Metal Oxide Nanocomposites. Группа авторов

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Metal Oxide Nanocomposites - Группа авторов

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to make a great contribution to both environmental treatment (emission cleaning and water purification) and renewable energy. Over the past few decades, the number of applications based on photocatalysis increased sharply; while a wide range of materials systems have been developed [73]. Photocatalytic H2 production from water is one of the most promising ways to realize a hydrogen economy for three reasons. (1) This technology is based on photon (or solar) energy, which is a clean, permanent source of energy, and mainly water, which is a renewable resource; (2) it is an environmental safe technology without undesirable by-products and pollutants; and (3) the photochemical conversion of solar energy into a storable form of energy, i.e. hydrogen allows to deal with the intermittent character and seasonal variation of the solar influx. Nano science and nanotechnology have boosted the modification of existing photocatalysts and the discovery and development of new candidate materials [74]. The rapidly increasing number of scientific publications constitutes clear bibliographical evidence for the significance of this hot topic. The valence holes are good oxidants and the conduction electrons are reductants. In most cases, the organic compounds are degraded by oxidation reaction involving photogenerated holes. Since 1972, scientists discovered the photocatalytic splitting of water on the illuminated single crystal TiO2 electrodes [75], the photocatalysis as a research area is of significant interest and photocatalytic processes have been extensively studied.

      These researchers proposed that nanoflowers and NPs indicated boosted photodegradation outcomes in comparison to nanoflowers, nanorods, nanotubes, as well as hour-glass-like ZnO spheres. To photodegrade phenol, Liu et al. used TiO2 nanostructures with various forms such as microspheres, NPs and nanorods though hydrothermal approach [82]. With nanorods to be photocatalyst, this group of researchers gained marvelous photodegradation outcomes. ZnO has come into the researchers’ focus since 1935, but its excellent features are discovered through modern methods and improved equipment [83]. Liang et al. [84] found that the generated graphene–TiO2 nanocrystal combination featured advanced photocatalytic performance in contrast to other TiO2 materials like P25, bare TiO2 and mixture of P25 and GO handled by hydrothermal procedure, in the splitting process of rhodamine B with UV irradiation, boosting a three-fold photocatalytic influence on P25. Metal oxide appearances indicate that it is good at decomposing organic molecules with great oxidizing ability for and superhydrophilicity [85, 86] and such traits could be adopted to generate wettability patterns, which have been adopted in many areas like in printed-circuit boards and offset printing, and can be used for fluid microchips in the future [87, 88].

, where, K2 is the spatial orientation factor of the dipole, N is the refractive index of the medium, φ is the fluorescence quantum yield of the donor and J is the overlap integral of the fluorescence emission spectrum of the donor and the absorption spectrum of the acceptor. On the relative positions basis of APTS and interfacial energy levels, the interfacial electron injection would be thermodynamically allowed from the excited singlet of APTS to CB of ZnO. On lighting at excitation wavelength both the APTS and ZnO are excited. Dual emission is anticipated due to LUMO → HOMO and CB → VB electron transfer. The probable is electron jump from the excited APTS to ZnO. Electron in LUMO of the excited APTS is of higher energy compared to that in the CB of ZnO. The inorganic nano size fillers with organic functional groups that attach to their surface by strong chemical bonds can be finally obtained. The interaction increases the surface tension of inorganic nano particles results f-ZnO. Binding interaction studies of NiO with AMB shows the unexpected results. The increased absorption observed with the dispersed NiO is due to the adsorption of AMB on the surface of NiO. Fluorescence enhancement resulted while adding the NiO to AMB. Azomethine nitrogen is involved in the binding process with Ag3O4 nanoparticles which was proved by molecular electrostatic potential. Morphological changes of Ag3O4 nanoparticles to AMB modified Ag3O4 nanoparticles confirm the binding of Ag3O4 nanoparticles to AMB. EDX spectrum of AMB modified Ag3O4 nanoparticles shows incorporation of AMB to Ag3O4 nanoparticles. The interaction between AMB and Ag3O4 occurs through static quenching mechanism.

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