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Photocatalysts for hydrogen generation and organic contaminants degradation  231



















           Fig. 10.13  Postulated mechanism of the visible light-induced photodegradation of acetone
           with PPY-Ag-TiO 2  nanocomposites. The relative band structures of PPY-Ag-TiO 2  make the
           photodegradation possible [45].
           Reprinted with permission Y. Yang, J. Wen, J. Wei, R. Xiong, J. Shi, C. Pan, Polypyrrole-
           decorated Ag-TiO2 nanofibers exhibiting enhanced photocatalytic activity under visible-light
           illumination. ACS Appl. Mater. Interfaces 5 (2013) 6201–6207. Copyright (2013) American
           Chemical Society.


           The photocatalytic activity of the PPY-Ag-TiO 2  system was found to be remarkable
           and attributed to favorable electron transfer to TiO 2  nanoparticles from PPy. Because
           the Fermi level of Ag nanoparticles lies just below the conduction band edge of TiO 2
           nanoparticles, electron transfer to Ag levels acted as an additional sink for electrons,
           thereby boosting the charge separation, as shown in Fig. 10.13. Immobilizing pho-
           tocatalyst nanoparticles such as regenerated cellulose or polymers on templates has
           also been recommended. These techniques immobilize the photocatalyst nanoparti-
           cles, reduce agglomeration, and help maintain high surface areas. Immobilization of
           CdS beads through a polymer D201 (polystyrene-divinylbenzene) matrix was found to
           cause the degradation of Rhodamine B, to inhibit the photocorrosion of CdS, and to fa-
           cilitate easy separation of the photocatalyst by mere filtration [46]. SnO 2 /TiO 2  nanopar-
           ticles (~10 nm) deposited on attapulgite could successfully degrade methyl orange dye
           [47]. The products could also be separated, which would promote recycling and reuse.
              Some water-stable MOFs have been developed recently and used to decontaminate
           heavy-metal ions under visible light-driven photocatalysis. In a study by Laurier and
           coworkers, a remarkably high visible light photocatalytic activity for iron(III)-oxide-
           based MOFs compared to the UV-responsive P25 reference catalyst was observed.
           For the commercial Fe 2 O 3  nanopowder, no photocatalytic activity could be observed
           in the system understudy, indicating that a fast electron-hole recombination was the
           dominant process under the experimental conditions.  The different Fe(III)-MOF
           samples showed clear visible-light photocatalytic activity. The highest overall visible
           light photocatalytic activity was measured for the metal-organic framework MIL-
           88B(Fe) [48]. MOF-5 was proposed as a photocatalyst for the degradation of organic
           contaminants. This MOF has a broad absorption band located in the 500–840 nm
           range, which can be assigned to delocalized electrons available on the  microsecond
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