CN111229322B - BiOCl/C 3 N 4 /UiO-66 ternary composite photocatalytic material - Google Patents

BiOCl/C 3 N 4 /UiO-66 ternary composite photocatalytic material Download PDF

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CN111229322B
CN111229322B CN202010068746.1A CN202010068746A CN111229322B CN 111229322 B CN111229322 B CN 111229322B CN 202010068746 A CN202010068746 A CN 202010068746A CN 111229322 B CN111229322 B CN 111229322B
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朱禹
吕华
赵素雅
朱文菲
沈欣茹
张启缘
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Abstract

The invention provides BiOCl/C 3 N 4 The preparation method of the/UiO-66 ternary composite photocatalytic material comprises the following steps: 1) Preparation C 3 N 4 : preparation of C from melamine 3 N 4 (ii) a 2) Preparation of BiOCl/C 3 N 4 A complex; 3) By changing BiOCl/C 3 N 4 The proportion of the BiOCl to the UiO-66 controls the content of binary and monomer in the composite material to prepare BiOCl/C 3 N 4 a/UiO-66 ternary composite material; the prepared composite material has higher photocatalytic degradation performance.

Description

BiOCl/C 3 N 4 /UiO-66 ternary composite photocatalytic material
Technical Field
The invention relates to BiOCl/C 3 N 4 A/UiO-66 ternary composite photocatalytic material belongs to the technical field of catalysts.
Background
In recent years, the world is facing the difficult problems of energy shortage and environmental pollution, the photocatalytic technology is one of the most effective ways for directly converting solar energy into chemical energy, the photocatalytic technology has the advantages of low energy consumption, simple and convenient operation, mild reaction conditions, capability of being carried out at normal temperature and normal pressure, and becomes a research hotspot in the aspect of processing environmental problems.
The photocatalysis technology can convert inexhaustible low-density solar energy into high-density electrochemical energy to remove organic pollutants and CO in water or air 2 The fields of methane preparation by reduction, hydrogen preparation by water photolysis and the like are widely applied, and a clean and efficient new way is provided for solving the two problems of global environmental pollution and energy crisis. The core of the photocatalytic technology is a photocatalyst. However, conventional semiconductor photocatalysts (e.g. TiO) 2 ZnO, etc.) are difficult to be industrially applied on a large scale due to the defects of low light quantum efficiency and solar energy utilization rate, etc. In order to promote the development of the photocatalytic technology to commercialization and practicability and fully exert the advantages of the photocatalytic technology in the aspects of environmental protection and new energy utilization, the design and development of other novel efficient photocatalytic composite nanomaterial systems are inevitable trends in the development of the photocatalytic technology. In recent years, bismuth-based semiconductor materials have attracted much attention because of their unique band structures, their excellent photocatalytic properties, and their advantages such as low cost, stable physicochemical properties, and environmental friendliness.
Disclosure of Invention
The invention aims at the problems, thereby providing a BiOCl/C 3 N 4 the/UiO-66 ternary composite photocatalytic material.
The specific technical scheme is as follows:
BiOCl/C 3 N 4 The preparation method of the/UiO-66 ternary composite photocatalytic material comprises the following steps:
1) Preparation C 3 N 4 : preparation of C from melamine 3 N 4
2) Preparation of BiOCl/C 3 N 4 A complex;
3) By changing BiOCl/C 3 N 4 The content of binary and monomer in the composite material is controlled by the proportion of the monomer to the UiO-66 to prepare the composite materialTo BiOCl/C 3 N 4 The ternary composite material of/UiO-66.
Further, step 1) C 3 N 4 The preparation method comprises the following steps:
1) 10g of melamine was weighed into a covered 50mL ceramic crucible and then heated from room temperature to 550 ℃ in a muffle furnace at a rate of about 20 ℃ for min -1
2) After the thermal polymerization reaction is finished, taking out the crucible, naturally cooling to room temperature, finally grinding the product uniformly, and drying in an oven at 70 ℃ for 12 hours to obtain a final product C 3 N 4
Further, biOCl/C 3 N 4 The preparation method of the compound comprises the following steps:
1) 0.5g of C was weighed out separately 3 N 4 Dissolving 0.1491g of KCl in 50mL of deionized water, and fully performing ultrasonic treatment for 20min to obtain a solution A;
2) 0.9304g of Bi (NO) is weighed 3 ) 3 ·5H 2 Placing O in 50mL of glacial acetic acid solution, and stirring strongly for 30min to completely dissolve the O to obtain solution B;
3) Dropwise adding the solution B into the solution A, fully stirring the suspension for 1h after the dropwise adding step is finished, and standing for 4h;
4) Centrifuging, washing with water for 2 times and washing with ethanol for 2 times, drying the obtained precipitate at 60 deg.C to obtain BiOCl/C 3 N 4 And (c) a complex.
Further, biOCl/C 3 N 4 The preparation method of the/UiO-66 ternary composite material comprises the following steps:
1) 0.2149g of ZrCl 4 0.1532g of terephthalic acid, 0.5g of BiOCl/C 3 N 4 Adding the compound and 3.5mL of acetic acid into 42mL of DMF, performing ultrasonic treatment for 30min, and transferring the mixture into a 50mL polytetrafluoroethylene reaction kettle to react for 24h at 120 ℃;
2) Cooling to room temperature, centrifuging, washing with DMF and ethanol for 3 times respectively, and drying at 80 deg.C to obtain BiOCl/C 3 N 4 The ternary composite material of/UiO-66.
The invention has the beneficial effects that:
1) BiOX has high photocatalytic activity mainly due to the fact that, on one hand, when electrons on a valence band are excited to a conduction band orbit, photo-generated electron-hole pairs are generated, biOX (X = Cl, br, I) has a unique layered structure and has enough space to polarize corresponding atoms and orbitals, and induced dipole moment can promote separation of the electron-hole pairs, so that the photocatalytic activity is greatly improved; in addition, the BiOX (X = Cl, br, I) is an indirect transition bandgap semiconductor, and excited electrons need to pass through a certain k layer to reach a valence band, so that recombination of the excited electrons and holes is reduced as much as possible. The combined action of the unique open structure and the indirect transition mode promotes the effective separation of the photo-generated electron-hole pairs, and the photo-generated carriers are quickly transferred, so that the BiOX has excellent photocatalytic performance.
2) The bismuth-based photocatalytic material has many advantages, mainly including the following two: first, bismuth has mainly two valence states, +3 and +5, and other intermediate valence states can be synthesized by different experimental methods. When the outer layer of electrons are lost, bismuth can be compounded and hybridized with other elements (such as O element) to form a valence band top end in a semiconductor, so that an s-p hybrid track is formed, the forbidden bandwidth of the S-p hybrid track is reduced, the transfer of photogenerated electrons and holes is facilitated, the recombination of photogenerated carriers is inhibited, and the photocatalytic performance can be improved. Secondly, the bismuth semiconductor material has a plurality of microscopic morphologies, most of the bismuth semiconductor material is of a multilayer structure, the specific surface area is high, and the bismuth semiconductor material is favorable for being compounded with other semiconductor materials, so that the photocatalytic performance of the bismuth semiconductor material is improved.
3) There is also room for improvement in the performance of bismuth-based semiconductor photocatalytic materials. The current research focus is to modify the bismuth semiconductor photocatalytic material to improve the photocatalytic performance of the bismuth semiconductor photocatalytic material. The modification of the bismuth-based photocatalytic material mainly focuses on synthesizing a novel semiconductor photocatalytic material, compounding the semiconductor photocatalytic material with other semiconductor photocatalysts to form a heterojunction and doping some elements for modification.
4) Graphite phase carbon nitride (g-C) 3 N 4 ) The molecular structure is similar to that of graphene, and the graphene is an organic polymer, high in cost performance and easy to synthesize; mono-lamellar g-C 3 N 4 Has large specific surface area, chemical stability and narrow band gapThe structure ensures that the photocatalyst has absorption capacity on visible light and has good application prospect in the field of photocatalysis.
5): the high specific surface area of MOFs disperses the active center to the maximum extent, and the regular and ordered pore channels increase the effective contact between the substrate and the active center; the pore structure is easy to functionalize, and catalytic active points are effectively fixed; the aperture is adjustable, the threshold limiting effect similar to that of a micro-reactor is realized, and the catalytic reaction efficiency is improved.
Drawings
FIG. 1 is C 3 N 4 (ii) an infrared spectrum;
FIG. 2 is an infrared spectrum of BiOCl;
FIG. 3 is an IR spectrum of UiO-66;
FIG. 4 shows BiOCl/C 3 N 4 (ii) an infrared spectrum;
FIG. 5 shows BiOCl/C 3 N 4 An IR spectrum of/UiO-66;
FIG. 6 is C 3 N 4 、BiOCl、UiO-66、BiOCl/C 3 N 4 And BiOCl/C 3 N 4 The XRD pattern of @ UiO-66;
FIG. 7 is C 3 N 4 、BiOCl、UiO-66、BiOCl/C 3 N 4 And BiOCl/C 3 N 4 @ UiO-66 degrades the photocatalytic activity of tetracycline under visible light.
Detailed Description
In order to make the technical scheme of the invention clearer and clearer, the invention is further described below by combining the attached drawings, and any scheme obtained by carrying out equivalent replacement and conventional reasoning on the technical characteristics of the technical scheme of the invention falls into the protection scope of the invention.
Example one
The specific technical scheme is as follows:
BiOCl/C 3 N 4 The preparation method of the/UiO-66 ternary composite photocatalytic material comprises the following steps:
1) Preparation C 3 N 4
(1) 10g of melamine was weighed into a covered 50mL ceramic crucible and then heated in a muffle furnace from room temperature to 550 ℃ at a rate of about 20 ℃ for min -1
(2) After the thermal polymerization reaction is finished, taking out the crucible, naturally cooling to room temperature, finally grinding the product uniformly, and drying in an oven at 70 ℃ for 12 hours to obtain a final product C 3 N 4
2) Preparation of BiOCl/C 3 N 4 Composite material
(1) 0.5g of C was weighed out separately 3 N 4 Dissolving 0.1491g of KCl in 50mL of deionized water, and fully performing ultrasonic treatment for 20min to obtain a solution A;
(2) 0.9304g of Bi (NO) is weighed 3 ) 3 ·5H 2 Placing O in 50mL of glacial acetic acid solution, and stirring strongly for 30min to completely dissolve the O to obtain solution B;
(3) dropwise adding the solution B into the solution A, fully stirring the suspension for 1h after the dropwise adding step is completed, and then standing for 4h;
(4) centrifuging, washing with water for 2 times and washing with ethanol for 2 times, drying the obtained precipitate at 60 deg.C to obtain BiOCl/C 3 N 4 Complexes of BiOCl with C 3 N 4 The theoretical mass ratio of (2);
3) Preparation of BiOCl/C 3 N 4 Ternary composite material of/UiO-66
(1) 0.2149g of ZrCl 4 0.1532g of terephthalic acid, 0.5g of BiOCl/C 3 N 4 Adding the compound and 3.5mL of acetic acid into 42mL of DMF, carrying out ultrasonic treatment for 30min, and transferring the mixture into a 50mL polytetrafluoroethylene reaction kettle to react for 24h at 120 ℃;
(2) cooling to room temperature, centrifuging, washing with DMF and ethanol for 3 times respectively, and drying at 80 deg.C to obtain BiOCl/C 3 N 4 Ternary composite material/UiO-66, biOCl/C 3 N 4 The theoretical mass ratio to UiO-66 is 1.
Example two
Using infrared spectroscopy to C 3 N 4 Performing analysis and identification, and the result is shown in figure 1; as can be seen from FIG. 1, C 3 N 4 At 808cm -1 The absorption peak corresponds to the out-of-plane stretching vibration of the C-N ring, and is in the range of 1239-1638cm -1 The absorption peak at (A) corresponds to C-N aromatic ring vibration; absorb thereinHaving C in the peak 3 N 4 Characteristic peaks appear.
EXAMPLE III
Analyzing and identifying BiOCl by using infrared spectroscopy, wherein the result is shown in figure 2;
as can be seen from FIG. 2, the A2u type vibration peak of the Bi-O bond was located at 508cm -1 At least one of (1) and (b); 767cm -1 The absorption peak at (b) corresponds to the asymmetric tensile vibration of the Bi — O bond. Furthermore, 1626cm -1 The stronger absorption peak corresponds to the bending vibration of the O-H bond of the water molecule on the surface of the catalyst; a BiOCl characteristic peak appears in the absorption peak.
The preparation method of BiOCl comprises the following steps: 0.9304g Bi (NO) 3 ) 3 ·5H 2 O was dissolved in 50mL of water and 4.5mL of acetic acid was added thereto, followed by stirring thoroughly, followed by dropwise addition to 50mL of an aqueous solution containing 0.1495g of KCl, stirring at room temperature for 1 hour, and standing for 1 hour. And (3) centrifugally separating the solid product, washing the solid product for 3 times by using deionized water and ethanol respectively, and drying the solid product at 80 ℃ to obtain the product.
Example four
The UiO-66 was analyzed and identified by infrared spectroscopy, the results are shown in FIG. 3; as can be seen from FIG. 3, 3434cm -1 The broader peak at this point corresponds to the-OH absorption peak of UiO-66, indicating that the material contains a large amount of water, due to the water absorbed by the porous adsorbent material of UiO-66; 1656cm -1 Vibration absorption attributable to the carbon-oxygen double bond C = O in the carboxyl group; 1407cm -1 Is formed by COO - The absorption peak due to stretching vibration of (2) is derived from the carboxyl group on terephthalic acid in UiO-66. In this absorption peak, characteristic UiO-66 peak appears.
EXAMPLE five
BiOCl/C by infrared spectroscopy 3 N 4 The complex was analyzed and identified, and the results are shown in FIG. 4; as can be seen from FIG. 4, C 3 N 4 At 808cm -1 The absorption peak corresponds to the out-of-plane stretching vibration of the C-N ring, and is 1244-1639cm -1 The absorption peak at (a) corresponds to the C-N aromatic ring vibration. The A2u type vibration peak of the Bi-O bond is located at 508cm -1 To (3). 767cm -1 The absorption peak at (b) corresponds to the asymmetric tensile vibration of the Bi — O bond. Furthermore, 1639cm -1 Strong suction ofThe peak is contracted corresponding to the bending vibration of the O-H bond of the water molecule on the surface of the catalyst; in BiOCl/C 3 N 4 In the absorption peak of the binary complex, C is as described above 3 N 4 And characteristic peaks of BiOCl were present.
EXAMPLE six
BiOCl/C by infrared spectroscopy 3 N 4 the/UiO-66 ternary composite material is analyzed and identified, and the result is shown in figure 5;
as can be seen in FIG. 5, C 3 N 4 At 808cm -1 The absorption peak corresponds to the out-of-plane stretching vibration of the C-N ring, and is 1244-1639cm -1 The absorption peak corresponds to C-N aromatic ring vibration; the A2u type vibration peak of the Bi-O bond is located at 508cm -1 To (3).
Furthermore, 1639cm -1 The stronger absorption peak corresponds to the bending vibration of the O-H bond of the water molecule on the surface of the catalyst; 3407cm -1 The broader peak at (b) corresponds to the-OH absorption peak of UiO-66, indicating that the material contains a large amount of water, because UiO-66 is the porous adsorbent material which absorbs water; 1657cm -1 Vibration absorption attributable to the carbon-oxygen double bond C = O in the carboxyl group; 1402cm -1 Is the absorption peak due to stretching vibration of COO-, which is derived from the carboxyl group on terephthalic acid in UiO-66. In the absorption peak of the ternary complex, C is as described above 3 N 4 And characteristic peaks of BiOCl and UiO-66 were present.
In addition, the spectrum has three characteristic peaks of the monomer; however, some characteristic peaks were reduced in intensity, and the carboxyl peak of UiO-66 was slightly changed and combined to 1639cm -1 It is probably caused by the change of the environment of the carboxyl of the UiO-66 caused by the doping of acetic acid in the preparation process of the composite material. Meanwhile, the result is basically consistent with the result reported in the literature, and is 1575cm -1 Is the characteristic absorption peak of C-N bending vibration in the benzene ring.
EXAMPLE seven
Using XRD to C 3 N 4 、BiOCl、UiO-66、BiOCl/C 3 N 4 And BiOCl/C 3 N 4 The results of the structure identification with @ UiO-66 are shown in FIG. 6. Monomer C 3 N 4 XRD and theoretical XRD of BiOCl, uiO-66The spectrogram is well matched, and the purity is high. BiOCl/C 3 N 4 Can find C in the XRD spectrum of the product 3 N 4 And BiOCl corresponding to 2 theta angle. After UiO-66 compounding, biOCl/C 3 N 4 The @ UiO-66XRD spectrum can correspond to the 2 theta angles of three monomers.
Example eight
Evaluation of C by degradation of Tetracycline under visible light with Tetracycline as the target contaminant 3 N 4 、BiOCl、UiO-66、BiOCl/C 3 N 4 And BiOCl/C 3 N 4 @ Uio-66 photocatalytic activity. The self-degradation of tetracycline is almost negligible when no catalyst is present.
As shown in FIG. 7, uiO-66 mainly exhibits adsorption property, C 3 N 4 And BiOCl can photodegrade 23% and 56% of tetracycline in one hour. Binary compound BiOCl/C 3 N 4 The photocatalytic performance of (A) is improved, which is mainly C 3 N 4 The visible light absorption of BiOCl is widened after the composition. BiOCl/C is enhanced due to the adsorption property of UiO-66 3 N 4 The limited domain effect of/UiO-66, the material after ternary composition can degrade 95% of tetracycline in 1 hour.

Claims (1)

1. BiOCl/C 3 N 4 the/UiO-66 ternary composite photocatalytic material is characterized by comprising the following preparation methods:
1) Preparation C 3 N 4 : preparation of C from melamine 3 N 4
2) Preparation of BiOCl/C 3 N 4 Complexes of BiOCl with C 3 N 4 The mass ratio of (1) is 2;
3) By changing BiOCl/C 3 N 4 The proportion of the BiOCl to the UiO-66 controls the content of the binary and the monomer in the composite material to prepare BiOCl/C 3 N 4 a/UiO-66 ternary composite material; biOCl/C 3 N 4 The mass ratio of the compound to UiO-66 is 1;
step 1) C 3 N 4 The preparation method comprises the following steps:
1) Balance10g of melamine was placed in a covered 50mL ceramic crucible and then heated from room temperature to 550 ℃ in a muffle furnace at a heating rate of 20 ℃ for min -1
2) After the thermal polymerization reaction is finished, taking out the crucible, naturally cooling to room temperature, finally grinding the product uniformly, and drying in an oven at 70 ℃ for 12 hours to obtain a final product C 3 N 4
BiOCl/C 3 N 4 The preparation method of the compound comprises the following steps:
1) Respectively weighing 0.5gC 3 N 4 Dissolving 0.1491g of KCl in 50mL of deionized water, and fully performing ultrasonic treatment for 20min to obtain a solution A;
2) 0.9304g of Bi (NO) is weighed out 3 ) 3 .5H 2 Placing O in 50mL of glacial acetic acid solution, and stirring strongly for 30min to completely dissolve the O to obtain solution B;
3) Dropwise adding the solution B into the solution A, fully stirring the suspension for 1h after the dropwise adding step is finished, and standing for 4h;
4) Centrifuging, washing with water for 2 times and washing with ethanol for 2 times, drying the obtained precipitate at 60 deg.C to obtain BiOCl/C 3 N 4 A complex;
BiOCl/C 3 N 4 the preparation method of the/UiO-66 ternary composite material comprises the following steps:
1) 0.2149g of ZrCl 4 0.1532g of terephthalic acid, 0.5g of BiOCl/C 3 N 4 Adding the compound and 3.5mL of acetic acid into 42mL of DMF, carrying out ultrasonic treatment for 30min, and transferring the mixture into a 50mL polytetrafluoroethylene reaction kettle to react for 24h at 120 ℃;
2) Cooling to room temperature, centrifuging, washing with DMF and ethanol for 3 times respectively, and drying at 80 deg.C to obtain BiOCl/C 3 N 4 the/UiO-66 ternary composite material.
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卤氧铋基光催化剂的制备及其性能的研究;叶坪;《中国优秀博硕士学位论文全文数据库(硕士)》;20150215;第23-24页第4.2.1节 *

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