Abstract:Photocatalysis has shown the ability to inactivate a wide range of harmful microorganisms with traditional use of chlorination. Photocatalysis combined with applied bias potential (photoelectrocatalysis) increases the efficiency of photocatalysis and decreases the charge recombination. This work examines the inactivation of fecal coliform bacteria present in real urban wastewater by photoelectrocatalysis using nanoparticulated films of TiO and TiO/Ag (4%w/w) under UV light irradiation. The catalysts were prepa… Show more
“…As expected, the presence of Ag was identified to significantly increase the response of TiO 2 towards bacterial inactivation. Upon an applied cell potential of 1.5 V the TiO 2 /Ag (4% w/w) photo-anode also achieved complete inactivation of fecal coliform bacteria in the solution within 6 min ( Domínguez-Espíndola et al., 2017 ). Brugnera et al.…”
Section: Quasi-direct Oxidationmentioning
confidence: 99%
“…Ag also alters the transport system within the cell membrane resulting in catastrophic permeability, osmoregulation, electron transport and respiration events that eventually lead to cell death ( Mafa et al., 2020 ). Domínguez-Espíndola et al. (2017) and Domínguez-Espíndola et al.…”
Disinfection is usually the final step in water treatment and its effectiveness is of paramount importance in ensuring public health. Chlorination, ultraviolet (UV) irradiation and ozone (O
3
) are currently the most common methods for water disinfection; however, the generation of toxic by-products and the non-remnant effect of UV and O
3
still constitute major drawbacks. Photo-assisted electrochemical advanced oxidation processes (EAOPs) on the other hand, appear as a potentially effective option for water disinfection. In these processes, the synergism between electrochemically produced active species and photo-generated radicals, improve their performance when compared with the corresponding separate processes and with other physical or chemical approaches. In photo-assisted EAOPs the inactivation of pathogens takes place by means of mechanisms that occur at different distances from the anode, that is: (i) directly at the electrode’s surface (direct oxidation), (ii) at the anode’s vicinity by means of electrochemically generated hydroxyl radical species (quasi-direct), (iii) or at the bulk solution (away from the electrode surface) by photo-electrogenerated active species (indirect oxidation).
This review addresses state of the art reports concerning the inactivation of pathogens in water by means of photo-assisted EAOPs such as photo-electrocatalytic process, photo-assisted electrochemical oxidation, photo-electrocoagulation and cathodic processes. By focusing on the oxidation mechanism, it was found that while quasi-direct oxidation is the preponderant inactivation mechanism, the photo-electrocatalytic process using semiconductor materials is the most studied method as revealed by numerous reports in the literature. Advantages, disadvantages, trends and perspectives for water disinfection in photo-assisted EAOPs are also analyzed in this work.
“…As expected, the presence of Ag was identified to significantly increase the response of TiO 2 towards bacterial inactivation. Upon an applied cell potential of 1.5 V the TiO 2 /Ag (4% w/w) photo-anode also achieved complete inactivation of fecal coliform bacteria in the solution within 6 min ( Domínguez-Espíndola et al., 2017 ). Brugnera et al.…”
Section: Quasi-direct Oxidationmentioning
confidence: 99%
“…Ag also alters the transport system within the cell membrane resulting in catastrophic permeability, osmoregulation, electron transport and respiration events that eventually lead to cell death ( Mafa et al., 2020 ). Domínguez-Espíndola et al. (2017) and Domínguez-Espíndola et al.…”
Disinfection is usually the final step in water treatment and its effectiveness is of paramount importance in ensuring public health. Chlorination, ultraviolet (UV) irradiation and ozone (O
3
) are currently the most common methods for water disinfection; however, the generation of toxic by-products and the non-remnant effect of UV and O
3
still constitute major drawbacks. Photo-assisted electrochemical advanced oxidation processes (EAOPs) on the other hand, appear as a potentially effective option for water disinfection. In these processes, the synergism between electrochemically produced active species and photo-generated radicals, improve their performance when compared with the corresponding separate processes and with other physical or chemical approaches. In photo-assisted EAOPs the inactivation of pathogens takes place by means of mechanisms that occur at different distances from the anode, that is: (i) directly at the electrode’s surface (direct oxidation), (ii) at the anode’s vicinity by means of electrochemically generated hydroxyl radical species (quasi-direct), (iii) or at the bulk solution (away from the electrode surface) by photo-electrogenerated active species (indirect oxidation).
This review addresses state of the art reports concerning the inactivation of pathogens in water by means of photo-assisted EAOPs such as photo-electrocatalytic process, photo-assisted electrochemical oxidation, photo-electrocoagulation and cathodic processes. By focusing on the oxidation mechanism, it was found that while quasi-direct oxidation is the preponderant inactivation mechanism, the photo-electrocatalytic process using semiconductor materials is the most studied method as revealed by numerous reports in the literature. Advantages, disadvantages, trends and perspectives for water disinfection in photo-assisted EAOPs are also analyzed in this work.
“…Fe-doped g-C 3 N 4 and P-doped g-C 3 N 4 for wastewater treatment have been synthesized [32,33]. In addition, various works concerning the photocatalytic treatment of real effluents with the use of TiO 2 , g-C 3 N 4 , Ag/g-C 3 N 4 , TiO 2 /Ag and g-C 3 N 4 /TiO 2 /Fe 3 O 4 @SiO 2 have been conducted in recent years [34][35][36][37]. For instance, studies using heterojunctions of g-C 3 N 4 like TiO 2 /g-C 3 N 4 for Cr(VI) removal [38] and Ag/Ag 3 VO 4 /g-C 3 N 4 for the degradation of tetracycline in wastewaters have been published [39].…”
The presence of pharmaceutically active compounds (PhACs) in the wastewater effluents has confirmed that conventional wastewater treatment technologies are not sufficiently effective in the pharmaceuticals' removal. The objective of the present study was to evaluate and compare the photocatalytic degradation of PhACs using TiO 2 -P25, graphitic carbon nitride (g-C 3 N 4 , CN) and a heterojunction of perovskite strodium titanate and graphitic carbon nitride SrTiO 3 /g-C 3 N 4 (20% g-C 3 N 4 , 20CNSTO) photocatalytic materials, in hospital wastewater effluents, by simulated solar irradiation. The experiments were performed by using real wastewater samples collected from the university hospital wastewater treatment plant (WWTP) effluent of Ioannina city (Northwestern Greece) and inherent pharmaceutical concentration levels. The analysis of the samples was accomplished by solid phase extraction followed by liquid chromatography-Orbitrap high-resolution mass spectrometry. In the cases of TiO 2 and CN, more than 70% of the initial concentration (e.g., venlafaxine) was degraded after 90 min, while 20CNSTO presented lower photocatalytic performance. Furthermore, some compounds were sporadically detected (e.g., fluoxetine) or their concentrations remained stable during the photocatalytic treatment time period (e.g., trimethoprim). In total 11 transformation products (TPs) were formed along the degradation processes and were identified by using liquid chromatography high resolution mass spectrometry.
“…1% DOC removed and~50% COD abatement (at 180 min) [102] Water from a natural source (Pance River in Cali, Colombia) and spiked with E. coli (5.5 mg L 20% and 85% of TOC were removed at pH 7.5 and 2.5, respectively (at 45 min) [104] 3 International Journal of Photoenergy The COD was abated smoothly up to 68% COD decrease after 90 min of Fenton reaction (1.6 h) [193] The hydrogen peroxide is generated in situ from the twoelectron oxygen reduction on cathodes such as reticulated vitreous carbon [46], gas diffusion electrodes [47], carbon felt [48,49], pristine graphene [50], and boron-doped diamond [51] from reaction (12), and Fe 2+ can be electrochemically regenerated, if it was initially added to the solution (reaction (13)) or electrochemically generated from a sacrificial iron anode (reaction (14) , enhanced by the photodecarboxylation of ferricarboxylate complexes under UV-visible light, followed by a very slow reaction rate with a low consumption of H 2 O 2 due to the disappearance of oxalic acid and free iron species complex with other organic oxidation by-products which reduced substantially the dissolved iron concentration and consequently the reaction rate [35].…”
Section: The Electrochemical Fenton-based (Ef) Processesmentioning
confidence: 99%
“…These two AOP have proved to be very effective for degrading a vast aqueous organic contaminants such as emerging [2,3], persistent [4][5][6][7][8][9], textiles [10][11][12][13], and bacteria [14][15][16] pollutants.…”
This literature research, although not exhaustive, gives perspective to solar-driven photocatalysis, such as solar photo-Fenton and TiO 2 solar photocatalysis, reported in the literature for the degradation of aqueous organic pollutants. Parameters that influence the degradation and mineralization of organics like catalyst preparation, type and load of catalyst, catalyst phase, pH, applied potential, and type of organic pollutant are addressed. Such parameters may also affect the photoactivity of the catalysts used in the studied solar processes. Solar irradiation is a renewable, abundant, and pollution-free energy source for low-cost commercial applications. Therefore, these solar processes represent an environmentally friendly alternative mainly because the use of electricity can be decreased/avoided.
scite is a Brooklyn-based organization that helps researchers better discover and understand research articles through Smart Citations–citations that display the context of the citation and describe whether the article provides supporting or contrasting evidence. scite is used by students and researchers from around the world and is funded in part by the National Science Foundation and the National Institute on Drug Abuse of the National Institutes of Health.