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Preparation、modification And Photocatalytic Activity Of Bi2WO6、BiVO4 Photocatalysts

Posted on:2022-08-17Degree:MasterType:Thesis
Country:ChinaCandidate:X F FengFull Text:PDF
GTID:2491306566996599Subject:Applied Chemistry
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The use of light synergistic semiconductor catalysis technology can degrade pollutants in water into small molecules such as CO2 and H2O.This technology generally does not require the addition of other reagents.It has the advantages of high efficiency,energy saving,envi-ronmental friendliness,and no secondary pollution,but it also has short response wave-lengths.,Narrow scope and other shortcomings.How to modify and increase the photore-sponse range of the semiconductor photocatalyst and reduce the hole-electron recombination rate has become one of the hot issues in the research of semiconductor photocatalysis tech-nology in recent years.This paper mainly studies the preparation,modification,optimization of bismuth-based photocatalysts and the degradation of organic pollutants,and discusses the mechanism of photocatalysis.The specific results are as follows:(1)Using Bi(NO33·5H2O and Na2WO4·2H2O as precursors,Bi2WO6 was prepared by hydrothermal method,and on this basis,heterojunction Bi2WO6/Ti O2 was prepared by gel sol method and butyl titanate Then load the rare earth metal La3+to prepare Bi2WO6/La2WO6/Ti O2.It has higher photocatalytic activity than any single component under visible light,and the degradation rate reaches 96.62%under the experimental conditions.The reason is that the rare earth metal La3+is doped,which introduces La3+into the crystal lattice of Ti O2.The SEM image presents a three-dimensional petal-like shape.UV-vis shows that the response light range of the composite photocatalyst has broadened to the visible light region.XRD shows that Bi2WO6 is an orthorhombic crystal system.The XPS spectrum confirmed that it contains Bi,W,O,Ti,La,and C elements.Infrared spectroscopy shows that it contains Bi-O,W-O,W-O-W,Ti-O,and La-O bonds.With Rh B as the target pollutant,the optimal conditions obtained by orthogonal experiments are 0.1 g catalyst,50 mg/L Rh B,and 200watts of visible light radiation,and the best degradation amount is 23.3 mg/g.(2)Use Na2WO4·2H2O and Bi(NO33·5H2O as raw materials to prepare Bi2WO6 hydro-thermally;use high-temperature calcined melamine as raw materials to prepare graphite phase g-C3N4;Na2S and Cd Cl2·2.5H2O are reacted to form by one-step precipitation method Cd S:The three-complex Bi2WO6/Cd S/g-C3N4 was prepared by hydrothermal method,and the deg-radation rate reached 94.62%under the experimental conditions.Infrared characterization contains WO,WOW,CC,CN bonds;XPS analysis detects the specified elements and binding energy;SEM image presents a three-dimensional petal-like shape,and Rh B is used as the tar-get pollutant.The orthogonal experiment is designed and the optimized process is 0.1 g cata-lyst,50 mg/L Rh B,200W incandescent visible light radiation,the maximum degradation amount is 23.089 mg/g.(3)Using melamine,butyl titanate and Bi2WO6 prepared by hydrothermal method as precursors,uniformly mixed by gel sol method to prepare Bi2WO6/Ti O2/g-C3N4.Under the experimental conditions,the degradation rate of Rh B reached 98.79%.The catalyst is charac-terized and analyzed by XRD,SEM,UV-Vis,XPS,IR and other characterization methods.XRD characterization can be explained by standard cards PDF#50-1250,PDF#12-2172,PDF#39-0256 Bi2WO6/Ti O2/g-C3N4;XPS spectrum contains elements W,O,Bi,Ti,O,C,N;infrared spectrum shows stretching vibration and bending vibration containing Bi-O bond,including Bi-O,WO,WOW,Ti-O,CN bond;UV-vis indicates that the response range has been red-shifted,extending to the visible light region;the SEM image shows a white fun-gus-like structure.With the aid of response surface experiments,the optimized conditions are that the dosage of catalyst is 0.01 g,the initial concentration is 36.87 mg/L,the volume of H2O2(volume ratio is 1:100)is 1 m L,and the optimal degradation amount is 161.852 mg/g.The main active substances that degrade Rh B in the capture experiment are·OH,·O2-,h+.Through the kinetic characteristics of Rh B degradation,the results show that different influ-encing factors have different rate constants,which can be described by first-order kinetic equations.(4)Using NH4VO3 and Bi(NO33.5H2O as raw materials,adding KCl and KBr,the Bi-VO4/BiOCl/BiOBr heterojunction was prepared by hydrothermal method,and the morpholo-gy,structure and performance of the sample were characterized.XRD proved that the water Thermally prepared BiVO4 is a monoclinic phase;infrared spectroscopy has strong absorption in the range of 700-850cm-1,which proves that it has VO bonds;SEM shows that Bi-VO4/BiOCl/BiOBr is a nanosheet self-assembled into a spherical shape.With basic fuchsia green as the target pollutant,the screening of catalysts showed that BiVO4/BiOCl/BiOBr has better photocatalyst performance than single-doped BiOCl,single-doped BiOBr and Bi-VO4,and the degradation rate is 98.79 under the experimental conditions.%.The optimized conditions of the orthogonal experiment are 0.1 g of catalyst,initial concentration of 50 mg/L,visible light radiation power of 200 w,volume of H2O2(volume ratio 1:100)of 6 m L,and maximum degradation of 24.09 mg/g.With the help of capture experiments,the degradation mechanism of basic fuchsia green was explored.The study showed that the main active sub-stances that degrade basic fuchsia green are·OH,·O2-,h+.
Keywords/Search Tags:Bi2WO6, modified Bi2WO6, BiVO4photocatalyst, modified BiVO4, basic fuchsin, rhodamine, photocatalytic degradatio
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