Abstract:Photo-assisted electrochemical process is a promising technology for a clean ecosystem. It is largely utilized for recovering metals and oxidizing recalcitrant organic compounds. This paper aims to discuss the performance of the photo-oxidation and reduction by applying semiconductor photo-catalysis as the anode and graphite as the cathode for treating rainwater in Tehran, Iran. Organic pollutants and different metals were investigated to study the probable roles of the anodic potential, the gap between electr… Show more
“…Hence, there is obvious evidence that the photo-oxidation of Pb(II) yielded of PbO 2 , by following the reaction in Equation ( 4). The formation of PbO 2 from Pb(II) photo-oxidation well agrees with the finding reported previously [8,9]. The formation of the solid PbO 2 is beneficial in terms of solid waste treatment due to the less toxic and handleable waste.…”
Section: Detection Of Pbo 2 Produced From the Photo-oxidationsupporting
confidence: 91%
“…It is inferred that the photocatalytic removal is i ated and/or accompanied by the adsorption step [18]. The enhancement of the visible tocatalytic-oxidation was promoted by lowering band gap energy (Eg), that allowed to be activated by visible light generating a lot of OH radicals for oxidation [16][17][18][19][20]23 The reactions of the formation of OH radicals and Pb(II) photo-oxidation were prese as Equation (1), Equation (2) [11][12][13][14] and Equation (3) [7][8][9]. The effective photocatal oxidation of Pb(II) under visible light provides a potential and promising method t applied on a larger scale for industrial wastewater treatment.…”
Section: Influence Of N Dopingmentioning
confidence: 99%
“…Currently, remediation of Pb(II) containing water by the photo-oxidation process through photo-Fenton method [7], under TiO 2 photocatalyst [8], and photo-assisted electrochemical [9] have also been developed. Furthermore, oxidation of Pb(II) by manganese salt has been studied [10].…”
Section: Introductionmentioning
confidence: 99%
“…Furthermore, oxidation of Pb(II) by manganese salt has been studied [10]. Oxidation seems to be the most interesting method since Pb(II) oxidation resulted in the non-toxic precipitate PbO 2 and is more easily handled [7][8][9][10].…”
The photocatalysis process over N-doped TiO2 under visible light is examined for Pb(II) removal. The doping TiO2 with N element was conducted by simple hydrothermal technique and using urea as the N source. The doped photocatalysts were characterized by DRUVS, XRD, FTIR and SEM-EDX instruments. Photocatalysis of Pb(II) through a batch experiment was performed for evaluation of the doped TiO2 activity under visible light, with applying various fractions of N-doped, photocatalyst mass, irradiation time, and solution pH. The research results attributed that N doping has been successfully performed, which shifted TiO2 absorption into visible region, allowing it to be active under visible irradiation. The photocatalytic removal of Pb(II) proceeded through photo-oxidation to form PbO2. Doping N into TiO2 noticeably enhanced the photo-catalytic oxidation of Pb(II) under visible light irradiation. The highest photocatalytic oxidation of 15 mg/L Pb(II) in 25 mL of the solution could be reached by employing TiO2 doped with 10%w of N content 15 mg, 30 min of time and at pH 8. The doped-photocatalyst that was three times repeatedly used demonstrated significant activity. The most effective process of Pb(II) photo-oxidation under beneficial condition, producing less toxic and handleable PbO2 and good repeatable photocatalyst, suggest a feasible method for Pb(II) remediation on an industrial scale.
“…Hence, there is obvious evidence that the photo-oxidation of Pb(II) yielded of PbO 2 , by following the reaction in Equation ( 4). The formation of PbO 2 from Pb(II) photo-oxidation well agrees with the finding reported previously [8,9]. The formation of the solid PbO 2 is beneficial in terms of solid waste treatment due to the less toxic and handleable waste.…”
Section: Detection Of Pbo 2 Produced From the Photo-oxidationsupporting
confidence: 91%
“…It is inferred that the photocatalytic removal is i ated and/or accompanied by the adsorption step [18]. The enhancement of the visible tocatalytic-oxidation was promoted by lowering band gap energy (Eg), that allowed to be activated by visible light generating a lot of OH radicals for oxidation [16][17][18][19][20]23 The reactions of the formation of OH radicals and Pb(II) photo-oxidation were prese as Equation (1), Equation (2) [11][12][13][14] and Equation (3) [7][8][9]. The effective photocatal oxidation of Pb(II) under visible light provides a potential and promising method t applied on a larger scale for industrial wastewater treatment.…”
Section: Influence Of N Dopingmentioning
confidence: 99%
“…Currently, remediation of Pb(II) containing water by the photo-oxidation process through photo-Fenton method [7], under TiO 2 photocatalyst [8], and photo-assisted electrochemical [9] have also been developed. Furthermore, oxidation of Pb(II) by manganese salt has been studied [10].…”
Section: Introductionmentioning
confidence: 99%
“…Furthermore, oxidation of Pb(II) by manganese salt has been studied [10]. Oxidation seems to be the most interesting method since Pb(II) oxidation resulted in the non-toxic precipitate PbO 2 and is more easily handled [7][8][9][10].…”
The photocatalysis process over N-doped TiO2 under visible light is examined for Pb(II) removal. The doping TiO2 with N element was conducted by simple hydrothermal technique and using urea as the N source. The doped photocatalysts were characterized by DRUVS, XRD, FTIR and SEM-EDX instruments. Photocatalysis of Pb(II) through a batch experiment was performed for evaluation of the doped TiO2 activity under visible light, with applying various fractions of N-doped, photocatalyst mass, irradiation time, and solution pH. The research results attributed that N doping has been successfully performed, which shifted TiO2 absorption into visible region, allowing it to be active under visible irradiation. The photocatalytic removal of Pb(II) proceeded through photo-oxidation to form PbO2. Doping N into TiO2 noticeably enhanced the photo-catalytic oxidation of Pb(II) under visible light irradiation. The highest photocatalytic oxidation of 15 mg/L Pb(II) in 25 mL of the solution could be reached by employing TiO2 doped with 10%w of N content 15 mg, 30 min of time and at pH 8. The doped-photocatalyst that was three times repeatedly used demonstrated significant activity. The most effective process of Pb(II) photo-oxidation under beneficial condition, producing less toxic and handleable PbO2 and good repeatable photocatalyst, suggest a feasible method for Pb(II) remediation on an industrial scale.
“…In this study, we believe the action of the wind that carries solid particles that settle on the roof surface affect the original rainwater composition. The presence of excessive iron and manganese in rainwater originated in natural minerals from the soil and dissolved in rainwater has been reported in previous works (Aziz et al 2020;Ebraheim et al 2021).…”
Section: Removal Of Fe 2+ and Mn 2+ In Rainwatermentioning
This study is about the use of naturally occurring filtering materials for rainwater treatment for drinking water proposal. Crushed gravel, ceramic spheres from natural clays, silica sand and natural zeolite were used as filtering materials. The mineralogical composition of filtering materials was determined, being the illite and mordenite the major components of ceramic spheres and natural zeolite, respectively. Naturally occurring materials were simultaneous evaluated on two configuration of pilot plant systems (biofilters) for rainwater treatment. Three columns were arranged in series with unstratified flooded beds. The first stage was packed using crushed gravel. The second stage was packed using ceramic spheres. The third stage was packed with silica sand for the first plant and a natural zeolite was used for the second pilot plant system. Finally, a last stage of ultraviolet disinfection was incorporated. The trial period was 90 days, and it was evaluated the removal of Fe+2 and Mn+2, total coliforms, faecal coliforms and Escherichia col (E. coli). The rainwater treatment system using natural zeolite provided better results than the one using silica sand at third stage. The concentration of Fe+2 and Mn+2 was below the maximum permissible limits within 45 days. The efficiency of the treatment systems was optimal within 45 days, after the efficiency decreased progressively. Then, it is an attractive proposal for rural areas in developing countries for single-family water treatment systems.
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