Luka Suhadolnik1, Živa Marinko1,2, Maja Ponikvar-Svet3, Gašper Tavčar3, Janez Kovač4, Miran Čeh1. 1. Department for Nanostructured Materials, Jožef Stefan Institute, Jamova 39, SI-1000 Ljubljana, Slovenia. 2. Jožef Stefan International Postgraduate School, Jamova 39, SI-1000 Ljubljana, Slovenia. 3. Department of Inorganic Chemistry and Technology, Jožef Stefan Institute, Jamova 39, SI-1000 Ljubljana, Slovenia. 4. Department of Surface Engineering and Optoelectronics, Jožef Stefan Institute, Jamova 39, SI-1000 Ljubljana, Slovenia.
Abstract
TiO2 nanotubular films prepared using the anodic oxidation process applied to various forms of metal titanium are promising materials for photocatalytic applications. However, during successive anodizations in batch-anodization cells, the chemical composition of the NH4F- and water-based ethylene glycol electrolyte changes with each subsequent anodization, which greatly affects the final photocatalytic properties of the annealed TiO2 nanotubular films. In the present study, 20 titanium discs (Φ 90 mm) were sequentially anodized in the same anodization electrolyte. The chemical composition of the electrolyte was measured after each anodization and correlated with the anodization current density, temperature, electrical conductivity, and pH of the electrolyte and with the morphology, structure, composition, and photocatalytic activity of the resulting TiO2 nanotube films. It was found that the length of the TiO2 nanotubes decreased with the age of the electrolyte due to its lower conductivity. The subsurface chemical composition was evaluated by time of flight secondary ion mass spectrometry (ToF SIMS) analyses, and the integrated ToF SIMS signals over a depth of 250 nm for the TiO2 nanotube films showed that the concentration of F- in the annealed TiO2 film increased with each subsequent anodization due to the increased pH value of the electrolyte. As a consequence, the concentration of the OH- and O2 - species decreased, which is a major reason for the reduced photocatalytic activity of the TiO2 films. It is proposed that the length of the TiO2 nanotubes does not play a decisive role in determining the photocatalytic activity of the TiO2 nanotube films. Finally, the best measured degradation results of 60% for caffeine were thus achieved for the first anodized titanium discs. After that the efficiency gradually decreased for each subsequent anodized disc.
TiO2 nanotubular films prepared using the anodic oxidation process applied to various forms of metaltitanium are promising materials for photocatalytic applications. However, during successive anodizations in batch-anodization cells, the chemical composition of the NH4F- and water-based ethylene glycol electrolyte changes with each subsequent anodization, which greatly affects the final photocatalytic properties of the annealed TiO2 nanotubular films. In the present study, 20 titanium discs (Φ 90 mm) were sequentially anodized in the same anodization electrolyte. The chemical composition of the electrolyte was measured after each anodization and correlated with the anodization current density, temperature, electrical conductivity, and pH of the electrolyte and with the morphology, structure, composition, and photocatalytic activity of the resulting TiO2 nanotube films. It was found that the length of the TiO2 nanotubes decreased with the age of the electrolyte due to its lower conductivity. The subsurface chemical composition was evaluated by time of flight secondary ion mass spectrometry (ToF SIMS) analyses, and the integrated ToF SIMS signals over a depth of 250 nm for the TiO2 nanotube films showed that the concentration of F- in the annealed TiO2 film increased with each subsequent anodization due to the increased pH value of the electrolyte. As a consequence, the concentration of the OH- and O2 - species decreased, which is a major reason for the reduced photocatalytic activity of the TiO2 films. It is proposed that the length of the TiO2 nanotubes does not play a decisive role in determining the photocatalytic activity of the TiO2 nanotube films. Finally, the best measured degradation results of 60% for caffeine were thus achieved for the first anodized titanium discs. After that the efficiency gradually decreased for each subsequent anodized disc.
Anodic
oxidation is a well-known process that was first used for
the protection of aluminum in the early 20th century. Its main purpose
is to increase the adherent strength and the thickness of the film
formed by a natural oxidation process.[1] The process is still used in industrial settings for protecting
and coloring aluminum.[2] However, with the
emergence of nanotechnology, researchers began to modify the anodic
oxidation process to produce porous structures that can be used as
a template for the synthesis of one-dimensional nanostructures[3,4] or as an immobilized nanostructured film on a metal substrate for
various applications.[5,6]Al2O3 is the most used template material,
obtained by the anodization of aluminum,[7] while TiO2 nanotubes, obtained by the anodization of
titanium, are the most investigated materials for the direct use of
anodized films. TiO2 nanotubes have a high surface area
and unique electronic, ionic, and biocompatibility properties, which
lead to many different applications.[8] Among
them, photocatalysis is the most studied and reported in the scientific
literature.[9]The most important characteristics
of an efficient TiO2 photocatalyst are its high activity,
low cost, and good stability.
Additionally, the ideal photocatalyst should be strongly adhered to
a support enabling a continuous photocatalytic reaction without the
need to remove and recycle the photocatalyst.[10] Immobilization can be most easily achieved with the use of an anodic
oxidation process, which at the same time allows the low-cost synthesis
of TiO2 nanotube films. Moreover, anodic oxidation enables
the optimization of the nanotube morphology by adjusting the anodization
conditions.[11]The influence of the
most important anodization parameters (anodization
voltage, time of anodization, and electrolyte composition and temperature)
on the morphology of TiO2 nanotubes has been well investigated.[12,13] At the same time, the process of nanotube growth during anodic oxidation
is well-known. Water in the electrolyte oxidizes Ti to form TiO2. In order to grow nanotubes rather than a compact TiO2 film, fluoride must be present in the electrolyte. It participates
in the TiO2 etching process and in the complexation of
titanium cations at the oxide/electrolyte interface.[14] This knowledge enables the synthesis of an immobilized
TiO2 photocatalyst with specific morphological characteristics,
which can be used for various applications.[15,16] However, in order for the anodic oxidation of titanium to be used
for the industrial production of TiO2 nanotube films, a
comprehensive understanding of the changes in the electrolyte’s
composition during the anodization process is needed.Recently,
there were a few studies pointing out the lack of reproducibility
of the anodization process when titanium metal is repeatedly anodized
in a fluoride-containing electrolyte solution. Lee et al. focused
on the influence of the electrolyte’s conductivity on the formation
of TiO2 nanotube films in a HF-based ethylene glycol electrolyte.[17] The authors tested the resulting anodic films
as anodes for dye-sensitized solar cells. Two other research groups
have studied the influence of electrolyte aging on the nanotube length
and diameter.[18,19] The anodization electrolyte used
in both studies was prepared with ethylene glycol, ammonium fluoride,
and water. The study by Gulati et al.[19] focused on the anodization of curved titanium surfaces, whereas
the study by Sopha et al.[18] determined
the influence of electrolyte aging on the anodization of flat titanium
foils. In the latter study, an adhesion analysis of the anodized nanotube
film was also carried out.Most of the studies reported in the
literature focused primarily
on the influence of the electrolyte’s aging on the morphological
changes to the TiO2 nanotube films. It has been reported
that the anodization electrolyte has to be preanodized in order to
prevent the TiO2 nanotube film’s delamination from
the substrate, thus improving its mechanical stability.[8] However, the range of electrolyte compositions
that allows the synthesis of high-quality immobilized TiO2 films in a reproducible way has not been yet reported and the electrolyte’s
aging was not linked to the application-related properties of the
grown TiO2 films.In the present work, the influence
of the anodization electrolyte’s
aging on its composition was studied. The aging was determined by
the number of hours during which the electrolyte was used for anodization.
Furthermore, the influence of the changes in the electrolyte’s
composition on the photocatalytic activity of annealed TiO2 nanotubes was determined using caffeine as a model degradation molecule.
During the anodization, the current–time curves and the electrolyte
temperature were recorded. After the anodization, the electrolyte’s
conductivity was measured and the fluoride and water contents were
accurately determined. To the best of our knowledge, the free-fluoride
content in an anodization electrolyte that has been used for various
times has not been measured and reported before. Additionally, the
concentration of negative ions in an annealed TiO2 film
up to a depth of 250 nm was also measured, which is essential for
explaining the photocatalytic activity of the anodized films.
Experimental Section
Anodic Oxidation of Titanium
Discs
Highly ordered TiO2 nanotube films were
grown in a well-defined
anodization setup shown in Figure . Titanium foils (200 μm thick, 99.8%, Baoji
Lyne Metals Co., Ltd.) were first laser cut into discs with a diameter
of 98.5 mm. The foils were then cleaned in acetone in an ultrasonic
bath, rinsed with ethanol, and dried under a stream of nitrogen. After
cleaning, the discs were anodized at a constant potential of 60 V
for 6 h in an ethylene glycol electrolyte with 0.3 wt % of ammoniumfluoride (99.99%, Sigma-Aldrich) and 2 vol % of deionized water. The
total volume of the anodization electrolyte at the beginning of the
experiments was 2 L. The area of the titanium disc exposed to the
electrolyte was fixed at approximately 50 cm2; the part
of the titanium disc that was exposed to the electrolyte had a diameter
of approximately 80 mm. The distance between the titanium anode and
the stainless-steel cathode with a surface area of 210 cm2 was kept constant at 90 mm. There was one anodization a day, and
the total number of anodized discs was 20. During each anodization
the current–time curve was measured and the electrolyte temperature
was monitored throughout the entire procedure. During this time the
anodization cell was covered with a lid to minimize the absorption
of water from the surrounding air and sealed immediately after the
anodization. The as-anodized amorphous titanium discs were washed
with deionized water and ethanol and annealed at 450 °C for 1
h in air (heating and cooling at 5 °C min–1).
Figure 1
Anodization setup in which 20 sequential anodizations were performed.
The area of the anodized titanium disc was approximately 50 cm2, whereas the area of the stainless-steel cathode immersed
into the electrolyte solution was approximately 210 cm2. The titanium anode was connected to the positive electric potential
while the cathode was connected to the negative one (b). The circle
on the back of the anodization cell (a) shows the position of the
temperature sensor.
Anodization setup in which 20 sequential anodizations were performed.
The area of the anodized titanium disc was approximately 50 cm2, whereas the area of the stainless-steel cathode immersed
into the electrolyte solution was approximately 210 cm2. The titanium anode was connected to the positive electric potential
while the cathode was connected to the negative one (b). The circle
on the back of the anodization cell (a) shows the position of the
temperature sensor.
Characterization
of the Anodization Electrolyte
The electrolyte was characterized
after each anodization in terms
of conductivity and chemical composition. The electrolyte’s
conductivity was measured with a ProLine Plus M330 conductivity meter
immediately after each anodization. The electrolyte’s pH was
measured before the first and after the last anodization using a benchtop
pH meter (Mettler Toledo). The electrolyte samples with a volume of
1 mL were withdrawn before the start of the next anodization when
the electrolyte composition reached a steady state (i.e., it was homogeneous
throughout the entire volume). The fluoride, ammonia and water contents
were determined in corresponding aliquots of the electrolyte sample.
A Metrohm model 906 Titrando analyzer and a combined fluoride-ion
selective electrode (Thermo Orion, model 9609) were used for the potentiometric
determination of the fluoride using the standard addition method with
the subtraction of a blank value.[20] The
content of water was determined by Karl Fischer titration using a
double platinum electrode (ISKRA HEP 0701) and an ISKRA voltmeter
(Iskra pH–meter MA 5740).[21] The
ammonia content was determined spectrophotometrically using a HACH
DR/2010 spectrophotometer.
Characterization of the
Anodized Films
The morphological characterization of the
anodized titanium discs
was carried out in a field-emission scanning electron microscope (FSEM)
(Jeol JSM-7600F). The lengths of the nanotubes were estimated from
5 cross-section cuts of the nanotubes of each sample. The structure
of TiO2 films was characterized with X-ray diffraction
(D5000 Bruker AXS diffractometer with Cu–Kα radiation;
λ = 1.5406 Å) and the surface composition was analyzed
with X-ray photoelectron spectroscopy (XPS) on a PHI-TFA XPS spectrometer
(Physical Electronics Inc.) equipped with Al-monochromatic source
of X-rays. Additionally, surface composition was evaluated by time
of flight secondary ion mass spectrometry (ToF SIMS). Mass spectra
of positive and negative secondary ions emitted from the surface were
acquired by ToF SIMS 5 instrument (ION TOF) using Bi+ ion
beam of 30 keV for spectra excitation and Cs+ ion beam
at 2 keV for ion sputtering during depth profile analyses. SIMS spectra
were collected during depth profile analyses from the surface to the
depth of 250 nm. Integral of specific fragments in SIMS spectra (F–, OH–, TiO–, O2–) were calculated and compared.
Photocatalytic Degradation of Caffeine
The photocatalytic
efficiency of the TiO2 nanotube arrays
was investigated by measuring the degradation of caffeine ((≥99.0%
HPLC grade, Sigma-Aldrich) with an initial concentration of approximately
50 mg L–1. The annealed discs were placed in a Petri
dish with 50 mL of the initialcaffeine solution and illuminated in
a sterilizer (Kambič I-265 CK UV) for 3 h. A sample with a
volume of 200 μL was collected after 30 min in the dark and
then four times during the illumination time. The experimental setup
was evaluated before the photocatalytic degradation tests were made.
No concentration gradients were detected despite static experimental
conditions being used. The results were also not influenced by the
sample-collection location. All the samples were analyzed in a high-precision
UV–vis-IR spectrophotometer.
Results
and Discussion
Monitoring the Anodization
Process
The anodic oxidation of the titanium was monitored
by measuring the
electrical current density, temperature, and electrical conductivity
of the electrolyte during the anodization. Additionally, the pH of
the electrolyte was measured at the beginning of the anodization experiments
and after the last anodization. All these parameters greatly influence
the growth of the TiO2 nanotubes, their morphology, and
properties. Figure shows current density vs time curves during the first 30 min of
the anodization of the titanium discs in electrolytes of different
ages: 0, 24, 72, and 114 h. The inset in Figure shows the current–time plot for the
entire 6 h anodization period together with the average electrolyte
temperature during the anodizations. It is evident that the current
density drops when the electrolyte is aging after subsequent anodizations.
The average current density during the first anodization was more
than three times higher than during the 20th (136 mA cm–2 compared to 42 mA cm–2). The changes in the current
density are the result of changes to the electrolyte’s composition.
The steady-state current density increases with an increasing fluoride
concentration, which strongly influences the morphology of the TiO2 nanotubes, since the higher the average current density,
the thicker the TiO2 film. In a certain range, the film
thickness affects its photocatalytic activity. Like the current density,
the temperature of the electrolyte during the anodization can strongly
influence the morphology of the grown TiO2 film.[17] The electrolyte’s temperature increases
only slightly during anodization, which can increase the current density.
However, to what extent does the temperature rise depend on the anodization
conditions (especially the applied voltage), the dimensions of the
anodization cell (they determine the volume of the electrolyte) and
the size (exposed surface area) of the electrodes. In our anodization
system there was only slight change in temperature during anodization,
and the average electrolyte temperature of the individual anodizations
did not differ much (the lowest average temperature was 20.3 °C
for the first anodization and the highest 25.7 °C in the 13th
anodization), and this did not significantly affect the morphology
and photocatalytic properties of the films.
Figure 2
Current density vs time
measured at the beginning of the anodization
of the titanium discs in different aged electrolytes (1st, 5th, 13th,
and 20th anodization). (inset) Current density vs time during the
entire anodization period, together with average temperature of the
anodization electrolyte.
Current density vs time
measured at the beginning of the anodization
of the titanium discs in different aged electrolytes (1st, 5th, 13th,
and 20th anodization). (inset) Current density vs time during the
entire anodization period, together with average temperature of the
anodization electrolyte.The electrical conductivity
of the electrolyte decreased with the
increasing number of anodizations (Figure ), which is due to the consumption of F– ions and NH4+ ions during the
anodization process. Fluoride ions have two main effects on the oxide-formation
process. First, they form water-soluble [TiF6]2– ions and prevent the formation of hydroxide. Second, they etch the
formed TiO2 so that a nanotubular layer is formed instead
of a compact one.[14] Since the fluoride
ions induce the chemical dissolution reaction and possess a small
ionic radius, a small fraction of fluoride ions can be incorporated
into the amorphous TiO2.[22,23]
Figure 3
Conductivity
of anodization electrolyte measured immediately after
the anodic oxidation of samples 5, 13, and 20 and of the starting
electrolyte (sample 0).
Conductivity
of anodization electrolyte measured immediately after
the anodic oxidation of samples 5, 13, and 20 and of the starting
electrolyte (sample 0).The as-grown TiO2 nanotubes are mostly amorphous and
have to be transformed to the anatase crystalline phase in order to
be photocatalytically active. During annealing in air above 280 °C,
most of the fluoride is removed in the form of HF from the TiO2 film.[22] The remaining fluoride
was measured with the ToF SIMS analysis of the annealed film; however,
it was determined that it is almost completely removed in the case
of annealing at 700 °C.[24] The concentration
of ammonium ions also influences the morphology of the TiO2 nanotubes.[25] They are consumed during
the anodization process due to the formation of the (NH4)2TiF6 salt,[26] followed
by the formation of ammonia (NH3), which is volatile under
alkaline conditions (eq ). The pH of the unused electrolyte was 5.5 ± 0.3, whereas the
pH of the electrolyte used for 20 anodizations was 8.5 ± 0.4,
due to the formation of ammonia and the electrolysis of the water
on the cathode, according to the following equationIt has been reported
that the pH of the electrolyte influences
the structure, morphology, and photoresponse of the TiO2 nanotube arrays.[27,28] The current density during anodization
is higher when it is performed in an acidic electrolyte. This results
in a thicker and denser oxide film.[29] The
change in the electrical conductivity is most noticeable after the
first anodization, since it decreases from 668 mS cm–1 (measured before the first anodization) to 561 mS cm–1 (measured after the second anodization), then it decreases very
slowly. It was observed that the concentrations of NH4+ and F– ions are not the only ones that
influence the electrolyte’s conductivity. The compounds that
are formed during the anodization process also play an important role,
since the Ti and F ions form salts. The electrolyte’s conductivity
influences the current density during the anodization and thus the
growth rate of the TiO2 nanotubes and their properties.
Our results for the electrolyte’s conductivity are in accordance
with some authors;[19,30] however, not all the authors
found that with an increasing number of anodizations the electrolyte’s
conductivity decreases.[17,18]
Analysis
of the Anodization Electrolyte’s
Composition
The starting electrolyte that was used in the
experiments consisted of ethylene glycol with 0.3 wt % ammonium fluoride
and 2 vol % deionized water. The measurements of the electrolyte’s
composition after the anodizations showed that F– ions and NH4+ ions were consumed during each
anodization (Figure , Table ). The water
content increased over time, since ethylene glycol is relatively hygroscopic
and tends to take up water from the surrounding air.[10] The concentration of water increased by about 35%, despite
the fact that the anodization cell was covered during every anodization
and sealed in between the individual anodizations. The increase in
water content in the electrolyte causes the formation of an initial
thick compact oxide layer that also reduces the growth rate of the
TiO2 nanotubes.[31]
Figure 4
Water content
and concentration of ammonium and fluoride ions in
the anodization electrolyte used for the anodization of an increasing
number of samples. Sample 0 represents the starting electrolyte.
Table 1
Concentration of Ammonium and Fluoride
Ions, Together with the Water Content, in the Anodization Electrolyte
Used for an Increasing Number of Samples
sample
0
1
5
13
20
w(F–) [%]
0.156
0.149
0.143
0.137
0.133
c(NH4+) [mg L–1]
0.134
0.127
0.107
0.132
0.120
w(H2O) [%]
1.98
no data
no data
no data
2.65
Water content
and concentration of ammonium and fluoride ions in
the anodization electrolyte used for the anodization of an increasing
number of samples. Sample 0 represents the starting electrolyte.As shown in Table , the concentration
of F– decreases with the increasing
number of anodizations. A similar trend is observed for the concentration
of NH4+, except that the measured values fluctuate
considerably. Nevertheless, it can be concluded that NH4+ is also consumed during the anodization process, most
probably as the volatile, gaseous ammonia evaporates from the anodizing
electrolyte. Lim et. al found that uniform nanotubes can be formed
at a NH4F content of 0.25–1.0 wt %.[32] However, our results show that changes in NH4F concentration result in noticeable morphological changes to the
TiO2 film, although the NH4F concentration did
not fall below 0.25 wt %. The reason for this is the changes in the
electrolyte’s pH. At higher pH, the formation of the (NH4)2TiF6 salt is reduced, and the nanotubes’
morphologies (surface structure, pore diameter, wall thickness, length)
are altered.[29] The most noticeable changes
in the film’s general appearance began with the 17th anodization,
as two different morphologies were easily distinguished, even at very
low magnifications (Figure S1). The reason
for this could be the presence of dissolved titanium salts that disrupt
the anodization process when their concentration is too high.
Structure, Composition, and Morphology of
the TiO2 Nanotube Films
The XRD analysis of the
annealed nanotubes films showed that the films are polycrystalline
in nature and that all the peaks corresponding to the TiO2 anatase crystal structure are clearly resolved (Figure S2). The additional XRD peaks in all the spectra correspond
to the metaltitanium substrate. The visibility of the Ti peaks depends
on the thickness of the TiO2 film. The comparison of the
highest intensity peaks for the TiO2 and Ti ratios and
also the absolute TiO2 peak intensities (all the XRD spectra
were recorded under same conditions) confirm that the TiO2 film (sample 1) is the thickest and that each subsequent anatase
TiO2 film is thinner.The XPS spectra acquired from
the surface of the TiO2 films (samples 1 and 20) did not
show any major differences. Signals of Ti 2p, O 1s, and C 1s are present
in all spectra and composition of the surfaces between these TiO2 films does not differ significantly (Figure S3). The XPS valence band spectra are also similar
(Figure S4). The estimated valence band
maxima are approximately 2.9 eV for all samples. However, the ToF
SIMS analysis which is much more sensitive than XPS analysis (analyzing
the region from the surface to depth of 250 nm) of the F– content showed that sample 1 contained much less F– than sample 20 (Figure S5). This could
be due to the acidic pH of 5.5 ± 0.3 during the first anodization
and the basic pH of 8.5 ± 0.4 during the last anodizations. This
is because the acidic pH mainly causes the formation of TiF62– ions, while different oxofluorides are formed
at the basic pH. The TiF62– ions are
soluble in the anodization electrolyte in comparison with the less
soluble oxofluorides, which to a greater extent remain in the TiO2 film.Figures and 6 show the top surfaces of the
anodized titanium
discs annealed at 450 °C. SEM micrographs of one unannealed sample
are shown in Figure S6. Since unannealed
samples are amorphous, the surface does not show any distinct features
as compared to annealed samples. The photographs of the discs in Figures and 6 show the macroscopic appearance of the films, while the SEM
images reveal the morphological characteristics of their surfaces.
Four samples are shown. The results indicate that the top surfaces
of the TiO2 films vary greatly. The anodization of the
first sample resulted in nanotubes with an almost completely closed
top surface, due to the excessive etching and the “nanograss”
formation on the top surface of the sample (Figure S7). The top surface of the first sample does not show any
visible irregularities. These only appeared during and after the 17th
anodization, when there were regions that appeared polished and free
of any oxide film. These regions became more pronounced with each
subsequent anodization and are shown for sample 20. In Figure , regions A and B are clearly
distinguished even at low magnifications. The SEM micrographs of these
regions reveal that the entire sample is anodized, but the morphology
in region A differs from that in B. The morphology of the top surface
of the TiO2 film in region B is very similar to that of
sample 1. The top surface of the nanotube film is almost completely
closed. The morphology of the film in region A is not typical for
anodized titanium, as a compact spongelike oxide was formed instead
of the nanotubes. The top surfaces of samples 5 and 13 consist of
very open nanotubes with a diameter of approximately 100 nm. We found
that the anodization electrolyte’s pH has an important influence
on the morphology of the nanotube film, and it slowly increased during
the experiments. It is known from the literature that morphologically
the most uniform and consistent nanotubes are grown in a neutral electrolyte
medium,[28] which is consistent with our
results. A slightly acidic or alkaline electrolyte caused a structural
disorder of the top surface of the nanotubes, which were relatively
closed. When the pH of the electrolyte was in the neutral region,
the top surface of the nanotubes was more regular and open. This occurred
in the case of the fifth anodization.
Figure 5
Top surface of anodized titanium discs
(samples 1, 5, 13): photographs
(left column) and high-magnification SEM images (right column).
Figure 6
Top surface of anodized sample 20: photograph (left-hand
side)
and high-magnification SEM images (right-hand side). Two distinctive
areas are observed: one with the formed TiO2 nanotubes
(B) and areas where only a compact TiO2 film is present
(A).
Top surface of anodized titanium discs
(samples 1, 5, 13): photographs
(left column) and high-magnification SEM images (right column).Top surface of anodized sample 20: photograph (left-hand
side)
and high-magnification SEM images (right-hand side). Two distinctive
areas are observed: one with the formed TiO2 nanotubes
(B) and areas where only a compact TiO2 film is present
(A).
Caffeine
Degradation
The photocatalytic
activity of the TiO2 nanotube arrays was determined by
measuring the degradation of caffeine. Figure shows the degradation of caffeine using
four different samples after different reaction times. The same figure
also shows the length of the TiO2 nanotubes for all four
samples. The length of nanotubes was measured from cross-sectional
SEM images (Figure S8).
Figure 7
Photocatalytic degradation
of caffeine using anodized titanium
discs (samples 1, 5, 13, and 20). The average TiO2 nanotube
film thickness (dots and the legend on the right-hand y-axis) is also shown for these samples.
Photocatalytic degradation
of caffeine using anodized titanium
discs (samples 1, 5, 13, and 20). The average TiO2 nanotube
film thickness (dots and the legend on the right-hand y-axis) is also shown for these samples.Samples 1 and 5 show similar activity, i.e., a degradation of approximately
60% of the initial caffeine during a UV illumination period of 3 h.
Samples 13 and 20 have a poorer photocatalytic performance. Both samples
achieved a degradation of approximately 44% of the caffeine after
the longest reaction time. In order to better describe the achieved
caffeine conversions, the photonic efficiencies (ξ) and initial
reaction rates (Ri) were calculated using
the equations described by Krivec et al.[10] Photonic efficiency is defined as the number of transformed reactant
molecules divided by the number of incident photons of monochromatic
light. It was calculated with eq , while the initial reaction rate was calculated from eq .Δc is the difference
in caffeine concentration in reaction time Δt. V is the volume of the caffeine solution, A is the geometric surface area, and I0 is photon flux. It is calculated from UV light intensity I (1.097 mW cm–1 during our experiments),
wavelength of UV light λ, Avogadros constant Na, Planck constant h, and the speed of
light c. The best photonic efficiency was approximately
0.43%, achieved with sample 5. The largest number of incident photons
was lost during the photocatalytic reaction on the surface of sample
20, whose photonic efficiency was approximately 0.31%. The initial
reaction rates followed the same order. The best achieved Ri was approximately 0.014 × 10–6 mol L–1 s–1. The photonic efficiencies
and the initial reaction rates of samples 1, 5, 13, and 20 are shown
in the Supporting Information (Figure S9). It is known from the literature that the photocatalytic activity
is influenced by the morphology and the length of the TiO2 nanotubes, whereby the photodegradation efficiency is improved with
increasing lengths of the nanotubes, due to higher surface area and
the increased light absorption.[33] However,
the photocatalytic activity is enhanced only to a certain extent,
since there exists a limited penetration depth of UV light.[34] The longer nanotubes have thinner walls and
greater volumes in the upper part of the tubes, meaning that the UV
light has to travel on a longer pathway before absorption and the
production of electron–hole pairs.[35] According to the data in the literature, many authors observed that
the best photocatalytic results were obtained with TiO2 nanotubes of different lengths. The following optimum nanotube lengths
were reported: 2.2,[34] 4.8,[33] and 7 μm.[35] Irrespective
of all the literature data, our results show that the length of the
nanotubes, when comparing samples that were anodized with different
ages of electrolytes, is not the decisive parameter in determining
the photocatalytic activity of the TiO2 films. The reason
why the thickness of the TiO2 film does not significantly
influence its photocatalytic activity is that our thinnest film (measured
for sample 20) already has had a thickness of approximately 15 μm,
which is more than the most often reported optimum thickness for the
nanotube films. The longest TiO2 nanotubes were grown during
the first anodization, when the electrolyte was still fresh and its
conductivity was the highest. The length of the nanotubes after 6
h of anodization was approximately 40 μm. Our findings regarding
the effect of the nanotubes’ morphology and length on their
photocatalytic activity are in accordance with a study conducted by
Mabiala Masiala et al. using H2SO4- and NaOH-based
anodization electrolytes. Those authors reported that anodization
in acid electrolytes results in stable oxide films with improved adhesion
to the titanium metal substrate and an improved photoresponse.[27] Our results show a gradual decrease in the photocatalytic
efficiency with the aging of the electrolyte due to an increase of
the electrolyte’s pH. Furthermore, the differences in the intensities
of the OH–, O2–, and
TiO– signals observed from the ToF SIMS analyses
of samples 1 and 20 (Figure ) also explain the differences in the photocatalytic activities
of all the samples. The signal intensities of all three negative ionic
fragments follow the same trend as the photocatalytic efficiencies
of the samples. The intensities observed for sample 1 are higher than
for sample 20. The obtained results are in accordance with the literature
data. Since the photocatalytic oxidation of caffeine proceeds via
hydroxyl radicals,[36] the concentration
of the surface OH– greatly influences the activity
of the catalyst. In sample 20, the concentration of the surface OH– is reduced due to the fluoride-exchange. It can be
seen in Figure S3 that the amount of F– in the nanotube films increases after the first anodization.
The difference in the intensity of the TiO– and
O2– species does not play a role in the
photocatalytic reactions. Due to the bombardment of the primary ion
beam of bismuth during the ToF SIMS analysis, there is a desorption
of TiO– and O2– species
originating from the TiO2 structure. However, some of the
oxygen (O2–) could also represent the
oxygen adsorbed as superoxo which plays an important role in the catalytic
oxidation reactions.[37]
Figure 8
Integrals of SIMS signals
of OH–, O2–, and TiO– ions over a depth
of 250 nm for samples 1 and 20. Regions A and B of sample 20 were
analyzed.
Integrals of SIMS signals
of OH–, O2–, and TiO– ions over a depth
of 250 nm for samples 1 and 20. Regions A and B of sample 20 were
analyzed.Figure summarizes
the results and correlates the changes in the electrolyte composition
due to repeated anodizations with the growth of the TiO2 nanotubes and their photocatalytic activity. It can be concluded
that changes in the electrolyte’s composition negatively affect
the growth rate of the nanotubes and their photocatalytic properties.
The electrolyte’s pH is gradually increasing, which plays a
very important role.
Figure 9
Effect of repeated anodic oxidations in the same electrolyte
on
the anodization electrolyte’s composition and conductivity,
as well as on the growth rate and photocatalytic activity of the grown
TiO2 nanotubes.
Effect of repeated anodic oxidations in the same electrolyte
on
the anodization electrolyte’s composition and conductivity,
as well as on the growth rate and photocatalytic activity of the grown
TiO2 nanotubes.
Conclusions
We studied the influence of an
anodization electrolyte’s
aging after sequential anodizations with respect to the morphology,
structure, composition, and photocatalytic activity of TiO2 nanotube films. Twenty titanium foils were anodized in the same
electrolyte to grow rigidly attached TiO2 nanotube films.
The samples were then annealed to transform the amorphous TiO2 to the anatase structure. As a general rule, it was found
that with each subsequent anodization the length of the TiO2 nanotubes gradually decreased, as did the corresponding photocatalytic
activities of the formed TiO2 films. A microstructural
characterization further revealed that the last anodized discs, apart
from the areas of formed TiO2 nanotubes, also contained
areas where only a compact TiO2 film was present. The electrolyte’s
aging was monitored by analyzing its chemical composition after each
anodization and by measuring the current density and the temperature
during the anodization, as well as the conductivity and pH of the
electrolyte. It was determined that the conductivity of the electrolyte
was decreasing with each anodization, while the pH value was increasing.
Although the concentration of F– in the electrolyte
after each subsequent anodization did not change significantly, an
integrated ToF SIMS signal over a depth of 250 nm showed that the
F– ions did incorporate into the TiO2 films and that the concentration of F– in the
last anodized disc was approximately three times higher than for the
first disc (Figure S3). On the other hand,
the concentration of OH– and O2– in the annealed TiO2 films showed the opposite trend.
It was concluded that a reduced concentration of OH– and O2– species at the TiO2 surface was the main factor responsible for the reduced photocatalytic
activity of the TiO2 films after successive anodizations
and that the decreased length of the TiO2 nanotubes after
each anodization does not have a significant effect on the photocatalytic
activity of the TiO2 films. Moreover, the length of the
TiO2 nanotubes is primarily governed by the current density,
which is a consequence of the electrolyte’s conductivity. Our
results also suggest that batch-type anodization cells cannot yield
reproducible TiO2 nanotube films due to aging of the anodization
electrolyte and that a continuous regeneration of the anodization
electrolyte is needed to obtain TiO2 films with comparable
photocatalytic activities.
Authors: Ilza Dalmázio; Leonardo S Santos; Renata P Lopes; Marcos N Eberlin; Rodinei Augusti Journal: Environ Sci Technol Date: 2005-08-15 Impact factor: 9.028