Miaogen Chen1, Tao Sun1, Wan Zhao2, Xiuru Yang2, Wenya Chang1, Xiaoxiao Qian2, Qian Yang2, Zhi Chen2. 1. Key Laboratory of Intelligent Manufacturing Quality Big Data Tracing and Analysis of Zhejiang Province, Department of Physics, China Jiliang University, Hangzhou 310018, China. 2. College of Materials and Chemistry, China Jiliang University, Hangzhou 310018, China.
Abstract
1T-MoS2 is in situ grown on TiO2 nanotubes (TNTs) using a hydrothermal method, forming a 1T-MoS2@TNTs composite, which is confirmed by its physical characterization. The prepared composites show enhanced photocatalytic performance for the degradation of tetracycline hydrochloride under visible light, and the improved photocatalytic activity is closely related to the loaded amount of 1T-MoS2. Therein, 0.5 wt % 1T-MoS2@TNTs can degrade 57% in 1 h, which is the highest photocatalytic efficiency observed in experiments so far. It is speculated that the introduction of 1T-MoS2 may optimize light absorption and charge separation/transport. The active species are identified and the reaction mechanism is proposed here.
1T-MoS2 is in situ grown on TiO2 nanotubes (TNTs) using a hydrothermal method, forming a 1T-MoS2@TNTs composite, which is confirmed by its physical characterization. The prepared composites show enhanced photocatalytic performance for the degradation of tetracycline hydrochloride under visible light, and the improved photocatalytic activity is closely related to the loaded amount of 1T-MoS2. Therein, 0.5 wt % 1T-MoS2@TNTs can degrade 57% in 1 h, which is the highest photocatalytic efficiency observed in experiments so far. It is speculated that the introduction of 1T-MoS2 may optimize light absorption and charge separation/transport. The active species are identified and the reaction mechanism is proposed here.
Environmental pollution
including water contamination is a serious
problem threatening sustainable development. Antibiotic residue is
one of the refractory pollutants in water, and diverse techniques
have been evolved for efficient disposal.[1] Among these approaches, photocatalysis is one of the most attractive
and booming methods because of its clean, nonpolluting, and efficient
properties.[2] TiO2 is one of
the most investigated photocatalysts; however, it experiences the
intrinsic limits of a wide band gap and fast recombination of photogenerated
carriers. One of the widely used approaches is to construct a heterojunction
for facing these obstacles.[2]Recently,
transition-metal sulfideMoS2, a typical two-dimensional
material with a graphene-like layered structure,[3] has attracted intense attention with wide applications.[4] Generally, MoS2 has several polymorphs
including metallic 1T and semiconducting 2H and 3R phases. Previous
studies have mainly focused on 2H-MoS2 due to its good
stability, and the other two phases may convert into the 2H phase
under specific conditions.[5] 2H-MoS2 has been widely used as a high-performance photocatalyst,
and intensive attempts have been made to improve its photocatalytic
activity by modification or exfoliation.[6] Additionally, MoS2 can work as an efficient cocatalyst
by modifying other semiconductor photocatalysts such as TiO2, which is one powerful strategy to realize highly efficient photocatalytic
performances[7] by tuning the light absorption
and the separation/transport of carrier.[8]As is known, metallic 1T-MoS2 has a single-layered
S–Mo–S
structure, in which each Mo atom is surrounded by six S atoms in an
octahedral lattice.[9] Recently, 1T-MoS2 has become a promising candidate for a wide range of applications
due to its plentiful active sites and high electronic conductivity
(6 orders of magnitude higher than that of 2H-MoS2), exhibiting
a better catalytic performance than the other semiconducting counterparts.[9] Lately, high-purity and stable 1T-MoS2 nanosheets were synthesized using a hydrothermal method showing
an excellent activity. 1T-MoS2 may also work as a cocatalyst,
which induces enhanced photocatalytic efficiency. Especially, its
unique metallic feature may improve the separation/transport of carriers
greatly,[10] which may lead to the potential
replacement of Pt in practical applications.[11] However, the facile immobilization of 1T-MoS2 on other
semiconductor photocatalysts with improved performance is still a
challenge.To date, considerable efforts have been made to optimize
the MoS2 nanocomposites and expand their practical use.[12−14] For example, Zheng et al. applied a hierarchical MoS2 nanosheet on a TiO2 nanotube (TNT) array to enhance the
photocatalytic and photocurrent performance.[12] Zhao et al. used the MoS2 quantum dots@TNTs composites
to improve the visible-light-driven high-efficiency photocatalysis.[13] In this work, 1T-MoS2 is successfully
grown on TNTs using an in situ hydrothermal method, which shows enhanced
photocatalytic performance for the degradation of antibiotic residues
in water. The prepared samples are characterized and the factors influencing
the photocatalytic activity are discussed. The active species are
studied and a reaction mechanism is suggested.
Results and Discussion
Powder X-ray diffraction (XRD) patterns of the synthesized 1T-MoS2, TNTs, and 1T-MoS2@TNTs samples are shown in Figure a. It is noticed
that metallic 1T-MoS2 has two obvious characteristic peaks
located at 13.9 and 33.2°, which could be assigned to its (002)
and (100) facets.[9] The peak of the (002)
facet is much greater than that of the (100) facet, indicating that
the prepared 1T-MoS2 sample has a well-crystallized (002)
facet.[15] As shown, the characteristic peaks
of TNTs are completely consistent with that of anatase TiO2,[16] which illustrates that the obtained
TNTs are anatase with good crystallinity.[17] As for 1T-MoS2@TNTs, the characteristic diffraction peaks
of TNTs are all present without an obvious decrease of the relative
peak intensity, which indicates that the growth of 1T-MoS2 does not destroy the crystal structure of TiO2. Additionally,
quite weak diffraction peaks are also observed, which may come from
the immobilized 1T-MoS2.
Figure 1
(a) XRD patterns of prepared 1T-MoS2, TNTs, and 1T-MoS2@TNTs; (b) Raman spectra of
1T-MoS2 and 1T-MoS2@TNTs.
(a) XRD patterns of prepared 1T-MoS2, TNTs, and 1T-MoS2@TNTs; (b) Raman spectra of
1T-MoS2 and 1T-MoS2@TNTs.Raman spectra are obtained to further identify the existence and
the phase characteristics of the prepared 1T-MoS2 and 1T-MoS2@TNTs. As shown in Figure b, the characteristic peaks at 151, 201, 283, and 337
cm–1 are observed, which could be attributed to
the J1, J2, E1g, and J3 of 1T-MoS2, respectively. Moreover, no obvious E2g peak of 2H-MoS2 is observed at 380 cm–1.[11] These results indicate that 1T-MoS2 is obtained and successfully grown and immobilized on TNTs.Furthermore, X-ray photoelectron spectroscopy (XPS) is employed
to analyze the prepared samples, as shown in Figures and S1. As shown
in Figure S1a, all the elements of Mo,
S, Ti, and O are present, suggesting the successful immobilization
of 1T-MoS2 on TNTs. As shown in Figure a, two main deconvoluted peaks are observed
at 227.4 and 230.6 eV on the Mo 3d spectra, which correspond to 3d3/2 and 3d5/2 of Mo4+ species.[17] The other two peaks at the binding energies
of 231.8 and 234.7 eV belong to Mo6+, which may come from
the unreacted MoO3 or the oxidized MoS2 in air.[15] Additionally, two weak peaks at 225.3 and 228.2
eV may belong to Mo3+, which should be derived from the
S vacancy in MoS2 and/or the formed crystal defects.[16] As shown in Figure b, the peaks at 161.8 and 160.5 eV could
be assigned to 2p3/2 and 2p1/2 of S2– from MoS2.[9] The other peaks
at 168.7 and 167.6 eV can be assigned to 2p1/2 and 2p3/2 of S4+ in sulfate groups (SO32–).[18]Figure c shows two peaks at 463.6 and 457.8 eV,
which could be attributed to Ti 2p of 1T-MoS2@TNTs. As
shown in Figure d,
two O 1s peaks at 530.5 and 529.1 eV are present. The first peak corresponds
to the O atom bonded to Ti, and the latter one is ascribed to the
surface hydroxyl species.[19] Compared with
the curves in Figure S1b,c, it could be
seen that both binding energies of Ti 2p and O 1s 1T-MoS2@TNTs are slightly shifted, which indicates the existence of electron
interaction between 1T-MoS2 and TNTs.
Figure 2
XPS spectra of (a) Mo
3d, (b) S 2p, (c) Ti 2p, and (d) O 1s on
1T-MoS2@TNTs.
XPS spectra of (a) Mo
3d, (b) S 2p, (c) Ti 2p, and (d) O 1s on
1T-MoS2@TNTs.Scanning electron microscopy
(SEM) images and energy-dispersive
spectrometry (EDS) mapping images are used to investigate the surface
morphology and elemental distribution of 1T-MoS2@TNTs,
as shown in Figure . As shown in Figure a, TiO2 has an obvious one-dimensional morphology with
diameters of about 10 nm. The existence of MoS2 is identified
by the EDS mapping from an arbitrarily selected area, shown in Figure b–g. As shown,
all the elements including Mo and S are evenly distributed in the
1T-MoS2@TNTs composites. In addition, no aggregated particles
are observed on the surface of TNTs. It indicates that 1T-MoS2 has been successfully grown on the TiO2 surface
with good dispersion.
Figure 3
(a) SEM image of 1T-MoS2@TNTs and (b) SEM images
with
the corresponding elemental mapping images of (c) all elements, (d)
Ti, (e) O, (f) Mo, and (g) S.
(a) SEM image of 1T-MoS2@TNTs and (b) SEM images
with
the corresponding elemental mapping images of (c) all elements, (d)
Ti, (e) O, (f) Mo, and (g) S.Transmission electron microscopy (TEM) and high-resolution TEM
(HRTEM) are applied to investigate the microstructure of the stable
1T-MoS2@TNTs composites, as shown in Figure . Figure a shows that 1T-MoS2@TNTs are completely
composed of nanotubes with a diameter of about 7.5 nm. HRTEM images
are shown in Figure b–d, and a more obvious tubular structure is observed in Figure b. The different
contrast at the tube wall is also present, which might be derived
from the loaded 1T-MoS2. For further understanding, high-resolution
pictures of the circled parts in Figure b are given in Figure c,d. The lattice of the light part is 0.35
nm, which could be assigned to the (101) facet of TiO2.
The tube wall is composed of several-layered TiO2, and
the thickness of each layer is about 0.72 nm. As for Figure d, lattice fringes with a width
of 0.26 nm can be attributed to the (100) facet of MoS2, which is at an angle of 120° from the TiO2 (101)
facet.[20] To get further information about
1T-MoS2 in 1T-MoS2@TNTs, the selected zone in Figure S2a was filtered by fast Fourier transform
filtration to remove the irrelevant noise based on the previous image-processing
procedure.[21] The obtained atomic arrangement
diagram and lattice dislocation are shown in Figure S2b,c, respectively. The characteristic trigonal lattice is
evidently seen in Figure S2a and the hexagonal
atomic arrangement of Mo of MoS2 is seen in Figure S2b, which confirms that the obtained
MoS2 has the 1T phase.[21]Figure S2c shows the lattice fringes in the same
direction with obvious dislocations indicating the presence of defects
in 1T-MoS2, which is in correspondence with the above XPS
results. Additionally, the a and b vectors give a length of 3.15 Å, which indicates that one Mo
atom may be surrounded by six S atoms, as shown in Figure S2d.
Figure 4
(a,b) HRTEM images of the 1T-MoS2@TNTs composite;
(c,d)
enlarged images of the selected zone.
(a,b) HRTEM images of the 1T-MoS2@TNTs composite;
(c,d)
enlarged images of the selected zone.The light response of the obtained samples is analyzed by UV–vis
diffuse reflectance spectroscopy, as shown in Figure a. Compared to TNTs, 1T-MoS2@TNTs
has stronger absorption in the visible region. At the same time, slight
red shifts of the spectrum could be observed for 1T-MoS2@TNTs as shown in Figure S3a, which indicates
that the interaction between 1T-MoS2 and TNTs may influence
the band energy.[20] The band gaps of prepared
photocatalysts are calculated by using the Tauc equation,[9] shown in Figures b and S3b. The band gap
of TNTs is 3.17 eV. However, the band gap of 1T-MoS2@TNTs
is decreased to 3.09 eV. More decreases are observed by further increasing
the contents of 1T-MoS2 and the values are 3.05, 3.03,
and 2.84 eV for 1.0 wt % 1T-MoS2@TNTs, 1.5 wt % 1T-MoS2@TNTs, and 2.0 wt % 1T-MoS2@TNTs (see Figure S3b), respectively. It is speculated that
the narrower band gap may improve the light harvesting, which facilitates
enhanced photocatalytic activity.
Figure 5
(a) UV–vis diffuse reflectance
spectra and (b) band gap
of TNTs and 1T-MoS2@TNTs.
(a) UV–vis diffuse reflectance
spectra and (b) band gap
of TNTs and 1T-MoS2@TNTs.The degradation of tetracycline hydrochloride (TC-HCl) under visible
light is carried out to investigate the photocatalytic performance
of the obtained samples, as shown in Figure a. Pristine 1T-MoS2 and TNTs can
only degrade about 10 and 23% TC-HCl in 1 h, respectively. In contrast,
1T-MoS2@TNTs (0.5 wt %) can degrade 57% TC-HCl under the
same conditions, which is higher than previously reported efficiencies
of 15 and 25%.[9,14] In addition, Figure S4 shows the degradation curves of 1T-MoS2@TNTs with different loaded amounts of 1T-MoS2, where
it is observed that the prepared 0.5 wt % 1T-MoS2@TNTs
exhibits the highest catalytic activity. The pseudo-first-order kinetics
fitting of the photodegradation is given in Figure b. The reaction rate constants k of TC-HCl decomposition are 1.1 × 10–3 and
4.4 × 10–3 min–1 for 1T-MoS2 and TNTs, respectively. Enhanced reaction rates are observed
for 1T-MoS2-loaded photocatalysts, and a maximum of 140
min–1 is achieved for 1T-MoS2@TNTs (0.5
wt %), which is 12.7 and 3.2 times more than those of 1T-MoS2 and TNTs. The full-wavelength absorption spectra of TC-HCl during
degradation on 1T-MoS2@TNTs are shown in Figure S5. The absorption from TC-HCl is clearly observed
and the absorption intensity decreases along with the reaction, indicating
that no other intermediates are formed. Cyclic experiments for TC-HCl
photodegradation have been conducted and the degradation rate is found
to be reduced from 56.2 to 36.8% after four cycles, as shown in Figure S6.
Figure 6
(a) Photocatalytic degradation of TC-HCl
by 1T-MoS2,
TNTs, and 1T-MoS2@TNTs and (b) pseudo-first-order kinetics
fitting of the photodegradation.
(a) Photocatalytic degradation of TC-HCl
by 1T-MoS2,
TNTs, and 1T-MoS2@TNTs and (b) pseudo-first-order kinetics
fitting of the photodegradation.Trapping experiments are performed to figure out the active ingredients
in the photocatalytic process by using 1T-MoS2@TNTs as
the photocatalyst, as shown in Figure . Ethylenediaminetetraacetic acid (EDTA), benzoquinone
(BQ), and tert-butyl alcohol (TBA) are used to scavenge
the holes (h+), superoxide (•O2–) radicals, and hydroxyl (•OH)
radicals, respectively. 10.0 mg of the photocatalyst is used and the
operation is similar to the above photodegradation processes. After
the addition of EDTA, BQ, and TBA, the degradation efficiency is obviously
reduced, which indicates that h+, •O2–, and •OH may be the
active species and responsible for the catalytic reaction.
Figure 7
Photocatalytic
degradation of TC-HCl over 1T-MoS2@TNTs
without and with addition of EDTA, TBA, and BQ.
Photocatalytic
degradation of TC-HCl over 1T-MoS2@TNTs
without and with addition of EDTA, TBA, and BQ.Photocurrent response and electrochemical impedance spectroscopy
(EIS) are employed to analyze the charge transfer in the photocatalytic
process. As shown in Figure a, the 1T-MoS2@TNTs composite has a much stronger
photocurrent than the pristine 1T-MoS2 and TNTs. This indicates
that 1T-MoS2@TNTs photocatalyst has better charge separation
efficiency, which accounts for its higher activity. EIS is used to
further clarify the charge transport on the prepared samples, as shown
in Figure b. 1T-MoS2@TNTs displays a much smaller EIS arc radius than TNTs, which
indicates that the addition of metallic 1T-MoS2 to TNTs
can reduce the resistance of TNTs.[20]
Figure 8
(a) Typical
photocurrent response and (b) EIS spectra of samples
1T-MoS2, TNTs, and 1T-MoS2@TNTs.
(a) Typical
photocurrent response and (b) EIS spectra of samples
1T-MoS2, TNTs, and 1T-MoS2@TNTs.The band structures of TNTs and 1T-MoS2 are obtained
from the Mott–Schottky results in Figure S7, which indicate that they are all n-type semiconductors.[16] Together with the above discussions, a mechanism
is proposed for the photodegradation of TC-HCl on 1T-MoS2@TNTs, as shown in Figure . The potentials of CB and VB of 1T-MoS2 are 0.18
and 1.98 eV, and those of TNTs are −0.4 and 2.8 eV, respectively.
The electrons are excited to the CB of TiO2 under visible-light
irradiation and migrated to the CB of 1T-MoS2 through the
formed interface. Meanwhile, the holes in the VB of TiO2 may transfer to the VB of 1T-MoS2. Consequently, a type
I heterojunction may be formed in the 1T-MoS2@TNTs composite,
which optimizes the photocatalytic activity by improving the charge
separation.[22]
Figure 9
Schematic illustrations
for the photogenerated charge carrier transfer
on 1T-MoS2@TNTs.
Schematic illustrations
for the photogenerated charge carrier transfer
on 1T-MoS2@TNTs.
Conclusions
In summary, 1T-MoS2@TNTs composites have been successfully
constructed by the in situ growth of 1T-MoS2 on the TNTs
using a hydrothermal process, which show enhanced photocatalytic performance
for the degradation of TC-HCl under visible light. The improved photocatalytic
activity is closely related to the loaded amount of 1T-MoS2, and the highest photocatalytic efficiency is observed on 0.5 wt
% 1T-MoS2@TNTs. The introduction of 1T-MoS2 may
optimize light absorption and charge separation/transport. The active
species are identified and a reaction mechanism is proposed. This
work may provide an alternative for the construction of a new photocatalyst
and also a new direction for application of 1T-MoS2 in
the energy and environmental fields.
Materials and Methods
Synthesis
of 1T-MoS2
The preparation of
1T-MoS2 was conducted according to the modified method
from ref (8). Typically,
1.96 mg MoO3, 0.10 g thioacetic acid (TAA), and 0.96 g
urea were dissolved in 80.0 mL of deionized water and stirred magnetically
(with a cylindrical stirring bar, 8 × 35 mm) for 2 h at a speed
of 400 rpm. Then, the solution was sealed in an autoclave and heated
at 200 °C for 12 h. After that, the solution was cooled down
to room temperature, and the solid product was collected and washed
with deionized water several times. The prepared 1T-MoS2 was dispersed in deionized water before further use.
Synthesis of
TNTs
TNTs were prepared using a hydrothermal
method.[23] Typically, 0.96 g of urea and
1.92 g of titanium sulfate were dissolved in 80.0 mL of deionized
water and stirred for 2 h. Then, the solution was transferred into
a reaction vessel and reacted at 220 °C for 12 h to obtain TiO2 powder. The obtained TiO2 powder was added to
100.0 mL of 10.0 mol/L NaOH solution and stirred for 4 h. Then, the
solution was transferred into a Teflon container and heated at 150
°C for 12 h. After washing with a 0.1 mol/L HNO3 aqueous
solution and deionized water, white products were obtained and ground
into powder for further use.
Synthesis of 1T-MoS2@TiO2
400
mg TiO2 powder was added into the mixed solution containing
2.1 mg TAA, 18 mg urea, and 1.8 mg MoO3 and stirred for
2 h. Then, the solution was sealed in an autoclave and heated at 200
°C for 12 h. After that, the solution was cooled down to room
temperature, and the solid product was collected and washed with deionized
water several times. The obtained samples were named as 1T-MoS2@TNTs (the content of 1T-MoS2 is 0.5 wt %). Other
samples with different MoS2 contents were similarly synthesized
by changing the concentrations of MoO3 precursors (Supporting Information).
Characterization
XRD was conducted at a scan rate of
10°/min on a Bruker D2 PHASER with Cu Kα-radiation. XPS
was obtained on the Axis Supra XPS instrument using Al Kα as
the source. SEM was conducted on a FE-SEM S-4800 (Hitachi). TEM was
carried out on the FEI F200S equipment at an accelerating voltage
of 200 kV.
Photoelectrochemical Measurements
Electrochemical testing
was carried out on the CHI 660E electrochemical workstation. 15.0
mg prepared MoS2, TNTs, and 1T-MoS2@TNTs were
separately dissolved in 3 mL of polyvinylidene fluoride solution and
coated on the fluorine-doped tin oxide conducting glass by spin coating
to form an electrode, respectively. A 300 W xenon lamp was used as
the light source for photocurrent testing.
Photocatalytic Performance
The photocatalytic performance
was studied by degrading the TC-HCl solution under visible light as
the model reaction. A 300 W xenon lamp worked as the light source
in the wavelength range of 420–780 nm, and the distance between
the lamp and liquid level was set as 15 cm. 1.0 mg of the photocatalyst
was dispersed in 100.0 mL of 20.0 mg/L TC-HCl solution. The reaction
solution was stirred magnetically at a speed of 200 rpm in the dark
for 1 h to achieve adsorption–desorption equilibrium. The concentration
of TC-HCl was investigated at its maximum adsorption of 356 nm on
the UV 2600 spectrophotometer. The pH values of the solution before
and after the reaction are 4.23 and 4.28, respectively, and not much
difference is observed.
Authors: Mark A Lukowski; Andrew S Daniel; Fei Meng; Audrey Forticaux; Linsen Li; Song Jin Journal: J Am Chem Soc Date: 2013-07-03 Impact factor: 15.419