Wenjuan Li1,2, Robert Liang2, Norman Y Zhou2, Zihe Pan3. 1. College of Art, Taiyuan University of Technology, 209 University Avenue, Jinzhong, Shanxi 030600, China. 2. Department of Mechanical and Mechanics, Waterloo Institute for Nanotechnology, University of Waterloo, 200 University AVE West, Waterloo, ON, Canada N2L 3G1. 3. Institute of Resources and Environmental Engineering, Shanxi University, 92 Wucheng Road, Taiyuan 030006, China.
Abstract
In this work, C-doped TiO2 nanorods were synthesized through doping carbon black into hydrothermally synthesized solid-state TiO2 nanowires (NWs) via calcination. The effects of carbon content on the morphology, phase structure, crystal structure, and photocatalytic property under both UV and solar light by the degradation of methylene blue (MB) were explored. Besides, the photoelectrochemical property of C-TiO2 was systematically studied to illustrate the solar light degradation mechanism. After doping with C, TiO2 NWs were reduced into nanorods and the surface became rough with dispersed particles. Results showed that C has successfully entered the TiO2 lattice, resulting in the lattice distortion, reduction of band gap, and the formation of C-Ti-O, which expands TiO2 to solar light activation. Comparing with P25 and anatase TiO2 NWs, doping with carbon black showed much higher UV light and solar light photocatalytic activity. The photocatalytic activity was characterized via the degradation of MB, showing that K ap was 0.0328 min-1 under solar light, while 0.1634 min-1 under UV irradiation. The main free radicals involved in methylene blue degradation are H+ and OH•-. Doping with carbon black led to the reduction of photocurrent in a long-term operation, while C-doping reduced the electron-hole recombination and enhanced the carrier migration.
In this work, C-doped TiO2nanorods were synthesized through doping carbon black into hydrothermally synthesized solid-state TiO2 nanowires (NWs) via calcination. The effects of carbon content on the morphology, phase structure, crystal structure, and photocatalytic property under both UV and solar light by the degradation of methylene blue (MB) were explored. Besides, the photoelectrochemical property of C-TiO2 was systematically studied to illustrate the solar light degradation mechanism. After doping with C, TiO2 NWs were reduced into nanorods and the surface became rough with dispersed particles. Results showed that C has successfully entered theTiO2 lattice, resulting in the lattice distortion, reduction of band gap, and the formation of C-Ti-O, which expands TiO2 to solar light activation. Comparing with P25 and anatase TiO2 NWs, doping with carbon black showed much higher UV light and solar light photocatalytic activity. The photocatalytic activity was characterized via the degradation of MB, showing that K ap was 0.0328 min-1 under solar light, while 0.1634 min-1 under UV irradiation. The main free radicals involved in methylene blue degradation are H+ and OH•-. Doping with carbon black led to the reduction of photocurrent in a long-term operation, while C-doping reduced the electron-hole recombination and enhanced the carrier migration.
Titanium
dioxide (TiO2) possesses outstanding photocatalytic
activity,[1] which has been extensively used
in wastewater purification,[2−5] water splitting,[6−8] volatile organic compound
degradation,[9] CO2 reduction,[10,11] etc. Nevertheless, TiO2 can only be activated by ultraviolet
light (UV, 5–9% in solar light) due to its large band gap (3.0–3.2
eV)[12] and fast recombination rate while
most of the solar light is wasted.[13] To
efficiently utilize the light energy, expanding the photoexcitation
spectra of TiO2 to solar light is more desirable. A series
of techniques have been developed to expand TiO2 to be
active under solar light (or visible light) through grafting (polymers
or nanoparticles),[14,15] doping,[16−18] coating,[19] etc. Among of these methods, doping is extensively
used to extend TiO2 to the visible light spectrum by narrowing
the band gap, separating photoelectrons, and reducing the recombination
rate of valance hole.[17,18]A variety of materials
including transition metals and nonmetal
elements (e.g., C,[20−23] N,[24] S,[25] B,[26] I,[27] etc.) have been
doped into TiO2 to achieve solar light activation.[28,29] However, doping with metal elements may cause poor thermal stability[30] and an increment of recombination centers due
to aggregation and larger particle size.[30,31] The critically thin doping (10–20 nm) layer at the interface
fails to act as both electron and hole traps under thermal treatment.[31] In comparison, doping with nonmetal elements
might generate the impurity band gap[32] and
create an overlap between the intrinsic band gap,[33] thereby expanding TiO2 to visible light activation.
Asahi et al.[34] first reported that visible
light excitation of TiO2could be achieved by N-doping.
N enters theTiO2 lattice and replaces O, resulting in
the formation of crystal defects, and the N 2p doping level overlaps
with O 2p, which narrows the band gap, thereby switching TiO2 into visible light activation.[35,36] Since then,
a variety of nonmetal-doped TiO2 photocatalysts have been
developed. Sakthivel et al.[37] compared
the visible light degradation efficiency of 4-chlorophenol, showing
that C-doped TiO2 was 5 times more active than N-dopedTiO2. Carbon is widely used as a doping agent due to its
large electron storage capacity, capability of absorbing visible light
in a wide range (400–800 nm), high efficiency in separating
photogenerated carriers, stabilization on the anatase phase, and conductivity
improvement.[38−41] Besides, C enters the lattice and generates a C–Ti–O
bond and forms a hybrid orbital above the valance band, and enhances
visible light adsorption of TiO2.[42,43] Zainullina et al.[44] reported that doping
with C resulted in visible excitation due to the formation of Ti 3d-C
2p-O 2p hybrid orbital states transition from the valance band to
the impurity band. Dong and co-workers[45] mixed Ti(SO4)2 and C12H22O11 with water to synthesize C-doped mesoporousTiO2 with visible light photocatalytic activity via hydrothermal
treatment. Colombo et al.[46] reported the
fabrication of C-doped TiO2 nanoparticles with visible
light activity by decreasing the recombination rate of electron/holes
through sol–gel doping glucose into TiO2. Wang et
al.[47] utilized benzoic acidas a carbon
source for doping into platelike TiO2, resulting in a lattice
expansion, thereby improving the visible light photocatalytic activity.
Wu et al.[48] synthesized carbon-dopedTiO2 nanoparticles through the hydrothermal reaction between titanium
tetra-n-butoxide and ethanol obtaining visible light
activity. Though carbon-dopedTiO2 has been synthesized
from sol–gel or hydrothermal reactions between organic carbon
and tetrabutyl orthotitanate or titanium compounds, introducing the
C atom into theTiO2 lattice to obtain uniformly doped
TiO2 and stable catalysts still remains a challenge. Especially,
doping carbon particles into the solid-state TiO2 powder
is difficult.To dope element C into TiO2, several
methods have been
reported, e.g., doping carbon into Ti in an oxygen atmosphere,[49] TiC oxidation.[50,51] Shen et al.[49] oxidized TiC powder in an air atmosphere at
different temperatures expanding TiO2 to visible light
irradiation. Varnagiris et al.[50] synthesized
carbon black-doped TiO2 (with the mixed-phase composition
of anatase and rutile) through magnetron sputtering, where thecarbon
powder wasplaced on theTi cathode and sputtered under DC current
in an oxygen atmosphere. The sputtering time was varied, and different
amounts of C were doped into TiO2. The highest degradation
rate constant under visible light irradiation of methylene blue was
1.14 × 10–3 min–1 after being
sputtered for 180 min. Nevertheless, the doping content of thecarbon
powder in TiO2 is difficult to precisely control. Besides,
the effects of doping content of carbon powder on the phase behavior,
crystal structure, and morphology are rarely reported.In this
work, C-doped TiO2nanorods were synthesized
through doping carbon black into hydrothermally synthesized solid-state
TiO2 nanowires (NWs) via calcination. The effects of carbon
content on the morphology, phase structure, crystal structure, and
the photocatalytic property under both UV and solar light by the degradation
of methylene blue (MB) were explored. Besides, the photoelectrochemical
property of C-TiO2 was systematically studied to illustrate
the solar light degradation mechanism. The photocatalytic activity
of varied amounts of carbon black-doped TiO2 nanorods was
compared to those of P25 and anatase TiO2 NWs, indicating
that doping with carbon black resulted in much higher UV light and
solar light photocatalytic activity via the degradation of MB. The
generated free radicals and the dominant free radicals on MB degradation
were also characterized. Results showed that C-doping into TiO2 leads to the lattice distortion and the formation of O–Ti–C
bond and reduces the band gap, thereby extending TiO2 to
the solar light activation region.
Results
and Discussion
The alkali hydrothermal method[52] was
utilized to synthesize TiO2 NWs and carbon black-doped
TiO2 (C-TiO2) nanorods from commercial TiO2 (P25). A certain amount of P25 was well dispersed into 10
M NaOH and hydrothermally treated at 260 °C for 24 h in a Teflon
autoclave (Figure ). The obtained intermediate was washed with 0.1 M HCl and DI water
to remove Na+ and adjust the pH to around 7. Then, it was
dried completely at 80 °C and heat-treated in an airtight tube
furnace to obtain TiO2 NWs under 700 °C for 2 h. Theas-prepared TiO2 NWs were mixed with a certain amount of
carbon black and thenheat-treated at 700 °C for 2 h in a N2-filled airtight tube furnace to obtain C-doped TiO2 nanorods (Figure ).
Figure 1
Schematic Illustration of the Fabrication Process of C-Doped TiO2.
Scheman class="Chemical">tic Illustration of the Fabrication Process of C-Doped TiO2.
Since P25 is composed of 20% rutile
and 80% anatase, the phase
composition of carbon black-doped TiO2 nanorods was investigated
via XRD. As shown in Figure a, only anatase was detected after doping with carbon black,
and increasing the doping content of carbon black does not lead to
peak shifting. The characteristic peaks of anatase were observed at
2θ values of 25.26, 36.88, 48.04, 53.80, 55.00, 62.62, 68.76,
70.32, and 75.04°, which correspond to (101), (004), (200), (105),
(211), (204), (116), (200), and (215). The relatively strong intensity
of these peaks indicates the good crystallinity of C-doped TiO2, and the increment of the doping content of C generated a
negligible effect on the phase structure of TiO2. Further
characterization was performed by calculating the crystallite size.
The crystallite size of TiO2 nanowires—(0.2% C)-TiO2, (0.5% C)-TiO2 and (1.0% C)-TiO2—was
calculated at 31.92 nm, 31.66 nm, 33.21 nm and 30.48 nm, respectively.
This result illustrates the negligible effects of carbon content on
the crystallite size of TiO2.
Figure 2
(a) XRD analysis of C-TiO2 nanorods at varied carbon
doping contents. (b) Raman shift of TiO2 NWs and C-doped
TiO2 nanorods at different doping contents.
(a) XRD analysis of C-TiO2 nanorods at varied n class="Chemical">carbon
doping contents. (b) Raman shift of TiO2 NWs and C-doped
TiO2 nanorods at different doping contents.
Figure b
shows
the Raman spectra of TiO2 NWs and C-doped TiO2 nanorods showing that doping with C caused obvious peak shifting
and widening (Figure b). Comparing with TiO2 NWs, significant peak shifting
was observed at 135, 488, and 605 cm–1 after doping
with carbon black. Furthermore, the peak shifting became more obvious
with the increment of C-doping content (Figure b). In detail, at the peak shift of 135 cm–1, the peaks after C-doping shifted to the right at
137, 139, and 142 cm–1 corresponding to (0.2% C)-TiO2, (0.5% C)-TiO2, and (1.0% C)-TiO2 (Figure b inset (1)). However,
the peaks shift to the left at 488 and 605 cm–1 (Figure b inset (2)) after
C-doping. The 488 peak shifts to 487, 486, and 482 cm–1, while the peak of 605 cm–1 shifts to 604, 602,
and 600 cm–1 after doping with 0.2, 0.5, and 1.0%
C correspondingly (Figure b inset (2)). Moreover, the peak shifts at 135, 488, and 605
cm–1 became wider with the increment of the doping
content of carbon black (Figure b insets). These results illustrate that doping with
carbon black induced the generation of defects or impure states, and
this phenomenon becomes more apparent with the increasing doping content
of carbon black.[53,54] Furthermore, the intensity of
these peaks is much stronger than that of TiO2 NWs (Figure b insets), indicating
the good crystallization of TiO2 nanorods after doping
with carbon black.[54]The morphology
of as-prepared specimens was characterized by scanning
electron microscopy (SEM) (Figure ). TheTiO2 NWs synthesized by the hydrothermal
reaction are relatively smooth with width and length of 200 nm and
several millimeters, respectively (Figure a,b). However, notable changes have been
observed from the SEM that the long nanowires were turned into short
nanorods after doping with carbon black (Figure c–e). Furthermore, the surface of
C-doped TiO2 nanorods became rough and dispersed with many
nanoparticles (Figure c–e). This phenomenon became more significant with the increment
of C-doping content. The composition of these dispersed nanoparticles
on (1.0% C)-TiO2 nanorods was analyzed by energy-dispersive
X-ray spectroscopy (EDX), which shows that the main composition included
C, Ti, and O (Figure f). Moreover, the content of C in C-doped TiO2 increased
with the increment of the doping load of carbon black (Figure S1). A continuous increase in the doping
load of C (2.0 and 3.0 wt %) caused a significant reduction of theaspect ratio of TiO2 nanorods, and more particles were
observed on the surface of TiO2 (Figure S2). The result shows the significant effects of carbon black
on the morphology change after doping.
Figure 3
Morphology of the as-prepared
TiO2 NWs and C-doped TiO2 through SEM characterization:
(a, b) TiO2 NWs,
(c) (0.2% C)-TiO2, (d) (0.5% C)-TiO2, (e) (1.0%
C)-TiO2, and (f) EDS analysis of (1.0% C)-TiO2.
Morphology of then class="Chemical">as-prepared
TiO2 NWs and C-doped TiO2 through SEM characterization:
(a, b) TiO2 NWs,
(c) (0.2% C)-TiO2, (d) (0.5% C)-TiO2, (e) (1.0%
C)-TiO2, and (f) EDS analysis of (1.0% C)-TiO2.
To further investigate the surface
structure of carbon black-doped
TiO2 nanorods, transmission electron microscopy (TEM) was
used to analyze the surface morphology and the results are compared
to the original TiO2 nanorods, which shows that the original
TiO2 is smooth and well crystallized (Figure a,b) while there are many nanoparticles
dispersed on the surface (Figure c,d). Some of thecarbon black nanoparticles coated
onto TiO2 nanorods (Figure c, yellow square) form a thin layer (around 7 nm) at
the interface, which can act as electron acceptors to separate electron
and holes and protect Ti3+ from oxidation.[23] The high-resolution image of the selected square in Figure c shows that there
is a disconnected area (Figure d) that might be formed by the doping of carbon black. Similarly,
at the edge of TiO2 nanorods (Figure e, selected area), the crystal faces were
not well aligned, showing a slight distortion (Figure f) due to the doped carbon black.
Figure 4
(a, b) TEM
images of original TiO2 nanorod. TEM image
of (0.5% C)-TiO2 nanorods: (c) carbon black coated onto
TiO2 nanorods, and (d) carbon black forming a thin layer
on the surface of TiO2 nanorod, and (e, f) the edge of
TiO2 nanorod is not well aligned after doping with C.
(a, b) TEM
images of original TiO2 nanorod. TEM image
of (0.5% C)-n class="Chemical">TiO2 nanorods: (c) carbon black coated onto
TiO2 nanorods, and (d) carbon black forming a thin layer
on the surface of TiO2 nanorod, and (e, f) the edge of
TiO2 nanorod is not well aligned after doping with C.
The effects of C loading on the chemical composition
of C-doped
TiO2 nanorods were analyzed via X-ray photoelectron spectroscopy
(XPS), which shows that a O–Ti–C bond was formed after
doping with 0.2% carbon black and that the intensity of the O–Ti–C
bond becomes stronger with the increment of the doping amount of C
(Figure a–c).
The content of C=C and C=O decreased with doping more
C, while the content of C–O increased with doping more C (Figure a–c and Table ). The atomic percentages
of O–Ti–C (283.0 eV), C=C (284.6 eV), C–O
(286.1 eV), and C=O (288.4 eV) are 9.95, 44.45, 33.91, and
11.69% in 0.5% C-TiO2 (Table ). In comparison, the intensity of O–Ti–C
in (1.0% C)-TiO2 (10.72%) is higher than that of the O–Ti–C
bond in (0.2% C)-TiO2 (5.76%). Interestingly, the intensities
of the C–O bonds in (0.5% C)-TiO2 (33.91%) are the
strongest (Table ).
It can be concluded that carbon black and N2 provided a
reduction atmosphere, which enhances the doping of C into theTiO2 lattice. Figure d–f illustrates the effects of C dosage on the O 1s,
showing that the content of the lattice O-ion state (O2–) at 529.5 eV and defects of O* at 531.6 eV increase with the increment
of doping loading of C (from 0.2 to 1.0%). Results showed that the
generation of theoxygen defects and oxygen vacancies (O*) lowers
the energy band through doping C in TiO2 NWs. The intensity
of the lattice O– in (1.0% C)-TiO2 is
much higher than that of (0.2% C)-TiO2, indicating that
doping more C enhances the generation of lattice O2–. Lattice oxygen vacancies can be used as an effective transfer medium
and electron acceptor, which can efficiently suppress the electrons
and holes in the compound, promoting the catalytic process. The XPS
results confirmed that carbon black doped into TiO2 nanorods
via the C atom entering the lattice and the formation of the C–Ti–O
bond at the interface of carbon black and TiO2 nanorods,
which showed negligible effects of Ti 2p (Figure S3).
Figure 5
Chemical states of C 1s and O 1s at varied carbon addition: (a)–(c)
C 1s of (0.2% C)-TiO2 nanorods, (0.5% C)-TiO2 nanorods, and (1.0% C)-TiO2 nanorods, respectively. (d)–(f)
O 1s of (0.2% C)-TiO2 nanorods, (0.5% C)-TiO2 nanorods, and (1.0% C)-TiO2 nanorods, respectively.
Table 1
Atomic Percent (%) of Different C
1s Chemical States of As-Prepared Samples
sample
(0.2% C)-TiO2
(0.5% C)-TiO2
(1.0% C)-TiO2
C 1s (C=C)
66.14
44.45
66.92
C 1s (C–O)
15.82
33.91
16.24
C 1s (C=O)
12.28
11.69
11.11
C 1s (O–Ti–C)
5.76
9.95
10.72
Chemical states of C 1s and O 1s at varied n class="Chemical">carbon addition: (a)–(c)
C 1s of (0.2% C)-TiO2 nanorods, (0.5% C)-TiO2 nanorods, and (1.0% C)-TiO2 nanorods, respectively. (d)–(f)
O 1s of (0.2% C)-TiO2 nanorods, (0.5% C)-TiO2 nanorods, and (1.0% C)-TiO2 nanorods, respectively.
The effects of C-doping content on the photocatalytic
activity
were characterized under UV and solar light via UV-DRS (Figure ). A relatively strong absorption
peak in UV spectral range (380–400 nm) and certain visible
light absorption in the visible light range (more than 400 nm) are
observed in C-doped TiO2 nanorods (Figure a). The absorption intensity of C-doped TiO2 nanorods increases with the increasing of the doping content
of C under solar light. According to the turning point in these curves,
a blueshift is observed, indicating the generation of electron–hole
pairs and the stronger ability of photocatalytic oxidation in C-doped
TiO2 nanorods. In comparison, theTiO2 NWs show
a weak UV light adsorption peak and a lower solar light adsorption
intensity (Figure a). The band gap of TiO2 NWs and C-doped TiO2 nanorods decreased with increasing doping amount of C. The band
energy (Figure b)
of doped samples was narrowed to 2.40–3.20 eV (Table S1 and Figure S4). This might be attributed
to the doping of the C atom in theTiO2 lattice and the
replacement of the O atoms, which narrow the band gap of TiO2.
Figure 6
Diffuse reflectance spectra of TiO2 NWs and C-doped
TiO2 nanorods between 200 and 600 nm (a) and the corresponding
band energy (b).
Diffuse reflectance spectra of TiO2 NWs and C-doped
TiO2 nanorods between 200 and 600 nm (a) and the corresponding
band energy (b).The photocatalytic property
of TiO2 NWs and C-doped
TiO2 nanorods is evaluated via the degradation of MB in
terms of ln(C0/C) and Kap under UV light and solar light irradiation,
respectively (Figures and S5). The photocatalytic degradation
efficiency of C-doped TiO2 nanorods increases notably with
the increment of C-doping content under UV light, and theKap value reaches to as high as 0.1634 min–1 (Figure a) and theMB solution turned transparent after degradation
for 15 min (Figure a, top right). The effect of C on enhancing the solar light photocatalytic
performance of C-TiO2 was also investigated. TheKap value of TiO2 NWs is 0.0112 cm–1 (Figure b), and theMB solution remained blue after degradation of
120 min (Figure b,
bottom right). Compared to TiO2 NWs, the highest Kap (0.0328 cm–1) was achieved
after doping 1.0% C (Figure b), showing the vital role of C in enhancing the solar light
photocatalytic activity. Furthermore, MB was quickly decomposed within
30 min under solar light using (1.0% C-TiO2) (Figure b, top right).
Figure 7
Photocatalytic
activities of TiO2 NWs and C-doped TiO2 nanorods
under (a) UV light and (b) solar light.
Photocatalytic
acn class="Chemical">tivities of TiO2 NWs and C-doped TiO2 nanorods
under (a) UV light and (b) solar light.
To verify the active species participating in MB photodegradation,
several charge-trapping agents were utilized to capture specific radical
species. It is well known that photoinduced charges, i.e., photoinduced
h+ and photoinduced e–, are generated
through the photoexcitation of TiO2. The photoinduced e– can react with the surface-absorbed O2 and
transform into intermediate species of superoxide radical anionsO2–, or recombine with photoinduced h+. The photoinduced h+ can participate in the degradation
or react with H2O/OH– producing active
hydroxyl radicals OH•. In this work, AgNO3, n-butyalcohol, and (NH4)2C2O4 were used as e–, OH–, and h+ scavengers, respectively. (0.5% C)-TiO2 nanorods
were used as a model to illustrate the generated active species and
were irradiated under 365 nm UV irradiation for 60 min following the
same procedure of C-TiO2 photodegradation of MB.As shown in Figure a, the degradation rate (D%) of 0.03 mM MB was 94.5%
(black), 95.9% with e– trapping agent (AgNO3), 21.2% with OH– trapping agent (n-butyalcohol), 15.8% with h+ trapping agent
((NH4)2C2O4), and 5.3%
with OH– + h+ trapping agents after UV
radiation for 40 min. The photoinduced e– was transformed
to O2– and then reacted with H2O generating H2O2, thereby producing OH– with the addition of trapping agent n-butyalcohol OH•. However, the remaining h+ may still act as active species (Figures a-(2), 21.2%). After adding (NH4)2C2O4 to trap h+, the
generation of OH– originated from photoinduced h+ was largely restricted, while the remaining OH– or O2– (produced by photoinduced e–) decomposed 15.8% MB, verifying that OH– or O2– may also act as active species.
With both OH– + h+ trapping agents added
in the solution, a slight degradation (5.3%) was observed, verifying
that the intermediate species of O2– was
not the main reaction species. The contribution rates of all species
are listed in Table S2. Figure b shows the digital image of
the degraded MB solution with varied scavengers at different degradation
times (0, 10, 20, 30, 40, 50, 60 min). The results verified that the
main free radicals in our study were OH– and the
photoinduced h+, which also play an important role in the
photodecomposition of MB.
Figure 8
(a) Photocatalytic activities of (0.5%C)-TiO2 under
UV light for 40 min with AgNO3, n-butyalcohol,
(NH4)2C2O4, and n-butylalcohol + (NH4)2C2O4 as charge-trapping agents and (b) the corresponding
degradation process in (a).
(a) Photocatalytic acn class="Chemical">tivities of (0.5%C)-TiO2 under
UV light for 40 min with AgNO3, n-butyalcohol,
(NH4)2C2O4, and n-butylalcohol + (NH4)2C2O4as charge-trapping agents and (b) the corresponding
degradation process in (a).
The photocurrent of the samples under UV irradiation was characterized
by performing six on–off cycles[55] with a duration of 120 s (Figure a). The average stable photocurrent of nanowire series
samples was close to each other and much lower than that of P25. P25
exhibited the highest photocurrent (8.0 μA/cm2) in
the first 20 s, which then dropped and remained at 3.4 μA/cm2 with increasing operation time, while the photocurrents of
TiO2 NWs and varied C-doped TiO2 were 6.0 μA/cm2 (TiO2 NWs), 7.2 μA/cm2 (0.2%
C), 7.2 μA/cm2 (0.5% C), and 6.4 μA/cm2 (1.0% C), which then decreased and remained stable at 0.67,
0.3, 0.8, and 0.9 μA/cm2, respectively. This result
illustrates that the instantaneous photocurrents in the first 20 s
of TiO2 NWs and C-TiO2 were close to that of
P25, while the long-term photocurrent of C-TiO2 dropped
sharply (Figure a).
The long-term photocurrent of C-TiO2 was restricted by
the doping of carbon black, implying the low transmission speed of
photocurrent in the long-term operation.
Figure 9
Photoelectric properties
of P25, TiO2 NWs, and C-doped
TiO2 nanorods: (a) photocurrent spectra, (b) EIS Nyquist
spectra, and (c) PL spectra.
Photoelectric properties
of n class="Gene">P25, TiO2 NWs, and C-doped
TiO2 nanorods: (a) photocurrent spectra, (b) EIS Nyquist
spectra, and (c) PL spectra.
Electrochemical impedance spectroscopy (EIS) is one of the most
powerful tools for studying the electrochemical processes occurring
at the electrode/electrolyte interface (medium-frequency region, MFR,
104–102).[56] The radius of AC impedance represents the resistance of carrier
migration (1/2Rct) and reveals the transportation
of charge carriers. Generally, a larger AC impedance radius stands
for the higher resistance of the charge carrier migration. The EIS
Nyquist spectra in Figure b show that the catalysts of C-doped TiO2 had a
lower Rct than those of P25 and TiO2 NWs, indicating the rapid electron transport of electron–hole
pairs through the electrode reaction. According to the EDX and XPS
results, the generated defects and the coated carbon black nanoparticle
(oxycarbides, C–O bond) might contribute to the decrease of
the charge transfer resistance. Although theas-prepared TiO2 NWs showed a lower generation of electron–hole pairs (Figure a), C-doping reduced
the resistance of carrier migration and enhanced the transport of
electron–hole pairs.Photoluminescence (PL) spectra were
measured to approximately characterize
the recombination rate of photoinduced charges; a higher PL intensity
normally indicates a higher carrier recombination. As shown in Figure c, the high intensity
in P25 verified the high recombination rate of photoinduced carriers,
which was in accordance with the results of photocurrent in Figure a. The intensity
was largely reduced in TiO2 NWs and C-TiO2 (0.2,
0.5, 1.0%). The lower PL intensity of C-doped samples revealed an
efficient separation of charge carriers. Though doping with carbon
black led to the reduction of photocurrent in the long-term operation,
C-doping reduced the electron–hole recombination and enhanced
the carrier migration.
Conclusions
In
summary, solar light-activated TiO2 nanorods were
fabricated by doping carbon black into solid-state TiO2 NWs under thermal heating treatment. The effects of doping content
on the surface morphology, crystal structure, photocatalytic activity
under both UV and solar light, and photoelectrochemical property were
systematically studied. Results showed that doping with C caused peak
shifting and widening, and this phenomenon became more apparent with
increasing doping loading of C. The doping of C also caused the transfer
of TiO2 NWs into short nanorods, and theaspect ratio decreased
with the increment of the doping content of C. The chemical composition
of TiO2 after doping with C showed that C entered the crystal
lattice and alternated O to generate O–Ti–C and oxygen
vacancies. The photocatalytic activities of doped TiO2 were
investigated under full-spectra solar light and UV light by degrading
methylene blue. Comparing with P25 and TiO2 NWs, UV and
solar light photocatalytic activity can be enhanced through C-doping,
and the degradation efficiency of MB under solar light reached as
high as 0.0328 min–1 in (1.0% C)-TiO2. Charge scavenger tests indicated that the major active species
were OH– and photogenerated holes during the photodegradation
of methylene blue. The EIS Nyquist spectra confirmed a faster surface
charge charier transport, and thePL spectra demonstrated an efficient
charge carrier separation in C-doped TiO2 catalysts, which
contributed to the enhancement of UV and solar light photocatalysis.
Experimental Section
Chemicals
Commercial
P25 (Evonik,
composites of rutile and anatase), NaOH (Sigma-Aldrich), N2 (99.9%), carbon black (99.95%, Sigma-Aldrich), deionized water (DI
water, supplied by the lab), HCl (20 wt %, Chemistore University of
Waterloo), and methylene blue (MB, Sigma-Aldrich).
Synthesis of Materials
Synthesis of TiO2 Nanowires
(TiO2 NWs)
Commercial P25 was employed as the
initial raw material to prepare TiO2 nanowires, which were
synthesized in an alkali hydrothermal solution. Typically, 2.0 g of
P25 powder was completely dispersed in a 10 M NaOH solution, followed
by magnetic stirring for 1 h. Then, it was put into a Teflon autoclave
and reacted under 260 °C for 24 h. The precursor was collected
by centrifugation after the complete reaction and washed with DI water
and 0.1 M HCl solution for complete ion exchange. After that, theas-prepared product wasplaced in an oven to dry completely at 80
°C. The dried powder was then put in a ceramic crucible and thermally
treated in a muffle furnace under 700 °C for 2 h to obtain the
anatase TiO2 nanowires, which were denoted asTiO2 NWs.
Synthesis of Carbon Black-Doped TiO2 (C-TiO2) Nanorods
Theas-prepared TiO2 NWs were used as a titanium source and carbon black (99.95%,
Sigma-Aldrich) was used as a C source (the weight ratios between carbon
black and TiO2 NWs are 0, 0.2, 0.5, and 1.0%). The obtained
specimens were labeled asTiO2 NWs, (0.2% C)-TiO2, (0.5% C)-TiO2, and (1.0% C)-TiO2. In a typical
experiment, carbon black nanoparticles and theas-prepared TiO2 NWs were mixed homogeneously in anhydrous ethanol with magnetic
stirring. After drying at 80 °C for 12 h, the mixture was transferred
into an airtight tube furnace and thermally treated at 700 °C
for 2 h under a nitrogen (N2, 99.9%) atmosphere.
Characterization
The phase composition
and crystal behavior of TiO2 NWs and C-TiO2 nanorods
were characterized by X-ray diffraction (XRD, Bruker D8 FOCUS) and
Raman spectroscopy (Raman, equipped with a He–Ne ion laser
at 633 nm, Renishaw, U.K.). The microstructure of the synthesized
samples was characterized by field emission scanning electron microscopy
(SEM, LEO-Ultra, Gemini, Germany). The surface chemical composition
of these specimens was characterized using X-ray photoelectron spectroscopy
(XPS, Thermo VG Scientific ESCALAB 250, Al Kα radiation, 5 ×
10–9 mbar of chamber vacuum, 0.2 mA of emission
current) equipped with a hemispherical analyzer (150 nm in radius).
The surface composition of these as-prepared specimens was calibrated
according to the standard C 1s at a fixed binding energy of 284.6
eV before fitting into the point peak software (CasaXPS). The optical
property and band gap energy of the prepared samples were measured
by an ultraviolet–visible diffuse reflection spectroscope (UV-DRS,
UV-2501PC, Shimadzu, Japan, 200–800 nm) with solid BaTiO3 as a reference. The photoelectric properties of the specimens
were characterized by an Autolab Electrochemical workstation (Nova2.1.1
software, Metrohm, China). EIS was measured by a three-electrode system,
glassy carbon electrode was selected as a counter electrode, saturated
calomel electrode as a reference electrode, stainless steel mesh (10
μm) as the base of the working electrode, a 1.0 M KOH solution
as an electrolyte, and the light source was a 300 W xenon lamp (PLS–SXE300/300UV,
PerfectLight, Beijing).[57,58] During the test of
AC impedance, the frequency range and amplitude were set at 100–10
MHz and 0.01 V, respectively. ThePL spectra were measured by a steady/transient
fluorescence spectrometer (FLS 980-STM, Edinburgh, U.K.), and the
excitation wavelength was set at 250 nm.
Photocatalytic
Performance Characterization
The photocatalytic property
of TiO2 NWs and C-TiO2 nanorods was evaluated
by the degradation of methylene blue
(MB, Sigma-Aldrich) solution under UV light and solar light. Before
adding TiO2 and C-doped TiO2 into the methylene
blue solution, a photolysis experiment was carried out to verify if
methylene blue can be degraded by solar light or UV light. The result
showed that methylene blue cannot be degraded by UV and solar light
(Figure S6). Then, TiO2 photocatalysts
were added into themethylene blue solution. In a typical test, 20
mg of TiO2 NWs and C-TiO2 nanorods were dispersed
into 50 mL of a 0.03 mM MB solution, respectively. Adsorption equilibrium
was obtained before illumination under magnetic stirring for 1 h in
a dark environment. After 1 h adsorption in the dark environment,
the adsorption reached the equilibrium state because the adsorption
lines overlapped at varied adsorption time (Figure S7). Photocatalytic degradation was carried out under the irradiation
of a UV lamp (Philips, the Netherlands, 400 W, 365 nm) or a xenon
lamp (Newport, 4.4 W/m2,150 W). In a typical degradation
experiment, 5 mL aliquots were taken out (the left solution was vigorously
stirred to maintain the homogeneous dispersion of the nanorods) using
a pipette at specific time points of 0, 10, 20, 30, 40, 50, 60, 80,
100, and 120 min to characterize the degradation rate of MB by UV–Vis
spectroscopy (UV-2501PC, Shimadzu, Japan) between 800 and 200 nm.The photoactivity of C-TiO2 nanorods was quantitatively
evaluated by calculating the apparent reaction rate constant (Kap) via the pseudo-first-order kinetic reactionwhere c0 and c are the original and final concentrations
of theMB solution,
respectively, and t stands for the relative irradiation
time. The generated active species were characterized using different
types of scavengers. In this work, AgNO3, n-butyalcohol, and (NH4)2C2O4 were used as e– scavenger, OH– scavenger, and h+ scavenger, respectively, during the
degradation of 0.03 mM MB under UV light irradiation.