Abstract:Quasi-monodispersed SnO 2 microspheres have been successfully synthesised by a microwave solvothermal method, in which polyethylene glycol is used as template, SnCl 4 .5H 2 O and urea as raw materials. The products have been characterised by X-ray diffraction, a scanning electron microscope, and a transmission electron microscope. Besides, the thermal behaviour of the products synthesised by solvothermal process has been studied through the thermogravimetry differential scanning calorimetry. Photocatalytic act… Show more
“…Additionally, the porous channel structure may facilitate better transport of contaminant molecules to reach catalytically active sites 55 . Reaction kinetics analyses reinforce that incorporation of the SnO 2 nanoparticles into the PS foams improves RhB photodegradation, with rate constants as high as 0.054 min -1 , being similar/higher than other reported systems, which are sometimes chemically more complex than these nanofoams 48,51,52…”
Section: Photocatalyst S Bet (M 2 /G) Ph K (Min -1 ) % (Photobleachsupporting
confidence: 61%
“…Considering that the radiation source used has constant flux, and the number of photocatalyst active sites is solely dependent on the surface area, pseudo first-order kinetics are expected, provided there is no catalyst poisoning during the process. According to 48 these results may be associated with N-de-ethylation of RhB, since, as shown in Fig. 8, N-de-ethylation cannot be totally avoided and will occur in parallel with the direct degradation pathway.…”
Section: Kinetics Of Rhb Degradationmentioning
confidence: 98%
“…Note that is not easy to compare these results, since besides RhB:SnO 2 molar ratio, irradiation power is an important factor, and the 60 W lamp used here is smaller than some others reported, such as 300 W for the work of Zhu et. al 48 . The first run showed 98.3% of RhB degradation; cycle 2, 98.3%; cycle 3 showed 97.8% degradation; cycle 4, 96.5% and the fifth degraded 82% of the initial dye.…”
Section: Photocatalyst S Bet (M 2 /G) Ph K (Min -1 ) % (Photobleachmentioning
Plastic debris is a major environmental concern, and to find effective ways to reuse polystyrene (PS) presents major challenges. Here, it is demonstrated that polystyrene foams impregnated with SnO are easily generated from plastic debris and can be applied to photocatalytic degradation of dyes. SnO nanoparticles were synthesized by a polymeric precursor method, yielding specific surface areas of 15 m/g after heat treatment to 700 °C. Crystallinity, size, and shape of the SnO particles were assessed by X-ray diffraction (XRD) and transmission electron microscopy (TEM), demonstrating the preparation of crystalline spherical nanoparticles with sizes around 20 nm. When incorporated into PS foams, which were generated using a thermally induced phase separation (TIPS) process, the specific surface area increased to 48 m/g. These PS/SnO nanofoams showed very good efficiency for photodegradation of rhodamine B, under UV irradiation, achieving up to 98.2% removal. In addition the PS/SnO nanofoams are shown to retain photocatalytic activity for up to five reuse cycles.
“…Additionally, the porous channel structure may facilitate better transport of contaminant molecules to reach catalytically active sites 55 . Reaction kinetics analyses reinforce that incorporation of the SnO 2 nanoparticles into the PS foams improves RhB photodegradation, with rate constants as high as 0.054 min -1 , being similar/higher than other reported systems, which are sometimes chemically more complex than these nanofoams 48,51,52…”
Section: Photocatalyst S Bet (M 2 /G) Ph K (Min -1 ) % (Photobleachsupporting
confidence: 61%
“…Considering that the radiation source used has constant flux, and the number of photocatalyst active sites is solely dependent on the surface area, pseudo first-order kinetics are expected, provided there is no catalyst poisoning during the process. According to 48 these results may be associated with N-de-ethylation of RhB, since, as shown in Fig. 8, N-de-ethylation cannot be totally avoided and will occur in parallel with the direct degradation pathway.…”
Section: Kinetics Of Rhb Degradationmentioning
confidence: 98%
“…Note that is not easy to compare these results, since besides RhB:SnO 2 molar ratio, irradiation power is an important factor, and the 60 W lamp used here is smaller than some others reported, such as 300 W for the work of Zhu et. al 48 . The first run showed 98.3% of RhB degradation; cycle 2, 98.3%; cycle 3 showed 97.8% degradation; cycle 4, 96.5% and the fifth degraded 82% of the initial dye.…”
Section: Photocatalyst S Bet (M 2 /G) Ph K (Min -1 ) % (Photobleachmentioning
Plastic debris is a major environmental concern, and to find effective ways to reuse polystyrene (PS) presents major challenges. Here, it is demonstrated that polystyrene foams impregnated with SnO are easily generated from plastic debris and can be applied to photocatalytic degradation of dyes. SnO nanoparticles were synthesized by a polymeric precursor method, yielding specific surface areas of 15 m/g after heat treatment to 700 °C. Crystallinity, size, and shape of the SnO particles were assessed by X-ray diffraction (XRD) and transmission electron microscopy (TEM), demonstrating the preparation of crystalline spherical nanoparticles with sizes around 20 nm. When incorporated into PS foams, which were generated using a thermally induced phase separation (TIPS) process, the specific surface area increased to 48 m/g. These PS/SnO nanofoams showed very good efficiency for photodegradation of rhodamine B, under UV irradiation, achieving up to 98.2% removal. In addition the PS/SnO nanofoams are shown to retain photocatalytic activity for up to five reuse cycles.
“…This may be due to the fact that RhB molecules absorb light photons and their excitation is possible [35,36]. On the other hand, it is well known that photocatalytic degradation of RhB can occur by two pathways [36,37]: as de-ethylation process in a stepwise manner (with the formation of the three intermediates from RhB to сompletely de-ethylated Rh110) or as a direct cleavage of the chromophore rings. The gradual blue shift in λmax of the spectrum of RhB is observed in the first case and the reduction in the absorbance without shift takes place in the second case.…”
“…The use of different mono-component photocatalyst such as TiO 2 [7][8][9], ZnO [10,11], SnO 2 [12,13] or WO 3 [14,15] demonstrated the feasibility of using a semiconductor to reduce the air pollutants content. Although efficient, these materials have limited response under Vis/solar irradiation, with negative consequences considering sustainability (energy consumption) and the overall cost of the photocatalytic process.…”
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