P25, even under CO . On the other hand, when FeO@P25 was
under an appropriate CO2 loading (ca. 50 and 100 kPa for
2
irradiated by sunlight, only with a wavelength longer than
FeO@P25 and P25, respectively) a balanced combination
4
1
20 nm (only molecular iron oxide was excited, Table 1, entry
4), smaller amount of cyclohexanone formed on FeO@P25 if
between the CO -modified surface properties of the catalysts and
2
the polarity of the liquid phase makes the formed cyclohexanone
and cyclohexanol promptly desorb from the catalysts surface,
which prevents the successive oxidation of the partially oxidized
products.
compared to that obtained by sunlight irradiation (320 nm < λ,
Table 1, entry 9), although similar selectivity (ca. 100%) were
attained. Also, no products were detected on FeO@SiO under
2
identical conditions (Table 1, entry 17), showing that the iron
oxide functioned as the photocatalysis of cyclohexane oxidation
As shown in Table 1 (entry 15), FeO@P25 was able to be
reused without significant loss of the activity. Moreover, it was
possible to synthesize the catalyst at larger scale by increasing
the amount of the added P25, iron source and solvent. These
facts show merits of the present system for practical applications.
In summary, we have reported a highly effective and selective
sunlight-induced photocatalytic oxidation of cyclohexane, in
only when it was adjacent to TiO . Moreover, no products were
2
detected on FeO@P25 without any irradiation, which revealed
that iron oxide did not work as a thermocatalyst. From these
observations, we considered a possible role of iron oxide in the
selective cyclohexane oxidation over FeO@P25 as follows: elec-
trons, which transfer from both the TiO valence band by UV
acetonitrile, to cyclohexanone and cyclohexanol on TiO (P25)
2
2
excitation, and iron oxide by visible light excitation (possibly
modified with iron oxide under a CO atmosphere. The present
2
2
8,29
due to the d–d transition of molecular iron oxide)
to the
success opens up new opportunities to synthesize a wide variety
of fine chemicals in an economically and environmentally favor-
able fashion.
TiO conduction band, effectively reduce adsorbed O to gener-
2
2
−
ate O . The obtained superoxide anion plays an important role
2
in the selective cyclohexane oxidation over FeO@P25. Lower
amount of cyclohexanone formed on FeO@P25 when only the
iron oxide was excited (Table 1, entries 9 and 14), which was
explained by that smaller amount of electrons, which were
Notes and references
2
8
†FeO@P25 was synthesized according to the literature: P25 (1.0 g,
Nippon Aerosil) was added to 6.5 × 10− mol L of a iron(III) acetyla-
cetonate in a mixed solvent (100 mL, ethanol/hexane = 3 : 17 v/v) and
the mixture was stirred at room temperature for 24 h. The product was
separated by centrifugation (3000 rpm, 20 min), washed repeatedly with
the same solvent, and calcined at 500 °C for 1 h. The reaction was
4
−1
−
necessary to generate O2 , were transferred to the conduction
band of TiO . The action spectrum (from 330 to 460 nm) in
2
cyclohexanone formation on FeO@P25 was in good agreement
with the UV-vis spectrum of P25 rather than that of FeO@P25
repeated three times. FeO@SiO
where SiO (Wako gel Q-63) was used instead of P25.
Adsorption tests were done in a similar way that conducted in photoca-
2
was synthesized in a similar way,
(Fig. 1), supporting the above hypothesis. The mineralization of
2
cyclohexane and the successive oxidation of cyclohexanone and
cyclohexanol hardly occurred to give only trace amounts of CO2
on FeO@P25 (especially under lower loading levels of CO2),
since iron oxide efficiently prevented the interactions between
bulky molecules, cyclohexane and the partially oxidized pro-
ducts, with the valence band holes on the P25 surface. The
‡
talytic conversions except that 10 mg of the catalyst and a solution of
cyclohexanone (2 mL) in acetonitrile (18 mL), which was not bubbled
with O , were mixed.
2
1
B. Ohtani, S. Tsuru, S. Nishimoto, T. Kagiya and K. Izawa, J. Org.
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2
3
4
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to suppress the photocatalytic decomposition activity of organic
32–34
compounds.
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When the atmosphere was changed from CO (or air) to Ar
2
6
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(
purged), larger amounts of cyclohexanone and CO formed on
2
FeO@P25 (Table 1, entry 16). Moreover, the yield and the selec-
tivity for cyclohexanone and cyclohexanol formation on
FeO@P25 and P25 varied with CO2 pressure (Table 1 and
7
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9
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Fig. 2, left). These results imply that CO dissolves in the liquid
2
phase and/or adsorbs on the catalyst surface depending on CO2
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2
3
5
adsorb on metal oxides, so that the surface modification of P25
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2
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1
1
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It is also thought that dissolved CO changes the polarity of the
liquid phase to influence the adsorption or the desorption of the
partially oxidized products, since it has been reported that the
2
1287.
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2
36,37
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varies with solvents.
To confirm the hypothesis, the adsorp-
1
tion of cyclohexanone from acetonitrile on FeO@P25 and P25
2
was investigated under controlled CO pressure.‡ As shown in
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the right of Fig. 2, the amount of the adsorbed cyclohexanone
2
on FeO@P25 and P25 varied with CO pressure, and the curves
2
2423.
almost mirrored the curves for CO2 pressure dependence of
the photocatalytic performance. Accordingly, it is plausible that
23 Y. Ide, N. Nakamura, H. Hattori, R. Ogino, M. Ogawa, M. Sadakane and
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1266 | Green Chem., 2012, 14, 1264–1267
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