Table 1 Structural parameters and photocatalytic performancesa
Catalyst
F/Ti SBET/m2 gÀ1 VP/cm3 gÀ1 Yield (%)
P25
0
0
45
81
0.20
0.34
0.21
0.11
0.015
6
7
36
54
62
Porous TiO2
F-doped TiO2
Polycrystalline TiOF2
0.060 86
2.0 17
5.6
Single-crystalline TiOF2 2.0
a
Reaction conditions: 0.050 g catalyst, 50.0 mL 5.0 Â 10À5
M
W Xenon lamps (l 4 420 nm),
4-chlorophenol, three 500
T = 30 1C, stirring rate = 800 rpm, reaction time = 6 h.
TiO2, and undoped TiO2, indicating the increase of recombination
rate between photoelectrons and holes.12 The single-crystalline
TiOF2 displayed a lower recombination rate than the poly-
crystalline TiOF2 owing to its higher crystallization degree
which facilitated the transfer of photo-induced electrons from
the bulk to the surface and thus, could effectively inhibit their
recombination with the photo-induced holes.13 Both the
polycrystalline TiOF2 and F-doped TiO2 exhibited lower
recombination rate than the undoped TiO2. A possible reason
was the increase of oxygen vacancies due to the replacement of
O by F, taking into account that the oxidation numbers of O
and F are À2 and À1, respectively. These oxygen vacancies
could capture photoelectrons and thus, inhibit their
recombination with photo-induced holes. This could also account
for the lower recombination rate of the polycrystalline TiOF2
than that of the F-doped TiO2 since the former contained much
higher F-content (F/Ti = 2) than the latter (F/Ti = 6%).
The photocatalytic performance was examined by using photo-
degradation of 4-chlorophenol under visible light irradiation (light
intensity = 600 mW cmÀ2, wavelength 4420 nm). Detailed
experimental procedures are described in ESI.w Table 1 lists
structural parameters and catalytic activities of different catalysts.
The undoped TiO2 and P25 displayed very low activity
(4-chlorophenol degradation yield o 10%) since they could not
be activated by visible light. The single-crystalline TiOF2 exhibited
higher activity than the F-doped TiO2, despite its lower SBET and
VP. This could be attributed to either stronger absorbance of
visible light or higher crystallization degree which effectively
inhibited the photoelectron–hole recombination.13 Despite the
lower SBET and VP, similar F-content and absorbance ability
for visible light (see Fig. 3A), the single-crystalline TiOF2 still
exhibited higher activity than the polycrystalline TiOF2, possibly
owing to the lower photoelectron–hole recombination resulting
from the enhanced crystallization degree and oxygen vacancies
(see Fig. 3B). This could be further confirmed by the photo-
catalytic degradation of 4-chlorophenol under UV-light
irradiation (Fig. S8, ESIw).
Fig. 4 Recycling test of TiOF2 and F-doped TiO2 photocatalysts.
Reaction conditions are given in Table 1.
In summary, this work developed a facile approach to synthe-
size single-crystalline TiOF2 by HF etching the TiO2/SiO2 nano-
composite prepared by aerosol-spraying. The TiOF2 was more
active and durable than the F-doped TiO2 in photocatalytic
degradation of 4-chlorophenol under visible irradiation, which
could be attributed to the intense spectral response in the visible
region, the high crystallization degree, the enhanced F–Ti inter-
action, and the strong hydrothermal stability. The well defined
TiOF2 single crystals also showed powerful optical, photo-
electrical, and biological properties, which might offer new
opportunities of applications in these areas.
This work was supported by the National Natural Science
Foundation of China (20825724), Shanghai Government
(2007CG59, S30406, 07dz22303, DZL807) and by Key
Laboratory of Resource Chemistry of Ministry of Education.
Notes and references
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This journal is The Royal Society of Chemistry 2009
5396 | Chem. Commun., 2009, 5394–5396