WO2024088432A1 - N-doped bismuth oxycarbonate composite graphite-phase carbon nitride material, and preparation method therefor and use thereof - Google Patents

N-doped bismuth oxycarbonate composite graphite-phase carbon nitride material, and preparation method therefor and use thereof Download PDF

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WO2024088432A1
WO2024088432A1 PCT/CN2023/129058 CN2023129058W WO2024088432A1 WO 2024088432 A1 WO2024088432 A1 WO 2024088432A1 CN 2023129058 W CN2023129058 W CN 2023129058W WO 2024088432 A1 WO2024088432 A1 WO 2024088432A1
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carbon nitride
phase carbon
oxycarbonate
graphite phase
nitride material
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French (fr)
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华英杰
贾仕豪
王崇太
韩慧敏
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海南师范大学
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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
    • 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
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/725Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
    • 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
    • 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
    • C02F2101/308Dyes; Colorants; Fluorescent agents
    • 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
    • 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

Definitions

  • the invention belongs to the technical field of photocatalytic materials for degrading wastewater pollutants, and particularly relates to an N-mixed bismuth oxycarbonate composite graphite phase carbon nitride material and a preparation method and application thereof.
  • An effective way to improve the photocatalytic performance of single semiconductors is to utilize the synergistic effect between two promising semiconductors to construct a heterojunction.
  • the close contact interface between the semiconductors, well-matched band energy and crystal plane coupling can effectively promote the separation and transfer of photogenerated electron-hole pairs, thereby accelerating surface photochemical reactions.
  • new S-type heterojunction photocatalysts have attracted widespread attention due to their inherent advantages in band structure.
  • the construction of S-type heterojunctions has become one of the effective methods to improve the photocatalytic performance of single semiconductors.
  • the present invention proposes a method to improve the shortcomings of limited visible light response and fewer active sites of photocatalysts by constructing an S-type heterojunction in monomeric bismuth oxycarbonate.
  • the present invention proposes a N-mixed bismuth oxycarbonate composite graphite phase carbon nitride material and its preparation method and application.
  • the present invention synthesizes N-mixed bismuth oxycarbonate with uniform morphology by hydrothermal method, and synthesizes N-mixed bismuth oxycarbonate composite graphite phase carbon nitride material by condensation reflux method using electrostatic adsorption method, effectively composites N-mixed bismuth oxycarbonate with graphite phase carbon nitride, and forms an effective and environmentally friendly S-type heterojunction of N-mixed bismuth oxycarbonate and monomer photocatalyst, overcoming the shortcomings of limited visible light response and fewer active sites of monomer photocatalyst, thereby generating more photogenerated carriers, and further improving the performance of photocatalytic degradation of organic dyes, antibiotics and phenolic pollutants in environmental water.
  • the present invention provides the following technical solutions:
  • a preparation method of an N-mixed bismuth oxycarbonate composite graphite phase carbon nitride material comprises the following steps: synthesizing N-mixed bismuth oxycarbonate by a hydrothermal method, and condensing and refluxing the N-mixed bismuth oxycarbonate and graphite phase carbon nitride by an electrostatic adsorption method to synthesize the N-mixed bismuth oxycarbonate composite graphite phase carbon nitride material.
  • hydrothermal synthesis of N-heterobismuth carbonate specifically includes the following steps:
  • Ammonium bismuth citrate and urea are placed in deionized water and stirred, and then polyvinyl pyrrolidone is added and stirred continuously, followed by hydrothermal treatment, centrifugation, washing and drying to obtain the N-heterobismuth carbonate.
  • the usage ratio of the ammonium bismuth citrate, urea and polyvinyl pyrrolidone is 2mmol:10mmol:600mg.
  • the temperature of the hydrothermal treatment is 60° C. and the time is 12 hours.
  • the process of synthesizing the N-mixed bismuth oxycarbonate composite graphite phase carbon nitride material by condensing and refluxing the N-mixed bismuth oxycarbonate and graphite phase carbon nitride by electrostatic adsorption method specifically includes the following steps:
  • the graphite phase carbon nitride is dispersed with a methanol aqueous solution to obtain a suspension, the N-heterobismuth oxycarbonate is added to the suspension and stirred to obtain a mixture, the mixture is condensed and refluxed, and the N-heterobismuth oxycarbonate composite graphite phase carbon nitride material is obtained after washing and drying.
  • the concentration of the graphite phase carbon nitride in the suspension is 3-15wt%, and preferably 10wt%.
  • the usage ratio of the suspension to the N-heterobismuth oxycarbonate is 150 mL: 1 g.
  • condensation reflux temperature is 75° C. and the time is 4 hours.
  • the present invention provides a method for preparing a N-doped bismuth oxycarbonate composite graphite phase carbon nitride material, comprising the following steps:
  • Step S1 Preparation of N-heterobismuth oxycarbonate
  • Step S2 Preparation of graphite phase carbon nitride
  • Step S3 Preparation of N-doped bismuth oxycarbonate composite graphite phase carbon nitride material
  • Deionized water and methanol solution are mixed in a volume ratio of 1:1 to obtain a methanol aqueous solution, graphite phase carbon nitride is added to the methanol aqueous solution, and a completely dispersed suspension is obtained after ultrasonic treatment for 30 minutes, wherein the concentration of graphite phase carbon nitride in the suspension is 3-15wt%, 1gp-BOC is introduced into 150mL of the above suspension, and magnetic stirring is performed for 24 hours to obtain a mixture, and finally the mixture is evaporated, condensed and refluxed for 4 hours at 75°C as an ambient temperature under continuous stirring conditions, and the mixture is taken out and washed with water and ethanol at 7000rpm for 5 minutes, three times each, and then dried in a vacuum drying oven at 60°C for 12 hours to obtain the N-heterocarbonate bismuth composite graphite phase carbon nitride material.
  • Material (CN/p-BOC)
  • graphite carbon nitride As a new type of organic photocatalyst, graphite carbon nitride has attracted much attention due to its inherent physical and chemical properties.
  • the electronic structure and surface properties of graphite carbon nitride also make it a photocatalyst with potential applications for degrading pollutants and generating renewable energy. Its two-dimensional structure can provide a good contact plane with other semiconductors, and nanojunctions are more easily formed.
  • the layered structure can promote the transfer of photogenerated charges on a tight interface, which is expected to improve the photocatalytic performance compared with a single photocatalyst.
  • the VB and CB of graphite carbon nitride are approximately 1.40 and -1.21 eV, respectively, and the VB and CB of N-heterobismuth carbonate are 1.48 and -0.78 eV, respectively.
  • the band gaps of graphite carbon nitride and N-heterobismuth carbonate materials can be cross-matched to form a composite photocatalyst, which can achieve directional carrier migration and promote the separation of photogenerated electron-hole pairs, thereby enhancing photocatalytic activity. Combining these two semiconductors into a composite photocatalyst promotes directional carrier migration and achieves rapid separation of photogenerated electron-hole pairs, thereby enhancing photocatalytic activity.
  • An N-mixed bismuth oxycarbonate composite graphite phase carbon nitride material prepared by the above preparation method has a SEM image of a peony flower shape.
  • the present invention has the following advantages and technical effects:
  • the present invention synthesizes uniform N-type bismuth carbonate by hydrothermal method, and synthesizes N-type bismuth carbonate and graphite carbon nitride into a composite material by condensation reflux using electrostatic adsorption method, thereby forming an effective and environmentally friendly S-type heterojunction of N-type bismuth carbonate composite graphite carbon nitride, which overcomes the disadvantages of monomer photocatalyst.
  • the present invention controls the ratio of graphite phase carbon nitride to N-bismuth oxycarbonate, thereby obtaining a composite material with a suitable energy band structure and optimal photocatalytic activity, thereby effectively improving the photocatalytic performance of the monomer.
  • the present invention utilizes the interaction between N-doped bismuth oxycarbonate and graphite-phase carbon nitride to compound N-doped bismuth oxycarbonate and graphite-phase carbon nitride to form an S-type heterojunction structure, which can broaden the light absorption range, enhance the light absorption intensity, and promote the separation and transfer of photogenerated carriers, thereby improving the photocatalytic degradation performance of the composite material.
  • FIG1 is a schematic diagram of a synthesis process for preparing N-bismuth oxycarbonate composite graphite phase carbon nitride material (CN/p-BOC) in Example 1 of the present invention
  • FIG2 is an SEM image of p-BOC, CN and 10 wt% CN/p-BOC prepared in Example 1 of the present invention, wherein a is p-BOC, b is CN, and c and d are 10 wt% CN/p-BOC at different magnifications;
  • FIG3 is a TEM image of p-BOC, CN and 10 wt% CN/p-BOC prepared in Example 1 of the present invention, wherein a is p-BOC, b is CN, and c and d are 10 wt% CN/p-BOC at different magnifications;
  • Figure 4 shows the photocatalytic degradation performance of the N-heterocarbonate bismuth composite graphite phase carbon nitride material prepared in different proportions under visible light for dye RhB (a), antibiotic TC (b) and CIP (c) and the degradation performance of all samples Kinetic curve of RhB (d).
  • Step S1 Preparation of N-heterobismuth oxycarbonate
  • Step S2 Preparation of graphite phase carbon nitride
  • Step S3 Preparation of N-doped bismuth oxycarbonate composite graphite phase carbon nitride material
  • Deionized water and methanol solution are mixed in a volume ratio of 1:1 to obtain 150 mL of methanol aqueous solution, graphite phase carbon nitride is added to the methanol aqueous solution, and a completely dispersed suspension is obtained after ultrasonic treatment for 30 minutes, wherein the concentration of graphite phase carbon nitride in the suspension is 10 wt%, 1 g p-BOC is introduced into 150 mL of the above suspension, and a mixture is obtained by magnetic stirring for 24 hours.
  • N-heterocarbonate bismuth composite graphite phase carbon nitride material (10wt% CN/p-BOC).
  • Example 2 Same as Example 1, except that the concentration of graphite phase carbon nitride in the suspension is 3wt%, and the obtained 3wt%CN/p-BOC.
  • Example 2 Same as Example 1, except that the concentration of graphite phase carbon nitride in the suspension is 5 wt %, resulting in 5 wt % CN/p-BOC.
  • Example 2 Same as Example 1, except that the concentration of graphite phase carbon nitride in the suspension is 15 wt %, resulting in 15 wt % CN/p-BOC.
  • Example 1 In order to verify the morphology and crystal phase characteristics of the N-mixed bismuth carbonate composite graphite phase carbon nitride material prepared by the present invention, the sample obtained in Example 1 was photographed with a thermal field emission scanning electron microscope (model: JSM-7001F) and a transmission electron microscope (model: JEOL JSM-2010). The results are shown in Figures 2 and 3.
  • Figure 2 is a SEM image
  • a is the p-BOC prepared in Example 1
  • b is the CN prepared in Example 1
  • c and d are 10wt% CN/p-BOC prepared in Example 1 at different magnifications
  • Figure 3 is a TEM image
  • a is the p-BOC prepared in Example 1
  • b is the CN prepared in Example 1
  • c and d are 10wt% CN/p-BOC prepared in Example 1.
  • pure p-BOC is in the shape of a 3D peony flower ball with a diameter of about 1.3 ⁇ m, while CN shows a typical layered structure, indicating that it contains one or more layers of stacked graphite-like structures.
  • the morphology of the 10wt% CN/p-BOC prepared in Example 1 is that the 3D p-BOC is wrapped by a CN layer with a two-dimensional structure, further indicating that CN is wrapped on p-BOC and the interface between CN and p-BOC is tight.
  • a flowing cooling water system was used to maintain the temperature at 30 °C to avoid thermal catalysis.
  • the solution was magnetically stirred for 30 min to allow the photocatalyst to reach adsorption-desorption equilibrium on the material surface. After turning on the lamp, 3 mL of the solution was taken at intervals of 15 min, centrifuged and filtered through 0.2 ⁇ m polyethersulfone to remove particles for subsequent analysis.
  • the concentration changes of the target pollutants were measured using a UV-visible spectrophotometer at the maximum absorption wavelengths of 554, 358 and 276 nm.
  • a flowing cooling water system was used to maintain the temperature at 30 °C to avoid thermal catalysis.
  • the solution was magnetically stirred for 30 min to allow the photocatalyst to reach adsorption-desorption equilibrium on the material surface. After turning on the lamp, 3 mL of the solution was taken at intervals of 15 min, centrifuged and filtered through 0.2 ⁇ m polyethersulfone to remove particles for subsequent analysis.
  • the concentration changes of the target pollutants were measured using a UV-visible spectrophotometer at the maximum absorption wavelengths of 554, 358 and 276 nm.
  • Example 1 50 mg of samples (p-BOC and 10 wt% CN/p-BOC prepared in Example 1) were placed in a photocatalytic reactor, and 100 mL of CIP ( ⁇ >400 nm) was photodegraded under a 250 W xenon lamp. A blank control group (CIP) without adding a catalyst sample was set up.
  • CIP blank control group
  • a flowing cooling water system was used to maintain the temperature at 30 °C to avoid thermal catalysis.
  • the solution was magnetically stirred for 30 min to allow the photocatalyst to reach adsorption-desorption equilibrium on the material surface. After turning on the lamp, 3 mL of the solution was taken at intervals of 15 min, centrifuged and filtered through 0.2 ⁇ m polyethersulfone to remove particles for subsequent analysis.
  • the concentration changes of the target pollutants were measured using a UV-visible spectrophotometer at the maximum absorption wavelengths of 554, 358 and 276 nm.
  • Example 1 According to FIG. 4 , it can be seen that the 10 wt % CN/p-BOC prepared in Example 1 has the best performance in degrading various pollutants.

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Abstract

An N-doped bismuth oxycarbonate composite graphite-phase carbon nitride material, and a preparation method therefor and the use thereof, which belong to the technical field of photocatalytic materials for degrading wastewater pollutants. An N-doped bismuth oxycarbonate is synthesized by means of a hydrothermal method, and the N-doped bismuth oxycarbonate and graphite-phase carbon nitride are then condensed and refluxed by means of an electrostatic adsorption method to synthesize the N-doped bismuth oxycarbonate composite graphite-phase carbon nitride material. The N-doped bismuth oxycarbonate and the graphite-phase carbon nitride are effectively compounded, and the N-doped bismuth oxycarbonate and the graphite-phase carbon nitride are compounded to form an S-shaped heterojunction structure by means of the interaction between the N-doped bismuth oxycarbonate and the graphite-phase carbon nitride, such that the light absorption range can be widened, the light absorption intensity can be enhanced, the separation and transfer of photon-generated carriers can be promoted, and the photocatalytic degradation performance of organic dyes, antibiotics and phenolic pollutants in environmental water is further improved.

Description

一种N杂碳酸氧铋复合石墨相氮化碳材料及其制备方法与应用A N-doped bismuth oxycarbonate composite graphite phase carbon nitride material and its preparation method and application 技术领域Technical Field
本发明属于降解废水污染物的光催化材料技术领域,特别涉及一种N杂碳酸氧铋复合石墨相氮化碳材料及其制备方法与应用。The invention belongs to the technical field of photocatalytic materials for degrading wastewater pollutants, and particularly relates to an N-mixed bismuth oxycarbonate composite graphite phase carbon nitride material and a preparation method and application thereof.
背景技术Background technique
环境污染日益严重,人们对清洁能源的需求日益增长是全球面临的严峻问题。为解决上述问题,已经采取许多策略和解决方案。其中,光催化技术在解决当前能源危机和环境恶化方面具有巨大潜力。在各种半导体光催化材料中,碳酸氧铋是一种很有前途的光催化剂,因为其具有吸引力的形态、出色的光化学稳定性。然而,碳酸氧铋的光催化性能受到以下两个原因的限制:(1)碳酸氧铋的宽带隙导致较差的可见光捕获能力;(2)光催化产生的电子-空穴对在碳酸氧铋中具有快速的复合速率,限制其光催化活性。因此,提高单体碳酸氧铋的光催化效率仍然是一个严峻的问题。The increasing environmental pollution and the growing demand for clean energy are serious problems facing the world. Many strategies and solutions have been adopted to solve the above problems. Among them, photocatalytic technology has great potential in solving the current energy crisis and environmental degradation. Among various semiconductor photocatalytic materials, bismuth oxycarbonate is a promising photocatalyst because of its attractive morphology and excellent photochemical stability. However, the photocatalytic performance of bismuth oxycarbonate is limited by the following two reasons: (1) the wide band gap of bismuth oxycarbonate leads to poor visible light capture ability; (2) the electron-hole pairs generated by photocatalysis have a fast recombination rate in bismuth oxycarbonate, which limits its photocatalytic activity. Therefore, improving the photocatalytic efficiency of monomeric bismuth oxycarbonate remains a serious problem.
提高单体半导体光催化性能的一种有效方法是通过利用两种有前途的半导体之间的协同效应,将两种半导体复合构筑异质结,利用半导体之间紧密接触的界面、匹配良好的能带能量和晶面耦合可有效地促进光生电子-空穴对的分离和转移,从而加速表面光化学反应。与传统异质结相比,新型S型异质结光催化剂因其本身能带结构的优势而受到广泛关注。S型异质结的构筑已经成为提高单体光催化性能的有效方法之一。An effective way to improve the photocatalytic performance of single semiconductors is to utilize the synergistic effect between two promising semiconductors to construct a heterojunction. The close contact interface between the semiconductors, well-matched band energy and crystal plane coupling can effectively promote the separation and transfer of photogenerated electron-hole pairs, thereby accelerating surface photochemical reactions. Compared with traditional heterojunctions, new S-type heterojunction photocatalysts have attracted widespread attention due to their inherent advantages in band structure. The construction of S-type heterojunctions has become one of the effective methods to improve the photocatalytic performance of single semiconductors.
基于此,本发明提出了一种通过在单体碳酸氧铋中构建S型异质结,来改善光催化剂可见光响应有限和活性位点较少的缺点。Based on this, the present invention proposes a method to improve the shortcomings of limited visible light response and fewer active sites of photocatalysts by constructing an S-type heterojunction in monomeric bismuth oxycarbonate.
发明内容 Summary of the invention
为解决上述技术问题,本发明提出了一种N杂碳酸氧铋复合石墨相氮化碳材料及其制备方法与应用。本发明通过水热法合成形貌均一的N杂碳酸氧铋,并利用静电吸附法,通过冷凝回流的方式合成N杂碳酸氧铋复合石墨相氮化碳材料,有效地将N杂碳酸氧铋与石墨相氮化碳进行复合,形成一种有效的、环保的N杂碳酸氧铋与单体光催化剂的S型异质结,克服单体光催化剂可见光响应有限和活性位点较少的缺点,从而产生更多的光生载流子,并进一步提高光催化降解环境水体有机染料、抗生素和酚类污染物的性能。In order to solve the above technical problems, the present invention proposes a N-mixed bismuth oxycarbonate composite graphite phase carbon nitride material and its preparation method and application. The present invention synthesizes N-mixed bismuth oxycarbonate with uniform morphology by hydrothermal method, and synthesizes N-mixed bismuth oxycarbonate composite graphite phase carbon nitride material by condensation reflux method using electrostatic adsorption method, effectively composites N-mixed bismuth oxycarbonate with graphite phase carbon nitride, and forms an effective and environmentally friendly S-type heterojunction of N-mixed bismuth oxycarbonate and monomer photocatalyst, overcoming the shortcomings of limited visible light response and fewer active sites of monomer photocatalyst, thereby generating more photogenerated carriers, and further improving the performance of photocatalytic degradation of organic dyes, antibiotics and phenolic pollutants in environmental water.
为实现上述目的,本发明提供了以下技术方案:To achieve the above object, the present invention provides the following technical solutions:
本发明的技术方案之一:One of the technical solutions of the present invention:
一种N杂碳酸氧铋复合石墨相氮化碳材料的制备方法,水热法合成N杂碳酸氧铋,将所述N杂碳酸氧铋与石墨相氮化碳利用静电吸附法,冷凝回流合成所述N杂碳酸氧铋复合石墨相氮化碳材料。A preparation method of an N-mixed bismuth oxycarbonate composite graphite phase carbon nitride material comprises the following steps: synthesizing N-mixed bismuth oxycarbonate by a hydrothermal method, and condensing and refluxing the N-mixed bismuth oxycarbonate and graphite phase carbon nitride by an electrostatic adsorption method to synthesize the N-mixed bismuth oxycarbonate composite graphite phase carbon nitride material.
进一步地,水热法合成N杂碳酸氧铋具体包括以下步骤:Further, the hydrothermal synthesis of N-heterobismuth carbonate specifically includes the following steps:
将柠檬酸铋铵和尿素放入去离子水中搅拌,之后加入聚乙烯吡咯烷酮继续搅拌,然后水热处理,离心、洗涤、干燥,得到所述N杂碳酸氧铋。Ammonium bismuth citrate and urea are placed in deionized water and stirred, and then polyvinyl pyrrolidone is added and stirred continuously, followed by hydrothermal treatment, centrifugation, washing and drying to obtain the N-heterobismuth carbonate.
更进一步地,所述柠檬酸铋铵、尿素和聚乙烯吡咯烷酮的用量比为2mmol∶10mmol∶600mg。Furthermore, the usage ratio of the ammonium bismuth citrate, urea and polyvinyl pyrrolidone is 2mmol:10mmol:600mg.
更进一步地,所述水热处理的温度为60℃,时间为12h。Furthermore, the temperature of the hydrothermal treatment is 60° C. and the time is 12 hours.
进一步地,将所述N杂碳酸氧铋与石墨相氮化碳利用静电吸附法,冷凝回流合成所述N杂碳酸氧铋复合石墨相氮化碳材料的过程具体包括以下步骤:Furthermore, the process of synthesizing the N-mixed bismuth oxycarbonate composite graphite phase carbon nitride material by condensing and refluxing the N-mixed bismuth oxycarbonate and graphite phase carbon nitride by electrostatic adsorption method specifically includes the following steps:
将石墨相氮化碳用甲醇水溶液分散得到悬浮液,将所述N杂碳酸氧铋加入所述悬浮液中搅拌得到混合物,将所述混合物冷凝回流,洗涤、干燥后得到所述N杂碳酸氧铋复合石墨相氮化碳材料。 The graphite phase carbon nitride is dispersed with a methanol aqueous solution to obtain a suspension, the N-heterobismuth oxycarbonate is added to the suspension and stirred to obtain a mixture, the mixture is condensed and refluxed, and the N-heterobismuth oxycarbonate composite graphite phase carbon nitride material is obtained after washing and drying.
更进一步地,所述石墨相氮化碳在悬浮液中的浓度为3-15wt%,作为优选浓度为10wt%。Furthermore, the concentration of the graphite phase carbon nitride in the suspension is 3-15wt%, and preferably 10wt%.
更进一步地,所述悬浮液与所述N杂碳酸氧铋的用量比为150mL∶1g。Furthermore, the usage ratio of the suspension to the N-heterobismuth oxycarbonate is 150 mL: 1 g.
更进一步地,所述冷凝回流的温度为75℃,时间为4h。Furthermore, the condensation reflux temperature is 75° C. and the time is 4 hours.
更具体地,本发明提出的一种N杂碳酸氧铋复合石墨相氮化碳材料的制备方法包括以下步骤:More specifically, the present invention provides a method for preparing a N-doped bismuth oxycarbonate composite graphite phase carbon nitride material, comprising the following steps:
步骤S1:N杂碳酸氧铋的制备Step S1: Preparation of N-heterobismuth oxycarbonate
将2mmol柠檬酸铋铵和10mmol尿素放入去离子水中,用转速为7000-8000rpm的搅拌器高速搅拌40min,随后将600mg的聚乙烯吡咯烷酮加到上述溶液中,持续高速搅拌50min,搅拌完成将溶液密封到100mL高压反应釜中,然后在60℃下进行水热处理12h,最后离心,并用水和乙醇在7000rpm条件下洗涤5min,各三次,干燥12h,得到N杂碳酸氧铋(p-BOC);2 mmol of ammonium bismuth citrate and 10 mmol of urea were placed in deionized water, and stirred at high speed for 40 min with a stirrer at a speed of 7000-8000 rpm, and then 600 mg of polyvinyl pyrrolidone was added to the above solution, and the high-speed stirring was continued for 50 min. After the stirring was completed, the solution was sealed in a 100 mL high-pressure reactor, and then hydrothermally treated at 60° C. for 12 h, and finally centrifuged, and washed with water and ethanol at 7000 rpm for 5 min, three times each, and dried for 12 h to obtain N-heterobismuth carbonate (p-BOC);
步骤S2:石墨相氮化碳的制备Step S2: Preparation of graphite phase carbon nitride
取10g尿素放入50mL坩埚中,并在马弗炉中以每分钟10℃的升温速率加热至550℃,保持温度4h,待马弗炉温度冷却后,取出研磨,得到石墨相氮化碳(g-C3N4);10 g of urea was placed in a 50 mL crucible and heated to 550° C. at a heating rate of 10° C. per minute in a muffle furnace. The temperature was maintained for 4 h. After the temperature of the muffle furnace was cooled, the urea was taken out and ground to obtain graphite phase carbon nitride (gC 3 N 4 );
步骤S3:N杂碳酸氧铋复合石墨相氮化碳材料的制备Step S3: Preparation of N-doped bismuth oxycarbonate composite graphite phase carbon nitride material
将去离子水与甲醇溶液按照1:1的体积比混合得到甲醇水溶液,在甲醇水溶液中加入石墨相氮化碳,超声处理30min后得到完全分散的悬浮液,石墨相氮化碳在悬浮液中的浓度为3-15wt%,将1gp-BOC引入150mL上述悬浮液中,磁力搅拌24h得到混合物,最后将混合物在连续搅拌条件下以75℃作为环境温度蒸发冷凝回流4h,取出用水和乙醇在7000rpm条件下洗涤5min,各三次,之后在60℃的真空干燥箱中干燥12h得到所述N杂碳酸氧铋复合石墨相氮化碳材 料(CN/p-BOC)。Deionized water and methanol solution are mixed in a volume ratio of 1:1 to obtain a methanol aqueous solution, graphite phase carbon nitride is added to the methanol aqueous solution, and a completely dispersed suspension is obtained after ultrasonic treatment for 30 minutes, wherein the concentration of graphite phase carbon nitride in the suspension is 3-15wt%, 1gp-BOC is introduced into 150mL of the above suspension, and magnetic stirring is performed for 24 hours to obtain a mixture, and finally the mixture is evaporated, condensed and refluxed for 4 hours at 75°C as an ambient temperature under continuous stirring conditions, and the mixture is taken out and washed with water and ethanol at 7000rpm for 5 minutes, three times each, and then dried in a vacuum drying oven at 60°C for 12 hours to obtain the N-heterocarbonate bismuth composite graphite phase carbon nitride material. Material (CN/p-BOC).
石墨相氮化碳作为一种新型的有机光催化剂,由于其固有的物理和化学性质而引起较多关注,石墨相氮化碳的电子结构和表面性质也使其成为一种具有潜在应用的光催化剂,用于降解污染物和产生可再生能源,其拥有的二维结构可以提供与其它半导体良好的接触平面,纳米结更容易的形成。此外,层状结构可以促进光生电荷在紧密界面上的转移,与单个光催化剂相比,有望提高光催化性能。As a new type of organic photocatalyst, graphite carbon nitride has attracted much attention due to its inherent physical and chemical properties. The electronic structure and surface properties of graphite carbon nitride also make it a photocatalyst with potential applications for degrading pollutants and generating renewable energy. Its two-dimensional structure can provide a good contact plane with other semiconductors, and nanojunctions are more easily formed. In addition, the layered structure can promote the transfer of photogenerated charges on a tight interface, which is expected to improve the photocatalytic performance compared with a single photocatalyst.
石墨相氮化碳的VB和CB分别约为1.40和-1.21eV,N杂碳酸氧铋的VB和CB分别为1.48和-0.78eV。由此可知,石墨相氮化碳和N杂碳酸氧铋材料的带隙可以交叉匹配,形成复合光催化剂可以实现载流子定向迁移,促进光生电子-空穴对的分离,从而增强光催化活性。将这两种半导体组成复合光催化剂,促进载流子的定向迁移,实现光生电子-空穴对的快速分离,从而增强光催化活性。The VB and CB of graphite carbon nitride are approximately 1.40 and -1.21 eV, respectively, and the VB and CB of N-heterobismuth carbonate are 1.48 and -0.78 eV, respectively. It can be seen that the band gaps of graphite carbon nitride and N-heterobismuth carbonate materials can be cross-matched to form a composite photocatalyst, which can achieve directional carrier migration and promote the separation of photogenerated electron-hole pairs, thereby enhancing photocatalytic activity. Combining these two semiconductors into a composite photocatalyst promotes directional carrier migration and achieves rapid separation of photogenerated electron-hole pairs, thereby enhancing photocatalytic activity.
本发明的技术方案之二:The second technical solution of the present invention:
一种上述制备方法制备得到的N杂碳酸氧铋复合石墨相氮化碳材料,该N杂碳酸氧铋复合石墨相氮化碳材料的SEM图像为牡丹花状。An N-mixed bismuth oxycarbonate composite graphite phase carbon nitride material prepared by the above preparation method has a SEM image of a peony flower shape.
本发明的技术方案之三:The third technical solution of the present invention:
上述N杂碳酸氧铋复合石墨相氮化碳材料在光催化降解有机染料、抗生素或酚类污染物上的应用。Application of the above N-mixed bismuth oxycarbonate composite graphite phase carbon nitride material in photocatalytic degradation of organic dyes, antibiotics or phenolic pollutants.
与现有技术相比,本发明具有如下优点和技术效果:Compared with the prior art, the present invention has the following advantages and technical effects:
1、本发明通过水热法合成形貌均一的N杂碳酸氧铋,利用静电吸附法通过冷凝回流的手段将N杂碳酸氧铋与石墨相氮化碳合成复合材料,形成一种有效的、环保的N杂碳酸氧铋复合石墨相氮化碳的S型异质结,克服单体光催化剂 可见光响应有限和活性位点较少的缺点,加速电荷分离,产生更多的光生载流子,改善单体光催化剂的光谱响应范围,从而实现高效的可见光催化氧化活性,并进一步提高光催化降解环境水体有机染料、抗生素和酚类污染物性能,具有光催化效率高、方法简单快捷和经济环保等优点。1. The present invention synthesizes uniform N-type bismuth carbonate by hydrothermal method, and synthesizes N-type bismuth carbonate and graphite carbon nitride into a composite material by condensation reflux using electrostatic adsorption method, thereby forming an effective and environmentally friendly S-type heterojunction of N-type bismuth carbonate composite graphite carbon nitride, which overcomes the disadvantages of monomer photocatalyst. It overcomes the shortcomings of limited visible light response and fewer active sites, accelerates charge separation, generates more photogenerated carriers, and improves the spectral response range of monomer photocatalysts, thereby achieving efficient visible light catalytic oxidation activity and further improving the photocatalytic degradation of organic dyes, antibiotics and phenolic pollutants in environmental water. It has the advantages of high photocatalytic efficiency, simple and fast method, and economy and environmental protection.
2、本发明在制备N杂碳酸氧铋复合石墨相氮化碳材料时通过控制石墨相氮化碳与N杂碳酸氧铋的比例,从而得到具有合适能带结构、拥有最佳光催化活性的复合材料,有效提高了单体的光催化性能。2. When preparing N-bismuth oxycarbonate composite graphite phase carbon nitride material, the present invention controls the ratio of graphite phase carbon nitride to N-bismuth oxycarbonate, thereby obtaining a composite material with a suitable energy band structure and optimal photocatalytic activity, thereby effectively improving the photocatalytic performance of the monomer.
3、本发明利用N杂碳酸氧铋与石墨相氮化碳之间的相互作用,将N杂碳酸氧铋与石墨相氮化碳进行复合并形成S型异质结结构,能够拓宽光吸收范围,增强光吸收强度,促进光生载流子的分离和转移,从而提升复合材料光催化降解性能。3. The present invention utilizes the interaction between N-doped bismuth oxycarbonate and graphite-phase carbon nitride to compound N-doped bismuth oxycarbonate and graphite-phase carbon nitride to form an S-type heterojunction structure, which can broaden the light absorption range, enhance the light absorption intensity, and promote the separation and transfer of photogenerated carriers, thereby improving the photocatalytic degradation performance of the composite material.
附图说明BRIEF DESCRIPTION OF THE DRAWINGS
构成本申请的一部分的附图用来提供对本申请的进一步理解,本申请的示意性实施例及其说明用于解释本申请,并不构成对本申请的不当限定。在附图中:The drawings constituting a part of the present application are used to provide a further understanding of the present application. The illustrative embodiments and descriptions of the present application are used to explain the present application and do not constitute an improper limitation on the present application. In the drawings:
图1为本发明实施例1制备N杂碳酸氧铋复合石墨相氮化碳材料(CN/p-BOC)的合成流程示意图;FIG1 is a schematic diagram of a synthesis process for preparing N-bismuth oxycarbonate composite graphite phase carbon nitride material (CN/p-BOC) in Example 1 of the present invention;
图2为本发明实施例1制备的p-BOC、CN及10wt%CN/p-BOC的SEM图像,其中a为p-BOC,b为CN,c、d为不同放大倍数下10wt%CN/p-BOC;FIG2 is an SEM image of p-BOC, CN and 10 wt% CN/p-BOC prepared in Example 1 of the present invention, wherein a is p-BOC, b is CN, and c and d are 10 wt% CN/p-BOC at different magnifications;
图3为本发明实施例1制备的p-BOC、CN及10wt%CN/p-BOC的TEM图像,其中a为p-BOC,b为CN,c、d为不同放大倍数下的10wt%CN/p-BOC;FIG3 is a TEM image of p-BOC, CN and 10 wt% CN/p-BOC prepared in Example 1 of the present invention, wherein a is p-BOC, b is CN, and c and d are 10 wt% CN/p-BOC at different magnifications;
图4为本发明制备的不同比例的N杂碳酸氧铋复合石墨相氮化碳材料在可见光下对染料RhB(a),抗生素TC(b)和CIP(c)光催化降解性能图与所有样品降解 RhB的动力学曲线(d)。Figure 4 shows the photocatalytic degradation performance of the N-heterocarbonate bismuth composite graphite phase carbon nitride material prepared in different proportions under visible light for dye RhB (a), antibiotic TC (b) and CIP (c) and the degradation performance of all samples Kinetic curve of RhB (d).
具体实施方式Detailed ways
现详细说明本发明的多种示例性实施方式,该详细说明不应认为是对本发明的限制,而应理解为是对本发明的某些方面、特性和实施方案的更详细的描述。Various exemplary embodiments of the present invention will now be described in detail. This detailed description should not be considered as limiting the present invention, but should be understood as a more detailed description of certain aspects, features, and embodiments of the present invention.
应理解本发明中所述的术语仅仅是为描述特别的实施方式,并非用于限制本发明。另外,对于本发明中的数值范围,应理解为还具体公开了该范围的上限和下限之间的每个中间值。在任何陈述值或陈述范围内的中间值以及任何其他陈述值或在所述范围内的中间值之间的每个较小的范围也包括在本发明内。这些较小范围的上限和下限可独立地包括或排除在范围内。It should be understood that the terms described in the present invention are only for describing a particular embodiment and are not intended to limit the present invention. In addition, for the numerical range in the present invention, it should be understood that each intermediate value between the upper and lower limits of the scope is also specifically disclosed. Each smaller range between the intermediate value in any stated value or stated range and any other stated value or intermediate value in the described range is also included in the present invention. The upper and lower limits of these smaller ranges can be independently included or excluded in the scope.
除非另有说明,否则本文使用的所有技术和科学术语具有本发明所述领域的常规技术人员通常理解的相同含义。虽然本发明仅描述了优选的方法和材料,但是在本发明的实施或测试中也可以使用与本文所述相似或等同的任何方法和材料。本说明书中提到的所有文献通过引用并入,用以公开和描述与所述文献相关的方法和/或材料。在与任何并入的文献冲突时,以本说明书的内容为准。Unless otherwise indicated, all technical and scientific terms used herein have the same meanings as those generally understood by those skilled in the art. Although the present invention describes only preferred methods and materials, any methods and materials similar or equivalent to those described herein may also be used in the implementation or testing of the present invention. All documents mentioned in this specification are incorporated by reference to disclose and describe the methods and/or materials associated with the documents. In the event of a conflict with any incorporated document, the content of this specification shall prevail.
在不背离本发明的范围或精神的情况下,可对本发明说明书的具体实施方式做多种改进和变化,这对本领域技术人员而言是显而易见的。由本发明的说明书得到的其他实施方式对技术人员而言是显而易见得的。本发明说明书和实施例仅是示例性的。It will be apparent to those skilled in the art that various modifications and variations may be made to the specific embodiments of the present invention description without departing from the scope or spirit of the present invention. Other embodiments derived from the present invention description will be apparent to those skilled in the art. The present invention description and examples are exemplary only.
关于本文中所使用的“包含”、“包括”、“具有”、“含有”等等,均为开放性的用语,即意指包含但不限于。The words “include,” “including,” “have,” “contain,” etc. used in this document are open-ended terms, meaning including but not limited to.
本发明实施例所用各原料均为通过市售购买得到。All raw materials used in the embodiments of the present invention are purchased from commercial sources.
以下通过实施例对本发明的技术方案做进一步说明。 The technical solution of the present invention is further illustrated by the following embodiments.
实施例1Example 1
步骤S1:N杂碳酸氧铋的制备Step S1: Preparation of N-heterobismuth oxycarbonate
将2mmol柠檬酸铋铵和10mmol尿素放入去离子水中,用转速为7000-8000rpm的搅拌器高速搅拌40min,随后将600mg的聚乙烯吡咯烷酮加到上述溶液中,持续高速搅拌50min,搅拌完成将溶液密封到100mL高压反应釜中,然后在60℃下进行水热处理12h,最后离心,并用水和乙醇在7000rpm条件下洗涤5min,各三次,干燥12h,得到N杂碳酸氧铋(p-BOC);2 mmol of ammonium bismuth citrate and 10 mmol of urea were placed in deionized water, and stirred at high speed for 40 min with a stirrer at a speed of 7000-8000 rpm, and then 600 mg of polyvinyl pyrrolidone was added to the above solution, and the high-speed stirring was continued for 50 min. After the stirring was completed, the solution was sealed in a 100 mL high-pressure reactor, and then hydrothermally treated at 60° C. for 12 h, and finally centrifuged, and washed with water and ethanol at 7000 rpm for 5 min, three times each, and dried for 12 h to obtain N-heterobismuth carbonate (p-BOC);
步骤S2:石墨相氮化碳的制备Step S2: Preparation of graphite phase carbon nitride
取10g尿素放入50mL坩埚中,并在马弗炉中以每分钟10℃的升温速率加热至550℃,保持温度4h,待马弗炉温度冷却后,取出研磨,得到石墨相氮化碳(g-C3N4,简称CN);10 g of urea was placed in a 50 mL crucible and heated to 550° C. at a heating rate of 10° C. per minute in a muffle furnace. The temperature was maintained for 4 h. After the temperature of the muffle furnace was cooled, the urea was taken out and ground to obtain graphite phase carbon nitride (gC 3 N 4 , referred to as CN).
步骤S3:N杂碳酸氧铋复合石墨相氮化碳材料的制备Step S3: Preparation of N-doped bismuth oxycarbonate composite graphite phase carbon nitride material
将去离子水与甲醇溶液按照1:1的体积比混合得到150mL甲醇水溶液,在甲醇水溶液中加入石墨相氮化碳,超声处理30min后得到完全分散的悬浮液,石墨相氮化碳在悬浮液中的浓度为10wt%,将1gp-BOC引入150mL上述悬浮液中,磁力搅拌24h得到混合物,最后将混合物在连续搅拌条件下以75℃作为环境温度蒸发冷凝回流4h,取出用水和乙醇在7000rpm条件下洗涤5min,各三次,之后在60℃的真空干燥箱中干燥12h得到N杂碳酸氧铋复合石墨相氮化碳材料(10wt%CN/p-BOC)。Deionized water and methanol solution are mixed in a volume ratio of 1:1 to obtain 150 mL of methanol aqueous solution, graphite phase carbon nitride is added to the methanol aqueous solution, and a completely dispersed suspension is obtained after ultrasonic treatment for 30 minutes, wherein the concentration of graphite phase carbon nitride in the suspension is 10 wt%, 1 g p-BOC is introduced into 150 mL of the above suspension, and a mixture is obtained by magnetic stirring for 24 hours. Finally, the mixture is evaporated, condensed and refluxed at 75°C as the ambient temperature under continuous stirring conditions for 4 hours, the mixture is taken out and washed with water and ethanol at 7000 rpm for 5 minutes, three times each, and then dried in a vacuum drying oven at 60°C for 12 hours to obtain N-heterocarbonate bismuth composite graphite phase carbon nitride material (10wt% CN/p-BOC).
本发明实施例1制备N杂碳酸氧铋复合石墨相氮化碳材料(CN/p-BOC)的合成流程示意图见图1。The schematic diagram of the synthesis process of preparing N-bismuth oxycarbonate composite graphite phase carbon nitride material (CN/p-BOC) in Example 1 of the present invention is shown in Figure 1.
实施例2Example 2
同实施例1,区别仅在于,石墨相氮化碳在悬浮液中的浓度为3wt%,得到 3wt%CN/p-BOC。Same as Example 1, except that the concentration of graphite phase carbon nitride in the suspension is 3wt%, and the obtained 3wt%CN/p-BOC.
实施例3Example 3
同实施例1,区别仅在于,石墨相氮化碳在悬浮液中的浓度为5wt%,得到5wt%CN/p-BOC。Same as Example 1, except that the concentration of graphite phase carbon nitride in the suspension is 5 wt %, resulting in 5 wt % CN/p-BOC.
实施例4Example 4
同实施例1,区别仅在于,石墨相氮化碳在悬浮液中的浓度为15wt%,得到15wt%CN/p-BOC。Same as Example 1, except that the concentration of graphite phase carbon nitride in the suspension is 15 wt %, resulting in 15 wt % CN/p-BOC.
一、形貌分析1. Morphology analysis
为验证本发明所制备的N杂碳酸氧铋复合石墨相氮化碳材料的形貌与晶相特征,将实施例1所得样品用热场发射扫描电子显微镜(型号:JSM-7001F)和透射电子显微镜(型号:JEOLJSM-2010)进行拍照,结果见图2和图3,图2为SEM图像,a为实施例1制备得到的p-BOC,b为实施例1制备得到的CN,c、d为不同放大倍数下实施例1制备得到的10wt%CN/p-BOC,图3为TEM图像,a为实施例1制备得到的p-BOC,b为实施例1制备得到的CN,c、d为实施例1制备得到的10wt%CN/p-BOC。In order to verify the morphology and crystal phase characteristics of the N-mixed bismuth carbonate composite graphite phase carbon nitride material prepared by the present invention, the sample obtained in Example 1 was photographed with a thermal field emission scanning electron microscope (model: JSM-7001F) and a transmission electron microscope (model: JEOL JSM-2010). The results are shown in Figures 2 and 3. Figure 2 is a SEM image, a is the p-BOC prepared in Example 1, b is the CN prepared in Example 1, c and d are 10wt% CN/p-BOC prepared in Example 1 at different magnifications, and Figure 3 is a TEM image, a is the p-BOC prepared in Example 1, b is the CN prepared in Example 1, and c and d are 10wt% CN/p-BOC prepared in Example 1.
由图2可看出,纯p-BOC为3D牡丹花球状,直径约1.3μm,而CN显示典型的层状结构,表明它包含一层或多层堆叠的类石墨结构,实施例1制备的10wt%的CN/p-BOC的形貌则是3D的p-BOC被具有二维结构的CN层包裹,进一步表明CN包裹在p-BOC上,CN和p-BOC之间的界面紧密。图3中d的插图中看出实施例1制备的10wt%的CN/p-BOC中晶格间距为0.273nm,对应于p-BOC的(110)平面。以上结果可以得出CN和p-BOC连接紧密,使其更容易形成异质结构,有利于光生载流子转移从而增强光催化活性。As can be seen from Figure 2, pure p-BOC is in the shape of a 3D peony flower ball with a diameter of about 1.3 μm, while CN shows a typical layered structure, indicating that it contains one or more layers of stacked graphite-like structures. The morphology of the 10wt% CN/p-BOC prepared in Example 1 is that the 3D p-BOC is wrapped by a CN layer with a two-dimensional structure, further indicating that CN is wrapped on p-BOC and the interface between CN and p-BOC is tight. The inset of Figure 3d shows that the lattice spacing of the 10wt% CN/p-BOC prepared in Example 1 is 0.273nm, corresponding to the (110) plane of p-BOC. The above results show that CN and p-BOC are closely connected, making it easier to form a heterostructure, which is beneficial to the transfer of photogenerated carriers and thus enhances the photocatalytic activity.
二、性能测试 2. Performance Test
以10mg/L的染料RhB(罗丹明)、抗生素TC和抗生素CIP为目标污染物进行光催化降解,以评价本发明实施例所制备材料的可见光催化氧化活性。10 mg/L of dye RhB (rhodamine), antibiotic TC and antibiotic CIP were used as target pollutants for photocatalytic degradation to evaluate the visible light catalytic oxidation activity of the material prepared in the embodiment of the present invention.
1.对RhB的可见光催化氧化活性1. Visible light catalytic oxidation activity of RhB
分别取50mg样品(实施例1制备的p-BOC、实施例1制备的10wt%CN/p-BOC、实施例2制备的3wt%CN/p-BOC、实施例3制备的5wt%CN/p-BOC以及实施例4制备的15wt%CN/p-BOC)置于光催化反应器中,在250W的氙灯下光降解100mLRhB(λ>400nm),并设置不加催化剂样品的空白对照组(RhB)。50 mg of samples (p-BOC prepared in Example 1, 10 wt% CN/p-BOC prepared in Example 1, 3 wt% CN/p-BOC prepared in Example 2, 5 wt% CN/p-BOC prepared in Example 3, and 15 wt% CN/p-BOC prepared in Example 4) were respectively placed in a photocatalytic reactor, and 100 mL of RhB (λ>400 nm) was photodegraded under a 250 W xenon lamp, and a blank control group (RhB) without adding a catalyst sample was set up.
采用流动冷却水系统使温度维持在30℃以避免热催化。氙灯照射前,将溶液磁搅拌30min,使光催化剂在材料表面达到吸附-脱附平衡。开灯后,在15min的时间间隔内,取3mL溶液,离心并通过0.2μm聚醚砜过滤去除颗粒,用于后续分析。用紫外-可见分光光度计在最大吸收波长554、358和276nm下测定目标污染物的浓度变化。A flowing cooling water system was used to maintain the temperature at 30 °C to avoid thermal catalysis. Before xenon lamp irradiation, the solution was magnetically stirred for 30 min to allow the photocatalyst to reach adsorption-desorption equilibrium on the material surface. After turning on the lamp, 3 mL of the solution was taken at intervals of 15 min, centrifuged and filtered through 0.2 μm polyethersulfone to remove particles for subsequent analysis. The concentration changes of the target pollutants were measured using a UV-visible spectrophotometer at the maximum absorption wavelengths of 554, 358 and 276 nm.
对RhB的可见光催化氧化活性测定结果见图4中的a。The results of the visible light photocatalytic oxidation activity measurement of RhB are shown in Figure 4a.
2.对TC的可见光催化氧化活性2. Visible light catalytic oxidation activity of TC
分别取50mg样品(实施例1制备的p-BOC和10wt%CN/p-BOC)置于光催化反应器中,在250W的氙灯下光降解100mLTC(λ>400nm),并设置不加催化剂样品的空白对照组(TC)。50 mg of samples (p-BOC and 10 wt% CN/p-BOC prepared in Example 1) were placed in a photocatalytic reactor, and 100 mL of TC (λ>400 nm) was photodegraded under a 250 W xenon lamp. A blank control group (TC) without adding a catalyst sample was set up.
采用流动冷却水系统使温度维持在30℃以避免热催化。氙灯照射前,将溶液磁搅拌30min,使光催化剂在材料表面达到吸附-脱附平衡。开灯后,在15min的时间间隔内,取3mL溶液,离心并通过0.2μm聚醚砜过滤去除颗粒,用于后续分析。用紫外-可见分光光度计在最大吸收波长554、358和276nm下测定目标污染物的浓度变化。A flowing cooling water system was used to maintain the temperature at 30 °C to avoid thermal catalysis. Before xenon lamp irradiation, the solution was magnetically stirred for 30 min to allow the photocatalyst to reach adsorption-desorption equilibrium on the material surface. After turning on the lamp, 3 mL of the solution was taken at intervals of 15 min, centrifuged and filtered through 0.2 μm polyethersulfone to remove particles for subsequent analysis. The concentration changes of the target pollutants were measured using a UV-visible spectrophotometer at the maximum absorption wavelengths of 554, 358 and 276 nm.
实施例1制备的p-BOC和10wt%CN/p-BOC对TC的可见光催化氧化活性 测定结果见图4中的b。Visible light photocatalytic oxidation activity of p-BOC and 10 wt% CN/p-BOC prepared in Example 1 for TC The measurement results are shown in Figure 4b.
3.对CIP的可见光催化氧化活性3. Visible light catalytic oxidation activity of CIP
分别取50mg样品(实施例1制备的p-BOC和10wt%CN/p-BOC)置于光催化反应器中,在250W的氙灯下光降解100mLCIP(λ>400nm),并设置不加催化剂样品的空白对照组(CIP)。50 mg of samples (p-BOC and 10 wt% CN/p-BOC prepared in Example 1) were placed in a photocatalytic reactor, and 100 mL of CIP (λ>400 nm) was photodegraded under a 250 W xenon lamp. A blank control group (CIP) without adding a catalyst sample was set up.
采用流动冷却水系统使温度维持在30℃以避免热催化。氙灯照射前,将溶液磁搅拌30min,使光催化剂在材料表面达到吸附-脱附平衡。开灯后,在15min的时间间隔内,取3mL溶液,离心并通过0.2μm聚醚砜过滤去除颗粒,用于后续分析。用紫外-可见分光光度计在最大吸收波长554、358和276nm下测定目标污染物的浓度变化。A flowing cooling water system was used to maintain the temperature at 30 °C to avoid thermal catalysis. Before xenon lamp irradiation, the solution was magnetically stirred for 30 min to allow the photocatalyst to reach adsorption-desorption equilibrium on the material surface. After turning on the lamp, 3 mL of the solution was taken at intervals of 15 min, centrifuged and filtered through 0.2 μm polyethersulfone to remove particles for subsequent analysis. The concentration changes of the target pollutants were measured using a UV-visible spectrophotometer at the maximum absorption wavelengths of 554, 358 and 276 nm.
实施例1制备的p-BOC和10wt%CN/p-BOC对CIP的可见光催化氧化活性测定结果见图4中的c。The results of the visible light photocatalytic oxidation activity measurement of p-BOC and 10 wt % CN/p-BOC prepared in Example 1 for CIP are shown in FIG. 4 c .
4.降解RhB的动力学曲线4. Kinetic curve of RhB degradation
样品(实施例1制备的p-BOC、实施例1制备的10wt%CN/p-BOC、实施例2制备的3wt%CN/p-BOC、实施例3制备的5wt%CN/p-BOC以及实施例4制备的15wt%CN/p-BOC)以及空白组(Blank)降解RhB的动力学曲线结果见图4中的d。The kinetic curve results of RhB degradation by the samples (p-BOC prepared in Example 1, 10 wt% CN/p-BOC prepared in Example 1, 3 wt% CN/p-BOC prepared in Example 2, 5 wt% CN/p-BOC prepared in Example 3, and 15 wt% CN/p-BOC prepared in Example 4) and the blank group (Blank) are shown in Figure 4d.
根据图4可以看出,实施例1制备的10wt%CN/p-BOC降解各种污染物都具有最佳性能。According to FIG. 4 , it can be seen that the 10 wt % CN/p-BOC prepared in Example 1 has the best performance in degrading various pollutants.
以上,仅为本申请较佳的具体实施方式,但本申请的保护范围并不局限于此,任何熟悉本技术领域的技术人员在本申请揭露的技术范围内,可轻易想到的变化或替换,都应涵盖在本申请的保护范围之内。因此,本申请的保护范围应该以权利要求的保护范围为准。 The above are only preferred specific implementations of the present application, but the protection scope of the present application is not limited thereto. Any changes or substitutions that can be easily thought of by any technician familiar with the technical field within the technical scope disclosed in the present application should be included in the protection scope of the present application. Therefore, the protection scope of the present application should be based on the protection scope of the claims.

Claims (10)

  1. 一种N杂碳酸氧铋复合石墨相氮化碳材料的制备方法,其特征在于,水热法合成N杂碳酸氧铋,将所述N杂碳酸氧铋与石墨相氮化碳利用静电吸附法,冷凝回流合成所述N杂碳酸氧铋复合石墨相氮化碳材料。A method for preparing an N-mixed bismuth oxycarbonate composite graphite phase carbon nitride material, characterized in that the N-mixed bismuth oxycarbonate is synthesized by a hydrothermal method, and the N-mixed bismuth oxycarbonate and graphite phase carbon nitride are condensed and refluxed by an electrostatic adsorption method to synthesize the N-mixed bismuth oxycarbonate composite graphite phase carbon nitride material.
  2. 根据权利要求1所述的N杂碳酸氧铋复合石墨相氮化碳材料的制备方法,其特征在于,水热法合成N杂碳酸氧铋具体包括以下步骤:The method for preparing the N-bismuth oxycarbonate composite graphite phase carbon nitride material according to claim 1 is characterized in that the hydrothermal synthesis of N-bismuth oxycarbonate specifically comprises the following steps:
    将柠檬酸铋铵和尿素放入去离子水中搅拌,之后加入聚乙烯吡咯烷酮继续搅拌,然后水热处理,离心、洗涤、干燥,得到所述N杂碳酸氧铋。Ammonium bismuth citrate and urea are placed in deionized water and stirred, and then polyvinyl pyrrolidone is added and stirred continuously, followed by hydrothermal treatment, centrifugation, washing and drying to obtain the N-heterobismuth carbonate.
  3. 根据权利要求2所述的N杂碳酸氧铋复合石墨相氮化碳材料的制备方法,其特征在于,所述柠檬酸铋铵、尿素和聚乙烯吡咯烷酮的用量比为2mmol∶10mmol∶600mg。The method for preparing N-heterobismuth oxycarbonate composite graphite phase carbon nitride material according to claim 2 is characterized in that the amount ratio of the ammonium bismuth citrate, urea and polyvinyl pyrrolidone is 2mmol:10mmol:600mg.
  4. 根据权利要求2所述的N杂碳酸氧铋复合石墨相氮化碳材料的制备方法,其特征在于,所述水热处理的温度为60℃,时间为12h。The method for preparing N-mixed bismuth oxycarbonate composite graphite phase carbon nitride material according to claim 2 is characterized in that the temperature of the hydrothermal treatment is 60° C. and the time is 12 hours.
  5. 根据权利要求1所述的N杂碳酸氧铋复合石墨相氮化碳材料的制备方法,其特征在于,将所述N杂碳酸氧铋与石墨相氮化碳利用静电吸附法,冷凝回流合成所述N杂碳酸氧铋复合石墨相氮化碳材料的过程具体包括以下步骤:The method for preparing the N-mixed bismuth oxycarbonate composite graphite phase carbon nitride material according to claim 1 is characterized in that the process of synthesizing the N-mixed bismuth oxycarbonate composite graphite phase carbon nitride material by condensing and refluxing the N-mixed bismuth oxycarbonate composite graphite phase carbon nitride material by an electrostatic adsorption method specifically comprises the following steps:
    将石墨相氮化碳用甲醇水溶液分散得到悬浮液,将所述N杂碳酸氧铋加入所述悬浮液中搅拌得到混合物,将所述混合物冷凝回流,洗涤、干燥后得到所述N杂碳酸氧铋复合石墨相氮化碳材料。The graphite phase carbon nitride is dispersed with a methanol aqueous solution to obtain a suspension, the N-heterobismuth oxycarbonate is added to the suspension and stirred to obtain a mixture, the mixture is condensed and refluxed, and the N-heterobismuth oxycarbonate composite graphite phase carbon nitride material is obtained after washing and drying.
  6. 根据权利要求5所述的N杂碳酸氧铋复合石墨相氮化碳材料的制备方法,其特征在于,所述石墨相氮化碳在悬浮液中的浓度为3-15wt%。The method for preparing the N-bismuth oxycarbonate composite graphite phase carbon nitride material according to claim 5, characterized in that the concentration of the graphite phase carbon nitride in the suspension is 3-15wt%.
  7. 根据权利要求5所述的N杂碳酸氧铋复合石墨相氮化碳材料的制备方法,其特征在于,所述悬浮液与所述N杂碳酸氧铋的用量比为150mL∶1g。The method for preparing the N-heterobismuth oxycarbonate composite graphite phase carbon nitride material according to claim 5 is characterized in that the usage ratio of the suspension to the N-heterobismuth oxycarbonate is 150 mL: 1 g.
  8. 根据权利要求5所述的N杂碳酸氧铋复合石墨相氮化碳材料的制备方法, 其特征在于,所述冷凝回流的温度为75℃,时间为4h。The method for preparing the N-mixed bismuth oxycarbonate composite graphite phase carbon nitride material according to claim 5, Characterized in that the condensation reflux temperature is 75°C and the time is 4 hours.
  9. 一种权利要求1-8任一项所述制备方法制备得到的N杂碳酸氧铋复合石墨相氮化碳材料。A N-bismuth oxycarbonate composite graphite phase carbon nitride material prepared by the preparation method according to any one of claims 1 to 8.
  10. 权利要求9所述N杂碳酸氧铋复合石墨相氮化碳材料在光催化降解有机染料、抗生素或酚类污染物上的应用。 Application of the N-heterobismuth oxycarbonate composite graphite phase carbon nitride material described in claim 9 in photocatalytic degradation of organic dyes, antibiotics or phenolic pollutants.
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