CN109158124A - A kind of carbonitride and BiOX composite photocatalyst material and preparation method thereof - Google Patents

A kind of carbonitride and BiOX composite photocatalyst material and preparation method thereof Download PDF

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Publication number
CN109158124A
CN109158124A CN201811163903.6A CN201811163903A CN109158124A CN 109158124 A CN109158124 A CN 109158124A CN 201811163903 A CN201811163903 A CN 201811163903A CN 109158124 A CN109158124 A CN 109158124A
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biox
composite photocatalyst
photocatalyst material
carbonitride
preparation
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李洪静
胡晓楠
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Fudan University
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Fudan University
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J27/00Catalysts comprising the elements or compounds of halogens, sulfur, selenium, tellurium, phosphorus or nitrogen; Catalysts comprising carbon compounds
    • B01J27/24Nitrogen compounds
    • B01J35/39
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/30Treatment of water, waste water, or sewage by irradiation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/34Organic compounds containing oxygen
    • C02F2101/345Phenols
    • 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 belongs to photocatalyst technology field, specially a kind of carbonitride and BiOX composite photocatalyst material and preparation method thereof.Composite photocatalyst material of the invention has layer structure, wherein carbonitride is denoted as g-C3N4, BiOX is denoted as BiOXaYb, X, Y=Cl, Br or I, and X ≠ Y, a+b=1;The present invention is by g-C3N4Presoma be put in Muffle furnace calcine be made g-C3N4, then mix with five water bismuth nitrates, surfactant and polyalcohol;It is added two kinds in potassium chloride, potassium bromide and liquor kalii iodide;Adjust the pH of mixed solution;Gained sample is filtered or is centrifuged, is washed to neutrality, g-C is made in dry, grinding3N4With BiOXaYbComposite photocatalyst material.The composite material has the characteristics that efficient visible light response, under the conditions of visible light shines, can efficient catalytic degrade in dirty (useless) water using bisphenol-A as the emerging organic pollutant of representative.Preparation method simple process of the present invention, operation are easy, and yield is high, low energy consumption, and preparation condition is mild, environmental-friendly.

Description

A kind of carbonitride and BiOX composite photocatalyst material and preparation method thereof
Technical field
The invention belongs to photocatalyst technology fields, and in particular to a kind of photochemical catalyst and preparation method thereof, more particularly to A kind of carbonitride (g-C3N4) and BiOX (BiOXaYb) composite photocatalyst material and preparation method thereof.
Background technique
As the Typical Representative in bismuth oxyhalide, bismuth oxychloride (BiOCl) is due to its stable chemical property, nontoxic Property, corrosion resistance, outstanding spectrochemical property and have layer structure and be widely used in photocatalysis field.But BiOCl, only to ultraviolet light response, greatly limits its practical application value due to its wider band gap.And introduce halogen atom (such as Br, I) can further improve the response to visible light.Meanwhile the non-metal semiconductive carbonitride (g-C of graphite-phase3N4) because The response to visible light is shown with relatively narrow band gap (about 2.7eV), is also applied due to its presoma cheap and easy to get It has a extensive future.However, g-C3N4Photo-generate electron-hole itself is easily compound, and photocatalytic activity will receive limitation.Therefore, BiOCl, halogen Plain atom and g-C3N4Compound efficient response to visible light can be achieved.
Traditional BiOCl preparation method usually requires high temperature and pressure, such as hydro-thermal method, and yield is lower, consumes energy higher.South China Polytechnics reports through dinectly bruning Bi2O3And C3N4Presoma and obtain a kind of g-C3N4/ bismuth system oxide is compound can Light-exposed catalyst can remove nearly 70% methyl orange (number of patent application: 201410809217.7) in 300 min;Tianjin science and technology is big Report using microwave method prepare a kind of high performance BiOCl/BiOBr catalysis material (number of patent application: 201610834479.8);Harbin Institute of Technology reports using surfactant, successfully makes under 160 DEG C of hydrothermal condition Standby Lacking oxygen high performance out enriches BiOCl-g-C3N4Hetero-junctions, and point out that the addition of surfactant can significantly increase Oxygenation vacancy (Applied Catalysis B:Environmental, 2018,220,290-302).It can be seen that BiOCl, Halogen atom, surfactant and g-C3N4The respective party face of visible light is played an important role improving catalysis material.But Up to the present, high-performance, the g-C with abundant Lacking oxygen are realized using surfactant3N4With BiOXaYbComposite material Preparation, there has been no relevant document reports.
Summary of the invention
The present invention is intended to provide a kind of simple process, operation be easy, high yield, low energy consumption, preparation condition is mild, environment is friendly Composite photocatalyst material and preparation method thereof good and with efficient visible light response.
Composite photocatalyst material provided by the invention is a kind of carbonitride (g-C3N4) and BiOX (BiOXaYb) compound Catalysis material, X, Y=Cl, Br or I, and+b=1 X ≠ Y, a;The composite photocatalyst material has layer structure.
Above-mentioned g-C3N4With BiOXaYbComposite photocatalyst material, wherein bismuth, oxygen, halogen, carbon and nitrogen each element high uniformity divide Cloth, and material has Lacking oxygen abundant.
G-C provided by the invention3N4With BiOXaYbCompound catalysis material, can be used for photocatalytic degradation municipal sewage, Emerging organic pollutant in industrial wastewater, polluted river water, is with a wide range of applications.
The present invention also provides above-mentioned g-C3N4With BiOXaYbThe preparation method of compound catalysis material, specific steps are such as Under:
(1) by quantitative g-C3N4Presoma be put in Muffle furnace, carry out calcination processing again;
It (2) again will be through the g-C of step (1) calcination processing3N4It is dissolved in water, obtains g-C3N4Aqueous solution;Ultrasonic disperse is uniform;
(3) under the conditions of 40 DEG C ~ 100 DEG C of low temperature, by the solution of step (2) and five water bismuth nitrate (Bi (NO3)3·5H2O), Surfactant and polyalcohol are uniformly mixed;
(4) be added into the solution of step (3) potassium chloride, any two kinds in potassium bromide and liquor kalii iodide it is uniformly mixed molten Liquid;
(5) pH of step (4) mixed solution is adjusted to 7.5 ~ 11.5, reaction 10min ~ for 24 hours;
(6) the resulting sample of step (5) is filtered or centrifugation, washing to neutrality, drying is ground to get g-C3N4With BiOClxI1-xComposite photocatalyst material.
In step (1), the g-C3N4Presoma be one of urea, melamine, dicyandiamide and sulphur ammonium etc. or Several, the quality of the presoma is 0.1g ~ 100g.The temperature of the calcination processing is 350 DEG C ~ 800 DEG C, and calcination time is 0.1h~ 100h;Preferred calcination temperature is 600 DEG C ~ 800 DEG C, and calcination time is 1h ~ 30h.
In step (2), the g-C3N4The concentration of aqueous solution be 0.5g/L ~ 100g/L, ultrasonic time be 10min ~ 24h;It is preferred that g-C3N4The concentration of aqueous solution is 5g/L ~ 60g/L, and ultrasonic time is 1h ~ 20h.
In step (3), the quality of the five water bismuth nitrates is 0.1g ~ 100g, and the surfactant is polyethylene Pyrrolidones (PVP), lauryl sodium sulfate, xylitol, polyacrylamide (PAM), cetyl trimethylammonium bromide (CTAB) and one or more of hexadecyltrimethylammonium chloride (CTAC) etc., dosage is 0.01g ~ 10g, and described is more First alcohol is one or more of ethyl alcohol, ethylene glycol, diethylene glycol (DEG), isopropanol and glycerine etc., and dosage is 1mL ~ 200mL.
In step (4), the concentration of the potassium chloride, potassium bromide and potassium iodide is all 0.1g/L ~ 50g/L.
The range of pH described in step (5) is 7.5 ~ 11.5, and the reaction time is 10min ~ for 24 hours.
Carbonitride (g-C prepared by the present invention3N4) and BiOX (BiOXaYb) composite photocatalyst material, it is shone in visible light Under the conditions of, can efficient catalytic degrade in dirty (useless) water using bisphenol-A as the emerging organic pollutant of representative.
The invention has the benefit that
Preparation method simple process of the present invention, operation are easy, and yield is high, low energy consumption, and preparation condition is mild, environmental-friendly.Preparation Composite photocatalyst material activity it is higher, have broader practice prospect.
Detailed description of the invention
Fig. 1 is g-C prepared by embodiment 13N4With BiOXaYbThe scanning electron microscope (SEM) of composite photocatalyst material Structure chart.
Fig. 2 is g-C prepared by embodiment 13N4With BiOXaYbThe transmission electron microscope (TEM) of composite photocatalyst material Structure chart.
Fig. 3 is g-C prepared by embodiment 13N4With BiOXaYbThe element mapping distribution map of composite photocatalyst material.
Fig. 4 is g-C prepared by embodiment 13N4With BiOXaYbComposite photocatalyst material under visible light illumination drop by photocatalysis Solve bisphenol-A.
Fig. 5 is g-C prepared by embodiment 23N4With BiOXaYbComposite photocatalyst material under visible light illumination drop by photocatalysis Solve bisphenol-A.
Fig. 6 is g-C prepared by embodiment 33N4With BiOXaYbComposite photocatalyst material under visible light illumination drop by photocatalysis Solve bisphenol-A.
Fig. 7 is g-C prepared by embodiment 43N4With BiOXaYbComposite photocatalyst material under visible light illumination drop by photocatalysis Solve bisphenol-A.
Fig. 8 is g-C prepared by embodiment 53N4With BiOXaYbComposite photocatalyst material under visible light illumination drop by photocatalysis Solve bisphenol-A.
Specific embodiment
Below in conjunction with specific example, explanation that the present invention is further elaborated, but the present invention be not limited in it is following Embodiment.
Embodiment 1
G-C of the invention3N4With BiOXaYbThe preparation method of composite photocatalyst material, comprising the following steps:
By 2gg-C3N4Presoma melamine be put in crucible with cover, calcine 2 h under the conditions of 550 DEG C with Muffle furnace. By 0.3 g g-C3N430 min of ultrasound after being mixed with the deionized water of 25 mL, to g-C under the conditions of 80 DEG C3N4Aqueous solution in Sequentially add 5.8gBi (NO3)3·5H230min is mixed after O, 0.5g PVP and 25mL glycerine, then 0.67gKCl is added dropwise With the 100mL mixed solution of the total 12mmol of 0.50g KI(KCl and KI), is adjusted under the conditions of pH is 9.0,80 DEG C and continued instead with ammonium hydroxide Answer 1h.By sample filtering and washing 3 times after reaction, then dry, grinding is to get g-C3N4With BiOXaYbComposite photocatalyst material (Fig. 1, Fig. 2 and Fig. 3).
The composite photocatalyst material is used to degrade 10 mg/L bisphenol-A (BPA) solution, when visible light shines 30 min, The degradation rate of BPA is 97.4 %(Fig. 4).
Embodiment 2
G-C in the present embodiment, in step (2)3N4Quality be 0.2 g, other each steps are same as Example 1.
The composite photocatalyst material is used to degrade 10 mg/LBPA solution, when visible light shines 30 min, the degradation of BPA Rate is 96.8 %(Fig. 5).
Embodiment 3
G-C in the present embodiment, in step (2)3N4Quality be 0.4 g, other each steps are same as Example 1.
The composite photocatalyst material is used to degrade 10 mg/LBPA solution, when visible light shines 30 min, the degradation of BPA Rate is 93.6 %(Fig. 6).
Embodiment 4
In the present embodiment, surfactant PVP is not added in step (3), other each steps are same as Example 1.
The composite photocatalyst material is used to degrade 10 mg/LBPA solution, when visible light shines 60 min, the degradation of BPA Rate is 38.8 %(Fig. 7).
Embodiment 5
In the present embodiment, do not add potassium iodide in step (4), i.e., 0.895g KCl(12 mmoL be only added) 100mL solution, Other each steps are same as Example 1.
The composite photocatalyst material is used to degrade 10 mg/LBPA solution, when visible light shines 60 min, the degradation of BPA Rate is only 4.4 %(Fig. 8).

Claims (8)

1. a kind of carbonitride and BiOX composite photocatalyst material have layer structure, wherein carbonitride g-C3N4, halogen Bismuth oxide is BiOXaYb, X, Y=Cl, Br or I, and+b=1 X ≠ Y, a.
2. carbonitride according to claim 1 and BiOX composite photocatalyst material, which is characterized in that bismuth in material, Oxygen, halogen, carbon and the distribution of nitrogen each element high uniformity.
3. a kind of preparation method of carbonitride as described in claim 1 and BiOX composite photocatalyst material, feature exist In, the specific steps are as follows:
(1) by quantitative g-C3N4Presoma is put in Muffle furnace, carries out calcination processing again;
It (2) will be through the g-C of step (1) calcination processing3N4It is dissolved in water, obtains g-C3N4Aqueous solution;Ultrasonic disperse is uniform;
(3) under the conditions of 40 DEG C ~ 100 DEG C of low temperature, by the solution of step (2) and five water bismuth nitrates, surfactant and polynary Alcohol is uniformly mixed;
(4) potassium chloride is added into the solution of step (3), any two uniformly mixed solution in potassium bromide and liquor kalii iodide;
(5) pH of step (4) mixed solution is adjusted to 7.5 ~ 11.5, reaction 10min ~ for 24 hours;
(6) the resulting sample of step (5) is filtered or centrifugation, washing to neutrality, drying is ground to get g-C3N4With BiOXaYb's Composite photocatalyst material.
4. the preparation method of carbonitride according to claim 3 and BiOX composite photocatalyst material, feature exist In, in step (1), the g-C3N4Presoma be one or more of urea, melamine, dicyandiamide and sulphur ammonium, should The quality of presoma is 0.1g ~ 100g;The calcination processing temperature be 350 DEG C ~ 800 DEG C, calcination time be 0.1h ~ 100h。
5. the preparation method of carbonitride according to claim 3 and BiOX composite photocatalyst material, feature exist In, in step (2), the g-C3N4The concentration of aqueous solution is 0.5g/L ~ 100g/L, and ultrasonic time is 10min ~ for 24 hours.
6. the preparation method of carbonitride according to claim 3 and BiOX composite photocatalyst material, feature exist In in step (3), the quality of the five water bismuth nitrate is 0.1g ~ 100g;The surfactant be polyvinylpyrrolidone, In lauryl sodium sulfate, xylitol, polyacrylamide, cetyl trimethylammonium bromide and hexadecyltrimethylammonium chloride One or more, dosage be 0.01g ~ 10g;The polyalcohol is ethyl alcohol, ethylene glycol, diethylene glycol (DEG), isopropanol and the third three One or more of alcohol etc., dosage are 1mL ~ 200mL.
7. the preparation method of carbonitride according to claim 3 and BiOX composite photocatalyst material, feature exist In in step (4), the concentration of the potassium chloride, potassium bromide and potassium iodide is all 0.1g/L ~ 50g/L.
8. carbonitride as described in claim 1 and BiOX composite photocatalyst material, in dirty (useless) water of efficient catalytic degradation In using bisphenol-A as the application in the emerging organic pollutant of representative.
CN201811163903.6A 2018-10-03 2018-10-03 A kind of carbonitride and BiOX composite photocatalyst material and preparation method thereof Pending CN109158124A (en)

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CN110756202A (en) * 2019-11-06 2020-02-07 新乡学院 Preparation method of ultrathin clustered BiOBr nano photocatalyst
CN110980867A (en) * 2019-12-09 2020-04-10 复旦大学 Sewage (rainwater) disinfection and purification treatment method by using solar energy
CN112023972A (en) * 2020-09-03 2020-12-04 上海应用技术大学 Composite photocatalytic material and preparation method and application thereof
CN112028038A (en) * 2020-09-01 2020-12-04 华东理工大学 Preparation method and application of alkalized carbon nitride nanotube

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CN110756202A (en) * 2019-11-06 2020-02-07 新乡学院 Preparation method of ultrathin clustered BiOBr nano photocatalyst
CN110980867A (en) * 2019-12-09 2020-04-10 复旦大学 Sewage (rainwater) disinfection and purification treatment method by using solar energy
CN112028038A (en) * 2020-09-01 2020-12-04 华东理工大学 Preparation method and application of alkalized carbon nitride nanotube
CN112023972A (en) * 2020-09-03 2020-12-04 上海应用技术大学 Composite photocatalytic material and preparation method and application thereof
CN112023972B (en) * 2020-09-03 2022-12-16 上海应用技术大学 Composite photocatalytic material and preparation method and application thereof

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