CN111790421B - Graphite-phase carbon nitride modified fabric visible-light-driven photocatalyst and one-step preparation method and application thereof - Google Patents

Graphite-phase carbon nitride modified fabric visible-light-driven photocatalyst and one-step preparation method and application thereof Download PDF

Info

Publication number
CN111790421B
CN111790421B CN202010560231.3A CN202010560231A CN111790421B CN 111790421 B CN111790421 B CN 111790421B CN 202010560231 A CN202010560231 A CN 202010560231A CN 111790421 B CN111790421 B CN 111790421B
Authority
CN
China
Prior art keywords
fabric
light
graphite
carbon nitride
formaldehyde
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.)
Active
Application number
CN202010560231.3A
Other languages
Chinese (zh)
Other versions
CN111790421A (en
Inventor
王鹏
王宗乾
李长龙
应丽丽
程绿竹
万颖萍
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.)
Anhui Polytechnic University
Original Assignee
Anhui Polytechnic University
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 Anhui Polytechnic University filed Critical Anhui Polytechnic University
Priority to CN202010560231.3A priority Critical patent/CN111790421B/en
Publication of CN111790421A publication Critical patent/CN111790421A/en
Application granted granted Critical
Publication of CN111790421B publication Critical patent/CN111790421B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • B01J35/39
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86Catalytic processes
    • B01D53/8668Removing organic compounds not provided for in B01D53/8603 - B01D53/8665
    • 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
    • B01J27/24Nitrogen compounds
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J31/00Catalysts comprising hydrides, coordination complexes or organic compounds
    • B01J31/02Catalysts comprising hydrides, coordination complexes or organic compounds containing organic compounds or metal hydrides
    • B01J31/06Catalysts comprising hydrides, coordination complexes or organic compounds containing organic compounds or metal hydrides containing polymers
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J31/00Catalysts comprising hydrides, coordination complexes or organic compounds
    • B01J31/02Catalysts comprising hydrides, coordination complexes or organic compounds containing organic compounds or metal hydrides
    • B01J31/06Catalysts comprising hydrides, coordination complexes or organic compounds containing organic compounds or metal hydrides containing polymers
    • B01J31/069Hybrid organic-inorganic polymers, e.g. silica derivatized with organic groups
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/30Wastewater or sewage treatment systems using renewable energies
    • Y02W10/37Wastewater or sewage treatment systems using renewable energies using solar energy

Abstract

The invention provides a graphite phase carbon nitride modified fabric visible light catalyst and a one-step preparation method and application thereof. When the prepared catalyst is used for indoor air purification, pollutants such as formaldehyde and the like can be rapidly degraded, and the removal rate of the pollutants can reach more than 99% within 90 minutes; and moreover, the catalyst has excellent recycling performance and can still have excellent catalytic performance after being washed by water.

Description

Graphite-phase carbon nitride modified fabric visible-light-driven photocatalyst and one-step preparation method and application thereof
Technical Field
The invention relates to a chemical catalyst technology, in particular to a graphite phase carbon nitride modified fabricA visible light photocatalyst, a one-step preparation method and application thereof, in particular to graphite phase carbon nitride (g-C) for promoting the decomposition of organic pollutants such as indoor formaldehyde gas and the like3N4) A modified fabric visible light catalyst and a preparation method thereof.
Background
The indoor harmful gas mainly comprises formaldehyde emitted by decorative materials and the like and methyl mercaptan, hydrogen sulfide, ammonia gas and the like generated in the living environment. The formaldehyde has the most serious harm to human bodies, becomes the pollutant with the most harm in indoor pollution, has strong irritation to eyes, respiratory tracts, skin and the like of human bodies, and causes symptoms such as nausea, bronchitis, conjunctivitis and the like when contacting low-concentration formaldehyde for a long time. The nanometer titanium dioxide can decompose and oxidize air pollutants such as formaldehyde adsorbed on the surface through photocatalysis, so that the concentration of the formaldehyde in the air is reduced, and the uncomfortable feeling of the environment is relieved or eliminated.
As a cheap and environment-friendly material, nano titanium dioxide is widely used for treating harmful gases in the air environment. The nanometer titanium dioxide photocatalyst is applied to textiles, can effectively degrade toxic and harmful gases in the air under the action of illumination, can decompose and harmlessly treat toxins released by bacteria or fungi, and has the functions of deodorization, stain resistance and the like. However, the band gap of nano-titania is relatively wide (3-3.2 eV), and can only absorb about 3-5% of the UV light in sunlight, which greatly limits the application of nano-titania [ Zhang S, Li J, Zeng M, ethyl. in situ synthesis of water-soluble magnetic carbon nitride phosphor and organic synthetic carbon dioxide performance [ J ]. ACS Applied Materials & interfaces.2013,5(23): 12735-. Therefore, it is very necessary to develop a catalyst having a high efficiency of visible light response.
In recent years, graphite phase carbon nitride (g-C)3N4) Because of its visible light response (band gap of 2.7e V), simple preparation method, wide source of raw materials, no toxicity, good thermal stability, and almost no chemical corrosion by any acid or alkali, etc., it has become the hot door of photocatalytic material [ Wang X,Blechert S,Antonietti M.Polymeric Graphitic Carbon Nitride for Heterogeneous Photocatalysis[J].ACS Catalysis.2012,2(8):1596-1606.]. However g-C3N4The catalyst is a powder catalyst, and the dispersion effect of the catalyst in aqueous solution is extremely poor due to the similar graphite phase structure, namely the van der Waals force action between single-layer carbon nitrides, so that the recombination between electron hole pairs is increased, and the photocatalytic performance is reduced. In addition, the powder catalysts all face the problem of difficult recycling, resulting in poor recycling and high cost. Modification and loading of the powder catalyst is currently a more efficient and feasible process. However, g-C3N4Generally, high catalytic activity can be achieved only by high-temperature calcination treatment, which is limited to the application of fiber materials and the like which are not resistant to high temperature.
Disclosure of Invention
The invention aims to provide a graphite-phase carbon nitride modified fabric visible-light-driven photocatalyst which has higher visible-light catalytic activity than the existing catalyst with nano titanium dioxide added, and g-C3N4Is not easy to fall off, can keep better catalytic performance even in visible light conditions indoors, and has excellent reusability.
The invention also aims to provide a one-step preparation method of the graphite-phase carbon nitride modified fabric visible-light-driven photocatalyst, which is simple in preparation method, low in energy consumption and environment-friendly.
Still another object of the present invention is to provide an application of a graphite-phase carbon nitride modified fabric visible light catalyst for catalyzing an oxidative degradation reaction of indoor formaldehyde gas, so as to enable organic pollutants such as formaldehyde in indoor air to undergo an oxidative degradation reaction more rapidly, thereby purifying indoor air.
The specific technical scheme of the invention is as follows:
a one-step preparation method of a graphite phase carbon nitride modified fabric visible light catalyst comprises the following steps:
1) mixing urea and transition metal salt, and heating to obtain modified liquid;
2) and (3) placing the fabric into the modification solution, and heating for reaction to obtain the graphite-phase carbon nitride modified fabric visible-light-driven photocatalyst.
The mass ratio of the urea to the transition metal salt in the step 1) is as follows: 0.5-1.5:1.
Further, the transition metal salt in the step 1) is zinc acetate, zinc sulfate, zinc nitrate, zinc chloride or copper acetate.
The heat treatment in the step 1) means treatment at 70 ℃ to 90 ℃ for 1 to 2 hours.
After the heating reaction in the step 1), carrying out vacuum drying, wherein the vacuum drying refers to vacuum drying for 12-24 hours at the temperature of 50-70 ℃. And (4) heating, and then drying in vacuum to remove water in the system.
Further, in the step 1), the modified liquid is stored in a sealed manner.
The fabric in step 2) is preferably a polyester fabric.
The dosage ratio of the fabric to the modification liquid in the step 2) is 1: 30-60 g/ml.
The heating reaction in the step 2) refers to a reaction for 12 to 36 hours at 180 to 240 ℃ under a sealed condition. Preferably, the reaction is carried out in a high temperature, high pressure autoclave with a polytetrafluoroethylene liner.
Further, the step 2) also comprises washing and vacuum drying the obtained product after the heating reaction is finished.
The invention provides a graphite-phase carbon nitride modified fabric visible-light-driven photocatalyst which is prepared by adopting the method. The graphite-phase carbon nitride modified fabric visible-light-induced photocatalyst is g-C loaded on fabric3N4The nano-sheet layer has the load of 20-60mg/g and the appearance of the product is light yellow.
The application of the graphite-phase carbon nitride modified fabric visible-light-driven photocatalyst provided by the invention is used for catalyzing the oxidative degradation reaction of formaldehyde, and is particularly used for catalyzing the oxidative degradation reaction of formaldehyde in indoor air; the specific application method comprises the following steps: the graphite phase carbon nitride modified fabric visible light photocatalyst is made into a curtain, and the curtain is placed indoors and used for catalytic degradation of formaldehyde in indoor air.
Furthermore, the visible-light-driven photocatalyst for the graphite-phase carbon nitride modified fabric can keep better catalytic performance under the condition of weak light radiation intensity.
According to the invention, urea and a transition metal salt compound can form a eutectic solvent system through heating and melting, and after the polyester fabric is placed in the system, the polyester fiber is slightly swelled, so that urea molecules can enter and permeate the surface layer of the polyester fiber, and thus graphite-phase carbon nitride is formed under the conditions of high temperature and high pressure and is more firmly fixed on the surface of the fiber. In addition, g-C not fixed to the surface of the fiber3N4Gradually form precipitate, and the formed eutectic solvent system can greatly promote g-C3N4Thereby promoting g-C3N4Combined with polyester fiber to increase g-C3N4Is fixed on the surface of the polyester fiber. In addition, g-C is formed in the reaction3N4The ammonia byproduct is generated in the process, so that the pressure in the sealed container is increased, the reaction is accelerated, the reaction is promoted to be carried out under the low-temperature condition, and the energy consumption and the production cost are further reduced. In addition, the glass transition temperature of the amorphous region of the polyester fiber is about 67 ℃, the glass transition temperature of the crystalline region is about 81 ℃, and the crystalline and reoriented region is about 120 ℃. When the modification temperature exceeds the glass transition temperature of the polyester fiber, the molecular chain of the amorphous area of the fiber starts to move; when the temperature reaches above 120 ℃, the molecular chain motion is intensified, micropores in the amorphous region are opened to form instant holes, and the g-C size smaller than the hole size3N4The nano-sheet layer precursor (urea) also rapidly enters the instant holes to enter the fiber due to Brownian motion at high temperature, and reacts to generate g-C3N4Nanosheets, g-C due to shrinkage of micropores when temperature is reduced3N4The nanosheets are left behind in the amorphous regions of the fiber. Due to g-C3N4The modified polyester fabric catalyst is fixed on the surface of polyester fiber in the synthesis process, and the catalyst is synthesized by one-step reaction, so that the modified polyester fabric catalyst has the advantages of excellent washing fastness, simple preparation process, moderate cost, easy operation and contribution to industrial popularization. The obtained catalyst can be used for treating pollutants such as formaldehyde in indoor airThe oxidative degradation reaction has higher catalytic activity. In addition, the catalyst of the invention can maintain better catalytic performance under the condition of weak light radiation intensity, can enable pollutants in indoor air such as formaldehyde and the like to carry out oxidation degradation reaction more quickly, and can be repeatedly utilized.
The invention can control g-C in the catalyst by adjusting the concentration of urea in the modification reaction, the reaction time and the temperature3N4And (4) preparing a series of catalyst products with different properties. In general, g-C3N4The load capacity of the modified polyester fabric catalyst is mainly controlled by using the initial concentration and the reaction time of urea in the synthetic reaction process, and the g-C of the obtained catalyst is obtained when the concentration of the urea is higher3N4The higher the content. For example, when a high-loading catalyst is used, the catalyst has the highest catalytic activity and is suitable for treating high-concentration indoor formaldehyde. The catalyst product actually prepared is not limited to this content range value as required. Meanwhile, the invention can be easily made into other shapes such as small particles or microparticles by a mechanical method.
Compared with the prior art, the catalyst prepared by the invention is used for promoting the oxidative degradation reaction of indoor formaldehyde gas, has higher catalytic activity than the existing nano titanium dioxide catalyst, and can maintain better catalytic performance even under the condition of weak light radiation intensity. And g-C3N4The catalyst is not easy to fall off, can keep better catalytic performance under the condition of indoor visible light, has excellent reusability, can enable organic pollutants such as formaldehyde in indoor air to carry out oxidative degradation reaction more quickly, and purifies the indoor air. When the air purifier is used for purifying indoor air, pollutants such as formaldehyde and the like can be rapidly degraded, and the removal rate of the pollutants can reach more than 99% within 90 minutes. Furthermore, due to g-C3N4Is fixed on the surface of the polyester fiber during synthesis, so that g-C3N4The modified polyester fabric visible-light-induced photocatalyst is prepared by a one-step method, so that the modified polyester fabric visible-light-induced photocatalyst has the advantages of excellent washing resistance, simple preparation process, low cost and easiness in operation, and is beneficial to industrial popularization; has excellent recycling performance and is washed by waterBut can have excellent catalytic performance.
Drawings
FIG. 1 shows the preparation of g-C according to examples 1, 2 and 3 of the present invention3N4A modified polyester fabric catalyst load variation graph;
FIG. 2 shows the preparation of g-C according to examples 1, 2 and 3 of the present invention3N4A comparison graph of the removal effect of the modified polyester fabric catalyst and the nano titanium dioxide loaded polyester fabric in the comparative example on formaldehyde;
FIG. 3 shows catalysts g-C according to the invention3N4-3 recycling properties for formaldehyde removal;
FIG. 4 shows catalysts g-C according to the invention3N4-3 and a comparison graph of formaldehyde removal effects before and after washing of the nano titanium dioxide loaded polyester fabric in the comparative example.
Detailed Description
Specific embodiments of the present invention are described below, but the claims of the present invention are not limited to these specific embodiments.
Example 1
The one-step preparation method of the graphite-phase carbon nitride modified fabric visible-light-induced photocatalyst comprises the following steps:
1) urea and copper acetate were mixed in a ratio of 0.5: 1, treating at 90 ℃ for 2 hours, then drying at 60 ℃ for 12 hours in vacuum, and finally sealing the obtained modified solution for later use;
2) immersing the polyester fabric into the modified solution prepared in the step 1), wherein the ratio of the weight of the polyester fabric to the volume of the modified solution is 1: 50 g/ml, then placing the mixture into a high-temperature high-pressure reaction kettle with a polytetrafluoroethylene lining, sealing the kettle, carrying out modification reaction for 24 hours at the temperature of 180 ℃, naturally cooling the mixture to room temperature, and then using distilled water to react the obtained light yellow fabric-shaped g-C3N4Washing the modified polyester fabric for 3-5 times, and then drying the washed modified polyester fabric for 12 hours in vacuum at 60 ℃ to obtain the graphite-phase carbon nitride modified fabric visible-light-induced photocatalyst prepared by the one-step method, which is abbreviated as g-C3N4-1。
Example 2
The one-step preparation method of the graphite-phase carbon nitride modified fabric visible-light-induced photocatalyst comprises the following steps:
the mass ratio of urea to copper acetate is 1: 1, the rest of the same example 1; obtaining the visible-light-driven photocatalyst of graphite-phase carbon nitride modified fabric prepared by one-step method, which is abbreviated as g-C3N4-2。
Example 3
The one-step preparation method of the graphite-phase carbon nitride modified fabric visible-light-induced photocatalyst comprises the following steps:
the mass ratio of the urea to the copper acetate is 1.5:1, the remainder of the same procedure as in example 1 gave a one-step preparation of a graphite-phase carbon nitride modified textile visible-light-induced photocatalyst, abbreviated as g-C3N4-3。
The invention adopts the following method to measure the loading capacity of the obtained catalyst: weighing and recording the weight of the fabric before the reaction is started, fully washing and drying the obtained fabric after the reaction is finished, weighing and recording, and further respectively calculating g-C in the obtained catalyst3N4The loading of (a) is in mg/g.
In FIG. 1 (examples 1-3), the g-C of the catalyst prepared increases with the urea concentration3N4The load amount gradually increases. This indicates that increasing the urea concentration can increase the g-C of the fabric3N4The amount of the supported. The reason is that the urea concentration increases, the more urea micromolecules enter the interior of the polyester fiber, and g-C is generated in the reaction process3N4The more so that the catalyst loading amount is gradually increased.
Comparative example
The nano titanium dioxide hydrosol modified polyester fabric comprises the following components:
1) preparing nano titanium dioxide hydrosol: firstly, dissolving 100 ml of butyl titanate in 130 ml of absolute ethyl alcohol at room temperature to form a butyl titanate ethanol solution; while adding 8.4 g of hydrochloric acid to 870 ml of distilled water to obtain a dilute aqueous hydrochloric acid solution; then dripping the butyl titanate ethanol solution into hydrochloric acid aqueous solution at room temperature under the stirring condition; after the dropwise addition is finished, stirring is continuously carried out for 5 hours to obtain milky white water dispersion; finally, the mixture is sealed, kept stand and aged for 5 to 7 days to form yellowish and semitransparent about 1100 ml of nano titanium dioxide hydrosol.
2) Soaking the polyester fabric into the nano titanium dioxide hydrosol prepared in the step 1), wherein the using amount ratio and the reaction conditions are the same as those of the example 1.
The visible-light-induced photocatalyst for graphite-phase carbon nitride modified fabric prepared by the one-step method in examples 1 to 3 and the nano titanium dioxide loaded polyester fabric prepared in the comparative example were measured in the aspect of formaldehyde degradation catalysis, specifically as follows:
purification experiment of formaldehyde in indoor air: the catalyst fabric samples obtained in the above examples and comparative examples, each having an area of 0.06 square meter, were first fixed on sample holders on both sides of the light source of a gas-phase photochemical reactor, at a distance of 6 cm, in which 36W energy-saving lamps (light intensity in the wavelength range of 400 nm to 1000 nm: 1.20 mW/cm) were placed. Then injecting 0.01 ml of formaldehyde into the surface of a heating plate in an environmental chamber under the conditions of room temperature and relative humidity of 45 +/-3%, and simultaneously starting an axial flow fan to ensure that formaldehyde gas is fully volatilized and the adsorption balance is achieved on the surface of a sample. And then, turning on a light source to perform a formaldehyde photocatalytic degradation reaction in the air, measuring the change of the concentration of the formaldehyde gas by using a POT400 type formaldehyde gas detector (Shenzhen Wanandei science and technology Limited) at intervals, and calculating the removal rate of the formaldehyde. The structure of the gas-phase photochemical reactor is as shown in the utility model CN 206950982U.
The above-mentioned results of the formaldehyde degradation effect are shown in fig. 2, and it can be found from fig. 2 (examples 1-3 and comparative example) that the formaldehyde removal rate is gradually increased with the increase of the catalytic reaction time in the presence of the modified polyester fabrics of the three examples of the present invention, the formaldehyde removal rate can reach more than 90% after 90 minutes of reaction, and the formaldehyde removal rate is increased with the increase of the loading amount. And when the comparative example finished polyester fabric exists, the formaldehyde removal rate is only less than 20% after the reaction is carried out for 90 minutes. This shows that the formaldehyde removal rate of the catalyst of the example of the present invention is significantly higher than that of the catalyst of the comparative example. This is because the nano titanium dioxide can only absorb ultraviolet light to oxidize formaldehydeWhile the catalysts of examples 1 to 3 according to the present invention can catalyze the decomposition of formaldehyde under visible light source conditions, the comparative example can only adsorb formaldehyde, but cannot remove it by oxidation. g-C in the catalyst of the invention3N4The formaldehyde remover can absorb visible light, generate electron migration and form an electron-hole pair, so that formaldehyde is subjected to oxidative decomposition reaction, and the formaldehyde removal rate is remarkably reduced. More importantly, when the finishing fabric of 3 embodiments of the invention exists, the formaldehyde removal rate in the test chamber can reach 99.9% after the load fabric exists for 2 hours, and the formaldehyde concentration is only 0.005 mg/L, which is far lower than the requirement of national indoor air quality standard.
The g-C obtained in example 3 is given in FIG. 33N4-3, the catalyst is repeatedly applied to the change of catalytic activity in the oxidation removal reaction of formaldehyde in the air under the visible light radiation condition, and the experimental conditions are consistent with the experimental conditions for purifying formaldehyde in the indoor air. The results showed that the formaldehyde removal rate hardly changed when it was reused 5 times. This means that the catalyst still maintains high catalytic activity after being repeatedly used for five times, and can still well oxidize and remove formaldehyde in the air. The catalyst also has good reusability and wide application prospect.
The catalyst obtained in example 3 and the nano titanium dioxide-loaded polyester fabric obtained in the comparative example were washed with water, respectively, and then the formaldehyde gas-removing effect thereof was measured. Water washing experiment of the obtained catalyst: the catalyst described in the example obtained above and the nano titanium dioxide-loaded polyester fabric of the comparative example were immersed in 100 ml of 5.0 g/l soap powder aqueous solution and stirred continuously at 50 ℃ for 120 minutes, and then applied to the photocatalytic oxidation removal reaction of formaldehyde in indoor air according to the experimental conditions for purification of formaldehyde in indoor air described above, and the removal rates of formaldehyde of the samples before and after washing were respectively measured, and the results are shown in fig. 4.
FIG. 4 shows the formaldehyde removal effect of the catalyst after water washing. The results show that the formaldehyde removal effect of the loaded fabric in example 3 is hardly reduced before and after washing with water, while the nano-diThe removal effect of the titanium oxide loaded polyester fabric on formaldehyde is obviously reduced. The result shows that the terylene visible light catalyst prepared by the invention has excellent washing fastness. This is mainly because of the g-C of the invention3N4The modified terylene photocatalyst is used for synthesizing g-C3N4Is prepared by3N4Slowly synthesized and gradually enlarged, and grows on the surface of the polyester fiber, and the polyester fiber can be firmly combined and are difficult to separate. When the nano titanium dioxide is loaded on the polyester fabric in the comparative example, the nano titanium dioxide is agglomerated before entering the interior of the fiber, particles become large, more particles are difficult to inlay on the surface of the fiber, and the bonding between the particles and the fiber is not firm, so that the nano titanium dioxide almost completely falls off from the surface of the fiber after washing, and the formaldehyde removal effect is obviously reduced.
In summary, a g-C of the present invention was used3N4The modified polyester fabric visible-light-driven photocatalyst and the preparation method thereof solve the problems that the common semiconductor catalyst contains heavy metal, can only absorb ultraviolet light, has low recycling rate, high energy consumption and the like. The urea and the transition metal salt used in the invention are easy for industrial production, low in toxicity and cost, easy for large-scale storage and transportation and industrial production, and have more excellent catalytic performance, high efficiency, low cost, environment-friendly performance and the like compared with semiconductor catalysts such as nano titanium dioxide, nano zinc oxide and the like.
The above-mentioned embodiments only express the embodiments of the present invention, and the description thereof is more specific and detailed, but not construed as limiting the scope of the present invention. It should be noted that, for a person skilled in the art, several modifications can be made without departing from the inventive concept, and these modifications all fall within the scope of protection of the present invention.

Claims (8)

1. A one-step preparation method of a graphite-phase carbon nitride modified fabric visible-light-induced photocatalyst is characterized by comprising the following steps:
1) mixing urea and transition metal salt, and heating to obtain modified liquid;
2) placing the fabric in the modification solution, and heating for reaction to obtain the graphite-phase carbon nitride modified fabric visible-light-induced photocatalyst;
the mass ratio of the urea to the transition metal salt in the step 1) is as follows: 0.5-1.5: 1;
the heating reaction in the step 2) refers to a reaction for 12 to 36 hours at 180 to 240 ℃ under a sealed condition.
2. The method according to claim 1, wherein the transition metal salt in step 1) is zinc acetate, zinc sulfate, zinc nitrate, zinc chloride or copper acetate.
3. The method according to claim 1, wherein the heat treatment in step 1) is treatment at 70 ℃ to 90 ℃ for 1 to 2 hours.
4. The preparation method according to claim 1, wherein after the heating reaction in step 1), vacuum drying is performed, and the vacuum drying is performed at 50 ℃ to 70 ℃ for 12 to 24 hours.
5. The method of claim 1, wherein the fabric in step 2) is a polyester fabric.
6. The method according to claim 1, wherein the ratio of the fabric to the modifying solution in step 2) is 1: 30-60 g/ml.
7. A graphite-phase carbon nitride modified fabric visible-light-induced photocatalyst prepared by the preparation method of any one of claims 1 to 6.
8. Use of the graphite-phase carbon nitride modified fabric visible-light-induced photocatalyst prepared by the preparation method according to any one of claims 1 to 6, for catalyzing the oxidative degradation reaction of formaldehyde.
CN202010560231.3A 2020-06-18 2020-06-18 Graphite-phase carbon nitride modified fabric visible-light-driven photocatalyst and one-step preparation method and application thereof Active CN111790421B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202010560231.3A CN111790421B (en) 2020-06-18 2020-06-18 Graphite-phase carbon nitride modified fabric visible-light-driven photocatalyst and one-step preparation method and application thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202010560231.3A CN111790421B (en) 2020-06-18 2020-06-18 Graphite-phase carbon nitride modified fabric visible-light-driven photocatalyst and one-step preparation method and application thereof

Publications (2)

Publication Number Publication Date
CN111790421A CN111790421A (en) 2020-10-20
CN111790421B true CN111790421B (en) 2022-07-12

Family

ID=72803567

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202010560231.3A Active CN111790421B (en) 2020-06-18 2020-06-18 Graphite-phase carbon nitride modified fabric visible-light-driven photocatalyst and one-step preparation method and application thereof

Country Status (1)

Country Link
CN (1) CN111790421B (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113926481A (en) * 2021-09-29 2022-01-14 东华大学 CNC/g-C3N4Nanocomposite material, preparation and application thereof

Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106223009A (en) * 2016-07-26 2016-12-14 东华大学 A kind of visible light catalyst self-cleaning antibacterial fabric and preparation thereof and application
CN107088434A (en) * 2017-06-22 2017-08-25 武汉纺织大学 A kind of g C3N4‑Cu2The preparation method and applications of O catalyst
CN107469869A (en) * 2017-08-23 2017-12-15 浙江理工大学 A kind of preparation method of photocatalytic fiber net
CN108654674A (en) * 2018-05-09 2018-10-16 浙江理工大学 A kind of photoresponse multifunctional fibrous material and its preparation method and application
CN108855172A (en) * 2017-05-09 2018-11-23 中国计量大学 The application of support type class graphite phase carbon nitride photochemical catalyst and its Photocatalytic Degradation of Formaldehyde
CN108927198A (en) * 2018-07-09 2018-12-04 华南理工大学 A kind of method that modified carbon nitride photocatalyst and its preparation synthesize xylonic with photochemical catalytic oxidation xylose
US10377631B1 (en) * 2018-04-25 2019-08-13 Charles Montross Catalyst solvents for carbon nitride

Patent Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106223009A (en) * 2016-07-26 2016-12-14 东华大学 A kind of visible light catalyst self-cleaning antibacterial fabric and preparation thereof and application
CN108855172A (en) * 2017-05-09 2018-11-23 中国计量大学 The application of support type class graphite phase carbon nitride photochemical catalyst and its Photocatalytic Degradation of Formaldehyde
CN107088434A (en) * 2017-06-22 2017-08-25 武汉纺织大学 A kind of g C3N4‑Cu2The preparation method and applications of O catalyst
CN107469869A (en) * 2017-08-23 2017-12-15 浙江理工大学 A kind of preparation method of photocatalytic fiber net
US10377631B1 (en) * 2018-04-25 2019-08-13 Charles Montross Catalyst solvents for carbon nitride
CN108654674A (en) * 2018-05-09 2018-10-16 浙江理工大学 A kind of photoresponse multifunctional fibrous material and its preparation method and application
CN108927198A (en) * 2018-07-09 2018-12-04 华南理工大学 A kind of method that modified carbon nitride photocatalyst and its preparation synthesize xylonic with photochemical catalytic oxidation xylose

Non-Patent Citations (4)

* Cited by examiner, † Cited by third party
Title
Molten-salt synthesis of g-C3N4-Cu2O heterojunctions with highly enhanced photocatalytic performance;Shiyu Zuo et al.;《Colloids and Surfaces A》;20180305;第546卷;摘要、第4节 *
光催化技术构建功能性纺织物在环境污染中的应用;张普智等;《化工设计通讯》;20200128(第01期);第241-243页 *
加热温度对尿素水溶液制备类石墨相氮化碳的影响及其机理;张华森等;《硅酸盐学报》;20171102(第02期);第125-131页 *
基于浸染工艺的纳米TiO2负载涤纶织物的制备及性能研究;陈震雷;《中国优秀硕士学位论文全文数据库 工程科技I辑》;20170815(第8期);第2. 3、3.1.1节,第29页第3段 *

Also Published As

Publication number Publication date
CN111790421A (en) 2020-10-20

Similar Documents

Publication Publication Date Title
Meng et al. Construction of g-C3N4/ZIF-67 photocatalyst with enhanced photocatalytic CO2 reduction activity
CN110339853B (en) C3N5Material, preparation method and application thereof
Wang et al. Polydopamine mediated modification of manganese oxide on melamine sponge for photothermocatalysis of gaseous formaldehyde
CN109759110A (en) A kind of N doping porous carbon loaded titanium dioxide photocatalyst and the preparation method and application thereof
Li et al. Surface hydroxylation of TiO2/g-C3N4 photocatalyst for photo-Fenton degradation of tetracycline
CN113164867B (en) Application of fullerene and fullerene derivative composite material in degrading formaldehyde and indoor VOCs or inhibiting bacteria
CN106861758B (en) A kind of preparation method of the MOF catalyst for PHOTOCATALYTIC AIR-PURIFYING
CN113926443B (en) Multi-component composite material for removing aldehyde through visible light catalysis, preparation method and air purifier
CN113908875B (en) Preparation method of visible light catalytic material and method for degrading air pollutants
CN109331817A (en) It is a kind of for decomposing the catalysis material and preparation method of organic matter in air
Wu et al. Study on TiO2/g-C3N4 S-Scheme heterojunction photocatalyst for enhanced formaldehyde decomposition
CN115197591A (en) Visible light catalytic composite material and preparation method thereof
Mohamed et al. Hollow N-TiO2/MnO2 nanocomposite based yeast biomass for gaseous formaldehyde degradation under visible light
CN111790421B (en) Graphite-phase carbon nitride modified fabric visible-light-driven photocatalyst and one-step preparation method and application thereof
Wang et al. Facile fabrication of the Ag nanoparticles decorated graphitic carbon nitride photocatalyst film for indoor air purification under visible light
CN108525651B (en) Preparation method of reduced titanium dioxide with high photocatalytic activity
Ping et al. Flexible TiO2 nanograss array film decorated with oxygen vacancies introduced by facile chemical reduction and their photocatalytic activity
Gu et al. One-step solvothermal synthesis of Au-TiO2 loaded electrospun carbon fibers to enhance photocatalytic activity
CN113101980A (en) TiO with visible light catalytic activity2Preparation method and application of/UiO-66 composite material
CN103752301B (en) Receiving bore alkali metal/titanates of alkali-earth metals photochemical catalyst and preparation method thereof
Qi-Jin et al. Heterogeneous photocatalytic degradation kinetic of gaseous ammonia over nano-TiO2 supported on latex paint film
CN115155624A (en) Heterojunction composite material for visible light catalysis aldehyde removal, preparation method thereof and method for visible light catalysis degradation of VOCs
CN113713826A (en) Fe3+/CoWO4Composite acoustic catalyst and preparation method and application thereof
CN102847558B (en) Method for preparing conjugated polyene/nano titanium dioxide visible-light-induced photocatalyst by taking natural rubber as raw material
CN111054349A (en) Preparation method of black porous zinc oxide photocatalyst

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