Polyvinyl chloride (PVC) ultrafiltration membranes were efficiently fabricated using a (0.1–0.5 wt.%) Ag 2 O@CuO heterojunction photocatalyst to form a PVC/Ag 2 O@CuO photocatalytic membrane (PM) stimulated by UV light. The PVC/Ag 2 O@CuO PM fabricated using the phase inversion process resulted in significant improvement in internal morphology, porosity, pure water flux, and separation efficacy of the doped membranes. The efficacy of the PVC/Ag 2 O@CuO PMs was evaluated in the elimination of Rhodamine B (RhB) dye. The highest photodegradation of RhB (96.9%) was obtained using the PM2 membrane that contains 0.3 wt.% Ag 2 O@CuO photocatalyst at an influent pH of 6.5, a feed RhB concentration of 5 mg/L, a RhB solution volume of 2000 mL, an influent flow rate of 1 L/min under UV light irradiation for 90 min. PM2 membrane demonstrated antifouling features in terms of flux recovery ratio, reversible fouling, irreversible fouling, and total fouling, and 90% of RhB was removed after five cycles of use. The kinetic results indicated that the photocatalytic oxidation of RhB dye by the PM2 membrane followed the pseudo‐first‐order kinetic model, with an apparent rate constant of 0.0289 min −1 . Studying the Langmuir–Hinshelwood model resulted in an intrinsic photocatalytic reaction rate constant of 0.7666 mg/L.min and an equilibrium adsorption constant of 0.045 L/mg.
Heterogeneous photocatalysts was a promising material for removing organic pollutants. Titanium dioxide (TiO2) was a suitable photocatalyst for its cost efficiency and high stability to reduce various pollutants. Enhancing TiO2 photocatalyst performance by doping with changed metals or non-metal ions and organic compounds have been reviewed. These methods could enhance photoelectrochemical activity via: (i) by a donor of electrons via electron-donor agents that would produce particular defects in TiO2 structure and capture transporters of charge; (ii) by reducing recombination rate of the charge transporters and increasi
The preparation of composite metal oxide to attain high efficiency in removing phenol from wastewater has a great concern. In the present study, the focus would be on adopting antimony-tin oxide coating onto graphite substrates instead of titanium; besides the effect of SbCl3 concentration on the SnO2-Sb2O3 composite would be examined. The performance of this composite electrode as the working electrode in the removal of phenol by sonoelectrochemical oxidation will be studied. The antimony-tin dioxide composite electrode was prepared by cathodic deposition with SnCl2 . 2H2O solution in a mixture of HNO3 and NaNO3, with different concentrations of SbCl3. The SnO2-Sb2O3 deposit layer’s structure and morphology were examined and the 4 g/l Sb
... Show MoreThis research includes description of the x-ray diffraction, morphology and sensing measurements of SnO2 doped In2O3 thin films synthesized by pulsed laser deposition method on glass and silicon wafer substrates. In2O3:SnO2 powders were obtained by mixing In2O3 with SnO2 in the desired ratio, and calcination the at temperature 1273 K for 5 hours. SnO2 doped In2O3 thin films with different ratios (0, 0.01, 0.03, 0.05, 0.07, and 0.09% wt.) were prepared using pulsed laser deposition method. The structural investigation using X-ray diffraction revealed that the mai
The A.C conductivity of three samples of lanthanide oxide : zinc oxide (La2O3)1-x(ZnO)x pellets with different zinc oxide content which were sintered 1273 K temperatures were studied using LRC meters in the frequency range of 50–106 Hz at temperature of 30 °C. The a.c conductivity, was analyzed depending of the universal power law proposed by Jonsher,. The slope of the relation between logarithm of a.c conductivity and angular frequency represent the s value were in the range (0.44-0.77) which found to increase by increasing of zinc oxide content which coincided with the small po
six specimens of the Hg0.5Pb0.5Ba2Ca2Cu3-y