“…XRD, TEM and XPS results testify that metallic Ag particles deposit on the rutile surface. Although high content of Ag addition can inhibit the recombination of photogenerated electrons and holes, it will cover the surface of rutile and hinder the absorption of light source and adsorption of RhB molecules, resulting in the decrease of photocatalytic activity [11, 22].…”
The pure rutile and Ag-rutile nanomaterials were synthesised using sol-gel route and the effect of Ag concentration on the composite photocatalyst activity was investigated. The results show that the Ag 0 particles are deposited on the rutile surface, forming Ag-rutile heterojunctions. The high concentration of Ag is beneficial to inhibit the recombination of electrons and holes, meanwhile, excessive Ag particles will hinder the absorption of light source and adsorption of RhB molecules. Therefore, 2% of Ag rutile exhibits the highest photocatalytic activity.
“…XRD, TEM and XPS results testify that metallic Ag particles deposit on the rutile surface. Although high content of Ag addition can inhibit the recombination of photogenerated electrons and holes, it will cover the surface of rutile and hinder the absorption of light source and adsorption of RhB molecules, resulting in the decrease of photocatalytic activity [11, 22].…”
The pure rutile and Ag-rutile nanomaterials were synthesised using sol-gel route and the effect of Ag concentration on the composite photocatalyst activity was investigated. The results show that the Ag 0 particles are deposited on the rutile surface, forming Ag-rutile heterojunctions. The high concentration of Ag is beneficial to inhibit the recombination of electrons and holes, meanwhile, excessive Ag particles will hinder the absorption of light source and adsorption of RhB molecules. Therefore, 2% of Ag rutile exhibits the highest photocatalytic activity.
“…The decrease cannot be attributed to the formation of new recombination centers due to the addition of excess Ag because the PL peak intensity of 3%Ag-ZnO and 5%Ag-ZnO is still lower than that of 1%Ag-ZnO. It was conrmed that Ag particles are loaded on the ZnO surface and excess Ag particles will hinder the absorption of light, [51][52][53] thus causing a drop in the photocatalytic activity. Table 1 lists the photocatalytic performance data reported in literature.…”
“…Hence, we confirmed the state of Fe in Fe/TNAs is Fe 3+ instead of Fe 0 as the findings in Figure 3 c. Figure 3 d shows that O has a characteristic peak at 530 eV, which represents the formation of Ti or Fe oxides [ 43 ]. Figure 3 e shows that the characteristic peaks of Ti at 458 eV and 464 eV correspond to Ti 2p 3/2 and Ti 2p 1/2 respectively, confirming that Ti exists in the form of Ti 4+ [ 44 ]. Table 2 shows the element percentage of Fe/TNAs-0.2 and Fe/TNAs-0.5 by XPS analysis.…”
This study used iron modified titanate nanotube arrays (Fe/TNAs) to remove E. coli in a photoelectrochemical system. The Fe/TNAs was synthesized by the anodization method and followed by the square wave voltammetry electrochemical deposition (SWVE) method with ferric nitrate as the precursor. Fe/TNAs were characterized by SEM, XRD, XPS, and UV-vis DRS to investigate the surface properties and light absorption. As a result, the iron nanoparticles (NPs) were successfully deposited on the tubular structure of the TNAs, which showed the best light utilization. Moreover, the photoelectrochemical (PEC) properties of the Fe/TNAs were measured by current-light response and electrochemical impedance spectroscopy. The photocurrent of the Fe/TNAs-0.5 (3.5 mA/cm2) was higher than TNAs (2.0 mA/cm2) and electron lifetime of Fe/TNAs-0.5 (433.3 ms) were also longer than TNAs (290.3 ms). Compared to the photolytic (P), photocatalytic (PC), and electrochemical (EC) method, Fe/TNAs PEC showed the best removal efficiency for methyl orange degradation. Furthermore, the Fe/TNAs PEC system also performed better removal efficiency than that of photolysis method in E. coli degradation experiments.
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