| This research used the montmorillonite (MMT) and multi-walled carbon nanotubes(MWCNTs) as the carrier,adopted the mental and non-mental doping to modify TiO2. Theprepared samples were characterized by different methods such as X-ray Diffraction(XRD)ã€Transmission Electron Microscopy(TEM)ã€UV-visible absorption spectrum(UV-vis). Thedegradation of dye wastewater was used as a model reaction to test the photocatalytic activityof the samples.(1)In-TiO2/MMT nanocomposite photocatalyst is composed by Sol-gel processes andSupercritical Fluid Drying (SCFD) methods. The results show that anatase type TiO2is formed,and the main particle size is between13~18nm. The photocatalytic activity is evaluated byphotocatalytic degradation of the concentration loss of MB.The degradation rate of MB and TOCare separately99.2%and63.9%,when the calcine temperature is700℃, the optimum doping ofIn is2%.(2) B-TiO2/MMT were prepared by Sol-gel method. The XRD result shows that theexisting form of TiO2is anatase, with no obvious agglomeration phenomenon. TEM showscatalyst particles dispersed well with uniform size. The catalyst’s absorption of light moves tolonger wavelengths.(3) In-TiO2/MNWCNTs were prepared by Sol-gel method and the samplesare dried by Supercritical Fluid Drying method. The result shows that TiO2in the photocatalystis anatase, the average particle diameter is about10nm. In-doped can decrease the band-gapenergy of titania. The photocatalyst degradation rate of MO and TOC are separately100%and76.7%, when the optimum dope of In is2%, and the concent of MWCNTs is3.0%.(4) TheB-TiO2/MWCNTs photocatalyst is composed by Sol-gel processes and Supercritical FluidDrying (SCFD) methods. The result shows that TiO2in the photocatalyst is anatase, B-dopeddidn’t affect the crystal form of the TiO2. And the band-gap energy can be reduced to3.02eV.The photocatalyst degradation rate of MO and MB were98.8%and99%, the degradation rateof TOC were74%and86%. |