2016
DOI: 10.1016/j.jece.2016.04.035
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Solar-light-harvesting degradation of aqueous ammonia by CuO/ZnO immobilized on pottery plate: Linear kinetic modeling for adsorption and photocatalysis process

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Cited by 41 publications
(22 citation statements)
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“…The kinetic evaluation of Ti_G photocatalytic properties (Figure 6) indicated the presence of two different intervals in the reaction pathway. The first interval (up to 240 min) corresponded to the induction period [35], followed by fast pollutant (Tr and Apd) removal [36], with a contribution of almost 75% in the total process. The second interval (from 240 to 480 min) showed a significant attenuation of the photocatalytic reaction rate, which can be attributed to surface inactivation due to the absorbance of the pollutant and the The first interval (up to 240 min) corresponded to the induction period [35], followed by fast pollutant (Tr and Apd) removal [36], with a contribution of almost 75% in the total process.…”
Section: Photocatalytic Propertiesmentioning
confidence: 99%
“…The kinetic evaluation of Ti_G photocatalytic properties (Figure 6) indicated the presence of two different intervals in the reaction pathway. The first interval (up to 240 min) corresponded to the induction period [35], followed by fast pollutant (Tr and Apd) removal [36], with a contribution of almost 75% in the total process. The second interval (from 240 to 480 min) showed a significant attenuation of the photocatalytic reaction rate, which can be attributed to surface inactivation due to the absorbance of the pollutant and the The first interval (up to 240 min) corresponded to the induction period [35], followed by fast pollutant (Tr and Apd) removal [36], with a contribution of almost 75% in the total process.…”
Section: Photocatalytic Propertiesmentioning
confidence: 99%
“…The photocatalytic ammonia degradation is a combination of photocatalytic and nonphotocatalytic reactions. On the basis of the published papers dealing with the photocatalytic ammonia degradation, the ammonia degradation initiates by surface oxidation of either H 2 O (path I) or NH 3 (path II) molecules through valence band holes. Both of the two paths lead to the formation of amide radical (•NH 2 ), the former through the attack of radical hydroxyl on NH 3 and the latter through deprotonation of NH 3 .…”
Section: Resultsmentioning
confidence: 99%
“…Compared with the degradation in the closed environment, the ventilation environment improved the removal rate of the target pollutants in a certain period of time and showed better removal effects. The reason may be that in an aqueous solution, ammonium ions (NH4 + ) can be partially ionized to ammonia and H + ; ammonia molecules are oxidized by successive attacks of OHradicals [8,24,25]. Under the dark reaction conditions, the composite the photocatalyst could not induce the formation of hydroxyl radicals with strong oxidation to achieve degradation as it lacked the excitation of the ultraviolet light on the semiconductor band.…”
Section: Under Natural Reaction Conditionsmentioning
confidence: 99%
“…Through an analysis carried out by Shavisi et al [8], it was indicated that 5 wt.% CuO loaded over ZnO could significantly increase the photocatalytic activity as 77.2% ammonia removal from synthetic wastewater was achieved within 240 min of solar irradiation time. Accordingly, ultraviolet and visible light are essential for the excitation of oxides (SnO2 and ZnO).…”
Section: Introductionmentioning
confidence: 99%