L Cano-Casanova1, A Ansón-Casaos2, J Hernández-Ferrer2, A M Benito2, W K Maser2, N Garro3, M A Lillo-Ródenas1, M C Román-Martínez1. 1. Grupo Materiales Carbonosos y Medio Ambiente, Departamento de Química Inorgánica e Instituto Universitario de Materiales (IUMA), Facultad de Ciencias, Universidad de Alicante, Ap.99, E-03080 Alicante, Spain. 2. Instituto de Carboquímica, ICB-CSIC, Miguel Luesma Castán 4, 50018 Zaragoza, Spain. 3. Institut de Ciència dels Materials (ICMUV), Universitat de València, 46980 Paterna, València, Spain.
Abstract
A series of nanostructured boron-TiO2 photocatalysts (B-X-TiO2-T) were prepared by sol-gel synthesis using titanium tetraisopropoxide and boric acid. The effects of the synthesis variables, boric acid amount (X) and crystallization temperature (T), on structural and electronic properties and on the photocatalytic performance for propene oxidation, are studied. This reaction accounts for the remediation of pollution caused by volatile organic compounds, and it is carried out at low concentrations, a case in which efficient removal techniques are difficult and costly to implement. The presence of boric acid during the TiO2 synthesis hinders the development of rutile without affecting the textural properties. X-ray photoelectron spectroscopy analysis reveals the interstitial incorporation of boron into the surface lattice of the TiO2 nanostructure, while segregation of B2O3 occurs in samples with high boron loading, also confirmed by X-ray diffraction. The best-performing photocatalysts are those with the lowest boron loading. Their high activity, outperforming the equivalent sample without boron, can be attributed to a high anatase and surface hydroxyl group content and efficient photo-charge separation (photoelectrochemical characterization, PEC), which can explain the suppression of visible photoluminescence (PL). Crystallization at 450 °C renders the most active sample, likely due to the development of a pure anatase structure with a large surface boron enrichment. A shift in the wavelength-dependent activity profile (PEC data) and the lowest electron-hole recombination rate (PL data) are also observed for this sample.
A series of nanostructured boron-TiO2 photocatalysts (B-X-TiO2-T) were prepared by sol-gel synthesis using titanium tetraisopropoxide and boric acid. The effects of the synthesis variables, boric acid amount (X) and crystallization temperature (T), on structural and electronic properties and on the photocatalytic performance for propene oxidation, are studied. This reaction accounts for the remediation of pollution caused by volatile organic compounds, and it is carried out at low concentrations, a case in which efficient removal techniques are difficult and costly to implement. The presence of boric acid during the TiO2 synthesis hinders the development of rutile without affecting the textural properties. X-ray photoelectron spectroscopy analysis reveals the interstitial incorporation of boron into the surface lattice of the TiO2 nanostructure, while segregation of B2O3 occurs in samples with high boron loading, also confirmed by X-ray diffraction. The best-performing photocatalysts are those with the lowest boron loading. Their high activity, outperforming the equivalent sample without boron, can be attributed to a high anatase and surface hydroxyl group content and efficient photo-charge separation (photoelectrochemical characterization, PEC), which can explain the suppression of visible photoluminescence (PL). Crystallization at 450 °C renders the most active sample, likely due to the development of a pure anatase structure with a large surface boron enrichment. A shift in the wavelength-dependent activity profile (PEC data) and the lowest electron-hole recombination rate (PL data) are also observed for this sample.
Environmental legislation
drives increasing emphasis on removing
toxic organic pollutants, like volatile organic compounds (VOCs),
from air.[1] Among VOCs, propene is one of
the main components of tobacco smoke, and it is present in vehicle
emissions and exhaust gases from several industries (petrochemicals,
foundry processes, etc.).[2,3] It has important harmful
effects on human health, even at low concentrations. Photocatalysis
has shown to be one of the most suitable techniques to successfully
degrade organic pollutants both in the gas and the liquid phase (leading
to its complete mineralization).[4−6]Titanium dioxide (TiO2) is considered an excellent and
widely used photocatalyst, with outstanding properties like high stability,
resistance to corrosive media, good biocompatibility, and relatively
low cost due to the abundance of titanium on the earth crust.[7−11] These properties and issues confer to TiO2 advantages
over other semiconductors like ZnO, CeO2, CdS, ZnS, and
so forth.[12,13] However, its photocatalytic efficiency is
hindered by the fast recombination of photogenerated holes and electrons
and its relatively wide band gap (3.2 eV) that limits its activity
to the near-UV region[14] and, thus, only
about 5% of solar irradiation can be used.[15,16] Many research studies have focused on combining TiO2 with
other elements or compounds with the purpose of increasing the TiO2 efficiency.[17,18]Recently, boron incorporation
into nanostructured TiO2 has been proposed as an alternative
to overcome some of the drawbacks
mentioned above. A potential benefit of the presence of boron is the
creation of electronic levels that could hinder the recombination
of the electron–hole pairs.[16,18−26] Density functional theory calculations suggest that the occupation
of interstitial sites or O substitution are more energetically favorable
than substitution of Ti by B atoms.[24] It
has been reported that the addition of boron to TiO2 sol–gel
precursors generally leads to interstitial B-doping, together with
the formation of B2O3 on the surface of the
TiO2 particles.[16,19,27,28] Some studies have also shown
that surface boron species can introduce residual charge, which can
increase the number of surface OH groups, being them correlated with
the incorporated B.[19,29]The positive influence
of boron has also been related to changes
in the TiO2 structure as it could inhibit the growth of
crystalline TiO2, leading to materials with increased surface
area[30] and anatase content.[18]Several studies have reported a photoactivity
improvement upon
B doping of TiO2,[16,18−26] but the interpretation is still controversial, especially regarding
the local structure around the boron impurity and the electronic effects
of the dopant species.[16,19,31] Zhang et al. reported highly efficient photocatalysts consisting
of B-TiO2 (3.5 at. B %) for gas phase degradation of benzene
under UV–vis light,[22] which are
more active than the commercial TiO2-P25. This improvement
is ascribed to a significant enhancement of the UV–vis light
absorption.[22] Ansón-Casaos et al.
prepared B-TiO2 photocatalysts by sol–gel synthesis
using boric acid,[16] leading to a slightly
improved photocatalytic efficiency in the degradation of diphenhydramine
(drug pollutant model) in water. UV–vis diffuse reflectance
analysis allowed to discard visible light absorption, and the activity
improvement was attributed to the crystalline structure and composition
of the photocatalysts. Jeong et al.[19] prepared
a boron-doped TiO2 anode (sol–gel, 2, 5, and 10
wt % B) for lithium-ion batteries, and they found a significant improvement
with respect to pristine TiO2, which was attributed to
the increased interplanar spacing of the TiO2 lattice due
to interstitial B atoms and/or to a larger amount of surface hydroxyl
groups. Dozzi et al. studied B- and F- doped TiO2 materials,
and they found that the photodegradation of formic and acetic acid
(in the liquid phase) can be correlated with the photocatalyst’s
structural features. The higher activity of the doped TiO2 with respect to the bare one was attributed to its higher surface
area (from 45 to 100 m2/g) and the hindered transformation
of anatase into rutile, whereas the surface B2O3 formed (observed by XPS) had no effect on the photoactivity.[27]Many of the indicated effects can be positive,
enhancing the photocatalytic
activity of TiO2 for propene oxidation, which is the target
reaction of the present study.With the aim of shedding light
on the role of boron in the physicochemical
properties of TiO2 modified with this element, the present
research focuses on the study of nanostructured B-TiO2 samples,
prepared by sol–gel synthesis using titanium tetraisopropoxide
and different amounts of boric acid and crystallization temperatures.
A detailed characterization has been carried out using a plethora
of techniques [gas adsorption, X-ray diffraction (XRD), X-ray photoelectron
spectroscopy (XPS), UV–vis spectroscopy, analysis of photoluminescence
(PL), photoelectrochemical characterization (PEC), and Raman scattering].
The prepared photocatalysts have been tested in the gas phase photocatalytic
oxidation of propene (100 ppmv), which accounts for remediation of
pollution caused by low-concentration VOCs, a case in which efficient
removal techniques are difficult and costly to implement.[4,32]The general mechanism of propene oxidation involves the following
steps (where R represents the organic
substrate)Reactions 5 and 6 are
an example of the possible interaction of the substrate with oxidant
species. In a general way: R–H + •OH/O2•–/h+ → mineralization
products.In the case of propene oxidation, the global reaction
can be written
asThe thorough characterization of the
B-TiO2 samples,
using techniques that allow an approach to the photocatalyst properties
from very different points of view and that will help to find a suitable
correlation between properties and activity of the photocatalysts,
is one of the main novelties of this study.
Experimental Section
Materials
Titanium(IV) isopropoxide
(TTIP, C12H28O4Ti, 97%, Sigma-Aldrich),
boric acid (H3BO3, 99.9%, Gilca), and 2-propanol
(C3H8O, >99.8%, Panreac AppliChem) were used
as-received. The well-known standard Aeroxide P25 TiO2 photocatalyst
from Degussa was used as a reference.
Synthesis of B-TiO2 Photocatalysts
The synthesis procedure is based on a previously optimized sol–gel
method.[16] In a typical preparation, 5 mL
of TTIP were diluted in 50 mL of isopropanol and added dropwise, under
constant stirring, to 50 mL of a water/isopropanol (1:1) mixture containing
a certain quantity of boric acid. The resulting gel was aged overnight,
filtered, and dried in an oven at 90 °C. The as-prepared amorphous
TiO2 was thermally treated in a horizontal quartz reactor
under an ambient atmosphere to induce crystallization. The obtained
materials are labeled as B-X-TiO2-T, where X refers to the amount of boric
acid (mg) added during the synthesis and T (°C)
to the crystallization temperature. Scheme illustrates the preparation and structure
of the catalysts.
Scheme 1
Illustration of the Photocatalysts Preparation and
Composition/Structure
The nominal B content in the resulting samples
was estimated taking
into account the yield of the TiO2 synthesis and assuming
that all the boron from the added boric acid remains in the final
product. More specifically, the average hydrolysis yield for 5 mL
TTIP was 1.5 ± 0.1 g, and the yield of the thermal crystallization
treatment was 81.5 ± 1.5%. Therefore, the boron content ranges
from 0.07 to 3.4 wt %.
Characterization
N2 adsorption–desorption
at −196 °C (Quantachrome Autosorb-6B Instrument) after
sample degasification (250 °C, 4 h) was used to characterize
the porous texture [the apparent Brunauer–Emmett–Teller
(BET) specific surface area (SBET) and
the total micropore volume (VDR N2, ϕ < 2 nm), applying BET and Dubinin Radushkevich
equations, respectively].[33] An estimation
of the mesopore volume (2 nm < ϕ < 50 nm, Vmeso) was calculated as VN ads (P/P0 = 0.9)
– VN ads (P/P0 = 0.2), expressed as liquid.[34] Total pore volume (VT) was determined as the volume of nitrogen adsorbed at P/P0 = 0.99 (as liquid).XRD measurements
were carried out in a Miniflex II Rigaku (30 kV/15 mA) equipment at
room temperature, with Cu Kα radiation, 2°/min scanning
rate, and 6–80° 2θ range. The average crystallite
size (B) was calculated with the Scherrer equation[35]where λ is 0.1540 nm (Cu Kα radiation
wavelength), K is a constant (taken as 0.93 considering
spherical grains),[36] and β and θ
are, respectively, the full width at half-maximum intensity (FWHM)
and the diffraction angle of the main peak for each crystalline phase.Crystalline TiO2 was characterized and quantified using
XRD data of 50/50 (wt/wt) B-TiO2/CaF2 mixtures,
as described in ref (37). Further explanations on the calculation of total crystallinity
and percentage of crystalline phases are reported in Section .High-resolution
transmission electron microscopy (HRTEM) in combination
with an energy-dispersive X-ray spectroscopy EDX (FEI Tecnai G2 system
with a Schottky field emission electron gun operated at 200 kV) were
used for characterizing TiO2 microstructure and chemical
composition in some prepared samples. For that purpose, TiO2 nanopowders were suspended in ethanol and dispersed on TEM grids.XPS was measured in a VG-Microtech Multilab 3000 spectrometer provided
with an Al anode working at 6 mA and 12 kV and with a pass energy
of 50 eV. Binding energies were referenced to the C 1s line at 284.6
eV.[38]PL and Raman scattering spectra
of cold-pressed pellets of the
powder catalysts were recorded using a laser diode as the excitation
source (λexc = 405 nm) and a ×50 microscope
objective to achieve an irradiance of about 108 W/m2. The laser light was rejected by a longpass edge filter,
which cutoff all signals below 200 cm–1. Spectra
were recorded with a HORIBA Jobin Yvon iHR320 spectrometer equipped
with a Peltier-cooled CCD detector. All measurements were carried
out at room temperature and atmospheric pressure with the samples
in contact with air.Diffuse reflectance measurements were carried
out on a Shimadzu
UV–vis 2501PC spectrophotometer equipped with an integrating
sphere. BaSO4 was used as reference material and for background
measurement. The measurement range studied was 220–900 nm,
with a 1.0 nm resolution and a spectral bandwidth of 5 nm. The spectra
recorded were transformed using the Kubelka–Munk function.For the PEC characterization, powder photocatalysts were suspended
in isopropanol using an ultrasound bath and immediately deposited
on fluorinated tin oxide (Solems SA, 80 Ω/sq) substrates by
spray coating.[39] The as-prepared films
were sintered at 450 °C for 2 h under ambient air. Specimens
were connected as working electrodes in a three-electrode configuration,
with a graphite bar as the counter electrode, the Ag/AgCl, 3 M NaCl
(E° = 0.210 V vs SHE) as the reference electrode,
and 0.1 M Na2SO4 as the electrolyte. The electrolyte
was deoxygenated by flowing N2 for longer than 10 min before
the measurements. The glass PEC cell was provided with a quartz window
and irradiated with a laboratory-scale solar simulator (150 W Xe arc
lamp by LOT-Quantum Design GmbH). The simulated solar spectrum was
the AM1.5G with a maximum irradiance of approximately 100 mW/cm2 (see Figure S1A). The wavelength-dependent
response was measured using a LOT Quantum Design monochromator (MSH-300).
Photocatalytic Oxidation of Propene
The photocatalytic tests of propene oxidation were carried out in
an experimental setup that consists of a quartz reactor (AFORA) and
a UV-A lamp (Philips, TL8 W/05 FAM, λmax = 365 nm)
located parallel to the photoreactor at a distance of about 1 cm.
Some experiments have been carried out using a visible lamp (Sylvania,
F8W/T5/54-765, Daylight). The spectra of both lamps can be seen in Figure S1, Supporting Information. A scheme of
the setup is shown elsewhere,[2] and a detailed
description of the experimental conditions has been previously reported
by Cano-Casanova et al.[40,41] The UV-A irradiance
of the Philips lamp was determined at 1 cm distance with a portable
Delta Ohm photo radiometer (model HD 2102.2) equipped with a UV-A
probe (LP 471 UVA), being 2.24 mW/cm2.In a typical
experiment, the photocatalyst (0.11 g) was placed on a quartz wool
plug inside the reactor and, after purging with helium (60 mL/min),
a stream of propene in air [100 ppmv propene, 30 or 60 mL/min (STP)]
was passed through the reactor at 25 °C. The outlet stream was
continuously monitored by mass spectrometry (Thermostar GSD 301 O1,
from Balzers), and once the signal was stabilized, the UV-lamp was
switched on, and the illumination was maintained for 3 h. The experiments
were repeated at least twice to check reproducibility.Blank
experiments (in the absence of the catalyst) and measurements
in dark show that propene conversion does not occur in these conditions.Propene conversion was calculated, as shown in eq where Cinitial C is the initial propene concentration (100
ppmv) and Cstationary C is the stationary propene concentration under illumination
(3 h reaction time). This is illustrated in Scheme .
Scheme 2
Drawing of the Variation of the Propene
Concentration under Illumination
(in Presence of a Photocatalyst), Parameters as Indicated Above.
Reaction products, i.e., carbon dioxide and
water, were also analyzed
by mass spectrometry. A calibration cylinder containing 300 ppmv CO2 in He was used for CO2 quantification. Mass scan
measurements (up to m/z = 100) allowed
to discard any additional oxidation compound, and the total mineralization
of propene was confirmed by the carbon balance,[2,3] according
to the following reactionThis condition was verified for each
experiment.
Results and Discussion
This section
includes the results of different characterization
techniques with the aim of analyzing: (i) the effect of the amount
of boric acid used and (ii) the effect of the crystallization temperature,
on the photocatalytic activity.
Characterization of the Prepared Samples
XRD Analysis and Textural Properties
XRD patterns of the B-X-TiO2-550 samples
(Figure ) show the
characteristic peaks of anatase [2θ values of 25.3° (101),
37.8° (004), 48.0° (200), 54.5° (105), 55° (211),
62.7° (204), 70.4° (116), and 74.5° (220)] and rutile
[2θ values of 27.5° (110), 36.1° (101), and 54.4°
(211)].[42,43] B-100-TiO2-550 and B-230-TiO2-550 samples show an additional peak at 2θ = 28.1°,
which corresponds to boric oxide (B2O3)[16,44] (inset of Figure ), resulting from the thermal decomposition of boric acid (boric
acid decomposes at about 150 °C into boric oxide and water[45]). B2O3 might also be present
in the other samples but it is not detected, either because the amount
is too low or it has low crystallinity.
Figure 1
XRD spectra for B-X-TiO2-550 samples.
Inset image: amplification of Figure in the 24–30° 2θ range.
XRD spectra for B-X-TiO2-550 samples.
Inset image: amplification of Figure in the 24–30° 2θ range.The XRD profiles of the B-X-TiO2-550
series (X ≠ 0) show that boron incorporation
does not take place in the bulk TiO2 crystallite and, thus,
it can be considered that boron atoms are not extensively inserted
in the anatase or rutile unit cells.The calculated percentage
of crystalline and amorphous phases and
the average crystallite size for all the prepared photocatalysts and
P25 are listed in Table . The percentages of anatase and rutile have been calculated using
the following equationswhere AAnatase,101, ARutile,110, and ACaF are the areas determined from the
XRD pattern.
Table 1
Crystalline Properties and Surface
Area in the B-X-TiO2-550 Series and P25a
crystalline
TiO2
average
crystallite size (nm)
sample
A (%)
R (%)
amorphous TiO2 (%)
A
R
SBET (m2/g)
B-0-TiO2-550
65
12
23
28
32
28
B-5-TiO2-550
75
2
23
25
19
33
B-10-TiO2-550
70
6
24
25
27
30
B-50-TiO2-550
56
6
38
25
29
24
B-100-TiO2-550
66
5
29
24
23
27
B-230-TiO2-550
70
7
23
27
25
25
P25
73
14
13
22
28
55
A = anatase, R = rutile.
A = anatase, R = rutile.Thus, the percentages of crystalline and amorphous
TiO2 are, respectively, WCryst = ACryst + RCryst and WAm = 100 – WCryst.These data show that, in general, the presence
of boric acid during
the TiO2 synthesis hinders the formation of rutile, stabilizing
up to some extent the anatase metastable phase, in agreement with
the literature.[18,30] Although differences between
the B-X-TiO2-550 samples regarding phase
composition are small, it can be highlighted that B-5-TiO2-550 is the one with the highest anatase and lowest rutile content,
whereas B-50-TiO2-550 has the lowest anatase content and
the highest proportion of amorphous TiO2.The specific
surface area (SBET) of
the B-X-TiO2-550 samples is about half
that of P25, ranging from 24 to 33 m2/g (see complete textural
properties in Table S1, Supporting Information),
and it does not significantly vary with the amount of boron present
in the sample.
HRTEM–EDX Characterization
The comparative TEM–HRTEM analysis of samples B-0-TiO2-550 and B-5-TiO2-550 (see Supporting Information, Figures S2 and S3) shows that the TiO2 nanoparticles have a similar particle size (50 nm average size),
but some interesting differences in the particles structure have been
observed. Thus, in sample B-0-TiO2-550 both monocrystal
and some polycrystalline nanoparticles are present, and most of them
also show amorphous domains, whereas B-5-TiO2-550 contains
mainly monocrystals.EDX analysis (Figure S2) has shown no differences between B-5-TiO2-550
and B-0-TiO2-550 samples. The lack of detectable signal
at the K-alpha emission of boron (expected at 0.183 keV) in the spectrum
of B-5-TiO2-550 in not surprising due to the low boron
content in this sample and the proximity of the K-alpha peak of C
(carbon is present in the TEM grids and produces a strong peak).
XPS Analysis
The XPS spectra survey
of the B-X-TiO2-550 samples series is
presented in Figure S4. Figure a–c shows the XPS spectra
of the B-X-TiO2-550 photocatalysts for
B 1s, O 1s, and Ti 2p, respectively (the latter in the 461–456
eV range, see full-range Ti 2p spectra in Figure S5). The corresponding binding energy (BE) values are collected
in Table . Note that
these values correspond to the maxima of the experimental spectra
except for O 1s, for which three binding energies have been obtained
from the fitted deconvoluted spectra of each oxygen contribution.
Figure 2
XPS data
of (a) B 1s, (b) O 1s, and (c) Ti 2p for the B-X-TiO2-550 samples. The original data are plotted
for B 1s, whereas for O 1s and Ti 2p, normalized data are presented
(to better observe the shifts).
Table 2
Binding Energies of B 1s, O 1s, and
Ti 2p for B-X-TiO2-550 Samples
BE (eV)
sample
B 1s
O 1s (I)
O 1s (II)
O 1s
(III)
Ti 2p3/2
B at%
B at. % (nom)a
B-0-TiO2-550
529.6
531.1
458.3
0.00
B-5-TiO2-550
192.1
529.8
531.2
532.4
458.8
2.8
0.14
B-10-TiO2-550
192.1
529.8
531.5
532.8
458.7
2.3
0.29
B-50-TiO2-550
192.2
529.8
531.3
532.4
458.7
6.0
1.41
B-100-TiO2-550
192.8
530.0
531.5
532.6
459.0
8.9
2.78
B-230-TiO2-550
192.8
530.2
532.3
532.9
459.0
10.2
6.12
Nominal atomic percentage of boron,
calculated according to the boric acid used and the yield of the preparation
method.
XPS data
of (a) B 1s, (b) O 1s, and (c) Ti 2p for the B-X-TiO2-550 samples. The original data are plotted
for B 1s, whereas for O 1s and Ti 2p, normalized data are presented
(to better observe the shifts).Nominal atomic percentage of boron,
calculated according to the boric acid used and the yield of the preparation
method.As shown in Figure a and in Table ,
the B 1s BE is around 192.1 eV in B-5-TiO2-550, B-10-TiO2-550, and B-50-TiO2-550 samples, while it is 192.8
eV in B-100-TiO2-550 and B-230-TiO2-550. As
the B 1s BE in B2O3 is 192.9 eV,[46,47] it can be assumed that boron is largely present as B2O3 on the surface of the B-100-TiO2-550 and
B-230-TiO2-550 samples, which is in agreement with the
presence of B2O3 determined by XRD (see Figure ). In the case of
the B-5-TiO2-550, B-10-TiO2-550, and B-50-TiO2-550 samples, boron is present in a less deficient electronic
state, which can be related to a lower interaction with electronegative
atoms such as O. Quesada-González et al.[48] in their study of B-TiO2 samples reported that
the B 1s BE of about 192 eV corresponds to interstitial B and that
a peak at 192.6 eV can be attributed to H3BO3 or B2O3. The assignation of a 191.8 eV BE
to interstitial B is also reported by Feng et al.[21] and Zhang et al.,[22] who also
found a 191.9 eV BE for B-TiO2 samples. They proposed that
B is incorporated into the TiO2 lattice and that its chemical
environment might be Ti–O–B.[22]These results evidence the presence of interstitial B in our
photocatalysts,
being easily detected by XPS analysis on the surface of the samples
with lower B loading, whereas it could probably be covered by B2O3 in the B-100-TiO2-550 and B-230-TiO2-550 samples. In the study of Quesada-González et al.,[48] the interstitial boron was detected by in-depth
XPS analysis.The O 1s spectra show that oxygen is present in
different electronic
states. In the case of B-0-TiO2-550, the main peak is due
to O bonded to Ti (at 529.6 eV, TiO2 lattice oxygen), and
a shoulder (at 531.1 eV) corresponding to O in surface OH groups[22] can be observed [identified as O(I) and O(II),
respectively] in Table .For the boron-containing samples, apart from the main O–Ti
peak, a two-component band, with its maximum at BE ≥ 532 eV,
can be observed. It corresponds to either O bonded to boron[22] or O in OH surface groups.[22] Such a band has been deconvoluted to distinguish these
two contributions (Figure ), and the one assigned to O–B has been identified
as O(III) in Table . As in the case of the B1s data, there are differences between B-100-TiO2-550 and B-230-TiO2-550 samples on one side, and
B-5-TiO2-550, B-10-TiO2-550, and B-50-TiO2-550 on the other side, both in the intensity and in the BE
of these O–B species. In agreement with the higher B content,
the proportion of O bonded to B species (O(III)) is noticeably higher
in the B-100-TiO2-550 and B-230-TiO2-550 samples
and, in line with B 1s BE and XRD data, these species largely correspond
to B2O3 on the TiO2 surface. In the
case of the B-5-TiO2-550, B-10-TiO2-550, and
B-50-TiO2-550 samples, the O–B bonds should correspond
to the surface interstitial species present in these samples.
Figure 3
O 1s XPS deconvoluted
spectra for the B-X-TiO2-550 samples.
O 1s XPS deconvoluted
spectra for the B-X-TiO2-550 samples.The BE of Ti 2p3/2 in sample B-0-TiO2-550
(458 eV) shows that, as expected, titanium is present as Ti4+ (Figures and S5). For the B-X-TiO2-550 series of samples, the BE is slightly shifted to higher values,
indicating that the presence of boron reduces the electron density
of Ti 2p.[26] This can be a consequence of
the proximity of boron atoms (more electronegative than Ti) located
in interstitial positions of the TiO2 structure. The displacement
seems to increase with the boron amount, being related to more boron
atoms located in interstices. It is important to point out that the
distortion of the TiO2 lattice produced as a consequence
of boron insertion has been detected by means of XPS data and not
by XRD, which indicates that it is not a bulk extensive phenomenon.
Then, it could be assumed that it happens mainly in a surface region.
The B2O3 identification by XRD analysis allows
considering that only a certain amount of boron can be hosted in the
TiO2 lattice, and the rest is deposited on the surface
of the TiO2 nanoparticles as B2O3.
Photocatalytic Activity
Figure shows propene conversion
data obtained with the two flow rates tested. Photolysis does not
occur, and these results indicate that all the prepared photocatalysts
are active, being two of them more active than the reference P25.
Furthermore, the same trend is found with the two propene flow rates,
which proves the reproducible performance of these catalysts. The
lower flow rate leads to a higher conversion because of the larger
contact time and/or the lower amount of propene molecules to be oxidized
per unit of time.
Figure 4
Propene conversion (%) at 30 and 60 mL/min for B-X-TiO2-550 photocatalysts and P25.
Propene conversion (%) at 30 and 60 mL/min for B-X-TiO2-550 photocatalysts and P25.The catalyst stability has been stated after confirming
that the
MS propene signal remains stable during the whole experiment. As no
decay was observed at all, it can be assumed that the catalysts remain
stable.The order in the activity of B-X-TiO2-550 samples is: B-5-TiO2-550 > B-10-TiO2-550
> B-0-TiO2-550 > B-50-TiO2-550 > B-100-TiO2-550 > B-230-TiO2-550.Samples B-5-TiO2-550 and B-10-TiO2-550 are
more active than the prepared bare TiO2 (sample B-0-TiO2-550) and also than P25. However, B-X-TiO2-550, with X = 50, 100, and 230 samples are
less active, and the photocatalytic activity decreases as the amount
of boric acid used increases, being sample B-230-TiO2-550
practically inactive. These results imply that interstitial boron
doping likely leads to electronic modifications that improve the TiO2 photoactivity. However, above a certain amount of boron,
there is an excess that segregates as B2O3 and
partially covers the interstitially boron-doped TiO2 surface,
with the consequent photocatalytic activity decrease. Thus, the very
good photocatalytic performance, shown by B-5-TiO2-550
and B-10-TiO2-550, seems to be related to the low, but
suitable, quantity of boron present and its location. The B-5-TiO2-550 sample contains the highest anatase and the lowest rutile
amount, and it has a certain content of surface interstitial boron.
These characteristics likely enhance the photocatalytic propene oxidation.Some selected samples were also tested under visible light. The
results are discussed in Section , but it can be anticipated that the activity is significantly
lower. Propene conversion (using 30 mL/min propene flow) of sample
B-5-TiO2-550 decreases from 74% (under UV light) to 18%
(under visible light) (compare data in Figures and S10).In order to better understand and to explain why the photocatalysts
that contain the lowest amount of boron show the best photocatalytic
activity, they were further characterized by means of PEC and PL measurements.
PEC and PL Characterization of the Most
Active Samples
Figure shows the analysis by cyclic voltammetry (CV) in the dark
and under irradiation in a solar simulator. In the dark, the shape
of the CV scans reflects the accessibility of electronic energy states
that are near the conduction band level,[49] which is located at around −1 V versus Ag/AgCl. The CV plot
of P25 is quite different from that of the B-X-TiO2-550 samples tested. Specifically, the hysteresis of P25 at
potentials below −0.7 V versus Ag/AgCl is wider, which can
be associated to the higher SBET and,
thus, to a larger charge accumulation on the surface. Besides, trap
states around −0.5 V are more clearly defined for P25, in particular
in the backward (negative currents) scan. All the B-X-TiO2 samples tested show a similar scan shape, as all
of them have close SBET values and, thus,
similar charge accumulation capacities.
Figure 5
CV scans in the dark
(a) and under full solar irradiation (b) using
various TiO2 specimens as working electrodes. Scan rate
= 20 mV s–1, irradiation intensity ∼100 mW
cm–2.
CV scans in the dark
(a) and under full solar irradiation (b) using
various TiO2 specimens as working electrodes. Scan rate
= 20 mV s–1, irradiation intensity ∼100 mW
cm–2.Under full solar spectrum irradiation, a photocurrent
is observed
at E > −0.35 V for the tested B-X-TiO2-550 samples, being the highest one for
B-5-TiO2-550 and B-0-TiO2-550 anodes. Besides,
both electrodes
show a particular distortion in the charge accumulation region, with
a clear feature at around −0.7 V (positive currents scan).
This feature points to the creation under irradiation of certain surface
states close to the conduction band, being particularly pronounced
for B-5-TiO2-550, which could explain the better photocatalytic
performance of this sample.Figure a shows
the PL spectra obtained for B-0-TiO2-550, B-5-TiO2-550, and P25, with an excitation source of 405 nm (see Figure S6 for the PL spectra of the complete
B-X-TiO2-550 series). This excitation
energy is slightly lower than rutile or anatase TiO2 band-gap
energies and, therefore, the absorption should correspond to transitions
from the valence band to shallow trap states that appear as an exponential
continuous tail just below the conduction band, being associated to
structural disorder and unbalanced Ti atoms on the surface.[50] The PL spectrum of P25 shows a wide band, which
can be deconvoluted into three different peaks centered at 442 nm
(blue), 530 nm (green), and 600 nm (yellow-red), respectively. The
blue peak is attributed to transitions between the shallow continuous
states and the valence band, while the green and red PL peaks involve
deep intermediate gap states originated by intrinsic point defects,
such as oxygen vacancies, and are typical of anatase TiO2.[50,51] In nanostructured TiO2, oxygen
vacancies are located close to the surface, and their densities can
be affected by environmental conditions. It has been widely reported
that O2 adsorption results in a significant reduction of
the PL intensity of anatase TiO2, and the opposite occurs
upon O2 desorption.[19]
Figure 6
(a) PL spectra
of B-0-TiO2-550, B-5-TiO2-550,
and TiO2-P25. (b) Expansion of the spectral range between
405 and 485 nm, showing the Raman scattering spectra in detail (the
scale has been changed to wavenumbers, and intensity is represented
in the logarithmic scale, for clarity).
(a) PL spectra
of B-0-TiO2-550, B-5-TiO2-550,
and TiO2-P25. (b) Expansion of the spectral range between
405 and 485 nm, showing the Raman scattering spectra in detail (the
scale has been changed to wavenumbers, and intensity is represented
in the logarithmic scale, for clarity).Sample B-0-TiO2-550 presents a PL spectra
similar to
that of P25, but with a more intense blue band, indicating a less
efficient charge relaxation toward trapped states near the surface.
On the other hand, B-5-TiO2-550 exhibits a drastic quenching
of all PL bands (red line in Figure a). The absorbance spectra of these two samples (see Figure S7) are very similar, indicating that
absorption is not affected by B incorporation (absorption in the visible
region does not occur), ruling out one of the possible mechanisms
by which B can modify the activity of TiO2 (substitution
of oxygen atoms would produce the TiO2 band gap narrowing).
However, the mentioned PL quenching reveals an overall reduction in
the recombination rate of photo-excited electrons and holes, which
can be explained by a more efficient charge separation and transfer
toward the surfaces.[52−55] This supports the interpretation of its highest photocatalytic activity.
The suppression of PL allows the observation of several sharp features
present in the blue region. These findings correspond to the resonant
Raman spectrum of the sample and have been plotted in more detail
in Figure b. The Raman
spectrum is dominated by three very intense peaks (below 1000 cm–1) labeled as the principal vibrational modes of anatase
TiO2. The low-frequency Eg mode
of anatase is not detected as it has been cut off by the Raman edge
filter. There are no traces of rutile modes, further confirming that
anatase is the most abundant crystallographic phase in these materials.
Similar peaks are observed in the spectrum of sample B-0-TiO2-550 but, surprisingly, not in the case of P25, which shows no resonant
Raman signal. Finally, sample B-5-TiO2-550 exhibits two
additional Raman bands at higher wavenumbers. These bands, which are
not seen in the Raman spectrum performed with green laser excitation
(not shown), have been linked to vibrational H–O–H bending
modes at 1600 cm–1 and to the stretching vibrational
modes of hydroxyl groups between 3000 and 3500 cm–1.[56] These observations would indicate,
on the one hand, the chemisorption of water molecules and, on the
other hand, the production of hydroxyl radicals under UV irradiation.[57] The presence of the latter band only in the
Raman spectrum of sample B-5-TiO2-550 could be linked to
its higher photocatalytic efficiency. Although the presence of boron
had no measurable effect in band gap narrowing, the highest photocatalytic
performance of this sample could be linked to its best photocurrent
response ability, the additional production of hydroxyl radical groups,
and the lowest recombination rate of electron/hole pairs.
Effect of the Crystallization Temperature
Sample B-5-TiO2-550, the most active in the B-X-TiO2-550 series, has been selected to study
the effect of the crystallization temperature on the properties of
these photocatalysts. Thus, after the sol–gel synthesis, B-5-TiO2 sample has been heat-treated at 350 and 450 °C to be
compared with B-5-TiO2-550. XRD patterns of the three B-5-TiO2-T photocatalysts (Figure S8 in Supporting Information) show the characteristic peaks
of anatase (see Section ), and only for B-5-TiO2-550, an incipient
peak of rutile can be observed. Inset of Figure S8 shows the enlarged 22–30° 2θ range, revealing
changes in the crystallinity of those samples. As expected, the peaks
become broader as the crystallization temperature decreases, which
means that the sample is less crystalline. Table summarizes the main properties of the B-5-TiO2-T series and the measured propene conversion.
Data corresponding to P25 are also included.
Table 3
Physicochemical Properties and Propene
Conversion for the B-5-TiO2-T Samples
and P25
sample
crystalline TiO2 (%)a
amorphous TiO2 (%)a
average crystallite size (nm)b
SBET (m2/g)c
B at. (%)d
propene conversion (%)e
B-5-TiO2-550
A (75)–R (2)
23
A (25) R
(19)
33
2.8
74
B-5-TiO2-450
A (76)
24
A (18)
29
5.4
84
B-5-TiO2-350
A (70)
30
A (11)
104
3.6
58
P25
A (73)–R (14)
13
22
55
61
Determined as indicated in the characterization
by XRD.
Calculated from
Scherrer’s
equation.
Calculated from
N2 adsorption
data.
Estimated from XPS
analysis.
Determined by eq at 30 mL/min.
Determined as indicated in the characterization
by XRD.Calculated from
Scherrer’s
equation.Calculated from
N2 adsorption
data.Estimated from XPS
analysis.Determined by eq at 30 mL/min.Regarding the calculated percentage of crystalline
and amorphous
phases and the average crystallite size for B-5-TiO2-T samples (calculated following the same procedure as for
the B-X-TiO2-550 set of samples, data
included in Table ), the B-5-TiO2-350 catalyst presents the lowest crystallinity
(30% of the amorphous phase) and smallest average crystal size (11
nm), whereas the B-5-TiO2-550 has the highest crystallinity,
even with a small amount of the rutile phase (2%). In addition, these
data agree with specific surface areas (SBET) obtained for these materials (Table ). The material prepared at 350 °C presents the
highest surface area, which is consistent with the largest proportion
of the amorphous phase and the smallest crystal size. Samples B-5-TiO2-450 and B-5-TiO2-550 show similar surface area
and crystallinity, although the effect of the temperature is reflected
in the higher average crystal size of the sample treated at 550 °C.B-5-TiO2-350 and B-5-TiO2-450 were also studied
by XPS, and they show features similar to sample B-5-TiO2-550 (see Figure S9 and Table S2 and Table S3 in Supporting Information). However, the sample prepared at 450
°C shows the highest boron atomic percentage, 5.4% (Table ), meaning that the
crystallization temperature most probably has an effect on the distribution
of boron atoms on the TiO2 surface. Finally, data in Table show that the catalyst
crystallization temperature influences propene conversion, being B-5-TiO2-450 the most active sample (84% propene conversion) and B-5-TiO2-350 the least active one.The higher activity of sample
B-5-TiO2-450 compared
to B-5-TiO2-550 (both have similar surface area) can be
explained considering that the first contains pure anatase, of lower
average crystal size, and larger amount of surface interstitial boron
atoms. The lower activity of sample B-5-TiO2-350 can be
related to the lower anatase content.The photocatalytic propene
oxidation under visible light using
B-5-TiO2-450, B-5-TiO2-550, and P25 samples
has also been studied. A previous blank experiment shows that, as
expected, propene photolysis does not occur, while the tested photocatalysts
led to relatively low propene conversion (around 15%), see Figure S10. The activity measured with visible
light is probably mainly related to the contribution of UV radiation
in the used visible lamp (see spectra in Figure S1, Supporting Information), although it seems that the three
tested photocatalysts have some features by which the relative activity
order under visible and UV light do not agree (Figure S10). In any case, the different lamp irradiances should
be taken into account: UV irradiance of the visible lamp, 0.049 mW
cm–2, is much lower than that of the UV-lamp, 22.4
mW cm-2, and the activity is not linearly related
with irradiance.[58] Nevertheless, the poor
response under visible light is in agreement with the lack of band
gap modification of TiO2 upon B incorporation (Figure S7 compares results of B-5-TiO2-550 and B-0-TiO2-550) and supports discarding substitutional
B doping.In order to explain the highest photocatalytic activity
of sample
B-5-TiO2-450 under UV light, the series of B-5-TiO2-T samples has been characterized by means
of PEC and PL measurements (like in the case of the B-X-TiO2-550 set of samples discussed above).
PEC and PL Characterization of B-5-TiO2-T Samples
The PEC characteristics
of the B-5-TiO2-450 electrode under CV conditions in the
dark (not shown) are analogous to those of B-0-TiO2-550
and B-5-TiO2-550 (Figure ). Under full solar light irradiation, all the specimens
develop an induced photocurrent at positive potentials versus Ag/AgCl.
The transient photocurrent response for those selected specimens is
shown in Figure a.
A high photocurrent could be related to an improved ability of this
sample to decrease the radiative recombination of photogenerated electron/hole
pairs. The intensity of light pulses shows an exponential decay, which
relates to the capacitive filling of surface states. The dynamics
shown by P25 is quite different from those of the sol–gel prepared
photocatalysts in the considered time scale, again connecting with
the link of higher surface area and charge accumulation. The B-5-TiO2-550 sample produces the highest intensity response. However,
when the photocurrent is analyzed as a function of the light excitation
wavelength using a monochromator (Figure b), samples B-0-TiO2-550 and B-5-TiO2-550, and P25 as well, show nearly identical wavelength-dependent
profiles, while B-5-TiO2-450 has clearly a shift in its
wavelength activity profile.
Figure 7
(a) Transient photocurrent measurements at a
constant potential
of 0 V vs Ag/AgCl and solar irradiation power of 70 mW cm–2 for electrodes containing P25, B-5-TiO2-450, B-0-TiO2-550, and B-5-TiO2-550. (b) Normalized photocurrent
as a function of the irradiation wavelength at a constant potential
of 0.4 V vs Ag/AgCl.
(a) Transient photocurrent measurements at a
constant potential
of 0 V vs Ag/AgCl and solar irradiation power of 70 mW cm–2 for electrodes containing P25, B-5-TiO2-450, B-0-TiO2-550, and B-5-TiO2-550. (b) Normalized photocurrent
as a function of the irradiation wavelength at a constant potential
of 0.4 V vs Ag/AgCl.Furthermore, diffuse reflectivity (Figure S7) shows that regardless the crystallization
temperature, all samples
present a linear uprise of the absorption pointing to the same indirect
band gap wavelength (427 nm), but B-5-TiO2-450 shows an
Urbach tail (usually due to defects or loss of crystallinity) into
the visible which is not present in the other two samples. This analysis
reveals subtle differences between samples B-5-TiO2-450
and B-5-TiO2-550 and allows to propose that the wavelength
shift of the photocurrent intensity maximum has a larger influence
on the photocatalytic activity for propene oxidation under 365 nm
UV light than the absolute intensity value.Finally, Figure contains, for comparison
purpose, PL spectra (excitation source
of 405 nm) of B-5-TiO2-T.
Figure 8
PL spectra of B-5-TiO2-550, B-5-TiO2-450,
and B-5-TiO2-350 photocatalysts. The intensity of the spectra
were normalized using the intensity of the anatase TiO2 Raman peaks, which should be proportional to the amount of excited
material.
PL spectra of B-5-TiO2-550, B-5-TiO2-450,
and B-5-TiO2-350 photocatalysts. The intensity of the spectra
were normalized using the intensity of the anatase TiO2 Raman peaks, which should be proportional to the amount of excited
material.Figure reveals
that the whole B-5-TiO2-T photocatalyst
series exhibits a quenching of all PL bands (compared with the B-0-TiO2-550 sample shown in Figure ). Thus, the reduction in the recombination rate of
photo-excited electrons and holes when boron is (mostly interstitially)
present is again confirmed. B-5-TiO2-450 and B-5-TiO2-550 samples show the lowest PL intensity within this series
(lowest recombination rate of electron and holes), supporting the
interpretation of their higher photocatalytic activities.
Conclusions
Nanostructured B-TiO2 photocatalysts (B-X-TiO2-550)
with different amounts of boron (X) have been prepared
by the sol–gel method and treated at
different crystallization temperature (T). All the
B-X-TiO2-550 catalysts have similar SBET values (25–30 m2/g). The
presence of boric acid during the TiO2 synthesis hampers
the formation of rutile and, thus, the B-TiO2 samples mostly
consist of anatase with minor quantities of rutile (<12%). XPS
analysis reveals that B occupies interstitial positions (close to
the surface), and when B is in excess, it is externally deposited
as B2O3. The activity of the B-TiO2 samples for propene photo-oxidation is highly influenced by the
boron content. Samples with low boron amount (X =
5 and 10) show the highest activity. The optimal behavior of these
samples can be explained by the presence of interstitial B, together
with a high crystallinity and high proportion of anatase. B2O3 deposits are formed in samples with higher boron loading,
which cover the active titania surface with the subsequent activity
decrease.PEC and PL data reveal significant differences between
samples.
The highest photocatalytic performance achieved is related to the
improvement of the photocurrent response ability (PEC), the production
of hydroxyl radicals (Raman scattering), and the lower recombination
rate of electron/hole pairs (PL), which points to a more efficient
charge separation measurements.The B-5-TiO2-450
sample is about 10% more active than
B-5-TiO2-550. This improvement is related to the increased
anatase content, lower average crystal size, and larger surface boron
enrichment. Also, its intrinsic photo-activity suitably shifts to
the wavelength of the light source (365 nm) and, as evidenced by PL
data, it shows a low electron/hole recombination rate.The present
study highlights the importance of a controlled and
accurate nanoscale doping of the titania surface in order to reach
the suitable modification that improves the photocatalytic activity
of TiO2. Also, it must be pointed out that the thorough
characterization with complementary techniques has allowed to understand
the effect of the interstitial B atoms in the photocatalytic behavior
of the prepared samples.
Authors: Miguel Quesada-González; Nicolas D Boscher; Claire J Carmalt; Ivan P Parkin Journal: ACS Appl Mater Interfaces Date: 2016-09-15 Impact factor: 9.229
Authors: Laura Cano-Casanova; Ana Amorós-Pérez; María Ángeles Lillo-Ródenas; María Del Carmen Román-Martínez Journal: Materials (Basel) Date: 2018-11-09 Impact factor: 3.623