2013
DOI: 10.1016/j.jiec.2012.12.036
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A comparison of fenton oxidation and photocatalyst reaction efficiency for humic acid degradation

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Cited by 33 publications
(7 citation statements)
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“…It is researched that attendance of AC in interaction by TiO 2 is beneficial due to its burly adsorption capability. In the same way it advances the relocation rate of the interfacial change and lessens the rejoining rate of the holes and electrons [260,261]. This synergistic effect of the interaction of AC and TiO 2 has been previously been stated for deprivation of some organic compounds in the photocatalytic process.…”
Section: Tio 2 : Ac Photocatalyst Systemmentioning
confidence: 65%
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“…It is researched that attendance of AC in interaction by TiO 2 is beneficial due to its burly adsorption capability. In the same way it advances the relocation rate of the interfacial change and lessens the rejoining rate of the holes and electrons [260,261]. This synergistic effect of the interaction of AC and TiO 2 has been previously been stated for deprivation of some organic compounds in the photocatalytic process.…”
Section: Tio 2 : Ac Photocatalyst Systemmentioning
confidence: 65%
“…Thus, the organic burning rate observed on TiO 2 : AC is like heading both with surface diffusion toxin particles with the photocatalytic process rate; because adsorption occurs gradually, the variation in relative pollutant proportion with irradiation time depends on both adsorption and photodecomposition, mainly at the start of ultraviolet treatment. It is stated that the variance of the proportion of phenol (as model of organic pollutants) remaining in the solution by ultraviolet treatment time is compared for TiO 2 : AC, which were prepared by hydrolysis of tetraisopropyl orthotitanate and heat treatment at 650 to 900 ∘ C. For example, we noted that, in the duration of first 1 hour, adsorption of pH occurs in native AC and after 3 hours, in the presence of UV irradiations saturation achieved [261]. Adsorption as well as the photodecomposition of pH takes place simultaneously, but on the other side the former is supposed to become the dominate method in the beginning, being similarly latter in the next stage [221,222] trend was based on two linear processes; the change of one process to the other takes place approximately in 1 hour of irradiation.…”
Section: Tio 2 : Ac Photocatalyst Systemmentioning
confidence: 99%
“…This increased leaching promotes the formation of radicals with sufficient oxidative potential to degrade the organic contaminants [72]. However, when the aqueous solution reaches neutral pH values, the oxidation rate of the process is delayed by the formation of solid iron oxyhydroxides (Equations ( 1)-( 4)), which are weaker activating agents than Fe 2+ (aq), resulting in decreased rate of production of HO• radicals [22,26,56]. The initial raise followed by the decay of Fe 2+ concentrations in aqueous medium after 5 min of treatment (at pH 4.5 and 5.5) shown in Figure 1(b) may indicate that there is a fast initial step of Fe dissolution caused by H 2 O 2 oxidation according to Equation (1).…”
Section: Effect Of Initial Phmentioning
confidence: 99%
“…These chemical modifications can result in the overall decrease of Total Organic Carbon (TOC) and Disinfection Byproduct Formation Potentials (DBPFP) in the treated water [17,19]. And among the AOPs, the Fenton process has already been proposed to optimize the removal of several organic contaminants from waters [8,[20][21][22][23]. This process utilizes hydrogen peroxide (H 2 O 2 ) and soluble iron (II) salts to produce a highly reactive radical (HO•) capable of oxidizing organic compounds in solution.…”
Section: Introductionmentioning
confidence: 99%
“…Accordingly, this set of preliminary experiments suggested important effects of light and air bubbling taking place in the degradation of NOM through the CWPO catalytic system in the presence of Al/Fe-PILCs. A priori, it established that the Al/Fe-PILC clay catalyst exhibits photocatalytic characteristics, possibly due to either or a combination of: (i) direct absorption of radiation by the active solid (purely photocatalytic activity), (ii) light absorption by the colored dissolved NOM (photo-sensitizing effect) [34] or (iii) taking into account that in both cases the catalytic process was assisted by hydrogen peroxide, the heterogeneous photo-Fenton process could be also involved. The main motivation of this study was just to determine which of these routes are mostly contributing to NOM's degradation under light irradiation by this catalytic system, and by means of what fraction of the natural sunlight (ultraviolet and/or visible).…”
Section: Cwpo Degradation Of Nom Under Optimal Conditionsmentioning
confidence: 99%