CN113769772B - Hydrochloric acid treated Nb-Mo co-doped g-C 3 N 4 Photocatalytic material and preparation method and application thereof - Google Patents

Hydrochloric acid treated Nb-Mo co-doped g-C 3 N 4 Photocatalytic material and preparation method and application thereof Download PDF

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CN113769772B
CN113769772B CN202111024811.1A CN202111024811A CN113769772B CN 113769772 B CN113769772 B CN 113769772B CN 202111024811 A CN202111024811 A CN 202111024811A CN 113769772 B CN113769772 B CN 113769772B
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hydrochloric acid
photocatalytic material
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CN113769772A (en
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李一杰
邢飞飞
陶然
范晓星
韩宇
张明怡
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Liaoning University
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Abstract

The invention discloses Nb-Mo codoped g-C treated by hydrochloric acid 3 N 4 A photocatalytic material, a preparation method and application thereof. Adding niobium oxide and molybdenum oxide powder into distilled water, then adding melamine, magnetically stirring at 80 ℃, and performing ultrasonic treatment to obtain a mixed solution; dropwise adding a hydrochloric acid solution into the obtained mixed solution, uniformly stirring by magnetic force, and drying to obtain a precursor; grinding the precursor, and calcining at high temperature in nitrogen atmosphere to obtain the target product Nb-Mo/g-C 3 N 4 A photocatalytic material. Nb-Mo ion co-doping g-C treated by hydrochloric acid prepared by using method of the invention 3 N 4 Photocatalytic material, improved g-C 3 N 4 The method has the advantages of low cost and easy operation, and can degrade organic pollutants by natural light under the condition of natural light.

Description

Hydrochloric acid treated Nb-Mo co-doped g-C 3 N 4 Photocatalytic material and preparation method and application thereof
Technical Field
The invention belongs to the technical field of photocatalysis, and particularly relates to high-activity Nb-Mo/g-C 3 N 4 A photocatalytic material and a preparation method and application thereof.
Background
Over the past decades, excessive emissions of toxic gases have created serious environmental problems that threaten human health. Various adsorbents have been studied to detect and remove toxic gases. Wherein the graphite carbon nitride (g-C) 3 N 4 ) A graphene-like porous layered material has attracted much interest because of its ease of synthesis, attractive electronic band structure, non-toxicity and high stability. Such organic semiconductors have shown tremendous potential applications in a variety of fields, including photocatalytic water splitting, photoreduction of carbon dioxide, organic pollutantsPhotolysis, solar energy conversion, and sensors. However, its inherent structure results in high electron-hole recombination rate and low photocatalytic activity, limiting its industrial application.
Disclosure of Invention
To solve the above problems, it is an object of the present invention to provide a hydrochloric acid-treated Nb-Mo co-doped g-C 3 N 4 The method is easy to operate, simple, convenient, low in cost, mild in condition and favorable for large-scale production.
The technical scheme adopted by the invention is as follows: hydrochloric acid treated Nb-Mo co-doped g-C 3 N 4 The photocatalytic material is doped with 0.25-0.5% of Nb ions and Mo ions in molar percentage, wherein the ratio of Nb ions to Mo ions = 1.
Hydrochloric acid treated Nb-Mo co-doped g-C 3 N 4 The preparation method of the photocatalytic material comprises the following steps:
1) Adding niobium oxide and molybdenum oxide powder into distilled water, then adding melamine, magnetically stirring at 80 ℃, and performing ultrasonic treatment to obtain a mixed solution;
2) Dropwise adding a hydrochloric acid solution into the mixed solution obtained in the step 1), uniformly stirring by magnetic force, and drying to obtain a precursor;
3) Grinding the precursor, and calcining at high temperature in nitrogen atmosphere to obtain the target product Nb-Mo/g-C 3 N 4 A photocatalytic material.
Further, in the above preparation method, step 1), the niobium oxide is Nb 2 O 5 (ii) a The molybdenum oxide is MoO 3
Further, the above-mentioned preparation process, step 1), is carried out in a molar ratio of Nb 2 O 5 :MoO 3 Melamine = (0.00125-0.0025): 0.0025-0.005): 1.
Further, in the preparation method, step 2), the drying temperature is 80 ℃.
Further, in the above preparation method, the molar ratio of hydrochloric acid to melamine = 0.345.
Further, in the above preparation method, step 3), the high temperature calcination is carried out at 550 ℃ for 2h.
Further, in the preparation method, the heating rate of the high-temperature calcination is 3 ℃/min.
The invention provides hydrochloric acid treated Nb-Mo co-doped g-C 3 N 4 The application of the photocatalytic material in the catalytic degradation of gas pollutants under visible light.
Further, the gaseous contaminant is isopropanol.
The invention has the beneficial effects that:
1. the invention provides hydrochloric acid treated Nb-Mo co-doped g-C 3 N 4 The photocatalytic material successfully constructs a doping structure with larger specific surface area, the structure can more easily move charges, and the photocatalytic activity can be effectively improved.
2. The hydrochloric acid treated Nb-Mo co-doped g-C 3 N 4 The preparation method of the photocatalytic material has the advantages of cheap and easily obtained raw materials, simple and convenient operation, greatly reduced cost, no toxicity, no environmental pollution and green chemistry.
3. The invention increases g-C 3 N 4 The specific surface area of (a) is to improve photocatalytic performance by increasing reaction sites and promoting bulk charge separation. In order to obtain a larger specific surface area, modification and doping are effective and simple methods for improving the photocatalytic performance, because the modification and doping can cause the change of the specific surface area, the invention adopts Nb-Mo ion co-doping to generate lattice defects, so that atoms in lattices are easier to migrate, the sensitivity to visible light is further improved, and the photocatalytic reaction efficiency is improved.
Drawings
FIG. 1 shows 0.5% of Nb-Mo/g-C of the photocatalyst prepared in example 1 3 N 4 、0.25%Nb-Mo/g-C 3 N 4 And pure g-C 3 N 4 XRD comparison pattern of (a).
FIG. 2 shows the 0.5% Nb-Mo/g-C ratio of different photocatalysts of example 2 3 N 4 、0.25%Nb-Mo/g-C 3 N 4 And pure g-C 3 N 4 The acetone production rate of (2) is shown in the graph.
Detailed Description
Example 1
Hydrochloric acid treated Nb-Mo codoped g-C 3 N 4 Photocatalytic Material (0.5% by volume Nb-Mo/g-C 3 N 4 )
The preparation method comprises the following steps:
1) Adding 0.0093g (0.0001 mol) Nb 2 O 5 And 0.0288g (0.0002 mol) of MoO 3 Adding the mixture into 45.5mL of distilled water, then adding 5g (0.04 mol) of melamine, magnetically stirring the mixture for 1h at the temperature of 80 ℃, and performing ultrasonic treatment for 1h to obtain a mixed solution;
2) Dropwise adding 4.5mL of hydrochloric acid solution into the mixed solution obtained in the step 1), uniformly stirring by magnetic force, putting into a drying oven, and drying at 80 ℃ for 12h to obtain a precursor;
3) Grinding the precursor obtained in the step 2), heating to 550 ℃ at the heating rate of 3 ℃/min in the nitrogen environment, and calcining at 550 ℃ for 2h to obtain the target product Nb-Mo co-doped g-C treated by hydrochloric acid 3 N 4 Photocatalytic material, in mol%, containing 0.5% of Nb and Mo, sample designation 0.5% 3 N 4
(II) hydrochloric acid treated Nb-Mo Co-doping g-C 3 N 4 Photocatalytic Material (0.25% Nb-Mo/g-C 3 N 4 )
The preparation method comprises the following steps:
1) 0.0046g (0.00005 mol) of Nb 2 O 5 And 0.0144g (0.0001 mol) MoO 3 Adding the mixture into 45.5mL of distilled water, then adding 5g (0.04 mol) of melamine, magnetically stirring the mixture for 1h at the temperature of 80 ℃, and performing ultrasonic treatment for 1h to obtain a mixed solution;
2) Dropwise adding 4.5mL of hydrochloric acid solution into the mixed solution obtained in the step 1), magnetically stirring uniformly, putting into a drying oven, and drying for 12 hours at 80 ℃ to obtain a precursor;
3) Grinding the precursor obtained in the step 2), heating to 550 ℃ at a heating rate of 3 ℃/min in a nitrogen environment, and calcining at 550 ℃ for 2h to obtain the target product, namely the Nb-Mo co-doped g-C treated by hydrochloric acid 3 N 4 Photocatalytic material, in mol%, containing 0.25% of Nb and Mo, sample number 0.25%Nb-Mo/g-C 3 N 4
(III) comparative example pure g-C 3 N 4 Photocatalytic material
The preparation method comprises the following steps: placing 5g of melamine in a crucible, heating to 550 ℃ at the heating rate of 3 ℃/min in a nitrogen environment, and calcining for 2h to obtain pure g-C 3 N 4 A photocatalytic material.
(IV) detection
FIG. 1 shows the content of Nb-Mo/g-C in sample 0.5% 3 N 4 Sample 0.25% Nb-Mo/g-C 3 N 4 And pure g-C 3 N 4 XRD test pattern of (1), sample 2.5% 3 N 4 And sample 0.5% Nb-Mo/g-C 3 N 4 Two diffraction peaks at 13.1 ℃ and 27.3 ℃ with pure g-C 3 N 4 Diffraction peaks coincide, and the main peak of the doped g-C3N4 catalyst still remains, indicating that the crystal structure is not changed. No compounds of Nb and Mo were observed in the doped g-C3N4 material, indicating that Nb and Mo are embedded in the g-C3N4 crystal planes in ionic form.
Example 2 application
Effect of different catalysts on catalytic degradation of isopropanol under visible light
The test process is as follows: filtering out ultraviolet simulated sunlight with 300W xenon lamp as light source, adjusting photocurrent to 18mA position, adjusting light intensity center to irradiate sample surface, fixing position, and respectively removing the residue from the sample by 0.5% Nb-Mo/g-C prepared in example 1 3 N 4 、 0.25%Nb-Mo/g-C 3 N 4 And pure g-C 3 N 4 Is placed in a 4cm container 2 In the glass tank, the glass tanks carrying the photocatalyst were placed in 325cm each 3 And finally, injecting 5ul of isopropanol liquid into the reactor, waiting for 2 hours until the isopropanol is completely volatilized into gas, starting timing after 20 minutes of illumination, and extracting one needle of the sample every 20 minutes for testing. The peak area of acetone generated by degrading isopropanol is recorded, and the concentration change point line graph of acetone generated by degrading isopropanol is calculated, and the result is shown in figure 2.
As can be seen from FIG. 2, the hydrochloric acid treatment produced according to the present invention had a content of 0.5% of Nb-Mo/g-C 3 N 4 g photo catalytic material has an acetone generation concentration which continuously increases along with time and is all higher than pure g-C 3 N 4 The effect is good. g-C prepared by the invention 3 N 4 Not only improves the photocatalytic activity, but also improves the yield to 1.5 times, improves the g-C 3 N 4 Photocatalytic performance.

Claims (4)

1. Hydrochloric acid treated Nb-Mo co-doped g-C 3 N 4 The preparation method of the photocatalytic material is characterized in that the Nb-Mo codoped g-C treated by hydrochloric acid 3 N 4 The photocatalytic material is doped with 0.5 percent of Nb ions and Mo ions according to molar percentage, wherein the Nb ions and the Mo ions are in a molar ratio of (1):
1) Mixing Nb with 2 O 5 And MoO 3 Adding the powder into distilled water, then adding melamine, magnetically stirring at 80 ℃, and performing ultrasonic treatment to obtain a mixed solution; in terms of mole ratio, nb 2 O 5 : MoO 3 Melamine = 0.00125-0.0025: 0.0025-0.005: 1;
2) Dropwise adding a hydrochloric acid solution into the mixed solution obtained in the step 1), uniformly stirring by magnetic force, and drying to obtain a precursor; hydrochloric acid to melamine =0.345 to 1 in molar ratio;
3) Grinding the precursor, and calcining at 550 ℃ for 2h in nitrogen atmosphere to obtain the target product Nb-Mo/g-C 3 N 4 A photocatalytic material.
2. The method of claim 1, wherein the drying temperature in step 2) is 80 ℃.
3. The method of claim 1, wherein the high temperature calcination is carried out at a temperature increase rate of 3 ℃/min.
4. Hydrochloric acid treated Nb-Mo co-doped g-C prepared according to the method of claim 1 3 N 4 Use of a photocatalytic material for the catalytic degradation of gaseous pollutants under visible light, characterized in that said gas isThe contaminant is isopropanol.
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CN103769187A (en) * 2013-12-18 2014-05-07 江苏悦达新材料科技有限公司 Preparation method of graphene/g-C3N4 compound photocatalyst
CN105944748B (en) * 2016-06-14 2018-10-16 辽宁大学 A kind of bigger serface graphite phase carbon nitride photochemical catalyst and its preparation method and application
CN106423244B (en) * 2016-10-09 2019-04-09 辽宁大学 A kind of porous g-C3N4Nanosheet photocatalyst and its preparation method and application
CN106492870A (en) * 2016-10-17 2017-03-15 阜阳师范学院 A kind of photochemical catalyst of doped metallic oxide and preparation method thereof
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