CN111298786B - Micrometer hexagonal prism MoO 3-x Preparation method of photocatalytic material - Google Patents

Micrometer hexagonal prism MoO 3-x Preparation method of photocatalytic material Download PDF

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CN111298786B
CN111298786B CN202010029363.3A CN202010029363A CN111298786B CN 111298786 B CN111298786 B CN 111298786B CN 202010029363 A CN202010029363 A CN 202010029363A CN 111298786 B CN111298786 B CN 111298786B
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moo
hexagonal prism
glucose
solution
photocatalytic
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CN111298786A (en
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唐成黎
张莉梅
董立春
杜多勤
陈泥程
张涛
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Chongqing University
Chongqing Chemical Industry Vocational College
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Chongqing Chemical Industry Vocational College
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    • B01J35/39
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/16Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J23/24Chromium, molybdenum or tungsten
    • B01J23/28Molybdenum
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01GCOMPOUNDS CONTAINING METALS NOT COVERED BY SUBCLASSES C01D OR C01F
    • C01G39/00Compounds of molybdenum
    • C01G39/02Oxides; Hydroxides
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/30Treatment of water, waste water, or sewage by irradiation
    • CCHEMISTRY; METALLURGY
    • C09DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
    • C09KMATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE
    • C09K11/00Luminescent, e.g. electroluminescent, chemiluminescent materials
    • C09K11/08Luminescent, e.g. electroluminescent, chemiluminescent materials containing inorganic luminescent materials
    • C09K11/67Luminescent, e.g. electroluminescent, chemiluminescent materials containing inorganic luminescent materials containing refractory metals
    • C09K11/68Luminescent, e.g. electroluminescent, chemiluminescent materials containing inorganic luminescent materials containing refractory metals containing chromium, molybdenum or tungsten
    • C09K11/681Chalcogenides
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01PINDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
    • C01P2004/00Particle morphology
    • C01P2004/01Particle morphology depicted by an image
    • C01P2004/03Particle morphology depicted by an image obtained by SEM
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01PINDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
    • C01P2004/00Particle morphology
    • C01P2004/30Particle morphology extending in three dimensions
    • C01P2004/40Particle morphology extending in three dimensions prism-like
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/308Dyes; Colorants; Fluorescent agents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/10Photocatalysts

Abstract

Micrometer hexagonal prism MoO 3‑x A preparation method of a photocatalytic material belongs to the technical field of photocatalytic materials. The invention reduces MoO by glucose 3 MoO with oxygen-enriched vacancies on the surface is prepared 3‑x Photocatalytic material. In particular to a method for preparing a composite material by Na 2 MoO 4 ·2H 2 O reacts with HCl, glucose is taken as a reducing agent, stirring is carried out at normal temperature or low temperature, and finally, the MoO with oxygen-enriched vacancies on the surface is obtained through washing and drying 3‑x A micro hexagonal prism material. The invention is directed to MoO 3 The forbidden band width is wider, the response to visible light is weak, and MoO is realized in the photocatalysis process 3 The hole-electron pair recombination rate is high, and the separation efficiency of photo-generated carriers is low, and Na is adopted 2 MoO 4 ·2H 2 O is used as a raw material, glucose is used as a reducing agent, and MoO with oxygen-enriched vacancies on the surface is prepared by an in-situ reduction method in an acidic aqueous solution 3‑x The material narrows the forbidden bandwidth of the material, has wider visible light response range, promotes the separation efficiency of photon-generated carriers, and improves the photocatalysis performance of the material.

Description

Micrometer hexagonal prism MoO 3-x Preparation method of photocatalytic material
Technical Field
The invention relates to a micron hexagonal prism MoO 3-x A preparation method of a photocatalytic material belongs to the technical field of photocatalytic materials, and particularly relates to a photocatalytic materialIs prepared by the preparation method of (1). The method is technically characterized by using Na 2 MoO 4 ·2H 2 O is used as a raw material, glucose reducer, and MoO with oxygen-enriched vacancies on the surface is prepared by adopting an in-situ reduction method under an acidic condition 3-x Photocatalytic material.
Background
With the continuous development of social economy, environmental pollution is a great concern, and meanwhile, people also put forward higher requirements on environmental quality, so that environmental protection and treatment problems are receiving more and more attention.
Organic dyes are important factors causing water pollution, and in recent years, a method for catalytically degrading organic pollutants in water by using a photocatalyst becomes an important means in the field of water pollution treatment. Compared with the traditional sewage treatment such as adsorption and precipitation, the photocatalysis method has the advantages of simple process, low energy consumption and the like, and can lead most of organic matters which are difficult to degrade at normal temperature and normal pressure to be oxidized and decomposed into CO 2 And H 2 O。
At present, more researches are carried out, and the photocatalyst with more mature technology is nano TiO 2 The photocatalyst has the advantages of high catalytic activity, good thermal stability, low price, no toxicity and the like. But due to TiO 2 The forbidden bandwidth of (2) is narrow (3.2 eV), the spectral absorption threshold is 387nm, and only the ultraviolet light part of the solar spectrum can be utilized. In addition, tiO 2 The electron-hole recombination rate generated by excitation is high, so that the light quantum efficiency is low, and the application range of the self-inherent defect is greatly limited. To solve this problem, researchers have desired to find other new semiconductor catalysts to replace or modify TiO 2
Molybdenum is a typical transition metal element, has rich chemical valence and numerous compounds, and therefore, has application in various fields such as catalysts, battery materials, superconducting materials, energy storage materials and the like. Wherein MoO 3 Is an N-type semiconductor material with a unique channel structure, and has gained wide attention in the fields of organic pollutant degradation, hydrogen production, solar cells, gas sensors and the like in recent years. Despite MoO 3 Has good application prospect as a photocatalyst,it still has some limitations, mainly MoO 3 The forbidden band width of (2) is wider, the response to visible light is lacking, and in addition, moO in the photocatalysis process 3 The hole-electron pair recombination rate is high, and the separation efficiency of the photogenerated carriers is low.
Research shows that the introduction of oxygen vacancy can promote the separation process of photon-generated carriers and expand MoO 3 And improves the photocatalytic performance of the light absorption range of the light-emitting diode. "Over 100-nm-Thick MoOx Films with Superior Hole Collection and Transport Properties for Organic Solar Cells" (Advanced Energy Materials,2018,8 (25)) published by Bei Yang et al, preparing a solution by using ammonium paramolybdate as a precursor and vitamin C as a reducing agent, spin-coating to form a film, and performing high-temperature annealing treatment to obtain MoO rich in oxygen vacancies 3-x A film. Experimental results show that the light absorption capacity of the film is greatly improved. Li Chunxiao et al published "high-performance lithium ion battery cathode material MoO 3-x Is carried out by molybdenum trioxide (MoO) 3 ) With oxalic acid dihydrate (H) 2 C 2 O 4 ·2H 2 O) is used as a main raw material, deionized water is used for preparing a solution, and isopropanol (C) 3 H 8 O) is used as a solvent, and is reacted for 12 hours at 120 ℃, and then is kept at 120 ℃ for 2 hours under argon atmosphere, so as to prepare the flower-shaped molybdenum oxide (MoO) with an oxygen defect structure 3-x ). But is reported at present in MoO 3 The process of introducing oxygen vacancies is complex.
Disclosure of Invention
The invention aims to solve the MoO 3 The forbidden bandwidth is wider, the response to visible light is lacking, the hole-electron pair recombination rate is high, and the separation efficiency of the photon-generated carriers is low.
The technical proposal adopted for realizing the purpose of the invention is to prepare a micron hexagonal prism MoO 3-x A photocatalytic material characterized by comprising the steps of:
1) Na is mixed with 2 MoO 4 ·2H 2 O is dissolved in deionized water;
the Na is 2 MoO 4 ·2H 2 The mol volume ratio (mol: L) of O to deionized water is 1:4-25;
2) Adding PEG-20000 into the solution in the step 1), and stirring until the solution is clear;
the PEG-20000 and Na 2 MoO 4 ·2H 2 The mass ratio (g: g) of O is 1:3-20;
3) Slowly dripping concentrated HCl into the solution obtained in the step 2), stirring for 30min, and uniformly mixing;
the volume ratio (L:L) of the concentrated HCl to the deionized water is as follows: 8-25;
4) Adding 0.2-1 g glucose into the solution in the step 3), and uniformly dispersing;
the glucose and Na 2 MoO 4 ·2H 2 The mass ratio (g: g) of O is 1:1-10;
5) Stirring the suspension liquid obtained in the step 4) at 25-80 ℃ for reaction for 1-12 h;
6) Washing the solution in the step 5) with deionized water, centrifuging to obtain a precipitate, and drying the precipitate at 60 ℃ for 10-20 h to obtain blue or deep blue MoO 3-x And (3) powder.
Compared with the prior art, the invention has the remarkable advantages that:
(1) The invention takes common glucose as a modifier and adopts a one-step reduction method to successfully prepare the surface oxygen-enriched vacancy MoO 3-x And a micron hexagonal prism.
(2) MoO prepared by the invention 3-x The material has wider visible light response range, high separation efficiency of photo-generated carriers, good photocatalytic activity and high degradation efficiency on organic matters.
(3) The preparation method is simple, can react at normal temperature or low temperature, and has short reaction time, economy and environmental protection.
Drawings
FIG. 1 (a) MoO prepared in example 1 3-x FIG. 1 (b) is an electron microscope (SEM) image of the material, and FIG. 2 shows MoO prepared in example 2 3 Electron Microscope (SEM) images of the material.
FIGS. 2 (a) and (b) are X-ray electron spectroscopy (XPS) spectra of the materials prepared in example 1 and example 2, respectively.
FIG. 3 is a Photoluminescence (PL) spectrum of the material prepared by examples 1 and 2.
FIG. 4 is a graph showing the photocatalytic performance test of the materials prepared in examples 1 and 2.
Detailed Description
The present invention will be further described with reference to the following examples and drawings, but it should not be construed that the scope of the subject matter of the present invention is limited to the following examples and drawings. Various substitutions and alterations are made according to the ordinary skill and familiar means of the art without departing from the technical spirit of the invention, and all such substitutions and alterations are intended to be included in the scope of the invention.
Example 1:
1) 1.2g of Na 2 MoO 4 ·2H 2 O is dissolved in 50ml deionized water;
2) Adding 0.1g of PEG-20000 into the solution in the step 1), and stirring until the solution is clear;
3) Slowly dripping 3.5ml of concentrated HCl into the solution in the step 2), and stirring for 30min;
4) Adding 0.5g glucose into the solution in the step 3), and uniformly dispersing;
5) Stirring the suspension in the step 4) at 60 ℃ for reaction for 4 hours;
6) Washing the solution obtained in the step 5) with deionized water, centrifuging to obtain precipitate, and drying the precipitate at 60 ℃ for 12h to obtain blue or deep blue MoO 3-x And (3) powder.
Example 2:
1) 1 to 2g of Na 2 MoO 4 ·2H 2 O was dissolved in 50ml deionized water.
2) 0.1g PEG-20000 was added to the solution in step 1) and stirred until the solution was clear.
3) 3.5ml of concentrated HCl is taken and slowly dripped into the solution in the step 2), and the mixture is stirred for 30min.
4) Washing the precipitate with deionized water and ethanol, centrifuging, and drying the precipitate at 60deg.C for 12 hr to obtain MoO 3 Micrometer columns.
SEM (FIG. 1) XPS (FIG. 2) test shows that MoO prepared according to the present invention 3 The micron rod presents regular hexagonal prism shape and has smooth surface; after modification treatment, moO 3 Surface portionMo of (c) is reduced from +6 to +5 to make MoO 3-x Part of the surface of the sample is defective, and many oxygen vacancies are formed. At the same time MoO 3-x The recombination ability of the photogenerated electron-hole pairs is effectively suppressed (fig. 3). Thus MoO 3-x In the photocatalytic reaction of the catalyst, more photo-generated electron-hole pairs can participate in the reaction, and the photocatalytic performance is more excellent (fig. 4).

Claims (2)

1. Micrometer hexagonal prism MoO 3-x The preparation method of the photocatalytic material is characterized by comprising the following steps: the method comprises the following steps:
1) Na is mixed with 2 MoO 4 ·2H 2 O is dissolved in deionized water;
the Na is 2 MoO 4 ·2H 2 The mol volume ratio (mol: L) of O to deionized water is 1:4-25;
2) Adding PEG-20000 into the solution in the step 1), and stirring until the solution is clear;
the PEG-20000 and Na 2 MoO 4 ·2H 2 The mass ratio (g: g) of O is 1:3-20;
3) Slowly dripping concentrated HCl into the solution obtained in the step 2), stirring for 30min, and uniformly mixing;
the volume ratio (L:L) of the concentrated HCl to the deionized water is as follows: 8-25;
4) Adding 0.2-1 g glucose into the solution in the step 3), and uniformly dispersing;
the glucose and Na 2 MoO 4 ·2H 2 The mass ratio (g: g) of O is 1:1-10;
5) Stirring the suspension liquid obtained in the step 4) at 25-80 ℃ for reaction for 1-12 h;
6) Washing the solution in the step 5) with deionized water, centrifuging to obtain a precipitate, and drying the precipitate at 60 ℃ for 10-20 h to obtain blue or deep blue MoO 3-x And (3) powder.
2. A micrometer hexagonal prism MoO according to claim 1 3-x The preparation method of the photocatalytic material is characterized in that the prepared MoO 3-x Is a micron hexagonal prism.
CN202010029363.3A 2020-01-07 2020-01-07 Micrometer hexagonal prism MoO 3-x Preparation method of photocatalytic material Active CN111298786B (en)

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Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009046343A (en) * 2007-08-17 2009-03-05 Kobe Univ High-purity molybdenum oxide thin film and its producing method
CN105664921A (en) * 2016-03-09 2016-06-15 陕西科技大学 Preparation method of high-performance nano W0.4Mo0.6O3 photocatalyst
CN108654599A (en) * 2018-06-15 2018-10-16 南京信息工程大学 A kind of hexagonal phase hydration molybdenum trioxide photocatalyst and the preparation method and application thereof
CN108745384A (en) * 2018-05-31 2018-11-06 苏州大学 Functionalization and hybridization nanotube C@MoS2/SnS2And the preparation method and application thereof
CN110586072A (en) * 2019-04-26 2019-12-20 福建工程学院 WO with novel structure3Micro-nano photocatalytic material

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009046343A (en) * 2007-08-17 2009-03-05 Kobe Univ High-purity molybdenum oxide thin film and its producing method
CN105664921A (en) * 2016-03-09 2016-06-15 陕西科技大学 Preparation method of high-performance nano W0.4Mo0.6O3 photocatalyst
CN108745384A (en) * 2018-05-31 2018-11-06 苏州大学 Functionalization and hybridization nanotube C@MoS2/SnS2And the preparation method and application thereof
CN108654599A (en) * 2018-06-15 2018-10-16 南京信息工程大学 A kind of hexagonal phase hydration molybdenum trioxide photocatalyst and the preparation method and application thereof
CN110586072A (en) * 2019-04-26 2019-12-20 福建工程学院 WO with novel structure3Micro-nano photocatalytic material

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
三氧化钼微米棒的制备及其光催化性质研究;宋继梅;尹扬俊;杨捷;张小霞;焦剑;;中国钼业(01);全文 *
硝酸辅助的六方相MoO_3的制备及其光催化性质;宋继梅;梅雪峰;王红;高菲;赵绍娟;胡海琴;;中国钼业(05);全文 *

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