CN105289673A - A kind of Bi2WO6/Ag3PO4 heterojunction composite photocatalyst and its preparation method and application - Google Patents

A kind of Bi2WO6/Ag3PO4 heterojunction composite photocatalyst and its preparation method and application Download PDF

Info

Publication number
CN105289673A
CN105289673A CN201510789041.8A CN201510789041A CN105289673A CN 105289673 A CN105289673 A CN 105289673A CN 201510789041 A CN201510789041 A CN 201510789041A CN 105289673 A CN105289673 A CN 105289673A
Authority
CN
China
Prior art keywords
composite photocatalyst
heterojunction composite
preparation
heterojunction
ag3po4
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN201510789041.8A
Other languages
Chinese (zh)
Inventor
鞠鹏
张盾
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Institute of Oceanology of CAS
Original Assignee
Institute of Oceanology of CAS
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Institute of Oceanology of CAS filed Critical Institute of Oceanology of CAS
Priority to CN201510789041.8A priority Critical patent/CN105289673A/en
Publication of CN105289673A publication Critical patent/CN105289673A/en
Pending legal-status Critical Current

Links

Classifications

    • 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

Landscapes

  • Catalysts (AREA)

Abstract

The invention belongs to the field of photocatalysis and specifically relates to a Bi2WO6/Ag3PO4 heterojunction composite photocatalyst and its preparation method and application. The Bi2WO6/Ag3PO4 heterojunction composite photocatalyst is composed of Bi2WO6 and Ag3PO4, wherein Ag3PO4 nanoparticles are deposited on the Bi2WO6 surface of a three-dimensional layered rod-like structure; and the molar ratio of Bi2WO6 to Ag3PO4 is 1:0.1-10. The preparation method of the invention has a simple process, is easy to control and is low-cost. A Bi2WO6/Ag3PO4 heterojunction structure with visible light response is constructed, photon-generated carrier separation is accelerated, and recombination probability of photogenerated electron-hole pairs is minimized. The Bi2WO6/Ag3PO4 heterojunction composite photocatalyst has high-efficiency photocatalytic activity and stability in visible light, has highly-efficient killing and degradation effects on harmful microbes and dye pollutants in a water body and has good practical value and potential application prospect in fields of water body purification, marine pollution prevention and the like.

Description

一种Bi2WO6/Ag3PO4异质结复合光催化剂及其制备方法和应用A kind of Bi2WO6/Ag3PO4 heterojunction composite photocatalyst and its preparation method and application

技术领域technical field

本发明属于光催化领域,具体涉及一种Bi2WO6/Ag3PO4异质结复合光催化剂及其制备方法和应用。The invention belongs to the field of photocatalysis, and in particular relates to a Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst and a preparation method and application thereof.

背景技术Background technique

光催化技术是一种利用光能进行物质转化的技术,自1972年日本科学家Fujishima和Honda首次报道TiO2在紫外光照下可以光解水产生氢气和氧气以后,半导体光催化技术受到了越来越多的关注[1]。对于半导体材料来说,它们可以在光照条件下产生电子-空穴对,一部分电子和空穴在体相内或表面相遇而复合,另一部分电子迁移到半导体表面具有很强的还原能力,可以与吸附的氧结合,生成具有强氧化性的自由基;而迁移到半导体表面的空穴有很强的氧化能力,可以将吸附在半导体表面的OH-和H2O氧化,产生强氧化性的自由基,比如·OH、·HO2、H2O2和·O2 -[2],可以直接与反应物发生作用并将其氧化分解,而且不产生二次污染。近年来,光催化技术的应用研究发展十分迅速,因其具有高效、无选择性、稳定性高、绿色无毒、无二次污染、能耗低、操作简便和低成本等突出优点,而且可以充分利用清洁无污染的太阳能,在污水处理、废气处理、空气净化、杀菌消毒、催化制氢、还原CO2等方面已经有广泛应用,并且效果良好。Photocatalytic technology is a technology that uses light energy for material conversion. Since Japanese scientists Fujishima and Honda first reported in 1972 that TiO2 can photolyze water to produce hydrogen and oxygen under ultraviolet light, semiconductor photocatalytic technology has received more and more attention. More attention [1] . For semiconductor materials, they can generate electron-hole pairs under light conditions, some of the electrons and holes meet and recombine in the bulk phase or on the surface, and the other part of the electrons migrate to the semiconductor surface, which has a strong reduction ability and can be combined with The adsorbed oxygen combines to generate strong oxidizing free radicals; and the holes that migrate to the semiconductor surface have strong oxidizing ability, which can oxidize the OH - and H 2 O adsorbed on the semiconductor surface to generate strong oxidizing free radicals. The radicals, such as ·OH, ·HO 2 , H 2 O 2 and ·O 2 - , etc. [2] , can directly interact with the reactants and oxidize and decompose them without secondary pollution. In recent years, the application research of photocatalytic technology has developed very rapidly, because of its outstanding advantages such as high efficiency, non-selectivity, high stability, green and non-toxic, no secondary pollution, low energy consumption, easy operation and low cost, etc., and can Making full use of clean and pollution-free solar energy has been widely used in sewage treatment, waste gas treatment, air purification, sterilization, hydrogen production, CO2 reduction, etc., and the effect is good.

近年来,人们对开发新型的可见光催化剂做了大量研究,其中包含了d0和d10电子构型的In3+、Ce3+、Bi3+、Ag+等。其中,Bi2WO6是一种最简单的Aurivillius型氧化物,是一种n型直接半导体材料,自1999年Kudo等首次报道了Bi2WO6在波长大于420nm的可见光辐射下具有光催化活性后[3],Bi2WO6因其较窄的禁带宽度(约2.7eV),能被可见光激发并在可见光下具有较高的催化活性从而作为一种新型可见光催化材料引起了越来越多的关注[4]。然而由于在单体Bi2WO6中激发的电子和空穴对的迁移距离长,体相复合的几率增加,不利于电子-空穴的快速分离,导致光催化活性相对不高。因此,可以通过半导体复合构建复合材料可以加速电子-空穴分离,提高单体材料的光催化性能[5,6]。Ag3PO4是一种新型高效的光催化材料,其特有的间接带隙、价带中光激发空穴的强氧化性,同时其电子迁移速率比空穴迁移速率更高,从而促使电子-空穴分离,使其具有良好的光催化性能;同时Ag空位缺陷能够参与光电子捕获,提供更多的光激发空穴,也有利于电子-空穴分离[7]。因此,现需要构建一种复合型催化剂。In recent years, people have done a lot of research on the development of new visible light catalysts, including In 3+ , Ce 3+ , Bi 3+ , Ag + etc. with d0 and d10 electron configurations. Among them, Bi 2 WO 6 is the simplest Aurivillius-type oxide and an n-type direct semiconductor material. Since 1999, Kudo et al. first reported that Bi 2 WO 6 has photocatalytic activity under visible light radiation with a wavelength greater than 420nm. After [3] , Bi 2 WO 6 has attracted more and more attention as a new type of visible photocatalytic material due to its narrow band gap (about 2.7eV), which can be excited by visible light and has high catalytic activity under visible light. More attention [4] . However, due to the long migration distance of electron and hole pairs excited in monomeric Bi 2 WO 6 , the probability of bulk phase recombination increases, which is not conducive to the rapid separation of electrons and holes, resulting in relatively low photocatalytic activity. Therefore, the construction of composite materials through semiconductor recombination can accelerate electron-hole separation and improve the photocatalytic performance of monomer materials [5,6] . Ag 3 PO 4 is a new type of high-efficiency photocatalytic material. Its unique indirect band gap, strong oxidation of photo-excited holes in the valence band, and its electron transfer rate is higher than the hole transfer rate, thus promoting the electron- Hole separation makes it have good photocatalytic performance; at the same time, Ag vacancy defects can participate in photoelectron capture, provide more photoexcited holes, and are also conducive to electron-hole separation [7] . Therefore, there is a need to construct a composite catalyst.

[1]K.Nakata,A.Fujishima.TiO2photocatalysis:Designandapplications[J].JournalofPhotochemistryandPhotobiologyC:PhotochemistryReviews,2012,13:169-189.[1] K. Nakata, A. Fujishima. TiO 2 photocatalysis: Design and applications [J]. Journal of Photochemistry and Photobiology C: Photochemistry Reviews, 2012, 13: 169-189.

[2]X.B.Chen,S.S.Mao.Titaniumdioxidenanomaterials:Synthesis,properties,modifications,andapplications[J].ChemicalReviews,2007,107:2891-2959.[2] X.B.Chen, S.S.Mao. Titaniumdioxide nanomaterials: Synthesis, properties, modifications, and applications [J]. Chemical Reviews, 2007, 107: 2891-2959.

[3]A.Kudo,S.Hijii。H-2orO-2evolutionfromaqueoussolutionsonlayeredoxidephotocatalystsconsistingofBi3+with6s(2)configurationandd(0)transitionmetalions[J].ChemistryLetters,1999,10:1103-1104.[3] A. Kudo, S. Hijii. H-2orO-2evolutionfromaqueoussolutionsonlayeredoxidephotocatalystsconsistingofBi 3+ with6s(2)configurationandd(0)transitionmetalions[J].ChemistryLetters,1999,10:1103-1104.

[4]X.F.Cao,L.Zhang,X.T.Chen,Z.L.Xue.Microwave-assistedsolution-phasepreparationofflower-likeBi2WO6anditsvisible-light-drivenphotocatalyticproperties[J].CrystEngComm,2011,13:306-311.[4] X.F.Cao, L.Zhang, X.T.Chen, Z.L.Xue. Microwave-assisted solution-phase preparation of flower-like Bi2WO6 and its visible-light-driven photocatalytic properties [J].

[5]Y.Hu,D.Z.Li,Y.Zheng,W.Chen,Y.H.He,Y.Shao,X.Z.Fu,G.C.Xiao.BiVO4/TiO2nanocrystallineheterostructure:Awidespectrumresponsivephotocatalysttowardsthehighlyefficientdecompositionofgaseousbenzene[J].AppliedCatalysisB:Environmental,2011,104:30-36.[5] Y.Hu, DZLi, Y.Zheng, W.Chen, YHHe, Y.Shao, XZFu, GCXiao. BiVO 4 /TiO 2 nanocrystalline heterostructure: Awidespectrum responsive photocatalyst towards the highly efficient decomposition of gaseous benzene [J]. .

[6]Z.J.Zhang,W.Z.Wang,L.Wang,S.M.Sun.Enhancementofvisible-lightphotocatalysisbycouplingwithnarrow-band-gapsemiconductor:AcasestudyonBi2S3/Bi2WO6[J].ACSAppliedMaterials&Interfaces,2012,4:593-597.[6] ZJ Zhang, WZ Wang, L. Wang, SMSun. Enhancement of visible-light photocatalysis by coupling with narrow-band-gapsemiconductor: Acase study on Bi 2 S 3 /Bi 2 WO 6 [J]. ACS Applied Materials & Interfaces, 2012, 4:593-597.

[7]Z.G.Yi,J.H.Ye,N.Kikugawa,T.Kako,S.X.Ouyang,H.Stuart-Williams,H.Yang,J.Y.Cao,W.J.Luo,Z.S.Li,Y.Liu,R.L.Withers.Anorthophosphatesemiconductorwithphotooxidationpropertiesundervisible-lightirradiation[J].NatureMaterials,2010,9:559-564.[7] Z.G.Yi, J.H.Ye, N.Kikugawa, T.Kako, S.X.Ouyang, H.Stuart-Williams, H.Yang, J.Y.Cao, W.J.Luo, Z.S.Li, Y.Liu, R.L.Withers.Anorthophosphatesemiconductorwithphotooxidationpropertiesundervisible-lightirradiation[ J]. Nature Materials, 2010, 9:559-564.

发明内容Contents of the invention

本发明的目的在于针对现有技术中存在的问题,提供一种Bi2WO6/Ag3PO4异质结复合光催化剂及其制备方法和应用。The object of the present invention is to provide a Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst and its preparation method and application in view of the problems existing in the prior art.

为实现上述目的,本发明采用以下技术方案实施:To achieve the above object, the present invention adopts the following technical solutions to implement:

一种Bi2WO6/Ag3PO4异质结复合光催化剂,由Bi2WO6和Ag3PO4组成;其中,Ag3PO4纳米颗粒沉积在三维分层棒状结构的Bi2WO6表面;Bi2WO6与Ag3PO4的摩尔比为1:0.1~10。A Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst consisting of Bi 2 WO 6 and Ag 3 PO 4 ; in which Ag 3 PO 4 nanoparticles are deposited on the Bi 2 WO 6 with three-dimensional layered rod-like structure Surface; the molar ratio of Bi 2 WO 6 to Ag 3 PO 4 is 1:0.1~10.

所述的Bi2WO6与Ag3PO4的摩尔比为1:0.1~5。The molar ratio of Bi 2 WO 6 to Ag 3 PO 4 is 1:0.1-5.

一种Bi2WO6/Ag3PO4异质结复合光催化剂的制备方法:A preparation method of Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst:

(1)Bi2WO6的制备:将Bi(NO3)3·5H2O分散于超纯水中,得到分散液;同时将Na2WO4·2H2O加入到超纯水中,磁力搅拌至完全溶解,得到溶解液;然后在磁力搅拌下将上述Na2WO4溶解液逐滴加入到上述Bi(NO3)3分散液中,得悬浮液,并调节悬浮液pH至5~9搅拌后将悬浮液转移至高压反应釜中,放入电热恒温鼓风干燥箱中120~180℃热处理12~36h,而后将反应釜冷却至室温,经抽滤、洗涤和40~80℃干燥2~10h可得到三维分层棒状结构的Bi2WO6;其中,Bi(NO3)3·5H2O与Na2WO4·2H2O的物质的量之比为2:1;(1) Preparation of Bi 2 WO 6 : Disperse Bi(NO 3 ) 3 ·5H 2 O in ultrapure water to obtain a dispersion; at the same time, add Na 2 WO 4 ·2H 2 O into ultrapure water, magnetic Stir until completely dissolved to obtain a solution; then add the above Na 2 WO 4 solution dropwise to the above Bi(NO 3 ) 3 dispersion under magnetic stirring to obtain a suspension, and adjust the pH of the suspension to 5-9 After stirring, transfer the suspension to a high-pressure reactor, put it into an electric constant temperature blast drying oven at 120-180°C for heat treatment for 12-36 hours, then cool the reactor to room temperature, filter, wash and dry at 40-80°C for 2 Bi 2 WO 6 with a three-dimensional layered rod-like structure can be obtained in ~10 hours; wherein, the ratio of Bi(NO 3 ) 3 ·5H 2 O to Na 2 WO 4 ·2H 2 O is 2:1;

(2)Bi2WO6/Ag3PO4异质结复合光催化剂的制备:将步骤(1)中得到的Bi2WO6分散于超纯水中得分散液,而后在磁力搅拌下加入AgNO3,搅拌至完全溶解得混合液,然后逐滴加入含磷酸根的前躯体溶液,之后继续避光搅拌2~8h,经抽滤、洗涤和40~80℃真空干燥2~10h可得到Bi2WO6/Ag3PO4异质结复合光催化剂;其中,含磷酸根的前躯体中磷酸根与AgNO3中银离子的物质的量之比为1:3。(2) Preparation of Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst: Disperse the Bi 2 WO 6 obtained in step (1) in ultrapure water to obtain a dispersion, and then add AgNO 3. Stir until the mixture is completely dissolved, then add the phosphate-containing precursor solution dropwise, then continue to stir in the dark for 2-8 hours, and then filter, wash and vacuum dry at 40-80°C for 2-10 hours to obtain Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst; wherein, the ratio of the amount of phosphate in the phosphate-containing precursor to the amount of silver ions in AgNO 3 is 1:3.

所述步骤(1)中调节悬浮液pH值采用浓度为0.1~5.0mol/L的NH3·H2O或NaOH。In the step (1), the pH value of the suspension is adjusted using NH 3 ·H 2 O or NaOH with a concentration of 0.1-5.0 mol/L.

所述步骤(2)中含磷酸根的前躯体为Na2HPO4、NaH2PO4、Na3PO4、K2HPO4、KH2PO4或K3PO4其中的一种。The phosphate-containing precursor in the step (2) is one of Na 2 HPO 4 , NaH 2 PO 4 , Na 3 PO 4 , K 2 HPO 4 , KH 2 PO 4 or K 3 PO 4 .

所述步骤(2)中Bi2WO6与加入的AgNO3的物质的量之比为1:0.3~15。The ratio of the amount of Bi 2 WO 6 to the added AgNO 3 in the step (2) is 1:0.3-15.

所述步骤(1)和步骤(2)中分散是采用超声分散10~60min,然后磁力搅拌10~60min。The dispersion in the step (1) and step (2) adopts ultrasonic dispersion for 10-60 minutes, and then magnetic stirring for 10-60 minutes.

一种Bi2WO6/Ag3PO4异质结复合光催化剂的应用,所述Bi2WO6/Ag3PO4异质结复合光催化剂作为水体中杀菌剂的应用。An application of a Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst, the application of the Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst as a fungicide in water.

一种Bi2WO6/Ag3PO4异质结复合光催化剂的应用,所述Bi2WO6/Ag3PO4异质结复合光催化剂在降解染料中的应用。An application of a Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst, the application of the Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst in degrading dyes.

一种Bi2WO6/Ag3PO4异质结复合光催化剂的应用,所述Bi2WO6/Ag3PO4异质结复合光催化剂在水体净化中的应用。An application of a Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst, the application of the Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst in water body purification.

Bi2WO6/Ag3PO4异质结复合光催化剂应用于水体中,对有害微生物铜绿假单胞杆菌(P.aeruginosa)和染料污染物亚甲基蓝(MB)的可见光催化杀灭和降解,采用500W氙灯作为光源,其波长范围为420~760nm;所述微生物浓度为106cfu/mL;所述亚甲基蓝浓度为20mg/L;所述Bi2WO6/Ag3PO4异质结复合光催化剂的用量为1.0mg/mL。Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst is applied in water body to catalyze the killing and degradation of harmful microorganisms Pseudomonas aeruginosa (P.aeruginosa) and dye pollutant methylene blue (MB). A 500W xenon lamp is used as the light source, and its wavelength range is 420-760nm; the concentration of the microorganism is 10 6 cfu/mL; the concentration of the methylene blue is 20 mg/L; the Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst The dosage is 1.0mg/mL.

其光催化活性具体测试方法为:采用500W氙灯作为光源,辅以滤光片;将微生物和亚甲基蓝溶液加入到反应器中,然后加入Bi2WO6/Ag3PO4异质结复合光催化剂,暗态吸附达到平衡后开始光照,光照过程中间隔一定时间取样,通过平板计数法和紫外可见分光光度法测定存活细菌浓度和残余亚甲基蓝浓度,计算杀灭率和降解率。所述的光源为氙灯,其波长范围为420~760nm;所述微生物浓度为106cfu/mL;所述亚甲基蓝浓度为20mg/L;所述Bi2WO6/Ag3PO4异质结复合光催化剂的用量为1.0mg/mL。The specific test method for its photocatalytic activity is: use a 500W xenon lamp as the light source, supplemented by a filter; add microorganisms and methylene blue solution into the reactor, and then add Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst, Lighting was started after the dark state adsorption reached equilibrium, and samples were taken at intervals during the lighting process. The concentration of surviving bacteria and the concentration of residual methylene blue were measured by plate counting and ultraviolet-visible spectrophotometry, and the killing rate and degradation rate were calculated. The light source is a xenon lamp with a wavelength range of 420-760nm; the microorganism concentration is 10 6 cfu/mL; the methylene blue concentration is 20mg/L; the Bi 2 WO 6 /Ag 3 PO 4 heterojunction compound The amount of photocatalyst used was 1.0 mg/mL.

本发明的有益效果在于:The beneficial effects of the present invention are:

本发明通过将Ag3PO4与Bi2WO6复合,构建具有异质结结构的复合材料,加速光生载流子在复合材料表面的分离,进而提高复合材料的光催化性能,对Bi2WO6和Ag3PO4两种材料在光催化领域的实际应用具有重大意义;具体:The present invention constructs a composite material with a heterojunction structure by compounding Ag 3 PO 4 and Bi 2 WO 6 to accelerate the separation of photogenerated carriers on the surface of the composite material, thereby improving the photocatalytic performance of the composite material. Bi 2 WO 6 and Ag 3 PO 4 are of great significance in the practical application of the two materials in the field of photocatalysis; specifically:

(1)本发明采用的制备方法工艺简单、易于控制、成本低廉;(1) The preparation method adopted in the present invention has simple process, easy control and low cost;

(2)本发明制备的由三维分层棒状结构Bi2WO6负载Ag3PO4纳米颗粒构建的Bi2WO6/Ag3PO4异质结复合光催化剂,具有较大的比表面积和良好的可见光吸收性能;(2) The Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst constructed by the three-dimensional layered rod-like structure Bi 2 WO 6 loaded with Ag 3 PO 4 nanoparticles prepared by the present invention has a large specific surface area and good Visible light absorption properties;

(3)本发明制备的Bi2WO6/Ag3PO4异质结复合光催化剂可见光催化活性相比Bi2WO6和Ag3PO4均显著提高,在500W氙灯照射下,1.0mg/mLBi2WO6/Ag3PO4异质结复合光催化剂对浓度为106cfu/mL的微生物20min杀灭率可达99.99%,对浓度为20mg/L的亚甲基蓝25min内实现完全降解;(3) Compared with Bi 2 WO 6 and Ag 3 PO 4 , the Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst prepared by the present invention has significantly improved visible light catalytic activity. 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst can kill 99.99% of microorganisms with a concentration of 10 6 cfu/mL in 20 minutes, and completely degrade methylene blue with a concentration of 20 mg/L within 25 minutes;

(4)本发明制备的Bi2WO6/Ag3PO4异质结复合光催化剂具有良好的稳定性和重复利用性,6次重复使用后仍然具有高效的光催化活性;(4) The Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst prepared by the present invention has good stability and reusability, and still has high-efficiency photocatalytic activity after 6 repeated uses;

(5)本发明制备的Bi2WO6/Ag3PO4异质结复合光催化剂具有异质结结构,加快了光生载流子的分离,减小了光生电子-空穴对的复合几率,提高了可见光催化活性和稳定性,在水体净化和海洋防污等领域具有很好的实用价值和潜在的应用前景。(5) The Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst prepared by the present invention has a heterojunction structure, which accelerates the separation of photogenerated carriers and reduces the recombination probability of photogenerated electron-hole pairs, The visible light catalytic activity and stability are improved, and it has good practical value and potential application prospects in the fields of water body purification and marine antifouling.

附图说明Description of drawings

图1为本发明所制备样品的X-射线衍射(XRD)图谱(其中横坐标为2θ(角度),单位为degree(度);纵坐标为Intensity(强度),单位为a.u.(绝对单位));Fig. 1 is the X-ray diffraction (XRD) collection of illustrative plates of the prepared sample of the present invention (wherein abscissa is 2θ (angle), unit is degree (degree); Ordinate coordinate is Intensity (strength), unit is a.u. (absolute unit)) ;

图2为本发明所制备样品的扫描电子显微镜(FESEM)照片:(A)Ag3PO4,(B)Bi2WO6,(C,D)Bi2WO6/Ag3PO4-1;Fig. 2 is a scanning electron microscope (FESEM) photo of samples prepared in the present invention: (A) Ag 3 PO 4 , (B) Bi 2 WO 6 , (C, D) Bi 2 WO 6 /Ag 3 PO 4 -1;

图3为本发明所制备样品的紫外可见漫反射光谱(UV-DRS)图(其中横坐标为Wavelength(波长),单位为nm(纳米),纵坐标为Absorbance(吸光度),单位为a.u.(绝对单位));Fig. 3 is the ultraviolet-visible diffuse reflectance spectrum (UV-DRS) figure (wherein abscissa is Wavelength (wavelength), unit is nm (nanometer), ordinate is Absorbance (absorbance), unit is a.u. (absolute) of the sample prepared by the present invention unit));

图4为本发明所制备的样品光催化降解反应中亚甲基蓝浓度随时间变化曲线(A)和光催化杀菌反应中铜绿假单胞杆菌的存活曲线(B)(其中A图中横坐标为Time(时间),单位为min(分钟),纵坐标为Ct/C0,C0为反应开始前亚甲基蓝初始浓度,Ct为反应时间为t时的亚甲基蓝浓度;B图中横坐标为Time(时间),单位为min(分钟),纵坐标为Celldensity(细胞浓度),单位为logCcfu/mL(菌落数));Fig. 4 is the survival curve (B) of Pseudomonas aeruginosa in the methylene blue concentration change curve (A) and the photocatalytic bactericidal reaction in the prepared sample photocatalytic degradation reaction of the present invention (wherein the abscissa is Time among the figure A (time) ), the unit is min (minutes), the ordinate is C t /C 0 , C 0 is the initial concentration of methylene blue before the reaction starts, and C t is the methylene blue concentration when the reaction time is t; the abscissa in B is Time (time) , the unit is min (minute), the ordinate is Celldensity (cell concentration), and the unit is logCcfu/mL (number of colonies));

图5为本发明实施例2中制备的Bi2WO6/Ag3PO4-1异质结复合光催化剂重复进行6次杀菌实验后的杀菌率(A)和XRD图谱(B)(其中A图中横坐标为Cyclenumbers(重复使用次数),纵坐标为Antibacterialrate(杀菌率),单位为%;B图中横坐标为2θ(角度),单位为degree(度),纵坐标为Intensity(强度),单位为a.u.(绝对单位))。Figure 5 shows the bactericidal rate (A) and XRD pattern (B) of the Bi 2 WO 6 /Ag 3 PO 4 -1 heterojunction composite photocatalyst prepared in Example 2 of the present invention after 6 repeated bactericidal experiments (A Among the figure, the abscissa is Cyclenumbers (repeated use times), the ordinate is Antibacterialrate (sterilization rate), and the unit is %; the abscissa in B is 2θ (angle), and the unit is degree (degree), and the ordinate is Intensity (strength) , the unit is au (absolute unit)).

具体实施方式detailed description

以下通过具体的实施例对本发明作进一步说明,有助于本领域的普通技术人员更全面的理解本发明,但不以任何方式限制本发明。The present invention will be further described through specific examples below, which will help those of ordinary skill in the art to understand the present invention more comprehensively, but the present invention is not limited in any way.

本发明通过水热合成法和原位沉淀法制备了Bi2WO6/Ag3PO4异质结复合光催化剂,该复合光催化剂具有良好的可见光吸收性能,构建的异质结结构加快了光生载流子的分离,减小了光生电子-空穴对的复合几率,在可见光下具有高效的光催化活性和稳定性,对水体中有害微生物和染料污染物具有高效的杀灭和降解效果,在水体净化和海洋防污等领域具有很好的实用价值和潜在的应用前景。同时该复合光催化剂制备方法具有简单易行、价格低廉和重复性好等特点。The present invention prepares Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst by hydrothermal synthesis method and in-situ precipitation method. The composite photocatalyst has good visible light absorption performance, and the constructed heterojunction structure accelerates photogeneration The separation of carriers reduces the recombination probability of photogenerated electron-hole pairs, has high photocatalytic activity and stability under visible light, and has efficient killing and degradation effects on harmful microorganisms and dye pollutants in water bodies. It has good practical value and potential application prospect in the fields of water body purification and marine antifouling. At the same time, the preparation method of the composite photocatalyst has the characteristics of simplicity, low cost, good repeatability and the like.

实施例1:Example 1:

Bi2WO6/Ag3PO4异质结复合光催化剂的制备方法:Preparation method of Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst:

(1)通过水热合成法制备三维分层棒状结构的Bi2WO6:称取5.0mmolBi(NO3)3·5H2O加入到30mL超纯水中,超声分散30min,然后磁力搅拌30min,得分散液;同时将5.0mmolNa2WO4·2H2O加入到30.0mL超纯水中,磁力搅拌至完全溶解,得到溶解液;之后向上述Bi(NO3)3分散液中逐滴加入上述Na2WO4溶解液,得悬浮液,而后用2.0mol/LNH3·H2O溶液调节悬浮液的pH为7,之后继续搅拌60min;搅拌结束后,将悬浮液转移至配有聚四氟乙烯内衬的高压反应釜中,放入电热恒温鼓风干燥箱中160℃热处理24h;反应结束后,将反应釜冷却至室温,产物经过抽滤,抽滤所得沉淀依次经超纯水和无水乙醇洗涤,而后于60℃干燥6h,可得到具有三维分层棒状结构的Bi2WO6(参见图1-3)。(1) Preparation of Bi 2 WO 6 with a three-dimensional layered rod-like structure by hydrothermal synthesis: Weigh 5.0 mmol Bi(NO 3 ) 3 ·5H 2 O into 30 mL of ultrapure water, ultrasonically disperse for 30 min, and then magnetically stir for 30 min. To obtain a dispersion; at the same time, add 5.0mmolNa 2 WO 4 2H 2 O to 30.0mL ultrapure water, stir magnetically until completely dissolved to obtain a solution; then add the above Bi(NO 3 ) 3 dispersion dropwise to the above Na 2 WO 4 solution to obtain a suspension, then use 2.0mol/LNH 3 ·H 2 O solution to adjust the pH of the suspension to 7, and then continue to stir for 60 minutes; after the stirring is completed, transfer the suspension to a In a high-pressure reaction kettle lined with ethylene, heat treatment at 160°C for 24 hours in an electric constant temperature blast drying oven; After washing with water and ethanol, and then drying at 60°C for 6 hours, Bi 2 WO 6 with a three-dimensional layered rod-like structure can be obtained (see Figures 1-3).

(2)通过原位沉淀法制备Bi2WO6/Ag3PO4异质结复合光催化剂:控制Bi2WO6与Ag3PO4的摩尔比为1:1,称取上述所得1.0mmolBi2WO6加入到30mL超纯水中,超声分散30min,然后磁力搅拌30min,得到分散液;之后称取3.0mmolAgNO3加入到上述Bi2WO6分散液中,搅拌至完全溶解,得到混合液;同时将1.0mmolNa2HPO4·12H2O加入到30mL超纯水中,磁力搅拌使其完全溶解,得到溶解液;然后将上述Na2HPO4溶解液逐滴加入到上述Bi2WO6与AgNO3的混合液中,继续在室温下避光搅拌5h;搅拌结束后,产物经过抽滤,抽滤所得沉淀依次经超纯水和无水乙醇洗涤,而后于60℃真空干燥箱中干燥6h,可得到Bi2WO6/Ag3PO4异质结复合光催化剂,记为Bi2WO6/Ag3PO4-1(参见图1-3)。(2) Preparation of Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst by in-situ precipitation method: control the molar ratio of Bi 2 WO 6 to Ag 3 PO 4 to 1:1, and weigh 1.0 mmol Bi 2 obtained above Add WO 6 into 30mL ultrapure water, ultrasonically disperse for 30min, and then magnetically stir for 30min to obtain a dispersion; then weigh 3.0mmol AgNO 3 and add it to the above Bi 2 WO 6 dispersion, stir until completely dissolved to obtain a mixed solution; at the same time Add 1.0mmol Na 2 HPO 4 ·12H 2 O into 30mL of ultrapure water, and stir it magnetically to completely dissolve to obtain a solution; then add the above Na 2 HPO 4 solution dropwise to the above Bi 2 WO 6 and AgNO 3 In the mixed solution, continue to stir at room temperature in the dark for 5 hours; after the stirring is completed, the product is filtered by suction, and the precipitate obtained by suction filtration is washed with ultrapure water and absolute ethanol in turn, and then dried in a vacuum oven at 60°C for 6 hours. A Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst was obtained, denoted as Bi 2 WO 6 /Ag 3 PO 4 -1 (see Figures 1-3).

对比实施例1:Comparative Example 1:

单体Ag3PO4的制备方法:The preparation method of monomer Ag 3 PO 4 :

通过共沉淀法制备。将3.0mmolAgNO3溶解到30mL超纯水中,磁力搅拌使其完全溶解;同时将1.0mmolNa2HPO4·12H2O加入到30mL超纯水中,磁力搅拌使其完全溶解,分别得到溶解液;然后将上述Na2HPO4溶解液在磁力搅拌下逐滴滴加到上述AgNO3溶解液中,得到悬浮液,继续在室温下避光搅拌5h;搅拌结束后,产物经过抽滤,抽滤后沉淀依次经超纯水和无水乙醇洗涤数次,而后于60℃真空干燥箱中干燥6h,可得到Ag3PO4单体材料,记为Ag3PO4(参见图1-3)。Prepared by co-precipitation method. Dissolve 3.0mmol AgNO 3 in 30mL ultrapure water, and stir it magnetically to dissolve completely; at the same time, add 1.0mmol Na 2 HPO 4 ·12H 2 O into 30mL ultrapure water, stir magnetically to dissolve it completely, and obtain the solution respectively; Then, the above-mentioned Na 2 HPO 4 solution was added dropwise to the above-mentioned AgNO 3 solution under magnetic stirring to obtain a suspension, and continued to stir at room temperature in the dark for 5 hours; after the stirring was completed, the product was subjected to suction filtration. The precipitate was washed several times with ultrapure water and absolute ethanol in sequence, and then dried in a vacuum oven at 60°C for 6 hours to obtain a single material of Ag 3 PO 4 , denoted as Ag 3 PO 4 (see Figure 1-3).

由图1可知,a曲线为实施例1制备的单体Bi2WO6的XRD图谱,所有衍射峰的位置与标准卡片JCPDSNo.73-1126完全吻合,均归属于斜方晶系的Bi2WO6,而且没有出现任何杂质相,可以确定实施例1制备的样品为纯的斜方相Bi2WO6。b曲线为对比实施例1制备的单体Ag3PO4的XRD图谱,由图可见,图中所有的衍射峰都与标准的立方晶系Ag3PO4相对应(JCPDSNo.06-0505),且没有杂相衍射峰出现,表明对比实施例1所制备的样品为纯的立方结构Ag3PO4。图中的c曲线为实施例1制备的Bi2WO6/Ag3PO4-1异质结复合光催化剂的XRD图谱,图谱中包含了立方相Ag3PO4和斜方相Bi2WO6的所有特征峰,说明Ag3PO4和Bi2WO6成功复合在一起形成复合材料。在复合材料的XRD图谱中没有出现其他杂质峰,说明复合材料中只是由Bi2WO6和Ag3PO4两种物质组成,并没有其他杂质相存在。It can be seen from Figure 1 that the curve a is the XRD pattern of the monomer Bi 2 WO 6 prepared in Example 1, and the positions of all diffraction peaks are completely consistent with the standard card JCPDS No.73-1126, and they all belong to orthorhombic Bi 2 WO 6 , and no impurity phase appeared, it can be confirmed that the sample prepared in Example 1 is pure orthorhombic Bi 2 WO 6 . Curve b is the XRD spectrum of the monomer Ag3PO4 prepared in Comparative Example 1 , as can be seen from the figure, all the diffraction peaks in the figure correspond to the standard cubic system Ag3PO4 ( JCPDSNo.06-0505 ), And no heterophase diffraction peak appeared, indicating that the sample prepared in Comparative Example 1 was pure cubic Ag 3 PO 4 . Curve c in the figure is the XRD pattern of Bi 2 WO 6 /Ag 3 PO 4 -1 heterojunction composite photocatalyst prepared in Example 1, which contains cubic phase Ag 3 PO 4 and orthorhombic phase Bi 2 WO 6 All the characteristic peaks, indicating that Ag 3 PO 4 and Bi 2 WO 6 are successfully combined to form a composite material. There are no other impurity peaks in the XRD spectrum of the composite material, indicating that the composite material is only composed of Bi 2 WO 6 and Ag 3 PO 4 , and no other impurity phases exist.

由图2(A)可见,对比实施例1制备的Ag3PO4为呈球状颗粒,结晶度较高,尺寸约为200nm,颗粒分散度良好,晶粒之间没有明显的团聚现象。由图2(B)可见,实施例1制备的Bi2WO6为三维分层的棒状结构,长约10μm,宽约1μm,这种分层的棒状结构是由许多规则的二维纳米薄片交叉堆积而成,每个纳米片大小约为100nm,厚度约为20nm。由图2(C)和图2(D)可见,实施例1制备的Bi2WO6/Ag3PO4-1异质结复合光催化剂由尺寸约为10μm的三维分层棒状结构Bi2WO6负载粒径约为50nm的Ag3PO4纳米颗粒组装而成,这种负载小颗粒的分层三维结构将具有较大的比表面积和良好的可见光吸收性能。It can be seen from Fig. 2(A) that the Ag 3 PO 4 prepared in Comparative Example 1 is spherical particles with high crystallinity, the size is about 200nm, the particle dispersion is good, and there is no obvious agglomeration phenomenon between crystal grains. It can be seen from Fig. 2(B) that the Bi 2 WO 6 prepared in Example 1 is a three-dimensional layered rod-like structure with a length of about 10 μm and a width of about 1 μm. This layered rod-like structure is composed of many regular two-dimensional nanosheets intersecting Stacked, the size of each nanosheet is about 100nm, and the thickness is about 20nm. It can be seen from Figure 2(C) and Figure 2(D) that the Bi 2 WO 6 /Ag 3 PO 4 -1 heterojunction composite photocatalyst prepared in Example 1 consists of a three-dimensional layered rod-like structure Bi 2 WO with a size of about 10 μm 6 Ag 3 PO 4 nanoparticles with a loading particle size of about 50nm are assembled. This layered three-dimensional structure loaded with small particles will have a large specific surface area and good visible light absorption performance.

由图3可见,Bi2WO6、Ag3PO4和Bi2WO6/Ag3PO4-1复合材料在紫外区和可见光区均有良好的吸收,显示出良好的可见光吸收性能。此外,具有良好可见光吸收性能的Ag3PO4与Bi2WO6复合大大提高了Bi2WO6的可见光吸收性能。It can be seen from Figure 3 that Bi 2 WO 6 , Ag 3 PO 4 and Bi 2 WO 6 /Ag 3 PO 4 -1 composite materials have good absorption in both ultraviolet and visible light regions, showing good visible light absorption performance. In addition, the combination of Ag 3 PO 4 with good visible light absorption performance and Bi 2 WO 6 greatly improves the visible light absorption performance of Bi 2 WO 6 .

实施例2:Example 2:

Bi2WO6/Ag3PO4异质结复合光催化剂的制备方法:Preparation method of Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst:

通过原位沉淀法制备,与实施例1不同之处在于,控制Bi2WO6与Ag3PO4的摩尔比为1:0.75,称取上述所得1.0mmolBi2WO6加入到30mL超纯水中,超声分散30min,然后磁力搅拌30min,得到分散液;之后称取2.25mmolAgNO3加入到上述Bi2WO6分散液中,搅拌至完全溶解,得到混合液;同时将0.75mmolNa2HPO4·12H2O加入到30mL超纯水中,磁力搅拌使其完全溶解,得到溶解液;然后将上述Na2HPO4溶解液逐滴加入到上述Bi2WO6与AgNO3的混合液中,继续在室温下避光搅拌5h;搅拌结束后,产物经过抽滤,抽滤所得沉淀依次经超纯水和无水乙醇洗涤,而后于60℃真空干燥箱中干燥6h,可得到Bi2WO6/Ag3PO4异质结复合光催化剂,记为Bi2WO6/Ag3PO4-0.75。Prepared by in-situ precipitation method, the difference from Example 1 is that the molar ratio of Bi 2 WO 6 to Ag 3 PO 4 is controlled to be 1:0.75, and 1.0 mmol Bi 2 WO 6 obtained above is weighed and added to 30 mL ultrapure water , ultrasonically dispersed for 30 minutes, and then magnetically stirred for 30 minutes to obtain a dispersion; then weighed 2.25 mmol AgNO 3 and added it to the above Bi 2 WO 6 dispersion, and stirred until completely dissolved to obtain a mixed solution; at the same time, 0.75 mmol Na 2 HPO 4 ·12H 2 O was added to 30mL of ultrapure water, and magnetically stirred to completely dissolve it to obtain a solution; then, the above-mentioned Na 2 HPO 4 solution was added dropwise to the above-mentioned Bi 2 WO 6 and AgNO 3 mixed solution, and continued to cool at room temperature Stir in the dark for 5 hours; after the stirring, the product is filtered by suction, and the precipitate obtained by suction filtration is washed with ultrapure water and absolute ethanol in turn, and then dried in a vacuum oven at 60°C for 6 hours to obtain Bi 2 WO 6 /Ag 3 PO 4 Heterojunction composite photocatalyst, denoted as Bi 2 WO 6 /Ag 3 PO 4 -0.75.

实施例3:Example 3:

Bi2WO6/Ag3PO4异质结复合光催化剂的制备方法:Preparation method of Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst:

通过原位沉淀法制备,与实施例1不同之处在于,控制Bi2WO6与Ag3PO4的摩尔比为1:0.5,称取上述所得1.0mmolBi2WO6加入到30mL超纯水中,超声分散30min,然后磁力搅拌30min,得到分散液;之后称取1.5mmolAgNO3加入到上述Bi2WO6分散液中,搅拌至完全溶解,得到混合液;同时将0.5mmolNa2HPO4·12H2O加入到30mL超纯水中,磁力搅拌使其完全溶解,得到溶解液;然后将上述Na2HPO4溶解液逐滴加入到上述Bi2WO6与AgNO3的混合液中,继续在室温下避光搅拌5h;搅拌结束后,产物经过抽滤,抽滤所得沉淀依次经超纯水和无水乙醇洗涤,而后于60℃真空干燥箱中干燥6h,可得到Bi2WO6/Ag3PO4异质结复合光催化剂,记为Bi2WO6/Ag3PO4-0.5。Prepared by in-situ precipitation method, the difference from Example 1 is that the molar ratio of Bi 2 WO 6 to Ag 3 PO 4 is controlled to be 1:0.5, and 1.0 mmol Bi 2 WO 6 obtained above is weighed and added to 30 mL ultrapure water , ultrasonically dispersed for 30 minutes, and then magnetically stirred for 30 minutes to obtain a dispersion; then weighed 1.5 mmol AgNO 3 and added it to the above Bi 2 WO 6 dispersion, and stirred until completely dissolved to obtain a mixed solution; at the same time, 0.5 mmol Na 2 HPO 4 ·12H 2 O was added to 30mL of ultrapure water, and magnetically stirred to completely dissolve it to obtain a solution; then, the above-mentioned Na 2 HPO 4 solution was added dropwise to the above-mentioned Bi 2 WO 6 and AgNO 3 mixed solution, and continued to cool at room temperature Stir in the dark for 5 hours; after the stirring, the product is filtered by suction, and the precipitate obtained by suction filtration is washed with ultrapure water and absolute ethanol in turn, and then dried in a vacuum oven at 60°C for 6 hours to obtain Bi 2 WO 6 /Ag 3 PO 4 Heterojunction composite photocatalyst, denoted as Bi 2 WO 6 /Ag 3 PO 4 -0.5.

实施例4:Example 4:

Bi2WO6/Ag3PO4异质结复合光催化剂的制备方法:Preparation method of Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst:

通过原位沉淀法制备,与实施例1不同之处在于,控制Bi2WO6与Ag3PO4的摩尔比为1:0.25,称取上述所得1.0mmolBi2WO6加入到30mL超纯水中,超声分散30min,然后磁力搅拌30min,得到分散液;之后称取0.75mmolAgNO3加入到上述Bi2WO6分散液中,搅拌至完全溶解,得到混合液;同时将0.25mmolNa2HPO4·12H2O加入到30mL超纯水中,磁力搅拌使其完全溶解,得到溶解液;然后将上述Na2HPO4溶解液逐滴加入到上述Bi2WO6与AgNO3的混合液中,继续在室温下避光搅拌5h;搅拌结束后,产物经过抽滤,抽滤所得沉淀依次经超纯水和无水乙醇洗涤,而后于60℃真空干燥箱中干燥6h,可得到Bi2WO6/Ag3PO4异质结复合光催化剂,记为Bi2WO6/Ag3PO4-0.25。Prepared by in-situ precipitation method, the difference from Example 1 is that the molar ratio of Bi 2 WO 6 to Ag 3 PO 4 is controlled to be 1:0.25, and 1.0 mmol Bi 2 WO 6 obtained above is weighed and added to 30 mL ultrapure water , ultrasonically dispersed for 30 minutes, and then magnetically stirred for 30 minutes to obtain a dispersion; then weighed 0.75 mmol AgNO 3 and added it to the above Bi 2 WO 6 dispersion, and stirred until completely dissolved to obtain a mixed solution; at the same time, 0.25 mmol Na 2 HPO 4 ·12H 2 O was added to 30mL of ultrapure water, and magnetically stirred to completely dissolve it to obtain a solution; then, the above-mentioned Na 2 HPO 4 solution was added dropwise to the above-mentioned Bi 2 WO 6 and AgNO 3 mixed solution, and continued to cool at room temperature Stir in the dark for 5 hours; after the stirring, the product is filtered by suction, and the precipitate obtained by suction filtration is washed with ultrapure water and absolute ethanol in turn, and then dried in a vacuum oven at 60°C for 6 hours to obtain Bi 2 WO 6 /Ag 3 PO 4 Heterojunction composite photocatalyst, denoted as Bi 2 WO 6 /Ag 3 PO 4 -0.25.

应用例1:Application example 1:

上述所得Bi2WO6/Ag3PO4异质结复合光催化剂应用于染料污染物亚甲基蓝MB的可见光催化降解:The Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst obtained above was applied to the visible light catalytic degradation of the dye pollutant methylene blue MB:

以500W氙灯作为光源,辅以滤光片滤掉紫外光,使其波长范围为420~760nm。将50mL20mg/L的亚甲基蓝溶液加入到50mL反应器中,加入50mg本发明制备的光催化剂,暗态吸附达到平衡后进行光催化反应,反应过程中间隔一定时间取样,离心分离后取上层清液在紫外-可见分光光度计上测定664nm波长下亚甲基蓝溶液的吸光度,得到亚甲基蓝溶液的残余浓度,以此计算降解率,空白实验和暗态实验作为对照实验(参见图4A)。A 500W xenon lamp is used as a light source, supplemented by a filter to filter out ultraviolet light, so that the wavelength range is 420-760nm. Add 50mL of 20mg/L methylene blue solution into a 50mL reactor, add 50mg of the photocatalyst prepared by the present invention, carry out the photocatalytic reaction after the dark state adsorption reaches equilibrium, take samples at regular intervals during the reaction process, and take the supernatant after centrifugation. The absorbance of the methylene blue solution at a wavelength of 664nm was measured on a UV-visible spectrophotometer to obtain the residual concentration of the methylene blue solution, and the degradation rate was calculated based on this. The blank experiment and the dark experiment were used as control experiments (see Figure 4A).

由图4(A)可见,空白实验中亚甲基蓝几乎没有降解,对实验的影响可以忽略。另外,暗态实验表明Bi2WO6/Ag3PO4-1异质结复合光催化剂因具有较大的比表面积而具有一定的吸附性能,但是对光催化反应的影响可以忽略。在可见光照下,Bi2WO6/Ag3PO4-1复合光催化剂显示出良好的光催化活性,光催化性能明显优于单体Bi2WO6和Ag3PO4,在25min光催化反应时间内对亚甲基蓝的降解率可达到100%。因此,将具有良好可见光吸收性能和光催化活性的Ag3PO4与Bi2WO6复合形成异质结结构可使光生电子-空穴在复合材料表面有效分离,并提高了复合材料的可见光吸收性能和比表面积,增强了复合材料的可见光催化性能。It can be seen from Figure 4(A) that methylene blue was almost not degraded in the blank experiment, and the influence on the experiment was negligible. In addition, the dark state experiments show that the Bi 2 WO 6 /Ag 3 PO 4 -1 heterojunction composite photocatalyst has a certain adsorption performance due to its large specific surface area, but its influence on the photocatalytic reaction can be ignored. Under visible light, the Bi 2 WO 6 /Ag 3 PO 4 -1 composite photocatalyst showed good photocatalytic activity, and the photocatalytic performance was significantly better than that of monomer Bi 2 WO 6 and Ag 3 PO 4 . The degradation rate of methylene blue can reach 100% in a short period of time. Therefore, combining Ag 3 PO 4 with good visible light absorption performance and photocatalytic activity with Bi 2 WO 6 to form a heterojunction structure can effectively separate photogenerated electrons-holes on the surface of the composite material and improve the visible light absorption performance of the composite material. and specific surface area, enhancing the visible light catalytic performance of the composite.

应用例2:Application example 2:

上述所得Bi2WO6/Ag3PO4异质结复合光催化剂应用于水体中,对有害微生物铜绿假单胞杆菌的可见光杀灭:The Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst obtained above is applied to the water body to kill the harmful microorganism Pseudomonas aeruginosa with visible light:

以500W氙灯作为光源,辅以滤光片滤掉紫外光,使其波长范围为420~760nm。以铜绿假单胞杆菌(P.aeruginosa,8.0×108cfu/mL)评价Bi2WO6/Ag3PO4异质结复合光催化剂的可见光催化杀菌性能:A 500W xenon lamp is used as a light source, supplemented by a filter to filter out ultraviolet light, so that the wavelength range is 420-760nm. Visible light catalytic bactericidal performance of Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst was evaluated with Pseudomonas aeruginosa (P.aeruginosa, 8.0×10 8 cfu/mL):

首先准备细菌悬液,将铜绿假单胞杆菌储存液接种到灭菌LB液体培养基中,然后将其置于37℃、150rpm的空气恒温摇床中,过夜培养。培养得到的细菌悬液离心后悬浮于0.01mol/LPBS(pH=7.4)缓冲液中,得到浓度为8.0×108cfu/mL的铜绿假单胞杆菌悬液。First prepare the bacterial suspension, inoculate the stock solution of Pseudomonas aeruginosa into the sterilized LB liquid medium, and then place it in an air constant temperature shaker at 37°C and 150rpm for overnight culture. The cultured bacterial suspension was centrifuged and suspended in 0.01 mol/LPBS (pH=7.4) buffer to obtain a Pseudomonas aeruginosa suspension with a concentration of 8.0×10 8 cfu/mL.

光催化实验中取49.5mL灭菌0.01mol/LPBS(pH=7.4)缓冲液加入到50mL反应器中,然后加入500μL细菌悬液,使反应液中细菌浓度为8.0×106cfu/mL,加入50mg本发明制备的光催化剂。暗态吸附达到平衡后进行光催化反应,反应过程中间隔一定时间取样,通过平板计数法确定细菌的存活率和杀菌率。具体步骤为:取1.0mL反应液,用0.01mol/LPBS(pH=7.4)缓冲液按照系列稀释法依次稀释几个梯度,然后从不同稀释倍数的溶液中取100μL至已经准备好的LB固体培养基上,将菌液均匀地涂抹在LB培养基上。将LB培养基倒置,放入电热恒温培养箱中37℃培养24h,通过计数培养基上长出的菌落个数,以及相应稀释倍数得出细菌浓度,以确定细菌的存活率和杀菌率。实验中每组实验均需平行测定3次,取平均值作为最后结果,空白实验和暗态实验作为对照实验(参见图4B)。In the photocatalytic experiment, 49.5 mL of sterilized 0.01mol/LPBS (pH=7.4) buffer solution was added to a 50 mL reactor, and then 500 μL of bacterial suspension was added to make the bacterial concentration in the reaction solution 8.0×10 6 cfu/mL. 50mg of the photocatalyst prepared by the present invention. After the dark state adsorption reached equilibrium, the photocatalytic reaction was carried out. During the reaction process, samples were taken at intervals, and the survival rate and bactericidal rate of bacteria were determined by plate counting. The specific steps are: take 1.0mL of the reaction solution, dilute several gradients sequentially with 0.01mol/LPBS (pH=7.4) buffer according to the serial dilution method, and then take 100μL from the solutions of different dilution times to the prepared LB solid culture Spread the bacterial solution evenly on the LB medium. Invert the LB medium, put it into an electric thermostat incubator and incubate at 37°C for 24 hours, count the number of colonies grown on the medium, and obtain the bacterial concentration by counting the corresponding dilution factor to determine the survival rate and sterilization rate of the bacteria. In the experiment, each group of experiments needs to be measured in parallel three times, and the average value is taken as the final result, and the blank experiment and dark state experiment are used as control experiments (see FIG. 4B ).

由图4(B)可见,在空白实验中铜绿假单胞杆菌的数目几乎没有变化,表明可见光照的影响可以忽略;而在黑暗条件下,铜绿假单胞杆菌的数目有一定减少,这是因为Bi2WO6/Ag3PO4-1异质结复合光催化剂中含有Ag元素,在水溶液中会有部分Ag+释放出来,Ag+也具有一定的杀菌性能,可以与细菌发生作用,导致细菌凋亡。而在可见光照下Bi2WO6/Ag3PO4-1异质结复合光催化剂显示出良好的光催化活性,光催化杀菌性能明显优于单体Bi2WO6和Ag3PO4,经过20min光照只有约2.9log的细菌存活,杀菌率可达到99.99%,若延长反应时间至30min,体系中细菌浓度已经可以忽略不计。因此,Bi2WO6/Ag3PO4-1异质结复合光催化剂具有极佳的光催化杀菌防污性能,可归因于Ag3PO4与Bi2WO6复合形成异质结结构,加速了光生电子-空穴的分离,提高了复合材料的光催化活性。同时,Bi2WO6/Ag3PO4-1异质结复合光催化剂具有较大的比表面积和良好的可见光吸收性能,导致其可见光催化性能提高,具有良好的可见光催化杀菌性能。It can be seen from Figure 4(B) that the number of Pseudomonas aeruginosa has almost no change in the blank experiment, indicating that the influence of visible light can be ignored; while under dark conditions, the number of Pseudomonas aeruginosa has a certain reduction, which is Because the Bi 2 WO 6 /Ag 3 PO 4 -1 heterojunction composite photocatalyst contains Ag element, some Ag + will be released in the aqueous solution, and Ag + also has certain bactericidal properties, which can interact with bacteria and cause Bacterial apoptosis. However, Bi 2 WO 6 /Ag 3 PO 4 -1 heterojunction composite photocatalyst showed good photocatalytic activity under visible light, and the photocatalytic bactericidal performance was significantly better than monomer Bi 2 WO 6 and Ag 3 PO 4 . Only about 2.9log of bacteria can survive under 20 minutes of light, and the bactericidal rate can reach 99.99%. If the reaction time is extended to 30 minutes, the concentration of bacteria in the system can be ignored. Therefore, the Bi 2 WO 6 /Ag 3 PO 4 -1 heterojunction composite photocatalyst has excellent photocatalytic sterilization and antifouling performance, which can be attributed to the complex formation of Ag 3 PO 4 and Bi 2 WO 6 to form a heterojunction structure, The separation of photogenerated electrons and holes is accelerated, and the photocatalytic activity of the composite material is improved. At the same time, the Bi 2 WO 6 /Ag 3 PO 4 -1 heterojunction composite photocatalyst has a large specific surface area and good visible light absorption performance, resulting in improved visible light catalytic performance and good visible light catalytic bactericidal performance.

应用例3:Application example 3:

上述所得Bi2WO6/Ag3PO4异质结复合光催化剂重复应用于水体中,对有害微生物铜绿假单胞杆菌的可见光杀灭:The Bi 2 WO 6 /Ag 3 PO 4 heterojunction composite photocatalyst obtained above is repeatedly applied in the water body to kill the harmful microorganism Pseudomonas aeruginosa with visible light:

将应用例2中的光催化杀菌中所用的Bi2WO6/Ag3PO4-1异质结复合光催化剂回收,分别用超纯水和无水乙醇多次洗涤,经干燥后按照应用例2中的步骤进行下一次光催化杀菌反应,连续进行6次,保持其他条件不变(参见图5)。Recover the Bi 2 WO 6 /Ag 3 PO 4 -1 heterojunction composite photocatalyst used in the photocatalytic sterilization in Application Example 2, wash it with ultrapure water and absolute ethanol several times, and dry it according to the application example The steps in 2 are carried out for the next photocatalytic sterilization reaction, which is carried out continuously for 6 times, keeping other conditions unchanged (see Figure 5).

由图5(A)可知,Bi2WO6/Ag3PO4-1异质结复合光催化剂对细菌的杀灭率在连续反应6次后并没有明显降低,依然保持在99%以上,显示出良好的重复利用性。将连续进行6次光催化杀菌实验的Bi2WO6/Ag3PO4-1异质结复合光催化剂回收,分别用超纯水和无水乙醇多次洗涤,经干燥后进行XRD测试,如图5(B)所示,从图中可以看出经过连续6次光催化杀菌反应后,Bi2WO6/Ag3PO4-1异质结复合光催化剂的晶体结构未发生改变,表现出良好的稳定性,在水体净化和海洋防污等领域具有很好的实用价值和潜在的应用前景。It can be seen from Figure 5(A) that the killing rate of bacteria by the Bi 2 WO 6 /Ag 3 PO 4 -1 heterojunction composite photocatalyst did not decrease significantly after 6 consecutive reactions, and remained above 99%, showing that Good reusability. The Bi 2 WO 6 /Ag 3 PO 4 -1 heterojunction composite photocatalyst that has been subjected to 6 consecutive photocatalytic sterilization experiments was recovered, washed with ultrapure water and absolute ethanol for multiple times, dried and then tested by XRD, as shown in As shown in Figure 5(B), it can be seen from the figure that after six consecutive photocatalytic sterilization reactions, the crystal structure of the Bi 2 WO 6 /Ag 3 PO 4 -1 heterojunction composite photocatalyst has not changed, showing With good stability, it has good practical value and potential application prospects in the fields of water body purification and marine antifouling.

Claims (10)

1. a Bi 2wO 6/ Ag 3pO 4heterojunction composite photocatalyst, is characterized in that: Bi 2wO 6/ Ag 3pO 4heterojunction composite photocatalyst is by Bi 2wO 6and Ag 3pO 4composition; Wherein, Ag 3pO 4nanoparticle deposition is at the Bi of three-dimensional layering club shaped structure 2wO 6surface; Bi 2wO 6with Ag 3pO 4mol ratio be 1:0.1 ~ 10.
2. Bi according to claim 1 2wO 6/ Ag 3pO 4heterojunction composite photocatalyst, is characterized in that: described Bi 2wO 6with Ag 3pO 4mol ratio be 1:0.1 ~ 5.
3. a Bi according to claim 1 2wO 6/ Ag 3pO 4the preparation method of heterojunction composite photocatalyst, is characterized in that:
(1) Bi 2wO 6preparation: by Bi (NO 3) 35H 2o is scattered in ultra-pure water, obtains dispersion liquid; Simultaneously by Na 2wO 42H 2o joins in ultra-pure water, and magnetic agitation, to dissolving completely, obtains lysate; Then under magnetic stirring by above-mentioned Na 2wO 4lysate dropwise joins above-mentioned Bi (NO 3) 3in dispersion liquid, obtain suspension, and after regulating pH of suspension to 5 ~ 9 to stir, suspension is transferred in autoclave, put into electric heating constant-temperature blowing drying box 120 ~ 180 DEG C of heat treatment 12 ~ 36h, then reactor is cooled to room temperature, the Bi of three-dimensional layering club shaped structure can be obtained through suction filtration, washing and 40 ~ 80 DEG C of drying 2 ~ 10h 2wO 6; Wherein, Bi (NO 3) 35H 2o and Na 2wO 42H 2the ratio of the amount of substance of O is 2:1;
(2) Bi 2wO 6/ Ag 3pO 4the preparation of heterojunction composite photocatalyst: by the Bi obtained in step (1) 2wO 6be scattered in ultra-pure water and obtain dispersion liquid, then add AgNO under magnetic stirring 3, be stirred to and dissolve to obtain mixed liquor completely, then dropwise add the precursor solution of phosphorous acid group, continue lucifuge afterwards and stir 2 ~ 8h, can Bi be obtained through suction filtration, washing and 40 ~ 80 DEG C of vacuum drying 2 ~ 10h 2wO 6/ Ag 3pO 4heterojunction composite photocatalyst; Wherein, phosphate radical and AgNO in the precursor of phosphorous acid group 3the ratio of the amount of substance of middle silver ion is 1:3.
4. Bi according to claim 3 2wO 6/ Ag 3pO 4the preparation method of heterojunction composite photocatalyst, is characterized in that: regulate suspension pH value to adopt concentration to be the NH of 0.1 ~ 5.0mol/L in described step (1) 3h 2o or NaOH.
5. Bi according to claim 3 2wO 6/ Ag 3pO 4the preparation method of heterojunction composite photocatalyst, is characterized in that: in described step (2), the precursor of phosphorous acid group is Na 2hPO 4, NaH 2pO 4, Na 3pO 4, K 2hPO 4, KH 2pO 4or K 3pO 4one wherein.
6. Bi according to claim 3 2wO 6/ Ag 3pO 4the preparation method of heterojunction composite photocatalyst, is characterized in that: Bi in described step (2) 2wO 6with the AgNO added 3the ratio of amount of substance be 1:0.3 ~ 15.
7. a kind of Bi according to claim 3 2wO 6/ Ag 3pO 4the preparation method of heterojunction composite photocatalyst, is characterized in that: disperse to be adopt ultrasonic disperse 10 ~ 60min, then magnetic agitation 10 ~ 60min in described step (1) and step (2).
8. a Bi according to claim 1 2wO 6/ Ag 3pO 4the application of heterojunction composite photocatalyst, is characterized in that: described Bi 2wO 6/ Ag 3pO 4heterojunction composite photocatalyst is as the bactericide in water body.
9. a Bi according to claim 1 2wO 6/ Ag 3pO 4the application of heterojunction composite photocatalyst, is characterized in that: described Bi 2wO 6/ Ag 3pO 4the application of heterojunction composite photocatalyst in degradation of dye.
10. a Bi according to claim 1 2wO 6/ Ag 3pO 4the application of heterojunction composite photocatalyst, is characterized in that: described Bi 2wO 6/ Ag 3pO 4the application of heterojunction composite photocatalyst in water body purification.
CN201510789041.8A 2015-11-17 2015-11-17 A kind of Bi2WO6/Ag3PO4 heterojunction composite photocatalyst and its preparation method and application Pending CN105289673A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201510789041.8A CN105289673A (en) 2015-11-17 2015-11-17 A kind of Bi2WO6/Ag3PO4 heterojunction composite photocatalyst and its preparation method and application

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201510789041.8A CN105289673A (en) 2015-11-17 2015-11-17 A kind of Bi2WO6/Ag3PO4 heterojunction composite photocatalyst and its preparation method and application

Publications (1)

Publication Number Publication Date
CN105289673A true CN105289673A (en) 2016-02-03

Family

ID=55187892

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201510789041.8A Pending CN105289673A (en) 2015-11-17 2015-11-17 A kind of Bi2WO6/Ag3PO4 heterojunction composite photocatalyst and its preparation method and application

Country Status (1)

Country Link
CN (1) CN105289673A (en)

Cited By (15)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105727933A (en) * 2016-03-16 2016-07-06 新乡医学院 Bismuth tungstate-bismuth molybdate heterojunction photocatalytic material, method for preparing same and application of bismuth tungstate-bismuth molybdate heterojunction photocatalytic material
CN106378168A (en) * 2016-10-19 2017-02-08 常州大学 Preparation method of manganese phosphate/yttrium phosphate composite catalyst
CN106732698A (en) * 2016-12-06 2017-05-31 安徽工业大学 A kind of p n heterojunction type visible-light photocatalysts Bi2WO6/Ag3PO4And preparation method thereof
CN107827296A (en) * 2017-07-28 2018-03-23 湖南大学 A kind of device and technique that methylene blue waste water is handled using silver phosphate composite photocatalyst
JP2018075525A (en) * 2016-11-09 2018-05-17 国立大学法人 筑波大学 Photocatalyst and method for producing the same
CN109621993A (en) * 2019-01-15 2019-04-16 湖南大学 Method for treating antibiotics with silver phosphate/multi-walled carbon nanotubes/bismuth tungstate composite photocatalytic material
CN109621994A (en) * 2019-01-15 2019-04-16 湖南大学 Silver phosphate/multi-walled carbon nanotubes/bismuth tungstate composite photocatalytic material and preparation method thereof
CN110227557A (en) * 2019-05-20 2019-09-13 湖南大学 Silver orthophosphate and the pucherite Three-element composite photocatalyst of polyaniline modified synergic and its preparation method and application
CN112264059A (en) * 2020-11-18 2021-01-26 安徽汇泽通环境技术有限公司 Preparation method of acid orange 7 pollutant photodegradation composite photocatalyst
CN112264060A (en) * 2020-10-22 2021-01-26 盐城工学院 Ag3PO4-Bi2WO6Preparation method and application of visible light photocatalyst
CN113559845A (en) * 2021-08-27 2021-10-29 陕西科技大学 A kind of bismuth vanadate/silver nitrate composite photocatalyst and preparation method thereof
CN114272944A (en) * 2022-01-20 2022-04-05 辽宁大学 Silver phosphate/cobalt tungstate composite acoustic catalytic material and preparation method and application thereof
CN114308089A (en) * 2021-12-30 2022-04-12 辽宁大学 A kind of Ag3PO4/CuWO4 composite material and its application in degrading organic dyes
CN114904521A (en) * 2021-02-09 2022-08-16 中国建筑材料科学研究总院有限公司 Au/Bi 2 WO 6 Mineral ternary composite material and preparation method and application thereof
CN116984007A (en) * 2023-07-31 2023-11-03 陕西科技大学 0D/2DAg 3 PO 4 /Bi 3 TiNbO 9 Heterojunction photocatalyst, preparation method and application thereof

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102764653A (en) * 2011-05-06 2012-11-07 中国科学院合肥物质科学研究院 Silver-modified bismuth tungstate composite photocatalyst, its preparation method and application thereof
CN103112898A (en) * 2013-02-06 2013-05-22 长安大学 Method for preparing flowerlike bismuth tungstate by hydrothermal process
CN103263919A (en) * 2013-05-15 2013-08-28 天津师范大学 A facile method for preparing Ag/Bi2WO6 heterostructure and in situ photocatalysis
CN104117355A (en) * 2014-07-14 2014-10-29 王丹军 A bismuth tungstate photocatalyst surface-modified by nanometer silver and a preparing method thereof

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102764653A (en) * 2011-05-06 2012-11-07 中国科学院合肥物质科学研究院 Silver-modified bismuth tungstate composite photocatalyst, its preparation method and application thereof
CN103112898A (en) * 2013-02-06 2013-05-22 长安大学 Method for preparing flowerlike bismuth tungstate by hydrothermal process
CN103263919A (en) * 2013-05-15 2013-08-28 天津师范大学 A facile method for preparing Ag/Bi2WO6 heterostructure and in situ photocatalysis
CN104117355A (en) * 2014-07-14 2014-10-29 王丹军 A bismuth tungstate photocatalyst surface-modified by nanometer silver and a preparing method thereof

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
GUOKAI FU等: "Ag3PO4/Bi2WO6 hierarchical heterostructures with enhanced visible light photocatalytic activity for the degradation of phenol", 《CATALYSIS COMMUNICATIONS》 *

Cited By (19)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105727933A (en) * 2016-03-16 2016-07-06 新乡医学院 Bismuth tungstate-bismuth molybdate heterojunction photocatalytic material, method for preparing same and application of bismuth tungstate-bismuth molybdate heterojunction photocatalytic material
CN106378168A (en) * 2016-10-19 2017-02-08 常州大学 Preparation method of manganese phosphate/yttrium phosphate composite catalyst
JP2018075525A (en) * 2016-11-09 2018-05-17 国立大学法人 筑波大学 Photocatalyst and method for producing the same
CN106732698A (en) * 2016-12-06 2017-05-31 安徽工业大学 A kind of p n heterojunction type visible-light photocatalysts Bi2WO6/Ag3PO4And preparation method thereof
CN107827296B (en) * 2017-07-28 2020-12-01 湖南大学 A device and process for treating methylene blue wastewater using silver phosphate composite photocatalyst
CN107827296A (en) * 2017-07-28 2018-03-23 湖南大学 A kind of device and technique that methylene blue waste water is handled using silver phosphate composite photocatalyst
CN109621994A (en) * 2019-01-15 2019-04-16 湖南大学 Silver phosphate/multi-walled carbon nanotubes/bismuth tungstate composite photocatalytic material and preparation method thereof
CN109621993A (en) * 2019-01-15 2019-04-16 湖南大学 Method for treating antibiotics with silver phosphate/multi-walled carbon nanotubes/bismuth tungstate composite photocatalytic material
CN110227557B (en) * 2019-05-20 2021-04-20 湖南大学 Silver phosphate and polyaniline synergistically modified bismuth vanadate ternary composite photocatalyst and its preparation method and application
CN110227557A (en) * 2019-05-20 2019-09-13 湖南大学 Silver orthophosphate and the pucherite Three-element composite photocatalyst of polyaniline modified synergic and its preparation method and application
CN112264060A (en) * 2020-10-22 2021-01-26 盐城工学院 Ag3PO4-Bi2WO6Preparation method and application of visible light photocatalyst
CN112264059A (en) * 2020-11-18 2021-01-26 安徽汇泽通环境技术有限公司 Preparation method of acid orange 7 pollutant photodegradation composite photocatalyst
CN114904521A (en) * 2021-02-09 2022-08-16 中国建筑材料科学研究总院有限公司 Au/Bi 2 WO 6 Mineral ternary composite material and preparation method and application thereof
CN114904521B (en) * 2021-02-09 2024-01-16 中国建筑材料科学研究总院有限公司 An Au/Bi2WO6/mineral ternary composite material and its preparation method and application
CN113559845A (en) * 2021-08-27 2021-10-29 陕西科技大学 A kind of bismuth vanadate/silver nitrate composite photocatalyst and preparation method thereof
CN113559845B (en) * 2021-08-27 2023-10-27 陕西科技大学 A kind of bismuth vanadate@silver phosphate composite photocatalyst and preparation method thereof
CN114308089A (en) * 2021-12-30 2022-04-12 辽宁大学 A kind of Ag3PO4/CuWO4 composite material and its application in degrading organic dyes
CN114272944A (en) * 2022-01-20 2022-04-05 辽宁大学 Silver phosphate/cobalt tungstate composite acoustic catalytic material and preparation method and application thereof
CN116984007A (en) * 2023-07-31 2023-11-03 陕西科技大学 0D/2DAg 3 PO 4 /Bi 3 TiNbO 9 Heterojunction photocatalyst, preparation method and application thereof

Similar Documents

Publication Publication Date Title
CN105289673A (en) A kind of Bi2WO6/Ag3PO4 heterojunction composite photocatalyst and its preparation method and application
CN105289674A (en) A kind of AgVO3/Ag3PO4 heterojunction composite photocatalyst and its preparation method and application
Wu et al. Visible-light-driven photocatalytic bacterial inactivation and the mechanism of zinc oxysulfide under LED light irradiation
CN103480399B (en) Micronano-structured and silver phosphate based composite visible light catalytic material and preparing method thereof
CN106423224B (en) A kind of BiVO4/BiOI heterojunction composite photocatalyst and its preparation method and application
CN103599802A (en) Preparation method of silver phosphate/graphene nanocomposite
CN102580714A (en) Graphene oxide/silver phosphate composite visible light catalyst and preparation method thereof
CN105268438B (en) A kind of plasma composite photo-catalyst and its preparation method and application
CN103240107B (en) Silver phosphate-bismuth vanadate multiplex photocatalyst and preparation method thereof
CN105214695A (en) A kind of Bi 2wO 6/ BiOI heterojunction composite photocatalyst and its preparation method and application
CN106334554A (en) ZnO/Ag composite nano-photocatalyst with high-efficiency photocatalytic activity under visible lights
CN106799219A (en) A kind of preparation method of titania nanoparticles/Graphene composite photocatalyst material
CN105457625A (en) A kind of Bi2WO6/BiVO4 heterojunction composite photocatalyst and its preparation method and application
CN105457663A (en) A kind of Bi2WO6/Ag3PO4 composite photocatalytic bactericide and its preparation method
CN111744503A (en) Z-shaped heterojunction MoS2/Bi2WO6Composite photocatalyst and preparation method and application thereof
CN105435847A (en) A Bi2WO6/BiOI@quaternary ammonium salt inorganic/organic composite photocatalytic fungicide and its preparation method
CN103120944A (en) Silver phosphate cuboid/P25 dual-function composition material and preparation method thereof
CN105597793A (en) Photocatalyst and preparation method and application thereof
Zhang et al. A novel gC 3 N 4 nanosheet/Ag 3 PO 4/α-Bi 2 O 3 ternary dual Z-scheme heterojunction with increased light absorption and expanded specific surface area for efficient photocatalytic removal of TC
Fu et al. Construction of Z-scheme AgCl/BiOCl heterojunction with oxygen vacancies for improved pollutant degradation and bacterial inactivation
CN113578368B (en) g-C 3 N 4 /Ag 3 PO 4 /BiFeO 3 Preparation method and application of composite visible light catalyst
CN106824233A (en) The method of photocatalysis antibacterial or degradation of organic substances
CN105688948A (en) Photocatalyst and preparing method and application thereof
CN105432663A (en) A kind of Ag/AgVO3 plasma composite photocatalytic bactericide and its preparation method and application
CN111686769A (en) Photocatalyst and preparation method and application thereof

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication

Application publication date: 20160203

RJ01 Rejection of invention patent application after publication