CN111085185B - CeO 2 :CDs/TiO 2 Nano material and application thereof in photocatalysis - Google Patents

CeO 2 :CDs/TiO 2 Nano material and application thereof in photocatalysis Download PDF

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CN111085185B
CN111085185B CN201911267476.0A CN201911267476A CN111085185B CN 111085185 B CN111085185 B CN 111085185B CN 201911267476 A CN201911267476 A CN 201911267476A CN 111085185 B CN111085185 B CN 111085185B
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CN111085185A (en
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白静怡
王鑫
刁国旺
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Abstract

The invention discloses CeO 2 :CDs/TiO 2 Nano material and its application in photocatalysis. The nano CeO with good crystal form, remarkably improved conductivity and obviously changed degradation performance is synthesized by a simple and convenient method 2 :CDs/TiO 2 A material. The invention takes rare earth oxide as a template and adopts a loading and coating technology to load CDs on the traditional CeO 2 On the nano material, the electron transmission rate in the nano material is accelerated, so that the recombination of photo-generated electrons and holes is reduced, the potential of the material in photodegradation application is stimulated based on the principle, and the degradation time is greatly shortened.

Description

CeO 2 :CDs/TiO 2 Nano material and application thereof in photocatalysis
Technical Field
The invention belongs to the field of catalytic chemistry, and particularly relates to a photocatalytic material as well as a preparation method and application thereof.
Background
At present, a common problem faced by human beings is the energy problem, and the problem of solving the energy is more and more important due to the increasing severity of the problems of environmental pollution, exhaustion of fossil fuels and the like. Solar energy is one of the most potential new energy sources for development as an inexhaustible, clean and pollution-free ideal energy source. In recent years, photocatalytic technology, an advanced oxidation method, has been widely used to degrade wastewater due to its ability to generate reducing electrons and oxidizing holes, thereby effectively degrading intractable organic pollutants.
To obtain a good performance photocatalyst, the material constituting the photocatalyst must have a high specific surface area to allow the particles to be sufficiently in contact with organic contaminants, and the photocatalyst should also have good electron transport properties and good solar benefitsAnd (5) the utilization rate. So that the photo-generated electrons can be transmitted to the outside in time, the recombination with the photo-generated electron holes is avoided, and the sunlight is utilized as much as possible. Although some conventional photocatalysts have been used to degrade wastewater in simulated sunlight, such as TiO 2 Unfortunately, the practical use of these conventional catalysts is limited because they respond only to uv light, which is only 5% of sunlight, making the material less efficient for sunlight. On the other hand, the simple nano titanium dioxide small particles are not beneficial to the contact of the photocatalyst and pollutants.
In order to realize high-efficiency degradation performance, the nanoparticles are combined with a proper material, so that the band gap energy of the material can be reduced, the internal resistance of the material can be reduced, the transition of photo-generated electrons is facilitated, the quantity of excited photo-generated electrons is increased, the electronic output characteristic is improved, all the excited photo-generated electrons are rapidly transferred into a reaction liquid as far as possible, the recombination of carriers in the conduction process can be inhibited, and the electron transmission efficiency and the electron collection efficiency can be improved. May also be made of TiO 2 The edge of the light absorption band generates red shift, so that the TiO 2-based photocatalyst responds to the excitation of a visible light source, and the composition of photo-generated electrons and photo-generated holes on the surface of the nanoparticles is reduced, thereby improving the utilization rate of sunlight.
The technology for degrading organic pollutants by using photocatalytic materials also has certain defects: although the degradation effect of the photocatalyst is good, the green photocatalyst is difficult to find, and the semiconductor material applied to the photocatalyst is limited.
Disclosure of Invention
The invention aims to provide CeO capable of effectively reducing the resistance of a photocatalyst and increasing the solar energy utilization rate 2 :CDs/TiO 2 And (3) nano materials.
The technical scheme of the invention comprises the following steps:
(1) Adding a sodium citrate solution into the urea solution to obtain a mixed solution of urea and sodium citrate;
(2) Adding cerous chloride into the mixed solution obtained in the step (1), uniformly stirring, slowly adding hydrogen peroxide, and stirring;
(3) Carrying out reaction on the mixed solution obtained in the step (2) by adopting a hydrothermal method, cooling, centrifugally cleaning and drying after the reaction is finished to obtain CeO 2
(4) The CeO obtained in the step (3) 2 Adding the mixture into the carbon point solution, and stirring for 12 hours;
(5) Filtering and drying the solution obtained in the step (4), putting the solution into ethanol, adding tetrabutyl titanate, stirring, centrifugally cleaning and drying to obtain the CeO 2 :CDs/TiO 2 And (3) nano materials.
Preferably, the mass ratio of urea to sodium citrate to cerous chloride is 5.
Preferably, the mass ratio of the cerous chloride to the hydrogen peroxide is 4; the hydrothermal reaction temperature is 180 ℃ and the hydrothermal reaction time is 22 hours.
Preferably, the Carbon Dot (CDs) solution is prepared by (a) dissolving citric acid in ultrapure water, ultrasonically dispersing and then vigorously stirring to homogenize the solution; (b) And carrying out hydrothermal reaction on the obtained dispersion, cooling and centrifuging after the reaction is finished, and reserving a supernatant to obtain a carbon dot solution.
Preferably, ceO 2 The mass ratio of the carbon dot solution to the carbon dot solution is 1.
Preferably, the mass ratio of tetrabutyl titanate to cerous chloride is 10.
The invention also provides CeO 2 :CDs/TiO 2 The application of the nano material in photocatalytic degradation of RhB (rhodamine B).
Compared with the prior art, the invention synthesizes the hollow material loaded with CDs and coated with TiO based on the rare earth oxide which is cheap and has wider application 2 . When CeO is present 2 Hollow nano material loaded with CDs and coated with TiO 2 After the thin layer, the resistance inside the composite material becomes small due to the good conductivity of CDs, while TiO 2 Coating of the thin layer allows TiO to be formed 2 With CeO 2 Forming heterojunction, and under the irradiation of visible light, the generated photogenerated electrons can be rapidly formed by TiO through the loaded CDs 2 Transfer of the conduction band to CeO 2 Layer, secondly, supported on TiO 2 With CeO 2 The intermediate CDs, acting both as electron acceptors and electron donors, facilitate electron transport in the TiO 2 With CeO 2 Meta-transfer, and TiO 2 Or CeO 2 The excess electrons can also be transferred to loaded CDs, which promotes the separation of photogenerated electrons and photogenerated holes, so that the photogenerated electrons have better photocatalytic performance, and the degradation of RhB is finally realized.
Drawings
FIG. 1 shows CeO 2 :CDs/TiO 2 EDS spectra of each element of the nano material.
FIG. 2 is a TEM image of CDs.
FIG. 3 shows CeO 2 :CDs/TiO 2 TEM images of nanomaterials.
FIG. 4 shows CeO 2 :CDs/TiO 2 SEM images of nanomaterials.
FIG. 5 shows CeO 2 :CDs/TiO 2 Ultraviolet-near infrared spectrogram of the nanometer material.
FIG. 6 shows CeO 2 :CDs/TiO 2 Photocurrent response graph of the nanomaterial.
FIG. 7 shows CeO 2 :CDs/TiO 2 The nano material is used for degrading RhB under the photocatalysis of each sample under the irradiation of visible light.
Detailed Description
In order to make the objects, technical solutions and advantages of the present invention more apparent, the present invention will be described in detail with reference to the accompanying drawings and embodiments.
The invention is in TiO 2 Adding CeO into 2 And the carbon dots are loaded, the electron transport mode of the material is changed through the loading of the carbon dots, and the internal resistance of the material is reduced and the transport speed is accelerated due to the addition of the carbon dots.
CeO of the invention 2 :CDs/TiO 2 The preparation method of the nano material comprises the following steps:
(1) Dissolving citric acid in ultrapure water, ultrasonically dispersing, mixing and uniformly stirring to prepare a colorless transparent solution;
(2) Placing the colorless transparent solution in a high-pressure hydrothermal reaction kettle for reaction;
(3) Cooling, centrifuging the light yellow liquid obtained by the reaction, and reserving the supernatant to obtain a carbon dot solution;
(4) Preparing a urea aqueous solution, and adding a sodium citrate solution to obtain a mixed solution of urea and sodium citrate;
(5) Adding cerium chloride into the mixed solution, uniformly stirring, slowly adding hydrogen peroxide, and stirring to obtain a light yellow mixed solution;
(6) Reacting the mixed solution by a hydrothermal method;
(7) After cooling, centrifugally cleaning and drying;
(8) Adding the dried sample into the solution of the carbon dots, and stirring for one night;
(9) Filtering and drying the powder, putting the powder into ethanol, adding tetrabutyl titanate, stirring, centrifugally cleaning, and drying to obtain CeO 2 :CDs/TiO 2 And (3) nano materials.
The application process is as follows: ceO is added 2 :CDs/TiO 2 The nano material is placed in RhB solution according to the feeding ratio of 0.5g/L, after dark reaction for 30min, a light source is turned on, reaction liquid is taken at certain intervals, solid is filtered out, and ultraviolet absorption spectrum data of the liquid is measured. The composite material prepared by the invention has better photocatalytic performance and higher degradation rate than pure CeO 2 The method is greatly improved. Under the dark reaction of 30 minutes, the photocatalyst is dispersed in the RhB solution uniformly under the condition of vigorous stirring, the influence of the dispersion unevenness of materials on the experiment is eliminated, and the measured data are in line with the linear condition. The light source is a 300W xenon lamp provided with a UVCUT420nm type optical filter. The data are recorded as UV absorption Spectroscopy data recording absorbance at wavelength 553 nm.
Examples
1、 CeO 2 :CDs/TiO 2 Preparation of nanomaterials
(1) Dissolving 0.4196g of citric acid in 10mL of ultrapure water, and placing the solution in an ultrasonic cleaning machine for ultrasonic treatment for 20min to completely disperse the solution; after stirring vigorously for 15min, adding the transparent liquid into a polytetrafluoroethylene high-pressure hydrothermal reaction kettle, reacting for 5h at 200 ℃, after the transparent liquid is naturally cooled, centrifuging the solution at 13000 rmp/min for 20min, and removing precipitates to obtain a light yellow solution, namely a carbon dot solution.
(2) 1.0793g of urea is placed in 170mL of ultrapure water for ultrasonic dispersion for 10min, 10mM/L of sodium citrate solution 83mL is added, reaction is carried out for 12min under vigorous stirring, 0.8889g of cerous chloride is added, stirring is carried out for 20min, 1mL of hydrogen peroxide is dripped at a constant speed at a speed of 10mL/min, and stirring is carried out continuously for 30min. Adding the faint yellow mixed solution formed by the reaction into a 50mL polytetrafluoroethylene high-pressure hydrothermal reaction kettle, reacting for 22h at 180 ℃, naturally cooling, centrifugally cleaning, and drying at 60 ℃ to obtain faint yellow CeO 2 And (3) sampling.
(3) 0.1263g of CeO was taken 2 Placing in 2.526g carbon dot solution, ultrasonically dispersing for 30min, stirring for 12h to make the carbon dots fully attached to CeO 2 The above. 20mg of the material with the carbon points attached is taken, 20mL of ethanol and 7mL of acetonitrile are added, 0.25mL of ammonia water is added at the rotating speed of 500r/min, stirring is carried out for 5min, 200 mu L of TBOT is added, and stirring is carried out overnight. The reaction solution is centrifugally cleaned at the rotating speed of 6500rmp/min, and the product is dried at 60 ℃ for later use.
2、CeO 2 :CDs/TiO 2 Characterization of nanomaterials
FIG. 1 shows CeO prepared according to the present invention 2 :CDs/TiO 2 EDS spectrum of the nano material, distribution of Ce element, C element, ti element and O element can be observed from the EDS spectrum to confirm CDs and TiO 2 Is surely supported on CeO 2 Thereon CeO is formed 2 :CDs/TiO 2 And (3) nano materials.
FIGS. 2 and 3 show the carbon dots and CeO prepared by the present invention, respectively 2 :CDs/TiO 2 The TEM image of the field emission transmission electron microscope of the nano material shows that the prepared carbon dots have uniform particle size which is approximately 3nm-5nm in FIG. 2; from FIG. 3, it can be seen that prepared CeO 2 :CDs/TiO 2 The nano material is of a double-layer hollow structure, the particle size is uniform, and the size is about 400 nm.
FIG. 4 shows the preparation of CeO according to the invention 2 :CDs/TiO 2 The SEM image of the field emission scanning electron microscope of the nano material shows that the material is a hollow sphere and is further determined to be a double-layer structure.
FIG. 5 shows the preparation of the inventionThe ultraviolet-near infrared spectrum of the composite material is shown in the specification, wherein a represents a pure carbon point, b represents pure titanium dioxide, c represents pure cerium dioxide, and d represents CeO 2 :CDs/TiO 2 The nano material can absorb light better than three pure substances, and has the best utilization rate of sunlight.
FIG. 6 shows the photocurrent response of the composite material prepared by the present invention under visible light irradiation, and curve a represents pure CeO 2 A photocurrent curve of (a); curve b represents CeO 2 /TiO 2 Curve c represents CeO 2 Photocurrent curve of CDs, curve d represents CeO 2 :CDs/TiO 2 Photocurrent curves for nanomaterials. As can be seen from the figure, ceO prepared by the present invention 2 :CDs/TiO 2 The nano material has the strongest photoresponse current capable of repeatedly responding, and shows that CeO 2 :CDs/TiO 2 The nanomaterial internal resistance is the smallest and the photocurrent the most stable.
3. Nano material photocatalysis performance test
100mL of RhB (C) was taken 0 = 1×10 -5 M), adding 50mg of photocatalyst into the suspension, and continuously stirring the suspension for 30min under dark conditions to ensure that the catalyst and the RhB reach adsorption-desorption equilibrium. At regular intervals, 4mL of the suspension was taken, centrifuged to remove the precipitate and the RhB concentration was further analyzed using a uv spectrophotometer to record absorbance at 553 nm.
FIG. 7 shows the photocatalytic performance curves of different comparative materials, curve a representing pure CeO 2 The performance curve of the photocatalytic degradation of RhB; curve b represents CeO 2 /TiO 2 The curve c represents CeO 2 The performance curve of photocatalytic degradation of CDs to RhB, and the curve d represents CeO 2 :CDs/TiO 2 Performance curve of nano material for photocatalytic degradation of RhB.
It is clearly observed from the figure that 2 Compared with three composite materials, the photocatalytic performance of the composite material is improved to different degrees, wherein CeO 2 :CDs/TiO 2 Photocatalytic activity of composite materialRelatively pure CeO 2 Significantly improved by CeO 2 :CDs/TiO 2 The degradation rate of the composite material to RhB reaches 95.52 percent under the irradiation of a xenon lamp with the wavelength of more than or equal to 420nm for 2 hours.
The results of these experiments show that: ceO prepared by the method of the invention 2 :CDs/TiO 2 The nanometer material effectively changes the internal electron transmission of the material, and improves the electron transmission efficiency and the collection efficiency; the utilization rate of sunlight is enhanced, and the time for degrading RhB by photocatalysis is obviously shortened.

Claims (3)

1. CeO (CeO) 2 :CDs/TiO 2 The preparation method of the nano material is characterized by comprising the following steps:
(1) Adding a sodium citrate solution into the urea solution to obtain a mixed solution of urea and sodium citrate;
(2) Adding cerous chloride into the mixed solution obtained in the step (1), uniformly stirring, slowly adding hydrogen peroxide, and stirring;
(3) Carrying out reaction on the mixed solution obtained in the step (2) by adopting a hydrothermal method, cooling, centrifugally cleaning and drying after the reaction is finished to obtain CeO 2
(4) The CeO obtained in the step (3) 2 Adding the mixture into a carbon point CDs solution, and stirring for 12 hours;
(5) Filtering and drying the solution obtained in the step (4), putting the solution into ethanol, adding tetrabutyl titanate, stirring, centrifugally cleaning and drying to obtain the CeO 2 :CDs/TiO 2 A nanomaterial;
wherein the mass ratio of urea to sodium citrate to cerous chloride is 5;
CeO 2 the mass ratio of the carbon point solution to the carbon point solution is 1;
the mass ratio of the cerous chloride to the hydrogen peroxide is 4;
the hydrothermal reaction temperature is 180 ℃ and the time is 22 hours;
the mass ratio of tetrabutyl titanate to cerous chloride is 10.
2. Prepared by the process of claim 1CeO 2 :CDs/TiO 2 And (3) nano materials.
3. CeO prepared by the method of claim 1 2 :CDs/TiO 2 The application of the nano material in photocatalytic degradation of rhodamine B.
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Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103212400A (en) * 2013-03-06 2013-07-24 山东大学 Cerium oxide/titanium dioxide nano belt surface heterostructure photocatalyst with capture-catalysis performance and preparation method thereof
CN103252201A (en) * 2012-02-17 2013-08-21 国家纳米科学中心 Au@CeO2 nanocomposite material having hollow core-shell structure, and preparation method thereof
CN104907060A (en) * 2015-04-24 2015-09-16 宿州学院 CeO2 / TiO2 heterojunction nano flower preparation method
CN106179304A (en) * 2016-07-28 2016-12-07 南昌航空大学 A kind of CeO possessing photo catalytic reduction performance2tiO2the preparation method of nano composite material
CN106277023A (en) * 2016-07-29 2017-01-04 扬州大学 The preparation method and applications of double-decker CeO2 nano-hollow ball
CN107243340A (en) * 2017-06-22 2017-10-13 南昌航空大学 A kind of preparation method of ceric oxide nanorod doping titanium dioxide nano particle photochemical catalyst

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103252201A (en) * 2012-02-17 2013-08-21 国家纳米科学中心 Au@CeO2 nanocomposite material having hollow core-shell structure, and preparation method thereof
CN103212400A (en) * 2013-03-06 2013-07-24 山东大学 Cerium oxide/titanium dioxide nano belt surface heterostructure photocatalyst with capture-catalysis performance and preparation method thereof
CN104907060A (en) * 2015-04-24 2015-09-16 宿州学院 CeO2 / TiO2 heterojunction nano flower preparation method
CN106179304A (en) * 2016-07-28 2016-12-07 南昌航空大学 A kind of CeO possessing photo catalytic reduction performance2tiO2the preparation method of nano composite material
CN106277023A (en) * 2016-07-29 2017-01-04 扬州大学 The preparation method and applications of double-decker CeO2 nano-hollow ball
CN107243340A (en) * 2017-06-22 2017-10-13 南昌航空大学 A kind of preparation method of ceric oxide nanorod doping titanium dioxide nano particle photochemical catalyst

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
Double-shell CeO2@TiO2 hollow spheres composites with enhanced light harvesting and electron transfer in dye-sensitized solar cells;Jingyi Bai,等;《Journal of Alloys and Compounds》;20170610;第864-871页 *
Wood powder-derived quantum dots for CeO2 photocatalytic and anticounterfeit applications;Xinchao Gong,等;《Optical Materials》;20190821;第109302页 *

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