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CN110813331A - BiOBr/TiO2 composite photocatalyst and preparation method thereof - Google Patents

BiOBr/TiO2 composite photocatalyst and preparation method thereof Download PDF

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Publication number
CN110813331A
CN110813331A CN201910766002.4A CN201910766002A CN110813331A CN 110813331 A CN110813331 A CN 110813331A CN 201910766002 A CN201910766002 A CN 201910766002A CN 110813331 A CN110813331 A CN 110813331A
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biobr
composite photocatalyst
tio2 composite
ethyl alcohol
absolute ethyl
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王军
伍水生
余江鸿
高颖
吴斌
王进龙
张析
周涛
王长征
赵坤
王源瑞
张红
白守元
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Northwest Research Institute of Mining and Metallurgy
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J27/00Catalysts comprising the elements or compounds of halogens, sulfur, selenium, tellurium, phosphorus or nitrogen; Catalysts comprising carbon compounds
    • B01J27/06Halogens; Compounds thereof
    • B01J27/135Halogens; Compounds thereof with titanium, zirconium, hafnium, germanium, tin or lead
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/30Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
    • B01J35/39Photocatalytic properties
    • 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
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/38Organic compounds containing nitrogen

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Abstract

The invention discloses a BiOBr/TiO2 composite photocatalyst and a preparation method thereof, wherein the molar ratio of bismuth element to titanium element in the BiOBr/TiO2 composite photocatalyst is 1:5 or 1:1 or 1:2.5 or 1:7.5 or 1:10 or 5:1 or 10: 1. The preparation method of the composite photocatalyst comprises weighing appropriate amount of Bi (NO)3)3.5H2Dissolving O and CTAB in absolute ethyl alcohol respectively, and then mixing the two solutions uniformly; weighing a proper amount of TBOT, dissolving the TBOT in absolute ethyl alcohol, and adding the TBOT into the prepared mixed solution; and magnetically stirring the mixed solution, reacting at constant temperature, cooling, alternately washing with deionized water and absolute ethyl alcohol for several times, and drying the product to obtain the catalyst. The BiOBr/TiO2 composite photocatalyst is simple to synthesize and low in cost, and can remarkably reduce the recombination of photo-generated electrons and holes and improve the photocatalytic performance. Can be widely usedThe method is widely applied to the environmental protection fields of photocatalytic sewage treatment, air purification and the like.

Description

BiOBr/TiO2 composite photocatalyst and preparation method thereof
Technical Field
The invention relates to the technical field of photocatalysts, in particular to a BiOBr/TiO2 composite photocatalyst and a preparation method thereof.
Background
The environmental pollution includes water pollution, light pollution, air pollution, heavy metal pollution and the like. Covers the fields of civil use, industry, commerce, military and the like, and the improvement and treatment of environmental pollution become more and more important. The photocatalytic material has potential application in the aspect of pollutant treatment, and the photocatalytic reaction carried out by utilizing solar energy is generally concerned about environmental improvement and energy development.
TiO2The photocatalyst has the advantages of good stability, low cost, no toxicity, no secondary pollution, easy doping modification and the like, so that the photocatalyst is considered as an ideal photocatalytic material, and is widely researched. But TiO22There are two drawbacks: (1) the forbidden band range is wider and is 3.2eV, and the utilization rate of light is low; (2) the recombination rate of photo-generated electrons and holes is high, and the photon efficiency is poor. These two drawbacks limit TiO2Practical application of (2), therefore, TiO is required2Modification studies were conducted to improve their photocatalytic properties.
Disclosure of Invention
The invention aims to provide a BiOBr/TiO2 composite photocatalyst and a preparation method thereof, wherein the BiOBr and TiO2 composite photocatalyst is prepared by using BiOBr and TiO2The photocatalyst is compounded to prepare the photocatalyst with high activity and universality under visible light.
In order to achieve the purpose, the technical scheme adopted by the invention comprises the following contents:
the molar ratio of the contents of bismuth and titanium in the BiOBr/TiO2 composite photocatalyst is 1:5 or 1:1 or 1:2.5 or 1:7.5 or 1:10 or 5:1 or 10: 1.
Preferably, the molar ratio of the bismuth element to the titanium element in the BiOBr/TiO2 composite photocatalyst is 1: 1.
A preparation method of a BiOBr/TiO2 composite photocatalyst comprises the following steps:
step one, weighing 0.6-6.0gBi (NO)3)3.5H2Dissolving O and 1.2g CTAB in 20ml of absolute ethyl alcohol respectively, and then uniformly mixing the two solutions;
step two, weighing 0.42-4.2g of TBOT, dissolving in 30ml of absolute ethyl alcohol, and adding into the mixed solution prepared in the step one;
step three, magnetically stirring the mixed solution prepared in the step two for 0.5h, then transferring the mixed solution into a high-temperature reaction kettle, and reacting for 10h at the constant temperature of 150 ℃; naturally cooling to room temperature, carrying out suction filtration, alternately washing with deionized water and absolute ethyl alcohol for a plurality of times, collecting the product, and drying the product in an oven at 80 ℃ for 5 hours to obtain the dried flower-shaped BiOBr/TiO2 composite photocatalyst.
Wherein: in the first step, CTAB is short for hexadecyl trimethyl ammonium bromide, and the chemical molecular formula is as follows: c19H42BrN; TBOT in the second step is short for butyl titanate, and the chemical molecular formula is C16H36O4Ti。
BiOBr as a novel narrow-band-gap semiconductor material (the forbidden band width is 2.5-2.9eV) has unique electronsStructure, good optical property and catalytic property. By utilizing the advantages of better activity and stability on various dyes and the like, the dye can react with TiO2The photocatalyst is compounded, and the photocatalyst with high activity and universality under visible light can be prepared.
CTAB is white or light yellow crystal to powder, has pungent smell, is easily dissolved in isopropanol, is soluble in water, generates a large amount of foam during oscillation, and can have good coordination with anionic, nonionic and amphoteric surfactants. Has excellent penetrating, softening, emulsifying, antistatic, biological degrading and sterilizing performance.
TBOT is colorless to light yellow liquid, is inflammable and low in toxicity, is a glassy solid at the temperature of below-55 ℃, is dissolved in most organic solutions except ketones, and has the relative density of 0.966, the boiling point of 310-314 ℃, the flash point of 76.7 ℃ and the refractive index of 1.486. The product can rapidly absorb moisture and decompose in air, has very high chemical activity on water, and can be hydrolyzed to generate Ti (OH)4And therefore, must be stored in an anhydrous environment. Is soluble in most organic solvents. Due to its moisture absorbing properties, the used straws and the like are cleaned in time.
The BiOBr/TiO2 composite photocatalyst prepared by the invention is simple to synthesize, low in cost, high in specific surface area and excellent in mesoporous structure, and can remarkably reduce the recombination of photo-generated electrons and holes and improve the photocatalytic performance. Can be widely applied to the environmental protection fields of photocatalytic sewage treatment, air purification and the like.
As shown in figure 1, under the irradiation of visible light for 20min, BiOBr/TiO prepared by the invention2The degradation rate of the composite photocatalyst to rhodamine B is as high as 98.98%. And BiOBr and TiO singly2The degradation rate of rhodamine B under the same conditions is 85.93% and 47.43% respectively.
Drawings
FIG. 1 is an electron microscope scan of a BiOBr/TiO2 composite photocatalyst according to the invention;
FIG. 2 shows the BiOBr/TiO2 composite photocatalyst and single BiOBr and TiO2XRD (X-ray powder diffraction) pattern of (a);
FIG. 3 is a graph of the present invention preparedThe BiOBr/TiO2 composite photocatalyst and the single BiOBr and TiO2A degradation rate contrast graph of rhodamine B under the same conditions;
FIG. 4 is a structural diagram of rhodamine B.
Detailed Description
The invention is described in further detail below with reference to the figures and specific examples.
Example 1
A BiOBr/TiO2 composite photocatalyst, wherein the molar ratio of bismuth element to titanium element is 1: 1.
The preparation method of the BiOBr/TiO2 composite photocatalyst comprises the following steps:
step one, weighing 0.6gBi (NO)3)3.5H2Dissolving O and 1.2g CTAB in 20ml of absolute ethyl alcohol respectively, and then uniformly mixing the two solutions;
step two, weighing 0.42g of TBOT, dissolving in 30ml of absolute ethyl alcohol, and adding into the mixed solution prepared in the step one;
step three, magnetically stirring the mixed solution prepared in the step two for 0.5h, then transferring the mixed solution into a high-temperature reaction kettle, and reacting for 10h at the constant temperature of 150 ℃; naturally cooling to room temperature, carrying out suction filtration, alternately washing with deionized water and absolute ethyl alcohol for a plurality of times, collecting the product, and drying the product in an oven at 80 ℃ for 5 hours to obtain the dried BiOBr/TiO2 composite photocatalyst.
Through inspection, the molar ratio of the contents of bismuth and titanium in the prepared BiOBr/TiO2 composite photocatalyst is 1: 1.
Wherein: in the first step, CTAB is short for hexadecyl trimethyl ammonium bromide, and the chemical molecular formula is as follows: c19H42BrN; TBOT in the second step is short for butyl titanate, and the chemical molecular formula is C16H36O4Ti。
And (3) observing the photocatalytic activity of the prepared BiOBr/TiO2 composite photocatalyst by taking degraded rhodamine B as a model reaction: 0.05g of the BiOBr/TiO2 composite photocatalyst sample prepared in this example was weighed out and dispersed in 50mL of a 3X 10 composite photocatalyst-5In mol/L rhodamine B water solution; before illumination, sampleMagnetically stirring the product in a dark condition for 30min to achieve adsorption-desorption balance, and taking an initial sample; after illumination begins, 3mL of reaction solution samples are taken every 5min, the BiOBr/TiO2 composite photocatalyst is removed by using a filter membrane, the absorbance of the filtrate is measured at the characteristic absorption wavelength (553nm) of RhB by using an ultraviolet visible spectrophotometer, and the concentration of rhodamine B can be determined by using a rhodamine standard curve. The light irradiation is carried out for 20min, and the degradation rate is 98.98 percent.
Example 2
A BiOBr/TiO2 composite photocatalyst, wherein the molar ratio of bismuth element to titanium element is 1: 5.
The preparation method of the BiOBr/TiO2 composite photocatalyst comprises the following steps:
step one, weighing 0.6gBi (NO)3)3.5H2Dissolving O and 1.2g CTAB in 20ml of absolute ethyl alcohol respectively, and then uniformly mixing the two solutions;
step two, weighing 2.1g of TBOT, dissolving in 30ml of absolute ethyl alcohol, and adding into the mixed solution prepared in the step one;
step three, magnetically stirring the mixed solution prepared in the step two for 0.5h, then transferring the mixed solution into a high-temperature reaction kettle, and reacting for 10h at the constant temperature of 150 ℃; naturally cooling to room temperature, carrying out suction filtration, alternately washing with deionized water and absolute ethyl alcohol for a plurality of times, collecting the product, and drying the product in an oven at 80 ℃ for 5 hours to obtain the dried BiOBr/TiO2 composite photocatalyst.
Through inspection, the molar ratio of the contents of bismuth and titanium in the prepared BiOBr/TiO2 composite photocatalyst is 1: 5.
Wherein: in the first step, CTAB is short for hexadecyl trimethyl ammonium bromide, and the chemical molecular formula is as follows: c19H42BrN; TBOT in the second step is short for butyl titanate, and the chemical molecular formula is C16H36O4Ti。
And (3) observing the photocatalytic activity of the prepared BiOBr/TiO2 composite photocatalyst by taking degraded rhodamine B as a model reaction: 0.05g of the BiOBr/TiO2 composite photocatalyst sample prepared in this example was weighed out and dispersed in 50mL of a 3X 10 composite photocatalyst-5In mol/L rhodamine B water solution(ii) a Before illumination, the sample is firstly magnetically stirred for 30min under the condition of keeping out of the sun to achieve adsorption-desorption balance, and an initial sample is taken; after illumination begins, 3mL of reaction solution samples are taken every 5min, the BiOBr/TiO2 composite photocatalyst is removed by using a filter membrane, the absorbance of the filtrate is measured at the characteristic absorption wavelength (553nm) of RhB by using an ultraviolet visible spectrophotometer, and the concentration of rhodamine B can be determined by using a rhodamine standard curve. The degradation rate is 97.72% after 20min of illumination.
Example 3
A BiOBr/TiO2 composite photocatalyst, wherein the molar ratio of the contents of bismuth and titanium is 1: 10.
The preparation method of the BiOBr/TiO2 composite photocatalyst comprises the following steps:
step one, weighing 0.6gBi (NO)3)3.5H2Dissolving O and 1.2g CTAB in 20ml of absolute ethyl alcohol respectively, and then uniformly mixing the two solutions;
step two, weighing 4.2g of TBOT, dissolving in 30ml of absolute ethyl alcohol, and adding into the mixed solution prepared in the step one;
step three, magnetically stirring the mixed solution prepared in the step two for 0.5h, then transferring the mixed solution into a high-temperature reaction kettle, and reacting for 10h at the constant temperature of 150 ℃; naturally cooling to room temperature, carrying out suction filtration, alternately washing with deionized water and absolute ethyl alcohol for a plurality of times, collecting the product, and drying the product in an oven at 80 ℃ for 5 hours to obtain the dried BiOBr/TiO2 composite photocatalyst.
Through inspection, the molar ratio of the contents of bismuth and titanium in the prepared BiOBr/TiO2 composite photocatalyst is 1: 10.
Wherein: in the first step, CTAB is short for hexadecyl trimethyl ammonium bromide, and the chemical molecular formula is as follows: c19H42BrN; TBOT in the second step is short for butyl titanate, and the chemical molecular formula is C16H36O4Ti。
And (3) observing the photocatalytic activity of the prepared BiOBr/TiO2 composite photocatalyst by taking degraded rhodamine B as a model reaction: 0.05g of the BiOBr/TiO2 composite photocatalyst sample prepared in this example was weighed out and dispersed in 50mL of a 3X 10 composite photocatalyst-5mol/L ofRhodamine B water solution; before illumination, the sample is firstly magnetically stirred for 30min under the condition of keeping out of the sun to achieve adsorption-desorption balance, and an initial sample is taken; after illumination begins, 3mL of reaction solution samples are taken every 5min, the BiOBr/TiO2 composite photocatalyst is removed by using a filter membrane, the absorbance of the filtrate is measured at the characteristic absorption wavelength (553nm) of RhB by using an ultraviolet visible spectrophotometer, and the concentration of rhodamine B can be determined by using a rhodamine standard curve. The light irradiation is carried out for 20min, and the degradation rate is 98.53 percent.
Example 4
A BiOBr/TiO2 composite photocatalyst, wherein the molar ratio of bismuth element to titanium element is 5: 1.
The preparation method of the BiOBr/TiO2 composite photocatalyst comprises the following steps:
step one, 3.0gBi (NO) is weighed3)3.5H2Dissolving O and 1.2g CTAB in 20ml of absolute ethyl alcohol respectively, and then uniformly mixing the two solutions;
step two, weighing 0.42g of TBOT, dissolving in 30ml of absolute ethyl alcohol, and adding into the mixed solution prepared in the step one;
step three, magnetically stirring the mixed solution prepared in the step two for 0.5h, then transferring the mixed solution into a high-temperature reaction kettle, and reacting for 10h at the constant temperature of 150 ℃; naturally cooling to room temperature, carrying out suction filtration, alternately washing with deionized water and absolute ethyl alcohol for a plurality of times, collecting the product, and drying the product in an oven at 80 ℃ for 5 hours to obtain the dried BiOBr/TiO2 composite photocatalyst.
Through inspection, the molar ratio of the contents of bismuth and titanium in the prepared BiOBr/TiO2 composite photocatalyst is 5: 1.
Wherein: in the first step, CTAB is short for hexadecyl trimethyl ammonium bromide, and the chemical molecular formula is as follows: c19H42BrN; TBOT in the second step is short for butyl titanate, and the chemical molecular formula is C16H36O4Ti。
And (3) observing the photocatalytic activity of the prepared BiOBr/TiO2 composite photocatalyst by taking degraded rhodamine B as a model reaction: 0.05g of the BiOBr/TiO2 composite photocatalyst sample prepared in this example was weighed out and dispersed in 50mL of a 3X 10 composite photocatalyst-5In mol/L rhodamine B water solution; before illumination, the sample is firstly magnetically stirred for 30min under the condition of keeping out of the sun to achieve adsorption-desorption balance, and an initial sample is taken; after illumination begins, 3mL of reaction solution samples are taken every 5min, the BiOBr/TiO2 composite photocatalyst is removed by using a filter membrane, the absorbance of the filtrate is measured at the characteristic absorption wavelength (553nm) of RhB by using an ultraviolet visible spectrophotometer, and the concentration of rhodamine B can be determined by using a rhodamine standard curve. The degradation rate is 66.30% after 20min of illumination.
Example 5
A BiOBr/TiO2 composite photocatalyst, wherein the molar ratio of bismuth element to titanium element is 1: 1.
The preparation method of the BiOBr/TiO2 composite photocatalyst comprises the following steps:
step one, weighing 6.0gBi (NO)3)3.5H2Dissolving O and 1.2g CTAB in 20ml of absolute ethyl alcohol respectively, and then uniformly mixing the two solutions;
step two, weighing 0.42g of TBOT, dissolving in 30ml of absolute ethyl alcohol, and adding into the mixed solution prepared in the step one;
step three, magnetically stirring the mixed solution prepared in the step two for 0.5h, then transferring the mixed solution into a high-temperature reaction kettle, and reacting for 10h at the constant temperature of 150 ℃; naturally cooling to room temperature, carrying out suction filtration, alternately washing with deionized water and absolute ethyl alcohol for a plurality of times, collecting the product, and drying the product in an oven at 80 ℃ for 5 hours to obtain the dried BiOBr/TiO2 composite photocatalyst.
Through inspection, the molar ratio of the contents of bismuth and titanium in the prepared BiOBr/TiO2 composite photocatalyst is 10: 1.
Wherein: in the first step, CTAB is short for hexadecyl trimethyl ammonium bromide, and the chemical molecular formula is as follows: c19H42BrN; TBOT in the second step is short for butyl titanate, and the chemical molecular formula is C16H36O4Ti。
And (3) observing the photocatalytic activity of the prepared BiOBr/TiO2 composite photocatalyst by taking degraded rhodamine B as a model reaction: 0.05g of the BiOBr/TiO2 composite photocatalyst sample prepared in the example was weighed out and dispersedAt a concentration of 3X 10 in 50mL-5In mol/L rhodamine B water solution; before illumination, the sample is firstly magnetically stirred for 30min under the condition of keeping out of the sun to achieve adsorption-desorption balance, and an initial sample is taken; after illumination begins, 3mL of reaction solution samples are taken every 5min, the BiOBr/TiO2 composite photocatalyst is removed by using a filter membrane, the absorbance of the filtrate is measured at the characteristic absorption wavelength (553nm) of RhB by using an ultraviolet visible spectrophotometer, and the concentration of rhodamine B can be determined by using a rhodamine standard curve. The light irradiation is carried out for 20min, and the degradation rate is 59.86%.
The BiOBr/TiO2 composite photocatalyst prepared by the invention is simple to synthesize, low in cost, high in specific surface area and excellent in mesoporous structure, and can remarkably reduce the recombination of photo-generated electrons and holes and improve the photocatalytic performance. Can be widely applied to the environmental protection fields of photocatalytic sewage treatment, air purification and the like.

Claims (3)

1. A BiOBr/TiO2 composite photocatalyst is characterized in that: the molar ratio of the bismuth element to the titanium element in the BiOBr/TiO2 composite photocatalyst is 1:5 or 1:1 or 1:2.5 or 1:7.5 or 1:10 or 5:1 or 10: 1.
2. The BiOBr/TiO2 composite photocatalyst as claimed in claim 1, wherein: the molar ratio of the bismuth element to the titanium element in the BiOBr/TiO2 composite photocatalyst is 1: 1.
3. A preparation method of a BiOBr/TiO2 composite photocatalyst is characterized by comprising the following steps: it comprises the following steps:
step one, weighing 0.6-6.0gBi (NO)3)3.5H2Dissolving O and 1.2g CTAB in 20ml of absolute ethyl alcohol respectively, and then uniformly mixing the two solutions;
step two, weighing 0.42-4.2g of TBOT, dissolving in 30ml of absolute ethyl alcohol, and adding into the mixed solution prepared in the step one;
step three, magnetically stirring the mixed solution prepared in the step two for 0.5-1h, then transferring the mixed solution into a high-temperature reaction kettle, and reacting for 10h at the constant temperature of 150 ℃; naturally cooling to room temperature, carrying out suction filtration, alternately washing with deionized water and absolute ethyl alcohol for a plurality of times, collecting the product, and drying the product in an oven at 80 ℃ for 5 hours to obtain the dried BiOBr/TiO2 composite photocatalyst.
Wherein: in the first step, CTAB is short for hexadecyl trimethyl ammonium bromide, and the chemical molecular formula is as follows: c19H42BrN; TBOT in the second step is short for butyl titanate, and the chemical molecular formula is C16H36O4Ti。
CN201910766002.4A 2019-08-19 2019-08-19 BiOBr/TiO2 composite photocatalyst and preparation method thereof Pending CN110813331A (en)

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CN111675302A (en) * 2020-04-28 2020-09-18 西北矿冶研究院 Method for degrading butyl xanthate in mineral processing wastewater
CN111790414A (en) * 2020-08-10 2020-10-20 齐鲁工业大学 Mixed crystal TiO2BiOBr composite material and preparation method and application thereof
CN112007633A (en) * 2020-09-15 2020-12-01 西北矿冶研究院 La/Bi2WO6Preparation method and application of photocatalyst
CN112007669A (en) * 2020-09-15 2020-12-01 西北矿冶研究院 Catalyst and preparation method and application thereof
CN113289646A (en) * 2021-05-05 2021-08-24 桂林理工大学 Core-shell structured nanoflower/nanoparticle bismuth oxybromide/titanium dioxide visible-light-driven photocatalyst and preparation method and application thereof
CN114733504A (en) * 2022-05-10 2022-07-12 杭州职业技术学院 Preparation method and application of self-cleaning gel with adsorption-photocatalysis synergistic effect
CN114733504B (en) * 2022-05-10 2023-12-19 杭州职业技术学院 Preparation method and application of self-cleaning gel with synergistic effect of adsorption and photocatalysis
CN115430441A (en) * 2022-09-29 2022-12-06 西安交通大学 Copper-doped bismuth oxybromide-titanium dioxide composite photocatalyst and preparation method and application thereof
CN115430441B (en) * 2022-09-29 2024-01-19 西安交通大学 Copper-doped bismuth oxybromide-titanium dioxide composite photocatalyst and preparation method and application thereof
CN116832837A (en) * 2023-03-21 2023-10-03 武汉理工大学 Flower ball-shaped TiO 2 Heterojunction material with/BiOBr core-shell structure and preparation method and application thereof

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