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Y. Wang et al. / Journal of Alloys and Compounds 637 (2015) 301–307
Scheme 1. Schematic illustration of the formation of 1D Fe3O4/C@ZnO core–shell composite microrods.
Table 1
As one of the most important multifunctional semiconductor
Control of ZnO particle size in 1D Fe3O4/C@ZnO composite microrods using different
materials, ZnO has been widely noted and studied due to their
low-cost, high quantum efficiency and high photocatalytic activity
and stability [24–29]. Because the synthetic methods of ZnO nano/
micro-structures are usually simple, low-temperature, non-toxic,
environmentally-friendly [30–36], ZnO has been regarded as a
promising photocatalytic material for realizing commercialization.
In this study, as a proof-of-concept demonstration of the functional
properties of the as-prepared 1D Fe3O4/C composite microrods, we
choose ZnO nanocrystal as a coating layer to form Fe3O4/C@ZnO
core–shell microrods, which exhibit obviously enhanced photocat-
alytic activity and excellent recyclability for the decolorization of
photosensitized dye Congo red (CR) under visible-light
illumination.
The detailed synthesis process is schematically demonstrated in
Scheme 1. Firstly, 1D Fe3O4/C composite microrods were synthe-
sized by one-pot magnetic-field inducing solvothermal method
[17]. Secondly, a uniform ZnO nanocrystal layer was deposited
on the surface of 1D Fe3O4/C microrods through a facile modified
hydrothermal process, which only requires Zn(Ac)2Á2H2O and
NaOH as reagents reacting at 60 °C for 2 h in water. It is found that
the size of ZnO nanocrystals and the thickness of shell layer can
also be tuned by varying the concentration of precursors.
Furthermore, the 1D Fe3O4/C@ZnO core–shell microrods not only
exhibit excellent photocatalytic activity for the decolorization of
CR under visible-light irradiation, but also can be readily recycled
by a simple magnet with virtually no loss in catalytic efficiency.
Therefore, this design provides a promising candidate for removing
toxic organic pollutants during water treatment process.
Zn2+ concentrations.
Sample Zn2+ concentration/ NaOH concentration/ ZnO particle size/
M
M
nma
Sa
Sb
Sc
Sd
0.0031
0.0063
0.0125
0.0250
0.0063
0.0125
0.0250
0.0500
9.0
11.1
13.7
17.6
a
ZnO particle size was calculated from XRD diffraction data.
groups (e.g., carboxylic) of the Fe3O4/C composites. Then, 5 mL of NaOH aqueous
solution was dropwise added and kept stirring at 60 °C for 2 h. Finally, the product
was collected by a magnet, and washed with distilled water and ethanol for several
times, then dried in an oven at 60 °C for 6 h. In order to optimize the properties of
the 1D Fe3O4/C@ZnO core–shell microrods for photocatalytic applications, different
concentrations of Zn(Ac)2Á2H2O and also corresponding NaOH were used, while the
other conditions remain unchanged. Products prepared with different concentra-
tions of Zn(Ac)2Á2H2O (0.0031, 0.0063, 0.0125 and 0.0250 M) by seeding and growth
process were assigned to sample codes Sa, Sb, Sc and Sd, respectively (see Table 1).
2.3. Characterization
Powder X-ray diffraction (XRD) measurements of the samples were performed
with a Philips PW3040/60 X-ray diffractometer using Cu Ka radiation at a scanning
rate of 0.06°sÀ1. Scanning electron microscopy (SEM) images were obtained by a
Hitachi S-4800 scanning electron microanalyzer with an accelerating voltage of
15 kV. Transmission electron microscopy (TEM) and high-resolution transmission
electron microscopy (HRTEM) were conducted at 200 kV with a JEM-2100F field
emission TEM. Further evidence for the composition of the products was inferred
from X-ray photoelectron spectroscopy (XPS), using an ESCALab MKII X-ray
photoelectron spectrometer with Mg Ka X-ray as the excitation source. The absorp-
tion spectra were measured using a PerkinElmer Lambda 900 UV–vis spectropho-
tometer at room temperature.
2. Experimental details
2.4. Photocatalytic activity measurement
All reagents were analytical grade, purchased from the Shanghai Chemical
Reagent Factory, and used as received without further purification.
Photocatalytic activities of the as-prepared 1D Fe3O4/C@ZnO core–shell com-
posite microrods were evaluated by the degradation of CR under visible-light
irradiation from a 500 W Xe lamp (CEL-HXF300) with a 420 nm cut off filter. The
reaction cell was placed in a sealed black box with the top opened, and the cut
2.1. Synthesis of 1D Fe3O4/C composite microrods
1D Fe3O4/C microrods were prepared according to our previous work [17].
Briefly, 0.4 g of FeCl3Á6H2O and 0.3 g of NaAc were dispersed into a mixed solvent
of 15 mL of ethylene glycol and 3 mL of ethylenediamine with the assistance of
ultrasonication. Then, 0.4 g of glucose was added into the above suspension, and
the resulting mixture was transferred into a 20 mL of Teflon-lined stainless steel
autoclave in the presence of an external magnetic field (0.2 T), and heated at
180 °C for 6 h. Finally, the as-obtained Fe3O4/C composite microrods were collected
and washed with distilled water and ethanol for several times by centrifugation,
then dried in an oven at 60 °C for 6 h.
off filter was placed to provide visible-light irradiation. In
a typical process,
20 mg of as-prepared photocatalysts was added into 20 mL of CR solution (concen-
tration: 100 mg LÀ1). After being dispersed in an ultrasonic bath for 5 min, the solu-
tion was stirred for 2 h in the dark to reach adsorption equilibrium between the
catalyst and the solution and then exposed to visible-light irradiation. The samples
were collected by a magnet at given time intervals to measure the CR concentration
by UV–vis spectroscopy. To further study the recyclability of the 1D Fe3O4/C@ZnO
core–shell composite microrods, we also examined the photocatalytic activity of
sample Sd for 10 rounds. The recycled photocatalyst sample was reused without
any post-treatment except being washed with ethanol and distilled water three
times after each photocatalytic degradation of CR.
2.2. Synthesis of 1D Fe3O4/C@ZnO core–shell microrods
ÅOH radical reactions were performed as follows. 5 mg of each 1D Fe3O4/C@ZnO
core–shell composite microrods with different ZnO nanocrystal sizes were
suspended in 10 mL of aqueous solution containing 100 mg LÀ1 of CR, 10 mM of
NaOH and 5 mM of terephthalic acid (TA), respectively. Before exposure to
visible-light, the suspension was stirred in the dark for 10 min.
After irradiated for 10 min, the products were collected by a magnet, and the rest
In a typical procedure, a certain amount of Zn(Ac)2Á2H2O was added into 20 mL
of distilled water to form a clear solution. 50 mg of Fe3O4/C composite microrods
was added to the above solution with the assistance of sonication for 10 min.
Subsequently, the mixture was stirred by a mechanical stirring, followed by heating
at 60 °C for 2 h to allow the Zn2+ ions fully interact with the surface functional