CN110560027B - Silver halide-biotite composite photocatalyst and preparation method thereof - Google Patents

Silver halide-biotite composite photocatalyst and preparation method thereof Download PDF

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CN110560027B
CN110560027B CN201910758939.7A CN201910758939A CN110560027B CN 110560027 B CN110560027 B CN 110560027B CN 201910758939 A CN201910758939 A CN 201910758939A CN 110560027 B CN110560027 B CN 110560027B
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biotite
silver halide
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composite photocatalyst
etched
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CN110560027A (en
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刘孝恒
张敏
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Nanjing University of Science and Technology
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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
    • B01J21/00Catalysts comprising the elements, oxides, or hydroxides of magnesium, boron, aluminium, carbon, silicon, titanium, zirconium, or hafnium
    • B01J21/16Clays or other mineral silicates
    • 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
    • B01J27/06Halogens; Compounds thereof
    • B01J27/08Halides
    • B01J27/10Chlorides
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • 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
    • 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
    • B01J37/0009Use of binding agents; Moulding; Pressing; Powdering; Granulating; Addition of materials ameliorating the mechanical properties of the product catalyst
    • B01J37/0018Addition of a binding agent or of material, later completely removed among others as result of heat treatment, leaching or washing,(e.g. forming of pores; protective layer, desintegrating by heat)
    • 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
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    • 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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    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
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Abstract

The invention discloses a silver halide-biotite composite photocatalyst and a preparation method thereof. According to the method, the biotite is etched and stripped by an alkali etching method to obtain a porous biotite nanosheet, and then the silver halide and the biotite are subjected to chemical bath deposition compounding to obtain the silver halide-biotite composite photocatalyst. The invention adopts chemical stripping, and the etched biotite has a micropore structure under the alkaline condition, so that the specific surface area and active sites of the biotite are increased, most metal ions are retained, and the conductivity is improved. The silver halide-biotite composite photocatalyst is used for photocatalytic degradation of 10mg/L rhodamine B, shows excellent catalytic performance, and has a degradation rate of more than 85% in 90 min.

Description

Silver halide-biotite composite photocatalyst and preparation method thereof
Technical Field
The invention relates to a silver halide-biotite composite photocatalyst and a preparation method thereof, belonging to the technical field of nano material preparation.
Background
TiO was discovered by Fujishima and Honda in 1972 2 After the electrode can carry out photocatalytic decomposition on water under the irradiation of ultraviolet light, the photocatalytic reaction of the nano semiconductor causes extensive research.
Biotite (BIO) is a natural clay silicate mineral and has the advantages of large specific surface area, abundant reserves, good thermal stability, uniform structure and the like. The chemical formula is (Mg, Fe, Al) 3 (Al,Si) 4 O10(OH) 2 ·4H 2 O, the most common morphology of this mineral is the layered structure. Yan, t.j. et al, used for selective removal of cations in wastewater by synthesizing ultra-thin sodium iron silicate two-dimensional nanosheets [ Yan, t.j., et al (2019). "ultrarhin sodium ferric silicate 2D nanosheets:A novel and robustadsorbent for selective removal of cationic dyes in wastewater."Journal of Alloys and Compounds,784,256-265.]. Interface Modification of Attapulgite at atom-molecule level, Zhang, J, et al, for Photocatalytic Water Splitting studies, to allow Natural silicates to participate as The catalyst host in catalytic reactions [ Zhang, J., et al (2016) ] "Strong Visible Light Photocatalytic Water Splitting Based on Natural Silicate Clay Mineral: The Interface Modification of Atomic at The Atomic-Molecular level," ACS stable Chem. Eng.,4, 4601-.]. Martini-costa, et al have high efficiency in degrading diclofenac, sulfamethoxazole, trimethoprim and carbamazepine pollutants by using vermiculite photocatalysis [ Zhou, T.Z., et al (2019) ]degradation of organic contaminants diclofenac, sulfamethoxazole, trimethoprim and carbazepine by bismuth subnitrate and verticillite a pilot porous collector ". Catalysis Today, DOI:10.1016 ]. The modification modes are all that natural silicate such as biotite is used as a carrier for modification, and only simple mechanical stripping is carried out to obtain thicker biotite nanosheets.
Disclosure of Invention
The invention aims to provide a silver halide-biotite composite photocatalyst with excellent catalytic performance and a preparation method thereof.
The technical solution for realizing the purpose of the invention is as follows:
the preparation method of the silver halide-biotite composite photocatalyst comprises the following steps:
step 1, stirring and dispersing biotite in 16-20 mol/L sodium hydroxide solution, carrying out hydrothermal reaction at 160-180 ℃, and after the reaction is finished, naturally cooling, centrifuging, washing and drying to obtain alkali-etched biotite nanosheets;
and 2, dispersing the alkali-etched biotite nanosheets in water, adding silver nitrate, stirring and mixing uniformly, then adding cetyl trimethyl ammonium bromide or cetyl trimethyl ammonium chloride, carrying out water bath reaction at 50-70 ℃, centrifuging, washing and drying after the reaction is finished, thus obtaining the silver halide-biotite composite photocatalyst.
Preferably, in step 1, the mass concentration of the biotite is 10 mg/mL.
Preferably, in step 1, the biotite is magnetically stirred in the sodium hydroxide solution for more than 2 hours, and the hydrothermal reaction is more than 24 hours.
Preferably, in the step 1, the centrifugation rate is 9000r/min, and the drying temperature is 60-80 ℃.
Preferably, in the step 2, the mass ratio of the silver nitrate to the alkali-etched biotite is 1: 1.
Preferably, in step 2, the molar concentration of the hexadecyl trimethyl ammonium bromide or chloride is 8 × 10 -3 mol/L。
Preferably, in step 2, the mixing time of the silver nitrate and the biotite is more than 0.5 h.
Preferably, in the step 2, the water bath reaction time is more than 3h, the centrifugation rate is 9000r/min, and the drying temperature is 60-80 ℃.
The silver halide-biotite composite photocatalyst prepared by the method has a nanosheet structure on the microscopic scale, and the silver halide dispersedly grows on the surface of the biotite.
Compared with the prior art, the invention has the advantages that:
(1) the layered natural silicate is stripped into a very thin biotite nanosheet by chemical stripping, so that the specific surface area and the active sites are greatly increased, and the layered natural silicate can be used as a main catalyst and an excellent carrier; (2) the biotite etched under the alkaline condition has a micropore structure, and meanwhile, most metal ions are reserved, the conductivity of the biotite is improved, and the structure is reconstructed; (3) the raw material biotite is rich in resources, low in price and easy to obtain, and the pretreatment mode is simple; (4) the silver halide-biotite composite photocatalyst is used for photocatalytic degradation of 10mg/L rhodamine B, shows excellent catalytic performance, and has a degradation rate of more than 85% in 90 min.
Drawings
FIG. 1 is a scheme of the synthesis scheme of the preparation process of the present invention.
FIG. 2 is a Zeta potential diagram of the alkali-etched biotite nanosheets prepared in example 1 in an aqueous environment.
FIG. 3 is a transmission electron microscope image of the materials prepared in example 1, example 2 and example 3.
Figure 4 is an XRD diffractogram of the materials prepared in example 1, example 2 and example 3.
Fig. 5 is a graph of the photocatalytic degradation performance of the silver chloride-biotite prepared in example 2.
Fig. 6 is a graph of the photocatalytic degradation performance of the silver bromide-biotite prepared in example 3.
Detailed Description
The present invention will be described in more detail with reference to the following examples and the accompanying drawings.
FIG. 1 is a synthesis mechanism diagram of the preparation method, wherein the biotite is dispersed in a sodium oxide solution after pretreatment, stirred and mixed, transferred to a polytetrafluoroethylene reaction kettle, subjected to solvothermal reaction, centrifuged, washed and dried to obtain the alkali-etched biotite material. And dispersing the alkali-etched biotite nanosheets in deionized water, sequentially adding silver nitrate, hexadecyl trimethyl ammonium chloride or hexadecyl trimethyl ammonium bromide, stirring in a water bath, centrifuging, washing and drying to obtain the silver halide-biotite composite photocatalyst.
Example 1
Firstly, mixing 500mg of biotite with 50mL of 20mol/L sodium hydroxide solution, and stirring for 2 hours on a magnetic stirrer;
secondly, transferring the solution obtained in the first step into a 100mL polytetrafluoroethylene reaction kettle, performing hydrothermal treatment for 24 hours, taking out and naturally cooling;
and thirdly, centrifugally washing the sample obtained in the second step, and drying at 60 ℃ to obtain the alkali-etched biotite nanosheet.
Example 2
Firstly, dispersing 30mg of alkali-etched biotite in 50mL of deionized water, and performing ultrasonic dispersion for 30 min;
secondly, quantitatively adding 30mg of silver nitrate into the solution obtained in the first step, and stirring for 1 h;
thirdly, adding hexadecyl trimethyl ammonium chloride into the solution obtained in the second step, and stirring for 2 hours in a water bath at the temperature of 60 ℃;
and fourthly, centrifugally washing the sample obtained in the third step, and drying the sample in a 60 ℃ drying oven for 12 hours to obtain the AgCl-biotite composite material.
Example 3
Firstly, dispersing 30mg of alkali-etched biotite in 50mL of deionized water, and performing ultrasonic dispersion for 30 min;
secondly, quantitatively adding 30mg of silver nitrate into the solution obtained in the first step, and stirring for 1 h;
thirdly, adding hexadecyl trimethyl ammonium bromide into the solution obtained in the second step, and stirring for 2 hours in a water bath at the temperature of 60 ℃;
and fourthly, centrifugally washing the sample obtained in the third step, and drying the sample in a 60 ℃ drying oven for 12 hours to obtain the AgBr-biotite composite material.
Example 4
Firstly, dispersing 30mg of AgCl-biotite composite material in 50mL of 10mg/L rhodamine B solution, and stirring for 1h in a dark room;
secondly, placing the suspension obtained in the first step under a 300W xenon lamp (lambda is more than 420nm) for illumination, and taking 3mL of liquid at intervals of 10 minutes;
thirdly, centrifuging the liquid sample obtained in the second step for 1min at 9000r/min, and removing the catalyst;
and fourthly, detecting the centrifuged liquid obtained in the third step in an ultraviolet-visible spectrophotometer to evaluate the photocatalytic performance.
Example 5
Firstly, dispersing 30mg of AgBr-biotite composite material in 50mL of 10mg/L rhodamine B solution, and stirring for 1h in a dark room;
secondly, placing the suspension obtained in the first step under a 300W xenon lamp (lambda is more than 420nm) for illumination, and taking 3mL of liquid at intervals of 10 minutes;
thirdly, centrifuging the liquid sample obtained in the second step for 1min at 9000r/min, and removing the catalyst;
and fourthly, detecting the centrifuged liquid obtained in the third step in an ultraviolet-visible spectrophotometer to evaluate the photocatalytic performance.
Comparative example 1
Firstly, dispersing silver nitrate in 50mL of deionized water, and performing ultrasonic dispersion for 30 min;
secondly, adding hexadecyl trimethyl ammonium chloride into the solution obtained in the first step, and stirring for 2 hours in a water bath at the temperature of 80 ℃;
And thirdly, centrifugally washing the sample obtained in the second step, and drying the sample in a 60 ℃ drying oven for 12 hours to obtain AgCl.
Comparative example 2
Firstly, dispersing silver nitrate in 50mL of deionized water, and performing ultrasonic dispersion for 30 min;
secondly, adding cetyl trimethyl ammonium bromide into the solution obtained in the first step, and stirring for 2 hours in a water bath at the temperature of 80 ℃;
and thirdly, centrifugally washing the sample obtained in the second step, and drying the sample in a 60 ℃ drying oven for 12 hours to obtain AgBr.
FIG. 2 is a Zeta potential diagram of the alkali-etched biotite nanosheet prepared in example 1 in a water environment, wherein the Zeta potential is negative, which indicates that the surface of the sample is negatively charged and is beneficial to the adsorption of metal cations.
Fig. 3 is a transmission electron microscope image of the materials prepared in example 1, example 2 and example 3, a is untreated biotite flakes, B is alkali etched mesoporous biotite flakes, C is a silver chloride-biotite nanocomposite, D is a lattice line of silver chloride, E is a silver bromide-biotite nanocomposite, and F is a high resolution transmission electron microscope image of silver bromide nanoparticles. Comparing the A diagram and the B diagram, the black mica sheet after alkali etching is in a mesoporous shape, which is beneficial to the increase of active sites and the compounding of materials. It can be seen from the C and E diagrams that a layer of silver halide grows on the mesoporous black mica sheet, which shows that the black mica sheet and the silver halide are well compounded. The good crystallinity of the silver halide synthesized in the water bath can be seen from the clear lattice lines in the D and F plots.
Figure 4 is an XRD diffractogram of the materials prepared in example 1, example 2 and example 3.
Fig. 5 is a graph of the photocatalytic degradation performance of the silver chloride-biotite prepared in example 2. As can be seen from the figure, the degradation rate of 10mg/L rhodamine B for degrading 50mL by 30mg of silver chloride-biotite catalyst within 90min reaches more than 95%.
Fig. 6 is a graph of the photocatalytic degradation performance of the silver bromide-biotite prepared in example 3. As can be seen from the figure, the degradation rate of 10mg/L rhodamine B for degrading 50mL by 30mg of silver bromide-biotite catalyst within 90min reaches more than 85%. In conclusion, the silver halide has good dispersibility on the biotite, and the biotite is tightly combined with the silver halide, so that the effective specific surface area of catalytic reaction is increased, the active sites are increased, and the catalytic activity is improved.

Claims (9)

1. The preparation method of the silver halide-biotite composite photocatalyst is characterized by comprising the following steps:
step 1, stirring and dispersing biotite in 16-20 mol/L sodium hydroxide solution, carrying out hydrothermal reaction at 160-180 ℃, naturally cooling, centrifuging, washing and drying after the reaction is finished, so as to obtain alkali-etched biotite nanosheets, wherein the magnetic stirring time of the biotite in the sodium hydroxide solution is more than 2 hours, and the hydrothermal reaction is more than 24 hours;
And 2, dispersing the alkali-etched biotite nanosheets in water, adding silver nitrate, stirring and mixing uniformly, then adding cetyl trimethyl ammonium bromide or cetyl trimethyl ammonium chloride, carrying out water bath reaction at 50-70 ℃, centrifuging, washing and drying after the reaction is finished, thus obtaining the silver halide-biotite composite photocatalyst.
2. The method according to claim 1, wherein the mass concentration of biotite in step 1 is 10 mg/mL.
3. The preparation method according to claim 1, wherein in the step 1, the centrifugation rate is 9000r/min, and the drying temperature is 60-80 ℃.
4. The preparation method according to claim 1, wherein in the step 2, the mass ratio of the silver nitrate to the alkali-etched biotite is 1: 1.
5. The method according to claim 1, wherein the molar concentration of cetyltrimethylammonium bromide or chloride in step 2 is 8 x 10 -3 mol/L。
6. The method according to claim 1, wherein in step 2, the silver nitrate is mixed with the biotite for 0.5h or more.
7. The preparation method according to claim 1, wherein in the step 2, the water bath reaction time is more than 3h, the centrifugation rate is 9000r/min, and the drying temperature is 60-80 ℃.
8. The silver halide-biotite composite photocatalyst prepared by the preparation method according to any one of claims 1 to 7.
9. The use of the silver halide-biotite composite photocatalyst according to claim 8 in photocatalytic degradation of organic dyes.
CN201910758939.7A 2019-08-16 2019-08-16 Silver halide-biotite composite photocatalyst and preparation method thereof Active CN110560027B (en)

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Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104689839A (en) * 2015-02-02 2015-06-10 河西学院 Preparation method for Ag-AgCl/attapulgite nano compound photocatalyst
CN109422270A (en) * 2017-08-29 2019-03-05 湖南大学 Mesoporousization bentonite and preparation method thereof

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20060293430A1 (en) * 2005-06-20 2006-12-28 Eastman Kodak Company Exfoliated clay nanocomposites

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104689839A (en) * 2015-02-02 2015-06-10 河西学院 Preparation method for Ag-AgCl/attapulgite nano compound photocatalyst
CN109422270A (en) * 2017-08-29 2019-03-05 湖南大学 Mesoporousization bentonite and preparation method thereof

Non-Patent Citations (4)

* Cited by examiner, † Cited by third party
Title
AgBr/TiO2(001)纳米片可见光光催化剂的制备;张旺喜等;《湖北工业大学学报》;20140430;第29卷(第2期);摘要、第1.1.2节和第2.1.1节 *
Highly efficient removal of organic dyes by novel as-synthesized AgBr/montmorillonite composite;LÜ Jianchang et al.;《Journal of Wuhan University of Technology-Mater. Sci. Ed.》;20190228;第34卷(第1期);摘要和第2.1节 *
硅藻土及复合材料孔结构和表面特性与调湿性能研究;胡志波;《中国优秀博硕士学位论文全文数据库(博士) 工程科技Ⅰ辑》;20180215(第2期);第4.1节、第4.2.3节、第4.3节、表 2.1和表 4.1 *
碘化银/硅藻土光催化剂的制备及可见光催化性能研究;龚久炎等;《无机盐工业》;20180131;第50卷(第1期);摘要和试验部分 *

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