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Charge-transfer-complex-mediated mechanism for TiO 2 -assisted photodegradation of colorless aromatic pollutants under visible illumination (Figure taken from [156]).  

Charge-transfer-complex-mediated mechanism for TiO 2 -assisted photodegradation of colorless aromatic pollutants under visible illumination (Figure taken from [156]).  

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This review is focused on studies related to the elimination of organic pollutants present in aqueous systems by titanium dioxide photocatalyst under visible light illumination. The titanium dioxide semi-conductor has emerged as a very promising technology for the oxidation and mineralization of aqueous organic pollutants because of its properties...

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... on the electronic property of TiO 2 (mixed phases, co-doped or multi-doped TiO 2 , crystallite size, etc.) and the molecular structure of the organic compounds. In visible- light irradiation the photocatalytic degradation of colorless aromatic pollutants by anatase TiO 2 powders proceeded via a charge- transfer-complex (CTC)-mediated pathway (Fig. 2) and a correla- tion between the chemical structure and the degradation rate of these pollutants was observed [156,157]. Wang et al., [156] found that an electron-donating substituent in benzene ring, which raises the highest occupied molecular orbital and lowers the ionization potential of the organic compound, was favorable to the ...

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... Compared to bulk rutile TiO2, both ER-TiO2 and CR-TiO2 samples had wider band gaps, which may be attributed to the quantum size effect from their nano-size feature [43]. ...
... Nanostructured semiconductors, such as SnO2, ZnO, and TiO2, can be used to detect a wide range of organic pollutants [7][8][9][10][11]. Tin (IV) Oxide (SnO2) is an n-type transparent semiconductor with a wide bandgap of 3.6 eV at 300 K [12,13]. ...
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... In order to resolve these problems modification of the band energy of TiO 2 is preferred, either by doping with metal/non-metal elements or by dye photosensitization [11][12][13]. In this context, one of the most efficient strategies for increasing TiO 2 photocatalytic efficiency is transition metal doping, which lowers the energy barrier from 3.2 eV to below 3.0 eV [14]. This decrease in the energy gap shifts the photocatalytic activities from UV light to the visible light region. ...
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... Nanostructured semiconductors, such as SnO2, ZnO, and TiO2, can be used to detect a wide range of organic pollutants [7][8][9][10][11]. Tin (IV) Oxide (SnO2) is an n-type transparent semiconductor with a wide bandgap of 3.6 eV at 300 K [12,13]. ...
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... It is important to note that some studies have demonstrated that photocatalytic processes are not characterized by a linear evolution of efficiency-irradiation. In view of this, to optimize the design of the processes it is important to adjust the flow of photons and sources of irradiation to the catalyst substrate and type of pollutant [56]. Globally, in most cases, high efficiency is observed by using UV radiation in the presence of TiO 2 catalysts for the abatement of CEC from water [51]. ...
... Aiming industrial processes applications, the photocatalyst should be active under the visible light spectrum since this is the largest fraction of sunlight radiation [56,58]. The mechanism for photocatalytic activity of TiO 2 under visible light radiation depends on the electronic properties of TiO 2 (crystalline phases, co-doped or multidoped, crystallite size, etc.) and the molecular structure of the organic compounds to be degraded [59,60]. ...
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... Nanostructured materials are widely used in various fields because of their unique properties. Nowadays, nanostructured titania has received much attention due to its high potential in photocatalytic applications, self-cleaning coatings, photovoltaic, heavy metal removal from industrial effluents, ceramic membranes, and gas sensors [1]. Among nanostructured materials, TiO 2 as a semiconductor is very useful in these applications. ...
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Formalin or hydrate of formaldehyde, a common disinfectant used in aquaculture, is not able to absorb sunlight, therefore its photodegradation must be catalyzed. To take advantage of sunlight for its photodegradation, TiO2-reduced graphene oxide (TiO2-rGO) nanocomposites with different GO contents (0.25-3.0wt%) were synthesized and characterized by scanning electron microscopy (SEM), UV-vis and ATR-FTIR spectroscopies. Additionally, their specific surface areas (SBET), pore volume and size were determined. The photocatalysts efficiency for formaldehyde (FM) degradation under simulated sunlight was assessed in aqueous solution. Among the nanocomposites considered, TiO2-rGO 0.5wt% was the most efficient, achieving 93.8±4.6 % of FM photodegradation in 90 min. The same irradiation conditions were applied in natural water matrices (aquaculture's freshwater and saltwater) to evaluate the influence of natural water constituents on photocatalysis. The photodegradation percentages obtained were 63.7±0.6 % and 16.0±1.4 % in aquaculture's freshwater and saltwater, respectively. This lower efficiency to photodegrade FM in natural aqueous matrices is attributed to the inhibition of photocatalytic oxidation of organic compounds caused by dissolved organic matter (DOM) and inorganic ions existing in the aquatic environment. Nevertheless, the results obtained for photocatalytic efficiency in natural waters are promising, suggesting a great potential of application in green photocatalysis to remove FM from contaminated freshwater.
... Higher concentrations of H 2 O 2 were produced with activated sludge in the anode chamber and the addition of the electron mediator ADQS to the anode. Cr 3+ reduction could occur via direct electrochemical reduction or via electrochemically-produced H 2 O 2 [186]. H 2 O 2 was shown to be a superior reducer because when H 2 O 2 was not formed (i.e., when the chamber was gassed with N 2 ), Cr 6+ was reduced at lower rates and lower removal efficiencies (42.5% with nitrogen after 12 h vs. about 100% with air after 4 h). ...
... ) and H 2 O 2 [186], which might also have contributed to the higher Cr 6+ reduction rates. ...
... Higher concentrations of H 2 O 2 were produced with activated sludge in the anode chamber and the addition of the electron mediator ADQS to the anode. Cr 3+ reduction could occur via direct electrochemical reduction or via electrochemically-produced H 2 O 2 [186]. H 2 O 2 was shown to be a superior reducer because when H 2 O 2 was not formed (i.e., when the chamber was gassed with N 2 ), Cr 6+ was reduced at lower rates and lower removal efficiencies (42.5% with nitrogen after 12 h vs. about 100% with air after 4 h). ...
... ) and H 2 O 2 [186], which might also have contributed to the higher Cr 6+ reduction rates. ...
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... Therefore, the development of photocatalysts showing a high activity under visible light irradiation is needed in order to be able to use the sunlight or rays from artificial sources more effectively in photocatalytic reactions. Many studies have attempted to develop visible light-sensitive photocatalysts using, for example, TiO 2 doped with metallic nanoparticles (NPs) such as Au, Ag or Cu [2][3][4][5]. This approach seems to be of interest for improving the photocatalytic effect in visible light due to the localized surface plasmon resonance band (LSPR) of the metallic NPs, which induces a high absorption in the visible range. ...
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