1. Composites of Ta2O5 and g-C3N4 with
different weight ratios of the precursors (urea/Ta2O5
= 3, 4 và 5) have been successfully synthesized with
a new method by calcining ure with Ta2O5 at
temperature of 500 °C.
2. The composites demonstrate photocatalytic
activity for degradation of methylene blue in
aqueous solution under visible light irradiation.
Among the composites, the sample derived from
thermal treatment at 500 oC, weight ratio of
urea/Ta2O5 = 4 exhibits the best photocatalytic
activity.
3. Decomposition rate of methylene blue on
CN-500/TaO-4 composite is more than 2.7 times the
g-C3N4 and 21.5 times higher than Ta2O5.
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Vietnam Journal of Chemistry, International Edition, 55(2): 172-177, 2017
DOI: 10.15625/2525-2321.2017-00439
172
The photocatalytic activity of g-C3N4/Ta2O5 composite
under visible light irradiation
Nguyen Thi Viet Nga
1*
, Vo Vien
1,2
1
Department of Chemistry, Quy Nhon University
2
Applied Research Institute for Science and Technology, Quy Nhon University
Received 28 February 2017; Accepted for publication 11 April 2017
Abstract
The g-C3N4/Ta2O5 composites were synthesized by heating mixtures of urea and Ta2O5 at 500
o
C. The as-prepared
samples were denoted as CN-500/TaO-W, where W is weight ratio of urea/Ta2O5 and equals to 3, 4 and 5. The
materials were characterized by X-ray diffraction, X-ray photoelectron spectroscopy, and Ultraviolet-visible diffuse
reflectance spectroscopy. The photocatalytic activity of CN-500/TaO-W samples was assessed by degradation of
methylene blue in aqueous solution under visible light. Among them, CN-500/TaO-4 exhibited the best performance.
An enhancement in photocatalytic activity of the composites is believed to be the presence of g-C3N4.
Keywords. g-C3N4, Ta2O5, photocatalytic activity, methylene blue, g-C3N4/Ta2O5 composite.
1. INTRODUCTION
The study of materials that could absorb light
from the sun to decompose organic pollutants in
water and air is not only an opportunity but also a
challenge for many researchers and attracts a lot of
interest from society. The semiconductors that
highly exhibit the catalytic performance under light
have been known as potential photocatalysts. They
possess many advantages including high efficiency
in conversion of solar energy, strongly catalytic
activity, highly capable decomposition of organic
pollutants, reusability and especially environmental
friend.
Among the semiconductors, in recent years,
Ta2O5 has attracted much attention in photocatalysis.
However, with the large band gap energy (about 3.8
to 5.3 eV), its photocatalytic activity only exhibits in
ultraviolet region [1], leading to limit its application
in practice. To solve this problem, many works have
been done to modify Ta2O5 by doping with some
other elements to improve optical absorbance in
visible light [2, 3].
At the same time, g-C3N4 material, a polymer
organic semiconductor with graphitic-like structure,
can absorb visible light (the band gap energy of
about 2.7 eV), taking a lot interest of researchers due
to its wide range of applications. However, the fast
recombination rate of photoinduced electron-hole
pair for this material leads to its low photoefficiency.
This is a drawback when using it in invidual status.
Therefore, many attempts to enhance the
photocatalytic performance of g-C3N4 by modifying
it with other elements have been done [4, 5].
To improve the photocatalytic capability of each
material when using them in separate systems, we
synthesized g-C3N4/Ta2O5 composite as described in
details in the previous works [6]. In this article, we
focused on effect of the ratio (urea/Ta2O5) on
properties of the products and evaluated their
photocatalytic activity by photodegrading methylene
blue in aqueous solution.
2. EXPERIMENTAL
2.1. Chemicals
Tantalum pentoxide (Ta2O5), urea (CH4N2O),
and methylene blue (C16H18N3S) were purchased
from Merck. All chemicals were analytical grade
and used without further treatment.
2.2. Synthesis
Urea and Ta2O5 were mixed with different
weight ratios (urea/Ta2O5 in weight = 3, 4 and 5).
The mixtures were put into a porcelain cup sealed
with aluminum foil and then calcined at 500
o
C with
a heating rate 10
o
C min
-1
for 2 hours. The samples
were denoted as CN-500/TaO-W, where W is
VJC, 55(2), 2017 Nguyen Thi Viet Nga et al.
173
weight ratio between urea and Ta2O5.
For comparison, pure g-C3N4 was also prepared
by heating urea at 500
o
C, and denoted as CN-500.
2.3. Characterization
Powder X-ray diffraction (XRD) patterns were
conducted using a Bruker D8 Advance with Ni-
filtered CuKα radiation (λ = 1.5418 Å). X-ray
photoelectron spectroscopy (XPS) was performed
using an ESCALab spectrometer (Thermo VG, UK)
with monochromated AlKα radiation. Ultraviolet-
Visible Diffuse reflectance spectroscopy (UV-Vis
DRS) was investigated on a GBC Instrument - 2885
spectrophotometer.
2.4. Photocatalytic Activity
To evaluate photocatalytic activity of the
prepared materials, methylene blue (MB) was
selected as an organic pollutant. To 200 mL of 50
mg/L MB solution, 0.1 g of the prepared sample was
dispersed under stirring and the solution kept in dark
condition for 3 h to reach equilibrium of adsorption-
desorption process. Then, the solution was irradiated
by visible light using a 75W-220V lamp with a filter
cutting UV rays. MB degradation was monitored by
taking suspension at irradiation time intervals of 1 h.
Each suspension was centrifuged to separate the
catalyst from the MB solution. The degradation rate
was calculated as a function of irradiation time from
the change in absorbance at wavelength of 663 nm
as measured using a UV-Vis spectrophotometer
(Jenway 6800).
3. RESULTS AND DISCUSSION
3.1. Characterization of catalysts
3.1.1. XRD
The XRD patterns of the samples in figure 1
show that the main diffraction peaks of all samples
are from orthorhombic Ta2O5 [7], indicating that
orthorhombic Ta2O5 phase still remains in the as-
prepared samples under thermal treatment of the
mixture of Ta2O5 and urea at 500
o
C.
In addition, it is worth to note that an extra peak
with 2θ value at about 13.2 and 27.3o belonging to g-
C3N4 [8] (figure 1) can be seen clearly for CN-
500/TaO-4. This diffraction is indexed to (100) and
(002) plane, respectively, for graphite-like layer
structure of g-C3N4. This peak is very strong for the
CN-500/TaO-5, proving a larger amount of g-C3N4
in this material.
Figure 1: XRD patterns of Ta2O5, CN-500 and
CN-500/TaO-3, CN-500/TaO-4 and CN-500/TaO-5
3.1.2. XPS
XPS was used to examine the surface
composition and chemical state of C, N, O and Ta in
the samples. Figure 2 and table 1 show XPS of C, N,
O and Ta of a representative sample, CN-500/
TaO-4.
Figure 2: XPS spectrum of CN-500/TaO-4
Table 1: Binding energy of Ta4f, O1s, C1s, N1s
Orbital Ta4f O1s C1s N1s
Ebinding
(eV)
25.5
27.3
530.6 287.7
284.5
398.6
For C1s XPS, in addition to the peak at 287.7
eV corresponding to the referenced C, a strong peak
at 284.5 eV can be attributed to carbon in the C-N-C
configurations of g-C3N4 [9, 10]. The presence of g-
C3N4 in the sample can be further confirmed by N1s
XPS in table 1. The intense pic at 398.6 eV may be
assigned to sp
2
hybridized aromatic nitrogen atoms
bonded to carbon atoms (N=C) [11]. The peak at
530.6 eV for O1s is usually reported as O in Ta2O5
VJC, 55(2), 2017 The photocatalytic activity of g-C3N4/Ta2O5
174
[12]. Also shown in table 1, Ta 4f7/2, and Ta 4f5/2
peaks appeared at 25.5 eV and 27.3 eV, respectively,
which correspond to Ta
5+
in Ta2O5 [12]. However,
compared to pure Ta2O5 (26.6 eV and 28.5 eV,
respectively), a slight shift to lower energy has been
obtained. Such a shift may be caused by presence of
an interaction between Ta and g-C3N4 in the
composite. These results rather demonstrated that
CN-500/TaO-4 is a composite consisting of Ta2O5
and g-C3N4.
3.1.3. UV–Vis DRS
The optical absorption spectra and band gap
energy of Ta2O5, CN-500/TaO-3, CN-500/TaO-4,
and CN-500/TaO-5 are shown in figure 3.
Figure 3: (A) UV–Vis DRS and (B) band gap
energy of Ta2O5, CN-500/TaO-3, CN-500/TaO-4,
CN-500/TaO-5
In figure 3A, Ta2O5 exhibits an absorption peak
centered at approximately 275 nm which is assigned
to the O2p to Ta5d charge transfer band of the Ta2O5
[13]. This peak can be observed in the composites,
however their intensity strongly reduced. Compared
to the pristine Ta2O5, a broad absorption band
covering the range of 300-500 nm with a peak
centered at about 380 nm for the composites has
been obtained. This broad absorption in the visible
light region may come from g-C3N4 in the
composites. This indicates that the g-C3N4 may serve
as a sensitizer to extend the absorption in visible
light region for the composites and thus improve
their photocatalytic activities under visible light
irradiation.
Based on the document [14] and Kubelka-Munk
equation [15], the band gap energy of the materials
was determined and shown in Figure 3B. With a
reduced band gap energy, CN-500/TaO-3, CN-
500/TaO-4, CN-500/TaO-5 materials might possess
good catalyst activity in visible light region.
The formation of the composites can be
explained by that when heating the mixture of urea
and Ta2O5, first, polymerization of urea can occur
via some following steps [16, 17]:
N
N
N
NH2
NH2 + 6CO2 + 3NH36CO(NH2)2 H2N
melamine
to
urea
N
N
N
NH2
NH2H2N
2
to
+ 2NH3
Melem
N
N
N N
N
NN
NH2
NH2H2N
to
+ 3NH3
Melon
N
N
N N
N
NN
NH2
NH2H2N
N
N
N
N
N N
NHN
N N
NH
N
N
N N N
N
N
N N N N N
N
NH2
NH2H2N
3
Melon
N
N
N
N
N N
NHN
N N
NH
N
N
N N N
N
N
N N N N N
N
NH2
NH2H2N
to
n
- NH3
N
N
N
N
NN
N
N N N
NN N
N
NN
N N
NN N
N
NN
N
N
N
N
NN
N
N N
NN N
N
N N
NN
NN
N
N
NN
N
NN
N N N
g-C3N4
The g-C3N4 was then formed on surface of the
Ta2O5 particles to yield the composites.
3.2. Photocatalytic Activity
The photocatalytic activity of the samples was
determined by degradation of MB in water under
visible light. For comparison, photocatalytic activity
of the pristine Ta2O5 and g-C3N4 (CN-500) was also
presented. Figure 4 shows the variation of MB
concentration (C/C0) versus irradiation time on the
five samples.
Ta2O5 exhibited a low photocatalytic activity in
visible light which may be due to its large band gap
energy. For g-C3N4 (CN-500), although relatively
VJC, 55(2), 2017 Nguyen Thi Viet Nga et al.
175
small band gap energy, about 2.70 eV [1], its
photocatalytic activity is still low. This is explained
by that the high recombination rate of electron-hole
pair in pure g-C3N4 [18] leads to reduced
photocatalytic activity.
Figure 4: Photocatalytic activity of Ta2O5, CN-500,
CN-500/TaO-3 and CN-500/TaO-4, CN-500/TaO-5
toward the degradation of MB
For g-C3N4/Ta2O5 composits, a difference in
catalytic performance of the materials can be
observed. On the CN-500/TaO-4 sample, the
decrease in C/C0 is much faster than for the others.
For the CN-500/TaO-3 and CN-500/TaO-5, the
decrease in C/C0 is slower compared to CN-
500/TaO-4. This may be attributed to a reduced
recombination rate of electron-hole in CN-500/TaO-
4. The photocatalytic activity of CN-500/TaO-4 is
better than that of Ta2O5 and g-C3N4, indicating that
a synergistic effect occurs in the composite during
the photocatalytic reaction. Graphitic g-C3N4 playing
a key role in enhancement of photocatalytic activity
for composites was discussed in several reports [19].
On the basis of a number of works published [20,
21], decomposition mechanism of MB on the g-
C3N4/Ta2O5 composites is proposed in figure 5A. In
these composites, the photogenerated electrons on
the conduction band of the g-C3N4 can directly inject
into the conduction band of Ta2O5. This
phenomenon can lead to a significant decrease in the
electron–hole recombination for the pure g-C3N4.
Hence, this may contribute to the enhancement of
photocatalytic reactivity.
However, for CN-500/TaO-3 and CN-500/
TaO-5 in this work, the photocatalytic activity is
lower than that of the pure g-C3N4. This may be
explained by that a small or too large amount of g-
C3N4 in the two materials as shown in the
characterizations does not form the synergistic effect
mentioned above. In CN-500/TaO-5, when covered
with a quite thick layer of g-C3N4, this material will
show photocatalyst closing to that of pure g-C3N4. In
contrast, with a smaller amount of g-C3N4, the
activity of CN-500/TaO-3 is close to Ta2O5. This
shows that a proper amount of g-C3N4 in composite is
very important.
Figure 5: (A) Proposed mechanism for the
photodegradation of MB on the g-C3N4/Ta2O5
composites; (B) linear plots of ln(C0/Ct) vs. time for
degradation of MB in aqueous solution under visible
light
In order to investigate kinetics of the
photocatalytic reactions, the Langmuir-Hinshelwood
model has been usually employed. For solid-liquid
reactions, the Langmuir–Hinshelwood equation can
be expressed:
r = k·θ = k·KC/(1 + KC) (1)
where r and k are the reaction rate and rate constant,
respectively, θ is the surface coverage, K is the
adsorption coefficient of the reactant, and C is the
equilibrium concentration of the reactant. When C is
at low concentration, K·C << 1, hence r = k·KC/(1 +
KC) ≈ k·K·C = kapp·C. Therefore, the pseudo first-
order kinetics equation (Eq. (2)) is applied:
ln(C0/Ct) = kapp·t (2)
where C0 and Ct are the reactant concentrations at
reaction times, t = 0 and t = t, respectively, kapp is the
apparent reaction rate constant.
A relationship between ln(C0/Ct) and t was
plotted in figure 5B. It can been clearly seen that the
plots of ln(C0/Ct) versus reaction time (t) are well
VJC, 55(2), 2017 The photocatalytic activity of g-C3N4/Ta2O5
176
fitted with the pseudo first-order rate model with
high correlation coefficients (R ≥ 0.995). From the
plots, the kapp values were calculated for CN-
500/TaO-4, CN-500 và Ta2O5 to be 0.129 và 0.047
và 0.006 h
-1
, respectively. These results show that
the reaction rate on the catalyst CN-500/TaO-4 is
much stronger than CN-500 and Ta2O5.
The above obtained results show that weight
ratio of urea and Ta2O5 in reaction mixture for the
synthesis of g-C3N4/Ta2O5 composites plays an
important role to determine their band gap energy
and photocatalytic properties.
4. CONCLUSIONS
1. Composites of Ta2O5 and g-C3N4 with
different weight ratios of the precursors (urea/Ta2O5
= 3, 4 và 5) have been successfully synthesized with
a new method by calcining ure with Ta2O5 at
temperature of 500 °C.
2. The composites demonstrate photocatalytic
activity for degradation of methylene blue in
aqueous solution under visible light irradiation.
Among the composites, the sample derived from
thermal treatment at 500
o
C, weight ratio of
urea/Ta2O5 = 4 exhibits the best photocatalytic
activity.
3. Decomposition rate of methylene blue on
CN-500/TaO-4 composite is more than 2.7 times the
g-C3N4 and 21.5 times higher than Ta2O5.
Acknowledgement. This research was partly
funded by TEAM project (code ZEIN2016PR431).
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Corresponding author: Nguyen Thi Viet Nga
Department of Chemistry, Quy Nhon University
No. 170, An Duong Vuong Street
Quy Nhon City, Binh Dinh Province
E-mail: nguyenthivietnga@qnu.edu.vn; Telephone number: 0914481795.
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