| Photocatalysis is the perfect way to treat wastewater,which not only utilizes solar power,but also no toxic by-product generates.Since the discovery of TiO2 using for water photolysis,semiconductor materials have been extensively studied in the field of photocatalysis.Magnetic ferrite materials have been applied in the field of photocatalysis due to their magnetic properties,Among these ferrite materials,NiFe2O4 is a very important spinel ferrite material.The band gap of NiFe2O4 is 1.7eV,as photocatalyst,absorbing visible-light,therefore the sunlight utilization ratio will improve significantly,simultaneously the magnetism of NiFe2O4 can resolve the problem of recycling.To the date,from the research of NiFe2O4 photocatalytic degradation,it is obvious to find NiFe2O4 directly degrades contaminant next to nothing.In this work,putting the template way to use,porous NiO,Fe2O3 are received,experimenting the photocatalytic degradation.Porous NiFe2O4 is prepared via the template way in different temperatures,studying the effect of temperature on the photocatalytic activity of NiFe2O4.The effect of template method,hydrothermal method and sol-gel method on the photocatalytic properties of NiFe2O4 samples is researched.Attempting to optimize the photocatalytic degradation of porous NiFe2O4 by loading with Bi2O3.Prime experiment contents and results:1.NiO and Fe2O3 are prepared by using cotton fiber as template,studying the photocatalytic properties.The photocatalytic degradation rates of NiO and Fe2O3 samples are 28%,63%,the adsorption rates of NiO and Fe2O3 samples are 24% and 46%.The experimental data tells that the Fe2O3 sample has the best photocatalytic degradation rate.2.Porous NiFe2O4 is prepared via the template way in different temperatures(400℃,500℃,600℃).According to the experimental data,the adsorption rate of the samples is 41%,33% and 29% at 400℃,500℃,600℃;the photocatalytic degradation rate of the samples at 400℃,500℃,600℃ is 63%,92% and 90%.The specific surface area of the samples at 400℃,500℃,600℃ is 9.38 m2/g,12.61 m2/g,7.21 m2/g.The sample of 500 ℃ has best photocatalytic degradation rate,indicating that the moderate crystallinity,specific surface area and adsorption rate can improve the photocatalytic degradation rate.3.Porous NiFe2O4 is prepared via the template way,comparing to the sample from hydrothermal and sol-gel process.According to the experimental data,the photocatalytic degradation rates of the samples obtained by hydrothermal method,sol-gel method and template method are 23%,69% and 92%,respectively;the adsorption rate of the samples is 23%,29% and 33% by hydrothermal method,sol-gel method and template method;The specific surface area of the samples obtained by hydrothermal method,sol-gel method and template method is 55.6 m2/g,3.59 m2/g,12.61 m2/g.The samples obtained by sol-gel method and template method are porous materials,while the average pore size of hydrothermal samples is 12.4nm,which belongs to mesoporous materials.The sample of 500℃ has best photocatalytic degradation rate,suggesting the moderate specific surface area,adsorption rate and pore size can improve the photocatalytic degradation rate.4.Preparation of α-Bi2O3 by direct calcination and porous NiFe2O4 loading the α-Bi2O3.According to the experimental data,α-Bi2O3 was not loaded onto porous NiFe2O4.Pure porous NiFe2O4(92%)was 51% higher than that of photocatalytic degradation of α-Bi2O3(41%)loading onto porous NiFe2O4,indicating that the larger particle size of α-Bi2O3 can not form an effective heterogeneous structure with porous NiFe2O4,which leads to the decrease of photocatalytic degradation rate.Hydrothermal preparation of small particle size β-Bi2O3 and porous NiFe2O4 loading with β-Bi2O3,forming β-Bi2O3/Ni Fe2O4 heterostructure.The photocatalytic degradation rate of pure porous NiFe2O4(92%)was 50% higher than that of β-Bi2O3(42%),showing that the smaller particle size of β-Bi2O3 is loaded on the surface of porous NiFe2O4,preventing the adsorbance of porous NiFe2O4,which leads to the decrease of photocatalytic degradation. |