CN116870920A - Preparation method and application of cuprous oxide-vanadium dioxide/vanadium pentoxide photocatalyst - Google Patents

Preparation method and application of cuprous oxide-vanadium dioxide/vanadium pentoxide photocatalyst Download PDF

Info

Publication number
CN116870920A
CN116870920A CN202311150334.2A CN202311150334A CN116870920A CN 116870920 A CN116870920 A CN 116870920A CN 202311150334 A CN202311150334 A CN 202311150334A CN 116870920 A CN116870920 A CN 116870920A
Authority
CN
China
Prior art keywords
photocatalyst
vanadium
cuprous oxide
vanadium pentoxide
preparation
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
CN202311150334.2A
Other languages
Chinese (zh)
Other versions
CN116870920B (en
Inventor
乐树坤
王鹏
刘全生
周华从
李娜
***
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Inner Mongolia University of Technology
Original Assignee
Inner Mongolia University of Technology
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Inner Mongolia University of Technology filed Critical Inner Mongolia University of Technology
Priority to CN202311150334.2A priority Critical patent/CN116870920B/en
Publication of CN116870920A publication Critical patent/CN116870920A/en
Application granted granted Critical
Publication of CN116870920B publication Critical patent/CN116870920B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • 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
    • 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
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/76Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/84Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J23/847Vanadium, niobium or tantalum or polonium
    • B01J23/8472Vanadium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/08Heat treatment
    • B01J37/10Heat treatment in the presence of water, e.g. steam
    • 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
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/722Oxidation by peroxides
    • 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
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/725Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
    • 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
    • C02F2101/34Organic compounds containing oxygen
    • 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
    • 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

The invention discloses a preparation method and application of a cuprous oxide-vanadium dioxide/vanadium pentoxide photocatalyst, which relate to the technical field of photocatalyst preparation and specifically comprise the following steps: s1: preparation of Cu 2 O; s2: preparing a cuprous oxide-vanadium dioxide/vanadium pentoxide composite material: cu is taken out 2 Dispersing O in deionized waterAdding vanadium pentoxide, isopropanol and benzyl alcohol, stirring vigorously to obtain a mixed solution B, transferring the mixed solution B into a hydrothermal reaction kettle for constant-temperature reaction, cooling to room temperature after the reaction is finished, washing with deionized water and absolute ethyl alcohol for 3 times, drying, and grinding to obtain the cuprous oxide-vanadium dioxide/vanadium heptaoxide photocatalyst. The photocatalyst has stable performance, good effect on degrading metronidazole, high light source utilization rate, low price of all raw materials, no pollution, simple preparation and low energy consumption, has good application prospect in solving the environmental pollution, energy crisis and photocatalysis application field, and can be produced in a large scale.

Description

Preparation method and application of cuprous oxide-vanadium dioxide/vanadium pentoxide photocatalyst
Technical Field
The invention relates to the technical field of photocatalyst preparation, in particular to a preparation method and application of a cuprous oxide-vanadium dioxide/vanadium heptaoxide photocatalyst.
Background
Along with the development of scientific technology, the usage amount of antibiotics in agriculture and medicine is gradually increased, so that the content of metronidazole in the ecological environment is also gradually increased, and the situation of general exceeding standard exists. The problem of environmental metronidazole pollution treatment is a worldwide problem, and the traditional technology such as adsorption, biological treatment, semi-permeable membranes and the like is difficult to completely degrade the metronidazole in the ecological environment, and has the advantages of high cost, slow reaction, easy secondary pollution, incapability of completely eliminating pollutants and the like.
The photocatalysis technology using the semiconductor and the derivative material thereof as media is a sustainable, pollution-free, economical and effective means, and can utilize clean and sustainable solar energy to treat toxic substances such as waste water, waste gas and the like in the environment, thereby improving the environmental cleanliness and effectively solving the environmental problems facing the human society. The vanadium-based catalyst has the advantages of low cost, good biocompatibility, easy acquisition, easy synthesis, good electrical and optical properties and the like, but the problems of complex preparation process, low light source utilization rate, limited catalytic properties and the like are generally existed.
Based on the above, the photocatalyst which is simple to prepare, excellent in catalytic performance and high in light source utilization rate is provided, and the technical problem to be solved by the person in the field is needed.
Disclosure of Invention
Aiming at the problems, the invention provides a preparation method and application of a cuprous oxide-vanadium dioxide/vanadium heptaoxide photocatalyst.
In order to achieve the above purpose, the technical scheme adopted by the invention is as follows:
as shown in fig. 1, the invention provides a preparation method of an ultrathin sheet cuprous oxide-vanadium dioxide/vanadium heptaoxide photocatalyst, which specifically comprises the following steps:
s1: preparation of Cu 2 O: weighing anhydrous copper sulfate, potassium sodium tartrate and sodium hydroxide in a beaker, adding deionized water, stirring for 10min, and obtaining a mixed solution A after the solution is blue-black; transferring the mixed solution A into a beaker containing glucose, continuously stirring, vacuum filtering after the solution presents bright red, washing a filter cake, and drying to obtain Cu 2 O;
S2: preparing a cuprous oxide-vanadium dioxide/vanadium pentoxide composite material: taking a certain amount of Cu prepared in the step S1 2 Dispersing O in deionized water, adding vanadium pentoxide, isopropanol and benzyl alcohol, vigorously stirring to obtain a mixed solution B, transferring the mixed solution B into a hydrothermal reaction kettle with a polytetrafluoroethylene lining, carrying out constant-temperature reaction in an electric blast drying box, cooling to room temperature after the reaction is finished, washing with deionized water and absolute ethyl alcohol for 3 times, drying, and grinding to obtain the cuprous oxide-vanadium dioxide/vanadium pentoxide photocatalyst.
Further, in the step S1, the mass ratio of the copper sulfate pentahydrate, the potassium sodium tartrate, the sodium hydroxide to the glucose is 1.2:1.2:1:1.
Further, in the step S1, the volume of deionized water is 200mL.
Further, in the step S2, the volume of deionized water is 36mL, the mass of vanadium pentoxide is 1.82g, the volume of isopropanol is 12.5mL, and the volume of benzyl alcohol is 1.5mL; the volume of polytetrafluoroethylene was 100mL.
Further, in the step S2, cu 2 The mass of O is one of 0.1274g, 0.2867g, 0.4915g and 0.7646 g.
Further, in the step S2, the stirring speed is 1100rpm, the isothermal reaction temperature is 180 ℃, the isothermal reaction time is 48 hours, the drying temperature is 80 ℃, and the drying time is 12 hours.
The invention also provides application of the cuprous oxide-vanadium dioxide/vanadium heptaoxide photocatalyst, and the photocatalyst is used for catalyzing and degrading metronidazole under visible light.
Further, the mass ratio of the photocatalyst to the metronidazole is 6:1.
Compared with the prior art, the invention has the beneficial effects that:
the method of the invention uses a one-step hydrothermal method to prepare cuprous oxide and VO 2 /V 3 O 7 The combination utilizes cuprous oxide to promote the transmission of photo-generated charge, accelerates the rapid separation of photo-generated electrons and holes, further promotes the conversion of persulfate to sulfate free radicals, and simultaneously ensures that the catalyst has good recoverability due to the mutual conversion of metals with different valence states. The photocatalyst composite material prepared by the method has stable performance, good effect on degrading metronidazole, high light source utilization rate, low price of all used raw materials, no pollution, simple preparation and low energy consumption, has good application prospect in solving environmental pollution, energy crisis and photocatalysis application fields, and can be produced in a large scale.
Drawings
FIG. 1 is a Cu of the present invention 2 O-VO 2 /V 3 O 7 Scanning electron microscope images of the samples;
FIG. 2 is a graph showing the effect of different catalysts of the present invention on photocatalytic metronidazole degradation under visible light.
Detailed Description
The present invention will be described in further detail with reference to examples in order to make the objects and advantages of the present invention more apparent. It should be understood that the specific embodiments described herein are for purposes of illustration only and are not intended to limit the scope of the invention.
The instruments, reagents, materials, etc. used in the following examples are conventional instruments, reagents, materials, etc. known in the art, and are commercially available. The experimental methods, detection methods, and the like in the following examples are conventional experimental methods, detection methods, and the like existing in the prior art unless otherwise specified.
Example 1
The present embodiment provides a Cu 2 O-VO 2 /V 3 O 7 The preparation method of the photocatalyst specifically comprises the following steps:
s1: preparation of Cu 2 O: 7.2g of copper sulfate pentahydrate, 7.2g of potassium sodium tartrate and 6g of sodium hydroxide are weighed into a 250mL beaker, 200mL of deionized water is added, and stirring is carried out for 10min, and after the solution is blue-black, a mixed solution A is obtained; transferring the mixed solution A into a 250mL beaker containing 6g of glucose, continuously stirring, vacuum filtering after the solution presents bright red, washing a filter cake, and drying to obtain Cu 2 O;
S2: preparation of Cu 2 O-VO 2 /V 3 O 7 Composite material: 0.1274g of Cu prepared in step S1 is taken 2 O is dispersed in 36mL of deionized water, 1.82g of vanadium pentoxide, 12.5mL of isopropanol and 1.5mL of benzyl alcohol are added, and the mixture is vigorously stirred at 1100rpm to obtain a mixed solution B; transferring the mixed solution B into a hydrothermal reaction kettle with a 100mL polytetrafluoroethylene lining, reacting for 48 hours at the constant temperature of 180 ℃ in an electric blowing drying box, cooling to room temperature after the reaction is finished, washing for 3 times by deionized water and absolute ethyl alcohol, drying for 12 hours at 80 ℃, and grinding to obtain 10wt%Cu 2 O-VO 2 /V 3 O 7 The photocatalyst, designated 10-Cu-V.
The embodiment also provides a Cu as described above 2 O-VO 2 /V 3 O 7 Application of photocatalyst for catalytic degradation of metronidazole under visible light, wherein the mass ratio of photocatalyst to metronidazole is 6:1。
Example 2
The present embodiment provides a Cu 2 O-VO 2 /V 3 O 7 The preparation method of the photocatalyst specifically comprises the following steps:
s1: preparation of Cu 2 O: 7.2g of copper sulfate pentahydrate, 7.2g of potassium sodium tartrate and 6g of sodium hydroxide are weighed into a 250mL beaker, 200mL of deionized water is added, and stirring is carried out for 10min, and after the solution is blue-black, a mixed solution A is obtained; transferring the mixed solution A into a 250mL beaker containing 6g of glucose, continuously stirring, vacuum filtering after the solution presents bright red, washing a filter cake, and drying to obtain Cu 2 O;
S2: preparation of Cu 2 O-VO 2 /V 3 O 7 Composite material: 0.2867g of Cu prepared in step S1 is taken 2 O is dispersed in 36mL of deionized water, 1.82g of vanadium pentoxide, 12.5mL of isopropanol and 1.5mL of benzyl alcohol are added, and the mixture is vigorously stirred at 1100rpm to obtain a mixed solution B; transferring the mixed solution B into a hydrothermal reaction kettle with a 100mL polytetrafluoroethylene lining, reacting for 48 hours at the constant temperature of 180 ℃ in an electric blowing drying box, cooling to room temperature after the reaction is finished, washing for 3 times by deionized water and absolute ethyl alcohol, drying for 12 hours at 80 ℃, and grinding to obtain 20wt% Cu 2 O-VO 2 /V 3 O 7 The photocatalyst, designated 20-Cu-V.
The embodiment also provides a Cu as described above 2 O-VO 2 /V 3 O 7 The photocatalyst is used for catalyzing and degrading metronidazole under visible light, wherein the mass ratio of the photocatalyst to the metronidazole is 6:1.
Example 3
The present embodiment provides a Cu 2 O-VO 2 /V 3 O 7 The preparation method of the photocatalyst specifically comprises the following steps:
s1: preparation of Cu 2 O: 7.2g of copper sulfate pentahydrate, 7.2g of potassium sodium tartrate and 6g of sodium hydroxide are weighed into a 250mL beaker, 200mL of deionized water is added, and stirring is carried out for 10min, and after the solution is blue-black, a mixed solution A is obtained; transfer mixture A to 250mL containing 6g glucoseContinuously stirring in a beaker, vacuum filtering after the solution presents bright red, washing a filter cake, and drying to obtain Cu 2 O;
S2: preparation of Cu 2 O-VO 2 /V 3 O 7 Composite material: 0.4915g of Cu prepared in step S1 is taken 2 O is dispersed in 36mL of deionized water, 1.82g of vanadium pentoxide, 12.5mL of isopropanol and 1.5mL of benzyl alcohol are added, and the mixture is vigorously stirred at 1100rpm to obtain a mixed solution B; transferring the mixed solution B into a hydrothermal reaction kettle with a 100mL polytetrafluoroethylene lining, reacting for 48 hours at the constant temperature of 180 ℃ in an electric blowing drying box, cooling to room temperature after the reaction is finished, washing for 3 times by deionized water and absolute ethyl alcohol, drying for 12 hours at 80 ℃, and grinding to obtain 30wt% Cu 2 O-VO 2 /V 3 O 7 The photocatalyst, designated 30-Cu-V.
The embodiment also provides a Cu as described above 2 O-VO 2 /V 3 O 7 The photocatalyst is used for catalyzing and degrading metronidazole under visible light, wherein the mass ratio of the photocatalyst to the metronidazole is 6:1.
Example 4
The present embodiment provides a Cu 2 O-VO 2 /V 3 O 7 The preparation method of the photocatalyst specifically comprises the following steps:
s1: preparation of Cu 2 O: 7.2g of copper sulfate pentahydrate, 7.2g of potassium sodium tartrate and 6g of sodium hydroxide are weighed into a 250mL beaker, 200mL of deionized water is added, and stirring is carried out for 10min, and after the solution is blue-black, a mixed solution A is obtained; transferring the mixed solution A into a 250mL beaker containing 6g of glucose, continuously stirring, vacuum filtering after the solution presents bright red, washing a filter cake, and drying to obtain Cu 2 O;
S2: preparation of Cu 2 O-VO 2 /V 3 O 7 Composite material: 0.7646g of Cu prepared in step S1 is taken 2 O is dispersed in 36mL of deionized water, 1.82g of vanadium pentoxide, 12.5mL of isopropanol and 1.5mL of benzyl alcohol are added, and the mixture is vigorously stirred at 1100rpm to obtain a mixed solution B; transfer mix B to hydrothermal with 100mL polytetrafluoroethylene linerIn a reaction kettle, carrying out constant-temperature reaction for 48h at 180 ℃ in an electric blast drying box, cooling to room temperature after the reaction is finished, washing for 3 times with deionized water and absolute ethyl alcohol, drying for 12h at 80 ℃, and grinding to obtain 40wt% Cu 2 O-VO 2 /V 3 O 7 The photocatalyst, designated 40-Cu-V.
The embodiment also provides a Cu as described above 2 O-VO 2 /V 3 O 7 The photocatalyst is used for catalyzing and degrading metronidazole under visible light, wherein the mass ratio of the photocatalyst to the metronidazole is 6:1.
Comparative example 1
Pure Cu 2 The preparation method of the O photocatalyst comprises the following steps: 7.2g of copper sulfate pentahydrate, 7.2g of potassium sodium tartrate and 6g of sodium hydroxide are weighed and placed in a 250mL beaker, dissolved in 200mL deionized water, stirred for 10min, and after the solution is blue-black, a mixed solution A is obtained; transfer mixture a to a 250ml beaker containing 6g glucose; continuously stirring, and vacuum filtering after the solution presents bright red; washing the filter cake, and drying to obtain the required Cu 2 O。
Comparative example 2
VO 2 /V 3 O 7 The preparation method of the photocatalyst comprises the following steps: dispersing 1.82g of vanadium pentoxide in 36mL of deionized water, adding 12.5mL of isopropanol and 1.5mL of benzyl alcohol, vigorously stirring to obtain a mixed solution, transferring the mixed solution into a hydrothermal reaction kettle for constant temperature reaction, cooling to room temperature after the reaction is finished, washing, drying and grinding to obtain VO 2 /V 3 O 7 A catalyst.
The photocatalysts prepared in the above examples 1-4 and comparative examples 1-2 are used for degrading and dissolving metronidazole under the condition of visible light, and the specific steps are as follows: 15mg of photocatalyst sample is taken and added into 50mL of 50mg/L metronidazole solution (the dosage ratio of the metronidazole to the mass of the photocatalyst is 1:6), ultrasound is carried out for 3min, and magnetons are added. Starting the photocatalytic instrument, starting revolution and starting stirring. The reaction system is placed in a photocatalysis instrument and stirred for 10min under the dark condition, so that the adsorption and desorption balance of the catalyst and the metronidazole is achieved. Sampling 5-6mL every five minutes, taking 2 times, after sampling,the circulating water was turned on, 10mg sodium Persulfate (PDS) was added, and the xenon lamp light source was turned on. Sampling for 4 times every 5min, and 5-6mL each time. After the experiment is finished, the light source is turned off, the photocatalytic instrument is turned off, and the circulating water is turned off. After the sample solution is filtered, an ultraviolet spectrophotometer is used for detecting absorbance, the photocatalytic degradation rate is calculated as shown in a formula 1, and the result is shown in the attached figure 2. The calculation formula is as follows:wherein C 0 At an initial concentration of C t For the concentration of metronidazole at time t, A 0 For the initial absorbance of the metronidazole solution, A t Is the absorbance of the metronidazole solution at time t.
As can be seen from FIG. 2, the 10-Cu-V photocatalyst of example 1 was able to degrade 87% of a 50mg/L metronidazole solution in 20min under irradiation with visible light. The 20-Cu-V photocatalyst of example 2 was able to degrade 93% of a 50mg/L metronidazole solution 20min under visible light irradiation. The 30-Cu-V photocatalyst of example 3 was capable of degrading 94.7% of a 50mg/L metronidazole solution under visible light irradiation for 20 min. The 40-Cu-V photocatalyst of example 4 was capable of degrading 92.2% of a 50mg/L metronidazole solution under visible light irradiation for 20 min. Cu of comparative example 1 2 Under the irradiation of visible light, the O photocatalyst can degrade 6% of 50mg/L metronidazole solution for 20 min. VO of comparative example 2 2 /V 3 O 7 The photocatalyst can degrade 25% of 50mg/L metronidazole solution in 20min under the irradiation of visible light. From this, it can be seen that Cu prepared in this example 1-4 2 O-VO 2 /V 3 O 7 The photocatalyst has good effect of degrading metronidazole, and is obviously superior to comparative examples 1-2.
In summary, the method of the embodiment uses a one-step hydrothermal method to convert cuprous oxide and VO 2 /V 3 O 7 The combination utilizes cuprous oxide to promote the transmission of photo-generated charge, accelerates the rapid separation of photo-generated electrons and holes, further promotes the conversion of persulfate to sulfate free radicals, and simultaneously ensures that the catalyst has good recoverability due to the mutual conversion of metals with different valence states. The photocatalyst composite material prepared by the method of the embodiment has stable performance and p-methyl nitrateThe azole has good degradation effect, high light source utilization rate, low price of all raw materials, no pollution, simple preparation and low energy consumption, has good application prospect in solving the environmental pollution, energy crisis and photocatalysis application fields, and can be produced on a large scale.
The foregoing description of the preferred embodiments of the invention is not intended to limit the invention to the precise form disclosed, and any such modifications, equivalents, and alternatives falling within the spirit and scope of the invention are intended to be included within the scope of the invention.

Claims (8)

1. A preparation method of a cuprous oxide-vanadium dioxide/vanadium pentoxide photocatalyst is characterized by comprising the following steps of: the method specifically comprises the following steps:
s1: preparation of Cu 2 O: weighing copper sulfate pentahydrate, potassium sodium tartrate and sodium hydroxide in a beaker, adding deionized water, stirring for 10min, and obtaining a mixed solution A after the solution is blue-black; transferring the mixed solution A into a beaker containing glucose, continuously stirring, vacuum filtering after the solution presents bright red, washing a filter cake, and drying to obtain Cu 2 O;
S2: preparing a cuprous oxide-vanadium dioxide/vanadium pentoxide composite material: taking a certain amount of Cu prepared in the step S1 2 Dispersing O in deionized water, adding vanadium pentoxide, isopropanol and benzyl alcohol, vigorously stirring to obtain a mixed solution B, transferring the mixed solution B into a hydrothermal reaction kettle with a polytetrafluoroethylene lining, carrying out constant-temperature reaction in an electric blast drying box, cooling to room temperature after the reaction is finished, washing with deionized water and absolute ethyl alcohol for 3 times, drying, and grinding to obtain the cuprous oxide-vanadium dioxide/vanadium pentoxide photocatalyst.
2. The method for preparing the cuprous oxide-vanadium dioxide/vanadium pentoxide photocatalyst, according to claim 1, which is characterized in that: in the step S1, the mass ratio of the copper sulfate pentahydrate, the potassium sodium tartrate, the sodium hydroxide and the glucose is 1.2:1.2:1:1.
3. The method for preparing the cuprous oxide-vanadium dioxide/vanadium pentoxide photocatalyst, according to claim 1, which is characterized in that: in the step S1, the volume of deionized water is 200mL.
4. The method for preparing the cuprous oxide-vanadium dioxide/vanadium pentoxide photocatalyst, according to claim 1, which is characterized in that: in the step S2, the volume of deionized water is 36mL, the mass of vanadium pentoxide is 1.82g, the volume of isopropanol is 12.5mL, and the volume of benzyl alcohol is 1.5mL; the volume of polytetrafluoroethylene was 100mL.
5. The method for preparing the cuprous oxide-vanadium dioxide/vanadium pentoxide photocatalyst, according to claim 1, which is characterized in that: in the step S2, cu 2 The mass of O is one of 0.1274g, 0.2867g, 0.4915g and 0.7646 g.
6. The method for preparing the cuprous oxide-vanadium dioxide/vanadium pentoxide photocatalyst, according to claim 1, which is characterized in that: in the step S2, the stirring speed is 1100rpm, the constant temperature reaction temperature is 180 ℃, the constant temperature reaction time is 48 hours, the drying temperature is 80 ℃, and the drying time is 12 hours.
7. The use of the cuprous oxide-vanadium dioxide/vanadium pentoxide photocatalyst prepared by the preparation method of the cuprous oxide-vanadium dioxide/vanadium pentoxide photocatalyst according to any one of claims 1-6, characterized in that: the photocatalyst is used for catalyzing and degrading metronidazole under visible light.
8. The use of a cuprous oxide-vanadium dioxide/vanadium pentoxide photocatalyst as claimed in claim 7, wherein: the mass ratio of the photocatalyst to the metronidazole is 6:1.
CN202311150334.2A 2023-09-07 2023-09-07 Preparation method and application of cuprous oxide-vanadium dioxide/vanadium pentoxide photocatalyst Active CN116870920B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202311150334.2A CN116870920B (en) 2023-09-07 2023-09-07 Preparation method and application of cuprous oxide-vanadium dioxide/vanadium pentoxide photocatalyst

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202311150334.2A CN116870920B (en) 2023-09-07 2023-09-07 Preparation method and application of cuprous oxide-vanadium dioxide/vanadium pentoxide photocatalyst

Publications (2)

Publication Number Publication Date
CN116870920A true CN116870920A (en) 2023-10-13
CN116870920B CN116870920B (en) 2023-11-21

Family

ID=88262590

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202311150334.2A Active CN116870920B (en) 2023-09-07 2023-09-07 Preparation method and application of cuprous oxide-vanadium dioxide/vanadium pentoxide photocatalyst

Country Status (1)

Country Link
CN (1) CN116870920B (en)

Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103301846A (en) * 2013-07-11 2013-09-18 中南大学 InVO4.Cu2O.TiO2 ternary complex and preparation method and application thereof
CN104495928A (en) * 2015-01-09 2015-04-08 中国科学院上海硅酸盐研究所 Preparation method of vanadium dioxide/zinc oxide nano composite powder
CN104617264A (en) * 2015-01-08 2015-05-13 南京航空航天大学 Synthetic method of high-performance one-dimensional nanostructure vanadium oxide lithium ion battery electrode material
WO2015109269A1 (en) * 2014-01-17 2015-07-23 The Board Of Regents Of The University Of Texas System Photoelectrochemical electrode with cupric/cuprous oxide coating
CN105727933A (en) * 2016-03-16 2016-07-06 新乡医学院 Bismuth tungstate-bismuth molybdate heterojunction photocatalytic material, method for preparing same and application of bismuth tungstate-bismuth molybdate heterojunction photocatalytic material
CN106732589A (en) * 2016-11-18 2017-05-31 中国计量大学 A kind of preparation method of cupric oxide/cuprous oxide/graphene nanocomposite material
CN107098429A (en) * 2017-04-12 2017-08-29 新乡医学院 A kind of BiVO4/BiPO4Composite and its preparation method and application
CN108704655A (en) * 2018-05-31 2018-10-26 武汉大学 A kind of preparation method of cuprous oxide and graphite phase carbon nitride heterojunction photocatalyst
WO2021258728A1 (en) * 2020-06-22 2021-12-30 武汉大学 Preparation method for pure phase cuprous oxide thin film having high crystalline quality
CN115155605A (en) * 2022-07-23 2022-10-11 南京信息工程大学 Novel Cu 2 O/BiVO 4 Preparation method and application of composite photocatalyst

Patent Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103301846A (en) * 2013-07-11 2013-09-18 中南大学 InVO4.Cu2O.TiO2 ternary complex and preparation method and application thereof
WO2015109269A1 (en) * 2014-01-17 2015-07-23 The Board Of Regents Of The University Of Texas System Photoelectrochemical electrode with cupric/cuprous oxide coating
CN104617264A (en) * 2015-01-08 2015-05-13 南京航空航天大学 Synthetic method of high-performance one-dimensional nanostructure vanadium oxide lithium ion battery electrode material
CN104495928A (en) * 2015-01-09 2015-04-08 中国科学院上海硅酸盐研究所 Preparation method of vanadium dioxide/zinc oxide nano composite powder
CN105727933A (en) * 2016-03-16 2016-07-06 新乡医学院 Bismuth tungstate-bismuth molybdate heterojunction photocatalytic material, method for preparing same and application of bismuth tungstate-bismuth molybdate heterojunction photocatalytic material
CN106732589A (en) * 2016-11-18 2017-05-31 中国计量大学 A kind of preparation method of cupric oxide/cuprous oxide/graphene nanocomposite material
CN107098429A (en) * 2017-04-12 2017-08-29 新乡医学院 A kind of BiVO4/BiPO4Composite and its preparation method and application
CN108704655A (en) * 2018-05-31 2018-10-26 武汉大学 A kind of preparation method of cuprous oxide and graphite phase carbon nitride heterojunction photocatalyst
WO2021258728A1 (en) * 2020-06-22 2021-12-30 武汉大学 Preparation method for pure phase cuprous oxide thin film having high crystalline quality
CN115155605A (en) * 2022-07-23 2022-10-11 南京信息工程大学 Novel Cu 2 O/BiVO 4 Preparation method and application of composite photocatalyst

Also Published As

Publication number Publication date
CN116870920B (en) 2023-11-21

Similar Documents

Publication Publication Date Title
CN112169819B (en) g-C 3 N 4 /(101)-(001)-TiO 2 Preparation method and application of composite material
Chen et al. Synergy effect between adsorption and heterogeneous photo-Fenton-like catalysis on LaFeO3/lignin-biochar composites for high efficiency degradation of ofloxacin under visible light
CN110560092B (en) MoS 2 /BiVO 4 Preparation method and application of heterojunction composite photocatalyst
CN105854863B (en) A kind of C/ZnO/TiO2The preparation method of composite Nano catalysis material
CN111672335B (en) Preparation method and application of CuO @ CuS/PVDF water treatment composite membrane
CN106140242A (en) A kind of visible-light response type boron nitride modifies carbon nitride photocatalyst and its preparation method and application
CN113262808A (en) Water-soluble graphite-phase carbon nitride nanosheet catalyst for efficiently removing formaldehyde at room temperature and preparation method thereof
CN111420668A (en) In-situ synthesis of α -Bi2O3/CuBi2O4Preparation method and application of heterojunction photocatalytic material
CN113457710A (en) PDI/g-C3N4/Bi2WO6Composite photocatalyst and preparation method and application thereof
CN114506955B (en) Microwave hydrothermal pretreatment modified carbon nitride and preparation method and application thereof
CN114054019B (en) Lithium, manganese and titanium composite oxide photocatalyst, preparation method and application thereof
CN110918099A (en) Method for treating hexavalent chromium-containing wastewater through photocatalytic reduction of nickel oxide-nickel cobaltate-black titanium dioxide composite
CN105056986A (en) Method for preparing flake shaped bismuth oxide nitrate hydroxide photocatalyst and catalyst application
CN116870920B (en) Preparation method and application of cuprous oxide-vanadium dioxide/vanadium pentoxide photocatalyst
CN111468100B (en) Preparation method of in-situ grown polyacid niobium/graphene photocatalyst and application of in-situ grown polyacid niobium/graphene photocatalyst in tetracycline degradation
CN115025783B (en) Synthetic method and application of multi-niobium oxygen cluster/ZIF-67 derivative composite material
CN113713798B (en) Preparation method of graphene quantum dot modified zinc oxide and application of degradation dye
CN110813381A (en) Composite photocatalytic material UiO-66@ BiOIO3And preparation method and application thereof
CN113244929B (en) Iron bismuth oxide Bi 2 Fe 4 O 9 Preparation method and application in organic wastewater treatment
CN115779946A (en) Boron-nitrogen co-doped titanium dioxide nanotube composite material and preparation method thereof
CN112517068B (en) Visible light catalyst for treating hexavalent chromium wastewater and synthesis method thereof
CN111744467A (en) CaTiO3/CaO/TiO2Preparation method and application of composite material
CN107737598A (en) A kind of Cu1.8Se/CuAgSe composite photocatalyst materials and preparation method thereof
CN117046515A (en) Preparation method and application of cuprous oxide composite vanadyl glycolate photocatalyst
CN116371432B (en) Composite photocatalytic nano material and preparation method and application thereof

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant