solution is one or more of tris (hydroxymethyl) aminomethane buffer solution, ammonia water and urea; stirring for 5-30 h at room temperature; the drying temperature is 60-100 ℃; the inert gas is one or more of nitrogen, helium and argon, and the gas flow rate is 20-180 mL/min; the roasting temperature is 300-1200 ℃.
A preparation method of a three-dimensional nitrogen-doped carbon-cerium oxide composite catalyst comprises the following steps:
dissolving dopamine in a mixed solution of distilled water and alcohol, adding PMMA as a template, adding a cerium ammonium nitrate solution while stirring, stirring until the mixture is uniform, adding an alkaline substance to adjust the pH value of the solution to be alkaline, and stirring at room temperature; and carrying out suction filtration, washing, drying and roasting in an inert atmosphere to obtain the three-dimensional nitrogen-doped carbon-cerium oxide composite material.
Further, the alcohol is methanol, ethanol, propanol, butanol or ethylene glycol, and the volume ratio of the alcohol to the water is 0.1-10; the concentration of the solution obtained after dissolving the dopamine is 0.01-100 g/L; the PMMA particle size is 10-800 nm, and the mass ratio of dopamine to PMMA is 50-0.1; the concentration of the ammonium ceric nitrate solution is 0.01-100 g/L, and the mass ratio of dopamine to ammonium ceric nitrate is 10-0.1; the alkaline substance used for adjusting the pH value of the solution is one or more of tris (hydroxymethyl) aminomethane buffer solution, ammonia water and urea; stirring for 5-30 h at room temperature; the drying temperature is 60-100 ℃; the inert gas is one or more of nitrogen, helium and argon, and the gas flow rate is 20-180 mL/min; the roasting temperature is 300-1200 ℃.
The nitrogen-doped carbon-cerium oxide composite catalyst and the application of the three-dimensional nitrogen-doped carbon-cerium oxide composite catalyst in formaldehyde catalytic oxidation reaction are provided.
The nitrogen-doped carbon-cerium oxide composite catalyst and the three-dimensional nitrogen-doped carbon-cerium oxide composite catalyst are applied to VOC (volatile organic compound) oxidation and CO oxidation reactions.
The invention has the following beneficial effects:
aiming at the problem that a noble metal catalyst used in the catalytic oxidation reaction of formaldehyde is expensive, the invention obtains the high-efficiency three-dimensional nitrogen-doped porous carbon-cerium oxide quantum dot non-noble metal catalyst by combining a template method with an in-situ metal complexing method in the polymerization process through a brand-new design scheme. In addition, the catalysts of the present invention are also suitable for other catalytic oxidation reactions, such as: toluene oxidation, CO oxidation, vinyl chloride oxidation, and the like.
Drawings
FIG. 1(a) is a 3D-CN-CeO solution at a resolution of 1 μm2Scanning electron microscope images of;
FIG. 1(b) is a graph showing 3D-CN-CeO at a resolution of 100nm2Scanning electron microscope images of;
FIG. 2(a) is a graph of 3D-CN-CeO at a resolution of 200nm2Transmission electron microscope photograph of (1);
FIG. 2(b) is a graph of 3D-CN-CeO at a resolution of 100nm2Transmission electron microscope photograph of (1);
FIG. 3(a) is 3D-CN-CeO2N of (A)2Isothermal adsorption and desorption curves;
FIG. 3(b) is 3D-CN-CeO2The pore distribution map of;
FIG. 4 is 3D-CN-CeO2XPS spectra of (a);
FIG. 5 is 3D-CN-CeO2High-resolution transmission electron microscope photographs;
FIG. 6 is 3D-CN-CeO2With CeO2XRD spectrum of (1);
FIG. 7(a) is a graph showing the activity of each catalyst in catalyzing the oxidation reaction of formaldehyde;
FIG. 7(b) is a TOF value comparison graph of formaldehyde conversion of each catalyst;
FIG. 8(a) shows CN-CeO2N of (A)2Isothermal adsorption and desorption curves;
FIG. 8(b) is CN-CeO2The pore distribution map of;
FIG. 9(a) is CN-CeO at a resolution of 1 μm2Scanning electron microscope images of;
FIG. 9(b) is CN-CeO at a resolution of 100nm2Scanning electrodeA mirror image;
FIG. 10(a) is CN-CeO at a resolution of 50nm2Transmission electron microscope photograph of (1);
FIG. 10(b) is CN-CeO at a resolution of 5nm2Transmission electron microscope photograph of (1);
Detailed Description
The invention is further illustrated by the following figures and examples.
Example 1
Nitrogen-doped carbon-cerium oxide composite material (CN-CeO)2) Preparation of
1g of dopamine was dissolved in 250mL of a mixture of distilled water and ethanol (the volume ratio of ethanol to water was 1:1), 100mL of a ceric ammonium nitrate solution (the concentration of the ceric ammonium nitrate solution was 3g/L) was added with stirring, and the mixture was stirred for 1 hour. Adjusting the pH value to 8.5 by Tris-buffer, stirring for 24h at room temperature, and carrying out suction filtration and washing with distilled water until the filtrate is neutral. Drying in a 60 ℃ oven for 12h, heating to 550 ℃ in Ar atmosphere at the heating rate of 5 ℃/min and the Ar flow rate of 50mL/min, preserving heat for 3h, and cooling to room temperature in Ar atmosphere to obtain the nitrogen-doped carbon-cerium oxide composite material which is named as CN-CeO2
FIGS. 9(a) and (b) are CN-CeO2FIG. 9 is a scanning electron micrograph of (A), CN-CeO2Exhibit a morphology similar to particle packing; FIGS. 10(a) and (b) are CN-CeO2The transmission electron micrograph of (1) is shown in FIG. 10, and the obtained material is CeO2Composite materials with CN, CeO2The particle size is about 2nm and is highly dispersed on the surface of a CN material. From CN-CeO2N of (A)2As shown in the physical adsorption experiments (FIGS. 8(a) and (b)), CN-CeO was found2Has a specific surface area of 67.7m2In terms of a/g, the average pore diameter is 1.4nm and 0.4 nm.
Three-dimensional nitrogen-doped carbon-cerium oxide composite material (3D-CN-CeO)2) The preparation of (1):
1g of dopamine was dissolved in 250mL of a mixture of distilled water and ethanol (the volume ratio of ethanol to water was 1:1), 3g of PMMA powder was added, 100mL of a cerium ammonium nitrate solution (the concentration of the cerium ammonium nitrate solution was 3g/L) was added with stirring, and the mixture was stirred for 1 hour. Adjusting the pH value to 8.5 by Tris-buffer, stirring for 24h at room temperature, filtering, washing with distilled water until the filtrate is neutral. Drying in a 60 ℃ oven for 12h, heating to 550 ℃ in Ar atmosphere at the heating rate of 5 ℃/min and the Ar flow rate of 50mL/min, preserving heat for 3h, cooling to room temperature in Ar atmosphere to obtain the three-dimensional nitrogen-doped carbon-cerium oxide composite material, and naming the three-dimensional nitrogen-doped carbon-cerium oxide composite material as 3D-CN-CeO2
FIG. 1 shows 3D-CN-CeO2The scanning Electron micrograph of (A) is 3D-CN-CeO, as shown in FIG. 12Shows a three-dimensional regular pore structure similar to a honeycomb, and the pore diameter of a big pore is about 100 nm. FIG. 2 shows 3D-CN-CeO2Transmission electron micrograph of (1), which can further prove that 3D-CN-CeO2The three-dimensional structure of (1). FIG. 3 shows 3D-CN-CeO2N of (A)2Isothermal adsorption and desorption curves and pore distribution diagram, from N of FIG. 32Physical adsorption experiment can obtain 3D-CN-CeO2Has a specific surface area of 255.8m2/g, a pore volume of 0.99cc/g, and average pore diameters of 2nm and 9.3 nm. This indicates that 3D-CN-CeO2The catalyst is a porous material with a hierarchical pore structure, has a mesopore structure while having macropores, and the unique pore structure is beneficial to mass transfer of reactants and exposure of active sites of the catalyst, so that the catalytic activity is greatly improved. FIG. 4 shows 3D-CN-CeO2The XPS spectrum of (A) was obtained from the XPS characterization of FIG. 4, 3D-CN-CeO2Mainly composed of C, N, O, Ce four elements, and the N content is 3%, which indicates that the finally formed porous carbon is N-doped carbon. The ICP test shows that 3D-CN-CeO2CeO in2Is 22 percent. FIG. 5 shows 3D-CN-CeO2The high-resolution projection electron microscope photograph of (1) from which CeO was confirmed2The carbon surface is in a state of high-dispersion quantum dots, and the average particle diameter is 1-2 nm. FIG. 6 shows 3D-CN-CeO2With CeO2XRD spectrum of (A) relative to CeO as can be seen in FIG. 62Material, 3D-CN-CeO2Does not exhibit significant CeO2A diffraction peak of (A), which indicates 3D-CN-CeO2Middle and small size CeO2In the amorphous state, with higher defective bits.
Example 2
Catalytic oxidation reaction of formaldehyde
The formaldehyde catalytic oxidation activity evaluation of the catalyst is carried out in a micro fixed bed reactor. 0.05g of catalyst is placed in a quartz reaction tube, mixed gas of formaldehyde with the formaldehyde concentration of 94ppm and air is introduced, the temperature is raised to 300 ℃ by the program, and the conversion rate of the formaldehyde is calculated by gas chromatography sampling analysis at intervals of 20 ℃.
FIG. 7 shows different catalysts (CN-CeO)2、3D-CN-CeO2、CeO2) The catalytic activity of formaldehyde oxidation of (1) is compared with that of (2). As can be seen from FIG. 7, 3D-CN-CeO2Shows the highest activity, the temperature for 100 percent conversion of formaldehyde is about 130 ℃, and CN-CeO2The temperature for 100% conversion of formaldehyde of (A) is 150 ℃, CeO2The temperature at which 100% conversion of formaldehyde is carried out is 300 ℃. Calculating the TOF value of the formaldehyde catalytic conversion, namely: CeO of unit mass2As the amount of formaldehyde converted per unit time of the catalyst, it was found that CN-CeO was present at 200 ℃2And 3D-CN-CeO2Respectively is CeO22.5 times and 5.3 times of the total weight of the composition. This is a good demonstration of the ultrahigh catalytic activity of the synthesized composite.

Claims (8)

1. A nitrogen-doped carbon-cerium oxide composite catalyst is characterized in that: the cerium oxide is dispersed on the surface of the nitrogen-doped carbon, and the weight content of the cerium oxide is 0.05-40%; the specific surface area of the nitrogen-doped carbon is 5-2000 m2The pore diameter is 0.2-50 nm; n atoms are doped in the porous carbon structure, and the doping amount of the N atoms is 1-15% of the mass of the porous carbon; the cerium oxide is quantum dots in a high dispersion state, and the average particle size is 0.1-3 nm.
2. A three-dimensional nitrogen-doped carbon-cerium oxide composite catalyst is characterized in that:
a) the nitrogen-doped carbon is a three-dimensional cross-linked porous carbon material with a honeycomb structure;
b) the cerium oxide is dispersed on the surface of the nitrogen-doped carbon, and the weight content of the cerium oxide is 0.05-40%;
the nitrogen-doped carbon is a macroporous-mesoporous grade porous carbon with a three-dimensional structure, the pore diameter of the macropores is 20-500 nm, the pore diameter of the mesopores is 2-10 nm, and the specific surface area is 30-3000 m2(ii)/g; n atoms are doped in the porous carbon structure, and the doping amount of the N atoms is 1-15% of the mass of the porous carbon;the cerium oxide is quantum dots in a high dispersion state, and the average particle size is 0.1-3 nm.
3. A process for preparing the catalyst of claim 1, wherein: the method comprises the following steps:
dissolving dopamine in a mixed solution of distilled water and alcohol, adding a cerium ammonium nitrate solution while stirring, stirring until the mixture is uniformly mixed, adding an alkaline substance to adjust the pH value of the solution to be alkaline, and stirring at room temperature; and carrying out suction filtration, washing, drying and roasting in an inert atmosphere to obtain the nitrogen-doped carbon-cerium oxide composite material.
4. The method for preparing the catalyst according to claim 3, wherein: the alcohol is methanol, ethanol, propanol, butanol or ethylene glycol, and the volume ratio of the alcohol to the water is 0.1-10; the concentration of the solution obtained after dissolving the dopamine is 0.01-100 g/L; the concentration of the ammonium ceric nitrate solution is 0.01-100 g/L, and the mass ratio of dopamine to ammonium ceric nitrate is 10-0.1; the alkaline substance used for adjusting the pH value of the solution is one or more of tris (hydroxymethyl) aminomethane buffer solution, ammonia water and urea; stirring for 5-30 h at room temperature; the drying temperature is 60-100 ℃; the inert gas is one or more of helium and argon, and the gas flow rate is 20-180 mL/min; the roasting temperature is 300-1200 ℃.
5. A process for preparing the catalyst of claim 2, wherein: the method comprises the following steps:
dissolving dopamine in a mixed solution of distilled water and alcohol, adding PMMA as a template, adding a cerium ammonium nitrate solution while stirring, stirring until the mixture is uniform, adding an alkaline substance to adjust the pH value of the solution to be alkaline, and stirring at room temperature; and carrying out suction filtration, washing, drying and roasting in an inert atmosphere to obtain the three-dimensional nitrogen-doped carbon-cerium oxide composite material.
6. The method for preparing the catalyst according to claim 5, wherein: the alcohol is methanol, ethanol, propanol, butanol or ethylene glycol, and the volume ratio of the alcohol to the water is 0.1-10; the concentration of the solution obtained after dissolving the dopamine is 0.01-100 g/L; the PMMA particle size is 10-800 nm, and the mass ratio of dopamine to PMMA is 50-0.1; the concentration of the ammonium ceric nitrate solution is 0.01-100 g/L, and the mass ratio of dopamine to ammonium ceric nitrate is 10-0.1; the alkaline substance used for adjusting the pH value of the solution is one or more of tris (hydroxymethyl) aminomethane buffer solution, ammonia water and urea; stirring for 5-30 h at room temperature; the drying temperature is 60-100 ℃; the inert gas is one or more of helium and argon, and the gas flow rate is 20-180 mL/min; the roasting temperature is 300-1200 ℃.
7. Use of a catalyst according to any one of claims 1-2 in the catalytic oxidation of formaldehyde.
8. Use of a catalyst according to any of claims 1-2 in oxidation of VOCs, CO oxidation reactions.
CN201711043909.5A 2017-10-31 2017-10-31 Nitrogen-doped carbon-cerium oxide composite material and preparation and application thereof Active CN107824212B (en)

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* Cited by examiner, † Cited by third party
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CN108620113B (en) * 2018-05-16 2020-08-25 内江师范学院 Preparation method of nitrogen-doped carbon-cerium composite nanosheet
CN108579790B (en) * 2018-05-25 2021-03-09 万华化学集团股份有限公司 Nitrogen-doped porous carbon catalyst, preparation method thereof and preparation method of beta-isophorone
CN109939718B (en) * 2019-04-15 2020-10-09 中国科学院化学研究所 Monatomic catalyst with high catalytic activity and preparation method and application thereof
CN113398977B (en) * 2021-07-08 2023-10-24 青岛大学 Nitrogen-doped carbon catalyst prepared by taking waste cigarette ends as carbon source, and preparation method and application thereof
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Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1919455A (en) * 2005-08-25 2007-02-28 中国科学院生态环境研究中心 Process for eliminating volatile organic pollutant by catalytic oxidation
CN103272558A (en) * 2013-04-24 2013-09-04 浙江大学 Nitrogen doped carbon xerogel material for absorbing heavy metal ions from water, and preparation method
JP2014019599A (en) * 2012-07-17 2014-02-03 Japan Health Sciences Foundation Method for preparing highly-dispersible nanomaterial
CN104084187A (en) * 2014-07-10 2014-10-08 大连理工大学 Carbon or nitrogen-doped carbon binding type metallic oxide nano-particle electrocatalyst and preparation method thereof
KR101570738B1 (en) * 2014-05-30 2015-11-20 서강대학교산학협력단 N-doped three dimensional porous carbon structure, preparing method thereof, and supercapacitor electrode including the same
CN106449173A (en) * 2016-11-03 2017-02-22 苏州科技大学 Cobalt oxide quantum dot-bionic graphene high-energy-storage electrode material and preparation method thereof
CN106861618A (en) * 2017-02-28 2017-06-20 西安交通大学 A kind of N doping porous hollow carbon ball carbon dioxide absorbing material and preparation method and application

Patent Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1919455A (en) * 2005-08-25 2007-02-28 中国科学院生态环境研究中心 Process for eliminating volatile organic pollutant by catalytic oxidation
JP2014019599A (en) * 2012-07-17 2014-02-03 Japan Health Sciences Foundation Method for preparing highly-dispersible nanomaterial
CN103272558A (en) * 2013-04-24 2013-09-04 浙江大学 Nitrogen doped carbon xerogel material for absorbing heavy metal ions from water, and preparation method
KR101570738B1 (en) * 2014-05-30 2015-11-20 서강대학교산학협력단 N-doped three dimensional porous carbon structure, preparing method thereof, and supercapacitor electrode including the same
CN104084187A (en) * 2014-07-10 2014-10-08 大连理工大学 Carbon or nitrogen-doped carbon binding type metallic oxide nano-particle electrocatalyst and preparation method thereof
CN106449173A (en) * 2016-11-03 2017-02-22 苏州科技大学 Cobalt oxide quantum dot-bionic graphene high-energy-storage electrode material and preparation method thereof
CN106861618A (en) * 2017-02-28 2017-06-20 西安交通大学 A kind of N doping porous hollow carbon ball carbon dioxide absorbing material and preparation method and application

Non-Patent Citations (4)

* Cited by examiner, † Cited by third party
Title
"Dopamine as the coating agent and carbon precursor for the fabrication of N-doped carbon coated Fe3O4 composites as superior lithium ion anodes";Cheng Lei et al.;《Nanoscale》;20121127;第5卷;第1168-1175页 *
"Enhancing the Catalytic Activity of Zeolitic Imidazolate Framework-8-Derived N-Doped Carbon with Incorporated CeO2 Nanoparticles in the Oxygen Reduction Reaction";Yue Yu et al.;《Chemistry A European Journal》;20170711;第23卷;第10690-10697页 *
"N-doped carbon nanotubes synthesized in high yield and decorated with CeO2 and SnO2 nanoparticles";Rui Zhang et al.;《Journal of Alloys and Compounds》;20110621;第509卷;第8621页右栏第2段、图2、第8624页左栏第2段 *
"氮掺杂多孔碳材料的合成及其应用研究";刘超;《中国优秀硕士学位论文全文数据库 工程科技I辑》;20150515;B015-14 *

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