J. Tong et al. / Journal of Catalysis 344 (2016) 474–481
475
employed to catalyze styrene oxidation [44]. From the viewpoint of
environmental protection, molecular oxygen was used as a green
and cheap oxidant, for which MOF-74(Cu/Co) [45], bulk Au parti-
cles [46], and gold nanoparticles supported on dendrimer resin
evaporated in an oil bath at 80 °C under continuous stirring until
a brown gel formed. After the reaction, the formed gel was dried
at 120 °C until a foamy xerogel was obtained. Then the produced
xerogel was ignited at 650 °C, a self-propagating combustion pro-
cess occurred, and an olive brown product was obtained after it
combusted completely. The Ce-doped samples were prepared as
[47], sulfur-doped graphene [48], and hollow iron oxide nanoshells
49] have been reported to be active catalysts. However, as a mild
[
oxidant, molecular oxygen is usually less efficient, with a low reac-
tion rate at ambient pressure. Compared with molecular oxygen,
described above and were designated as CFO-Ce0.1, CFO-Ce0.3
,
and CFO-Ce0.5, respectively. For comparison, pristine CoFe O
2 4
H
2
O
2
is a green and more efficient alternative. Various catalysts
have been used to catalyze styrene oxidation using H as oxi-
dant, such as N -type bis(diazoimine) complexes supported on
silica [50], platinum nanoclusters supported on TiO anatase [51],
phosphomolybdic acid supported on ionic-liquid-modified MCM-
1 [52], zinc phthalocyanine supported on multiwalled carbon
nanotubes [53], Ag–WO catalyst [54], V-MCM-48 [55], Ti-
was also prepared and was designated as CFO-A. The samples were
ground finely and screened by a 300 mesh sieve before character-
ization and employment as catalysts for oxidation of styrene with
hydrogen peroxide.
2 2
O
4 4
O
2
4
2.3. Oxidation of styrene
3
containing mesoporous silica [56], and iron oxide nanoparticles
supported on mesoporous silica-type materials [57]. Based on the
mentioned advantages of ferrites, several examples have been
reported for oxidation of styrene using ferrites as catalysts, such
The selective oxidation of styrene was carried out in a 25 mL
Schlenk tube. In a typical procedure, 0.06 mmol (ca. 15.0 mg, based
on the given formula Ce Co1ꢀxFe of catalyst, 2.0 mL
17.4 mmol) of styrene, 10 mL of solvent, and 2.7 mL of hydrogen
peroxide (30%), styrene:H molar ratio of 2:3, were added suc-
x
2 4
O )
(
2 4 x 4
as nickel and zinc ferrites [26], SrFe O [28], Mg Fe3ꢀxO [29],
2 2
O
CaFe [58], Ni–Gd ferrites [59], spinel Mg–Cu ferrites [60], and
2 4
O
cessively into the flask. The flask was then immersed in an oil bath
at a desired temperature for a desired reaction time under stirring
with an optimum stirrer speed of 1200 rpm, at which the highest
conversion rate could be obtained (Fig. S1; see the Supporting
Information). It is clear from Fig. S1 that the reaction is effected
by diffusion limitation. Under the above conditions, the atmo-
sphere in the tube included mainly air, vapor of substrate, water,
supported noble metals [1,54,61]. Being a terminal olefin, styrene
is difficult to oxidize, and most of these oxidation reactions were
limited by complicated preparation procedures, high costs, harsh
conditions, or low efficiency.
2 4
In our previous work [62], CoFe O nanocrystals synthesized by
sol–gel autocombustion were proved to be a highly active and
easily recovered catalyst for the oxidation of cyclohexane by
molecular oxygen without addition of solvents or reductants. As
part of our interest in hydrocarbon oxidation catalyzed by spinel
ferrites, we are reporting here that rare earth metal Ce-doped
cobalt ferrites synthesized by a sol–gel autocombustion method
can efficiently catalyze the oxidation of styrene to produce ben-
zaldehyde, and their catalytic activities can be greatly enhanced
2 2
and solvent, and oxygen from decomposition of H O . The pressure
in the tube ranged from 1.1 to 1.2 atm. After the reaction, the tube
was cooled to room temperature. The gas-phase mixture was col-
lected and analyzed by gas chromatography (GC) equipped with
a 5A molecular sieve column and a thermal conductivity detector
(
TCD). Liquid-phase aliquots were identified by GC-MS and
quantified by GC equipped with an SE-54 capillary column and a
hydrogen flame ionization detector (FID) using toluene as internal
standard. The detected products in the liquid phase included the
main product benzaldehyde and byproducts phenylacetaldehyde,
styrene oxide, benzoic acid, phenylacetic acid, and formaldehyde.
Trace of CO was detected in the gas phase. The amount of resid-
2 4 2
when compared with those of pristine CoFe O and CeO .
2
. Experimental
2.1. Materials and equipment
ual H
2
O
2
was determined by iodometric titration [63,64] and the
All reagents were of analytical grade and were used as received.
X-ray diffraction (XRD) patterns of the samples were collected
using a PANalytical X’Pert Pro diffractometer with CuK radiation.
Scanning electron microscopy (SEM) and transmission electron
microscopy (TEM) micrographs were obtained using a JSM-
2
H O
2
utilization efficiency was defined as follows: H utiliza-
2 2
O
tion efficiency = [(mol (benzaldehyde + phenylacetaldehyde +
a
styrene oxide) + 2 ꢂ mol (benzoic acid + phenylacetic acid))/mol
(
2
H O
2
)
consumed] ꢂ 100%.
5
600LV and a Hitachi H-600 microscope, respectively. Metal con-
tent was determined by inductively coupled plasma (ICP) on a Per-
kin–Elmer ICP/6500 atomic emission spectrometer. BET surface
area measurements were performed on a Micromeritics ASAP
3. Results and discussion
3.1. Characterization of the catalysts
2
010 instrument at liquid nitrogen temperature. The oxidation
products were determined by an HP 6890/5973 GC/MS instrument
and quantified by a Shimadzu GC-2010 gas chromatograph using
toluene as internal standard.
3.1.1. The XRD characterization
The XRD patterns of the Ce-doped samples are shown in Fig. 1.
The average particle sizes (based on the Scherrer equation) and lat-
pffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffi
2
2
2
tice parameters (based on the formula a ¼ d h þ k þ l ,
2d sin h ¼ nk) based on the most intense diffraction peaks of the
spinel phase of the samples are shown in Table 1. It can be con-
firmed from Fig. 1 that the main phase in Ce-doped samples is spi-
nel (JCPDS No. 22-1086). It can also be confirmed that the minor
2.2. Preparation of the catalysts
The rare earth metal cerium-doped cobalt ferrite samples
Ce Co1ꢀxFe O (x = 0.1, 0.3, 0.5) were prepared by a sol–gel auto-
x 2 4
combustion route under optimized conditions reported in our pre-
2
new phases of CeO (PDF No. 801792) formed and their contents
vious work [62]. In a typical procedure, stoichiometric amounts of
increased with increasing Ce content.
Co(NO
3
)
2
ꢁ6H
2
O, Ce(NO
3
)
3
ꢁ6H
2
O, Fe(NO
3
)
3
ꢁ9H
2
O, and citric acid
Table 1 shows that the lattice parameters of the Ce-doped sam-
ples increased from 8.3812 to 8.3870 Å with increase of Ce from 0
were completely dissolved in distilled water with a 1:1 molar ratio
ꢀ
1
4+
of metals to citric acid and a 0.1 mol L concentration of metals.
Concentrated ammonia (25–28%) was added slowly under con-
stant stirring to adjust the solution to neutral. The solution was
to 0.5. This confirms that Ce , with a larger radius of 0.101 nm,
2
+
3+
partly replaced Co
0.067 nm, respectively.
or Fe , with small radii of 0.082 and