Herein we reported the effect of doping and addition of surfactant on SnO2 nanostructures for enhanced photocatalytic activity. Pristine SnO2, Zn-SnO2 and SDS-(Zn-SnO2) was prepared via simple co-precipitation method and the product was annealed at 600 °C to obtain a clear phase. The structural, optical, vibrational, morphological characteristics of the synthesized SnO2, Zn-SnO2 and SDS-(Zn-SnO2) product were investigated. SnO2, Zn-SnO2 and SDS-(Zn-SnO2) possess crystallite size of 20 nm, 19 nm and 18 nm correspondingly with tetragonal structure and high purity. The metal oxygen vibrations were present in FT-IR spectra. The obtained bandgap energies of SnO2, Zn-SnO2 and SDS-(Zn-SnO2) were 3.58 eV, 3.51 eV and 2.81 eV due to the effect of dopant and surfactant. This narrowing of bandgap helped in the photocatalytic activity. The morphology of the pristine sample showed poor growth of nanostructures with high level of agglomeration which was effectively reduced for other two samples. Product photocatalytic action was tested beneath visible light of 300 W. SDS-(Zn-SnO2) nanostructure efficiency showed 90% degradation of RhB dye which is 2.5 times higher than pristine sample. Narrow bandgap, crystallite size, better growth of nanostructures paved the way for SDS-(Zn-SnO2) to degrade the toxic pollutant. The superior performance and individuality of SDS-(Zn-SnO2) will makes it a potential competitor on reducing toxic pollutants from wastewater in future research.
Wastewater management has become necessary in this industrialized era to meet the water needs of the world. Wastewater is one of the major crises in depletion of the environment. Photocatalysis is considered as the best way to remove pollutants. Therefore, in this study, pure and g-C3N4-SnWO4 nanocomposites were produced employing hydrothermal route. Prepared composites were studied by various techniques. SnWO4 band gap were altered by introduction of g-C3N4. The morphology was uniformly developed by the addition of g-C3N4 to the SnWO4. Evans Blue dye was employed as model pollutant. The photocatalytic action was improved by adding g-C3N4, which formed a heterojunction with SnWO4. The calculated rate constant was 0.000878, 0.0068, 0.01 and 0.0122 min-1 for EB, SnWO4-EB, 0.1 g g-C3N4-SnWO4-EB and 0.2 g g-C3N4-SnWO4-EB. The rate constant increased for 0.2 g g-C3N4-SnWO4 photocatalyst. A heterojunction appeared between g-C3N4 and SnWO4 facilitated SnWO4 for better e-/h+pair's separation and a lower recombination rate, which increased photocatalytic action of product. 0.2 g of g-C3N4-SnWO4 is a promising candidate for future wastewater degradation.