CN114797906B - BiOCl@Bi 2 S 3 In-situ synthesis method and application of composite material - Google Patents

BiOCl@Bi 2 S 3 In-situ synthesis method and application of composite material Download PDF

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CN114797906B
CN114797906B CN202110108476.7A CN202110108476A CN114797906B CN 114797906 B CN114797906 B CN 114797906B CN 202110108476 A CN202110108476 A CN 202110108476A CN 114797906 B CN114797906 B CN 114797906B
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CN114797906A (en
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兰东辉
陈琨
李薇
易兵
沈静
邓人杰
陈镇
伍水生
区泽堂
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Hunan Institute of Engineering
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    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J27/00Catalysts comprising the elements or compounds of halogens, sulfur, selenium, tellurium, phosphorus or nitrogen; Catalysts comprising carbon compounds
    • B01J27/06Halogens; Compounds thereof
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    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/30Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
    • B01J35/39Photocatalytic properties
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    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
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    • 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
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    • C02F2103/34Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32
    • C02F2103/343Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32 from the pharmaceutical industry, e.g. containing antibiotics
    • 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

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Abstract

The invention discloses a BiOCl@Bi 2 S 3 The in-situ synthesis method and application of the composite material comprise the following steps: dissolving bismuth source in alcohol solution to obtain solution A; (2) Vitamin B 1 Dissolving hydrochloride in water to obtain a solution B, and then adding the solution B into the solution A under stirring to obtain a mixed solution C; (3) Carrying out hydrothermal treatment on the mixed solution C, and carrying out solid-liquid separation, washing and drying to obtain the BiOCl@Bi 2 S 3 A composite material. The invention uses vitamin B 1 The hydrochloride is used as a chlorine source and a sulfur source and is used as a surfactant, and is subjected to vitamin B after bismuth oxychloride is generated 1 In-situ etching of a sulfur source decomposed by hydrochloride is beneficial to BiOCl and Bi 2 S 3 The heterojunction is built by recombination, the separation of photo-generated electrons and holes is promoted, the degradation of antibiotics and volatile organic pollutants (VOCs) can be efficiently catalyzed under the condition of visible light, and the activity of the catalyst is almost unchanged after the catalyst is recycled for many times.

Description

BiOCl@Bi 2 S 3 In-situ synthesis method and application of composite material
Technical Field
The invention belongs to the technical field of material preparation and environmental protection, and in particular relates to a BiOCl@Bi alloy 2 S 3 In-situ synthesis method of composite materialThe method is applied to visible light catalytic antibiotic degradation and VOCs degradation.
Background
The method adopts the visible light catalytic technology, directly utilizes solar energy to realize complete mineralization and degradation of toxic and harmful organic pollutants in the environment through the semiconductor photocatalytic material, is a low-cost green common technology, and has good application prospect in the field of environmental protection. The key of the visible light catalysis technology is the development of efficient and stable semiconductor catalysts. The existing semiconductor photocatalyst mainly has the following problems: (1) Part of semiconductor materials have low light absorption efficiency and can only absorb ultraviolet light (accounting for 4 percent of solar energy); (2) The photo-generated holes and electrons are easy to be combined, and the separation efficiency is low; (3) The preparation process of the photocatalyst is complex, and toxic and harmful solvents or structure directing agents are required to be introduced; (4) it is difficult to realize mass production of the photocatalyst. Therefore, the development of a green, simple and easily-produced photocatalyst synthesis method in large scale has important significance in preparing the efficient and stable visible light catalyst.
BiOCl and Bi 2 S 3 The material has a lamellar structure, and the forbidden band width is respectively 3.0-3.5 eV and 1.3-1.7 eV. The BiOCl has a larger forbidden bandwidth and usually has better photocatalytic activity only in the ultraviolet region. Bi (Bi) 2 S 3 The narrow forbidden band width is a potential photocatalyst responding to visible light, but due to the fact that the valence band and the conduction band are relatively close, the photo-generated electron-hole recombination rate is high, and the photo-generated electron-hole recombination rate is generally required to be compounded with other materials to show good catalytic activity. BiOCl and Bi have been reported in the literature 2 S 3 The heterojunction is built by compounding, so that the visible light absorption is improved, the generation of photo-generated electrons and holes is facilitated, the separation of the photo-generated electrons and the holes is promoted, and the photocatalysis performance is improved.
Currently synthesizing BiOCl and Bi 2 S 3 The composite material is prepared by a hydrolysis method, a water (solvent) thermal method, an alcohol thermal method, a soft template method, a high-temperature solid phase method, a reverse microemulsion method and the like, and is etched by a sulfur source, so that the synthesis process is complex, and acid or alkali and a surfactant are generally required to be added.
Disclosure of Invention
In order to solve the problems existing in the prior art, the invention aims to provide a BiOCl@Bi 2 S 3 In-situ synthesis method of composite material by using vitamin B 1 The hydrochloride is used as a chlorine source and a sulfur source and is used as a surfactant, and is subjected to vitamin B after bismuth oxychloride is generated 1 In-situ etching of a sulfur source decomposed by hydrochloride is beneficial to BiOCl and Bi 2 S 3 The heterojunction is built by recombination, the separation of photo-generated electrons and holes is promoted, the degradation of antibiotics and volatile organic pollutants (VOCs) can be efficiently catalyzed under the condition of visible light, and the activity of the catalyst is almost unchanged after the catalyst is recycled for many times.
In order to solve the problems, the invention adopts the following technical scheme:
BiOCl@Bi 2 S 3 The in-situ synthesis method of the composite material comprises the following steps:
(1) Dissolving a bismuth source in an alcohol solution to obtain a solution A;
(2) Vitamin B 1 Dissolving hydrochloride in water to obtain a solution B, and then adding the solution B into the solution A under stirring to obtain a mixed solution C;
(3) Carrying out hydrothermal treatment on the mixed solution C, and carrying out solid-liquid separation, washing and drying to obtain the BiOCl@Bi 2 S 3 A composite material.
Preferably, in the step (1), the bismuth source is selected from one or more of bismuth nitrate pentahydrate, bismuth chloride and bismuth citrate.
Preferably, in the step (1), the alcohol is one or more selected from methanol, ethanol, isopropanol, ethylene glycol and glycerol.
Preferably, in the step (1), the concentration of the bismuth source in the solution A is 0.05-0.2 mol/L.
Preferably, in step (2), vitamin B is present in the solution B 1 The concentration of the hydrochloride is 0.1 to 0.5mol/L.
Preferably, in step (2), the bismuth source and vitamin B 1 The molar ratio of the hydrochloride is 1-5: 1.
preferably, in the step (3), the temperature of the hydrothermal treatment is 80-160 ℃ and the time is 6-24 hours.
The invention also provides the synthesized BiOCl@Bi 2 S 3 The application of the composite material takes the composite material as a photocatalyst for degrading antibiotics or VOCs under visible light;
the method comprises the following specific steps: at room temperature, biOCl@Bi 2 S 3 The composite material is added into water with the concentration of 15-150 mg/L of antibiotics or gas with the concentration of 0.2-2 mg/L of VOCs, and the reaction is carried out for 0.1-12 h.
Preferably, the antibiotic is selected from one or more of ciprofloxacin, norfloxacin, ofloxacin, tetracycline, sulfamethoxazole, sulfadimidine and terramycin, and the BiOCl@Bi 2 S 3 The mass ratio of the composite material to the antibiotics is 1:0.01 to 0.1.
Preferably, the VOCs are selected from one or more of formaldehyde, toluene, benzene and xylene, and the BiOCl@Bi 2 S 3 The mass ratio of the composite material to the VOCs is 1: 0.005-0.05.
Compared with the prior art, the invention has the technical effects that:
1. vitamin B in the invention 1 The hydrochloride is used as a chlorine source and a sulfur source and is also used as a surfactant, so that a uniform structure is formed, and acid, alkali and the surfactant are avoided.
2. The invention adopts an in-situ synthesis method, and is covered with vitamin B after bismuth oxychloride is generated 1 And the in-situ etching of the sulfur source decomposed by the hydrochloride is beneficial to constructing a heterojunction and promoting the separation of photo-generated electrons and holes.
3. BiOCl@Bi in the invention 2 S 3 The composite material can efficiently catalyze degradation of antibiotics and VOCs under visible light, and the catalytic material can be recycled.
Detailed Description
In order to make the objects, technical solutions and advantages of the present invention more apparent, the present invention will be described in further detail with reference to specific embodiments. 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.
Example 1
At room temperature, 5mmol of bismuth nitrate pentahydrate is weighed and dissolved in 100mL of glycol solution to obtain solution A; 5mmol vitamin B 1 Dissolving hydrochloride in 10mL of water to obtain a solution B; then slowly dripping the solution B into the solution A under stirring to obtain a mixed solution C; sealing the mixed solution C in a crystallization kettle, treating at 160 ℃ for 6 hours, cooling, washing and drying to obtain a material which is BiOCl@Bi 2 S 3 -1 a composite material.
Example 2
At room temperature, 5mmol of bismuth citrate pentahydrate is weighed and dissolved in 50mL of isopropanol solution to obtain solution A; 1mmol vitamin B 1 Dissolving hydrochloride in 10mL of water to obtain a solution B; then slowly dripping the solution B into the solution A under stirring to obtain a mixed solution C; sealing the mixed solution C in a crystallization kettle, treating for 12 hours at 105 ℃, cooling, washing and drying to obtain a material which is BiOCl@Bi 2 S 3 -2 a composite material.
Example 3
Weighing 5mmol of bismuth chloride pentahydrate, and dissolving in 25mL of ethanol solution at room temperature to obtain solution A; 2mmol vitamin B 1 Dissolving hydrochloride in 10mL of water to obtain a solution B; then slowly dripping the solution B into the solution A under stirring to obtain a mixed solution C; sealing the mixed solution C in a crystallization kettle, treating at 80 ℃ for 24 hours, cooling, washing and drying to obtain a material which is BiOCl@Bi 2 S 3 -3 a composite material.
Example 4
At room temperature, 5mmol of bismuth nitrate pentahydrate is weighed and dissolved in 50mL of glycol solution to obtain solution A; 1.67mmol vitamin B 1 Dissolving hydrochloride in 10mL of water to obtain a solution B; then slowly dripping the solution B into the solution A under stirring to obtain a mixed solution C; sealing the mixed solution C in a crystallization kettle, treating at 135 ℃ for 12 hours, cooling, washing and drying to obtain a material which is BiOCl@Bi 2 S 3 -4 a composite material.
Comparative example 1
At room temperature, 5mmol of bismuth nitrate pentahydrate is weighed and dissolved in 50mL of glycol solution to obtain solution A; 2.5mmol vitamin B 1 Hydrochloride saltDissolving in 10mL of water to obtain a solution B; solution B was then slowly added dropwise to solution a with stirring, stirred for 12h, cooled, washed and dried and the resulting material was designated BiOCl.
Comparative example 2
At room temperature, 5mmol of bismuth nitrate pentahydrate is weighed and dissolved in 50mL of glycol solution to obtain solution A; will 10 mmole Na 2 S is dissolved in 30mL of water to obtain solution B; then slowly dropwise adding the solution B into the solution A under stirring, stirring for 12h, cooling, washing and drying to obtain a material which is named Bi 2 S 3
Comparative example 3
1.3g of BiOCl (5 mmol) prepared in comparative example 1 was weighed and ultrasonically dispersed in 50mL of ethylene glycol to obtain dispersion A; 1.28g of Bi prepared in comparative example 2 was weighed 2 S 3 (2.5 mmol) was ultrasonically dispersed in 20mL of water to give dispersion B; slowly dripping the dispersion liquid B into the dispersion liquid A, stirring for 12 hours, washing and drying to obtain a material which is BiOCl@Bi 2 S 3 -5。
Antibiotic degradation:
at room temperature, 40mg of the materials prepared in examples 1-4 and comparative examples 1-3 were added into 40mL of an aqueous solution containing antibiotics at a certain concentration, dispersed by light-shielding ultrasonic for 15min, subjected to dark reaction for 30min, turned on a 300W xenon lamp light source, filtered to remove the catalyst after a certain period of reaction, the residual concentration was detected, and the degradation rate was calculated as shown in Table 1:
TABLE 1 antibiotic degradation Rate data sheet
Example 1 Example 2 Example 3 Example 4 Comparative example 1 Comparative example 2 Comparative example 3
Antibiotics Ciprofloxacin Terramycin Ofloxacin Norfloxacin Norfloxacin Norfloxacin Norfloxacin
Degradation time (h) 12 7.5 4.5 1 1 1 1
Initial concentration (mg/L) 100 60 45 10 10 10 10
Residue ofConcentration (mg/L) 3.5 4.1 2.8 0.12 5.8 6.9 3.2
Degradation rate (%) 96.5 93.2 93.8 98.8 42 31 68
TABLE 2 BiOCl@Bi of example 1 2 S 3 -1 degradation cycle performance of ciprofloxacin with catalytic initial concentration of 100mg/L
Circulation for 1 time Cycling for 2 times Cycling 3 times Circulation for 4 times Cycling 5 times
Degradation rate (%) 96.5 96.3 96.0 96.0 95.8
Note that: after single use, the product is filtered, washed and dried for repeated use.
VOCs degradation:
100mg of the materials prepared in examples 1-4 and comparative examples 1-3 were added to 250mL of VOCs gas with a certain concentration at room temperature, a 300W xenon lamp light source was turned on, after a certain period of reaction, a gas sampler was used for sampling and detecting the residual concentration, and the adsorption rate was calculated as shown in Table 3:
TABLE 3 VOCs degradation Rate data sheet
Figure SMS_1
Figure SMS_2
TABLE 4 BiOCl@Bi for example 4 2 S 3 -4 photocatalytic initial concentration of 1mg/L formaldehyde gas degradation cycle usability
Circulation for 1 time Cycling for 2 times Cycling 3 times Circulation for 4 times Cycling 5 times
Degradation rate (%) 99.2 99.1 99.1 99.0 98.7
Note that: and after the single use is finished, the product is directly reused.

Claims (9)

1. BiOCl@Bi 2 S 3 The in-situ synthesis method of the composite material is characterized by comprising the following steps of:
(1) Dissolving a bismuth source in an alcohol solution to obtain a solution A;
the alcohol is one or more selected from methanol, ethanol, isopropanol, ethylene glycol and glycerol;
(2) Vitamin B 1 Dissolving hydrochloride in water to obtain a solution B, and then adding the solution B into the solution A under stirring to obtain a mixed solution C;
(3) Carrying out hydrothermal treatment on the mixed solution C, and carrying out solid-liquid separation, washing and drying to obtain the BiOCl@Bi 2 S 3 A composite material.
2. The in situ synthesis process according to claim 1, wherein: in the step (1), the bismuth source is selected from one or more of bismuth nitrate pentahydrate, bismuth chloride and bismuth citrate.
3. The in situ synthesis process according to claim 1, wherein: in the step (1), the concentration of the bismuth source in the solution A is 0.05-0.2 mol/L.
4. The in situ synthesis process according to claim 1, wherein: in the step (2), vitamin B in the solution B 1 The concentration of the hydrochloride is 0.1-0.5 mol/L.
5. A BiOCl@Bi according to claim 1 2 S 3 The in-situ synthesis method of the composite material is characterized by comprising the following steps of: in step (2), the bismuth source and vitamin B 1 The molar ratio of the hydrochloride is 1-5: 1.
6. the in situ synthesis process according to claim 1, wherein: in the step (3), the temperature of the hydrothermal treatment is 80-160 DEG C o And C, the time is 6-24 hours.
7. The BiOCl@Bi synthesized by the in-situ synthesis method as claimed in any one of claims 1 to 6 2 S 3 The application of the composite material is characterized in that: the photocatalyst is used as a photocatalyst for degrading antibiotics or VOCs under visible light;
the method comprises the following specific steps: at room temperature, biOCl@Bi 2 S 3 The composite material is added into water with the concentration of 15-150 mg/L of antibiotics or gas with the concentration of 0.2-2 mg/L of VOCs, and the reaction is carried out for 0.1-12 h.
8. The BiOCl@Bi according to claim 7 2 S 3 The application of the composite material is characterized in that: the antibiotic is selected from one or more of ciprofloxacin, norfloxacin, ofloxacin, tetracycline, sulfamethoxazole, sulfamethazine and terramycin, and the BiOCl@Bi 2 S 3 The mass ratio of the composite material to the antibiotics is 1:0.01 to 0.1.
9. The BiOCl@Bi according to claim 7 2 S 3 The application of the composite material is characterized in that: by a means ofThe VOCs are selected from one or more of formaldehyde, toluene, benzene and xylene, and the BiOCl@Bi 2 S 3 The mass ratio of the composite material to the VOCs is 1: 0.005-0.05.
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