Wenjuan Liab,
Robert Liangbc,
Anming Hubd,
Zhaohui Huanga and
Y. Norman Zhou*bc
aSchool of Materials Science and Technology, China University of Geosciences, Beijing 100083, P.R. China
bDepartment of Mechanical and Mechatronics, University of Waterloo, Waterloo N2L 3G1, Ontario, Canada. E-mail: nzhou@uwaterloo.ca; Tel: +1-519-888-4567 ext. 36095
cWaterloo Institute for Nanotechnology, University of Waterloo, Waterloo, ON N2L 3G1, Ontario, Canada
dMechanical, Aerospace, & Biomedical Engineering Department, University of Tennessee – Knoxville, Knoxville, TN 37996-2210, USA
First published on 6th August 2014
A facile and efficient way of generating oxygen vacancies in visible light activated one-dimensional iodine doped TiO2 photocatalysts was first reported in this work. A two-step hydrothermal synthesis was used to synthesize TiO2 nanomaterials modified by iodic acid (HIO3) as a dopant. Detailed analysis was conducted to illustrate the intrinsic doping/reaction mechanisms of iodic acid in the modification of the TiO2 matrix. The phase and structure evolution were deduced from X-ray diffraction (XRD), Raman, and scanning electron microscopy (SEM). X-ray photoelectron spectroscopy (XPS) was conducted to analyze the generation of oxygen vacancies and the formation of I–O–Ti bonds in the TiO2 lattice. Multi-valences of iodine, due to the reduction of iodic acid, facilitated the generation of oxygen vacancies and 3d state Ti3+ species in the TiO2 lattice. The visible light absorption and enhanced photocatalytic activity of the TiO2 nanomaterials were attributed to existing oxygen vacancies, iodine multi-valences in I–O–Ti bonds, and 3d state Ti3+ sites in the TiO2 lattice. The photocatalytic degradation efficiency under visible light (λ > 400 nm) followed a pseudo first-order kinetic model. Rutile nanowires using a two-step synthesis method produced the highest methylene blue (10 mg L−1) degradation rate constant, Kap, of 7.92 × 10−3 min−1 compared to other synthesized nanomaterials. The Kap value obtained was an order of magnitude greater than commercial P25 (3.87 × 10−4 min−1) and pristine TiO2 nanowires (4.18 × 10−4 min−1). The iodine doped TiO2 photocatalysts can be used in TiO2/light irradiation advanced oxidation processes (AOPs) in water treatment using sunlight or a visible light source, rather than an ultraviolet irradiation source.
Over the past few decades, research work has been done aiming at expanding photoabsorption to the visible light region and enhancing the photocatalytic activities of TiO2 by doping either non-metal (N,9–11 C,12–14 S,15 I,16–19) or metal atoms (Fe,20 Ag,21 Mo,22 Cu,23 Au
24). Among these modifications, non-metal doped TiO2 materials exhibit promising visible driven photocatalytic activities compared to pristine or other metal doped TiO2 materials. The band gap modification using non-metals does not create recombination centers that occur with metal doping.11
Iodine has also been extensively used for visible light activated TiO2 photocatalysts with multiple chemical states of iodine. The different chemical states of iodine in TiO2 dramatically affect their photocatalytic activity.16–19 Iodine doping and surface modification may also induce oxygen vacancies and oxygen sub-stoichiometry, which lowers the bandgap of photocatalysts.25–27 Oxygen defects, which lie close to the conduction band (CB) of titania, can act as active electron traps. Electrons and holes can be promoted to the surface by visible light absorption where they are involved in degradation of pollutant.26 TiO2 with a high oxygen deficiency may possess visible-light absorption and photocatalytic activities under the irradiation of light wavelengths longer than 400 nm, and the overlap between the oxygen defect states and titania CB states leads to a band gap decrease.27
A facile and effective way of generating oxygen vacancies in one-dimensional TiO2 photocatalysts through iodine modification was first reported in this work. The enhanced visible activated iodine modified TiO2 nanomaterials were obtained via simple two-step hydrothermal synthesis. The products were characterized by X-ray diffraction (XRD), Raman spectroscopy, Scanning electron microscopy (SEM) characterization, X-ray photoelectron spectroscopy (XPS) and UV-Vis diffuse reflectance spectra (UV-DRS). The nature of the extended absorption edge, visible light driven photocatalytic activity, and microstructures in iodine modified TiO2 were investigated in terms of both phase evolution and surface/bulk oxygen defects. The chemical reactions of iodine (HIO3) and its doping mechanisms along with detailed XPS analysis on the generation of Ti3+ sites, I–O–Ti bonds, and oxygen vacancies were revealed. The formation of I–O–Ti bonds substitution via I5+ substitution with Ti4+ was also discussed.
:
I = 1
:
0.5) into the solution; then the fully mixed solution was transferred into a Teflon-lined stainless steel autoclave. The autoclave was placed in a furnace where the temperature was set to 150 °C or 250 °C for 24 hours. The resultant white precipitate was washed multiple times with MilliQ water (resistivity: 18.2 Ω cm) to remove excess ions. The wet powder was then filtered and dried in an oven at 80 °C overnight. The dried powder was calcined at 450 °C for 2 h in a furnace to obtain iodine modified TiO2. The prepared samples were labelled as 1-I/TiO2-150 and 1-I/TiO2-250 denoting the temperatures that the nanomaterials were synthesized. For comparison, a reference sample of pristine TiO2 nanowires (NWs) were hydrothermally synthesized following the same procedure at 260 °C except without the addition of iodic acid. The dried products were calcined at a temperature of 700 °C to improve the crystallinity of anatase.8
:
I = 1
:
0.5) was added into a solution containing 10 M NaOH alkaline solution and pristine TiO2 NWs produced in the first step. The mixed solution was transferred to an autoclave and heated at 150 °C or 250 °C. The samples were dried at 80 °C overnight and a post-calcination was employed at 450 °C to obtain samples of 2-I/TiO2-150, 2-I/TiO2-250, respectively.The visible light photocatalytic activity of the prepared samples was studied by the photodegradation of methylene blue (MB) in aqueous solution. In a typical experiment, 20 mg of prepared TiO2 photocatalysts were dispersed into 50 mL of MB solution (0.03 mM). Before illumination, the suspension was kept in the dark at room temperature by magnetic stirring for 60 min. Photocatalytic degradation was assessed in the presence or absence of simulated visible light irradiation provided by a 150 W Xenon lamp (Newport, USA) equipped with a 400 nm cut-off filter (Thorlabs, USA). The irradiance was 4.4 W m−2 at 0.2 m from the end of the collimating column. During the photoreaction process, aliquots of 5 mL were collected at specific time points. The collected aliquots were centrifuged at 3000 rpm to remove remaining photocatalysts and the concentration of MB was determined by UV-Vis spectroscopy at 663 nm using a standardized calibration curve.
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| Fig. 1 X-ray diffraction spectra of as prepared (a) Pristine TiO2 NWs, (b) 1-I/TiO2-150, and (c) 1-I/TiO2-250. | ||
Raman analysis (Fig. 2) was also conducted to further verify the phase of the one-step samples. The peaks observed match well with the characteristic peaks of anatase12.13 at Raman shifts of 143 (E1g), 196 (E2g), 395 (B1g), 514 (A1g), 638 (E3g) cm−1, with respect to the reference sample and the iodine modified sample at 150 °C. For modified samples at 250 °C, the other observed Raman peaks at around 142 (B1g), 445 (Eg) and 609 (A1g) cm−1 are all characteristic peaks of rutile.8,28 Additionally, second-order scattering features of rutile can also be observed, with prominent shifts at 235 cm−1 and 252 cm−1 as multi-photon vibration modes.8,34 This observation is in agreement with those obtained from the X-ray diffraction data (Fig. 1). The Raman characteristic peaks for the one-step process are similar to the two-step process (Fig. S2 in ESI†).
Scanning electron microscopy (SEM) morphologies of TiO2 NWs and iodine modified TiO2 are given in Fig. 3. Fig. 3a–d depict TiO2 nanomaterial structures synthesized under a one-step process, whereas Fig. 3e and f show TiO2 nanomaterial structures synthesized under a two-step process. Fig. 3a and b represent pristine TiO2 NWs that have a width of 50–200 nm and lengths in the micron-scale. These results are similar with previous literature in which the same hydrothermal procedure was adopted.31,32 The iodine modified samples at 150 °C have a fine particle-like (Fig. 3c – one-step) and a sheet-like (Fig. 3e – two-step) morphology consisting of aggregated particles having poor crystal growth, which is shown in the XRD results. Additionally, Fig. 3d (one-step) and Fig. 3f (two-step) depict evenly distributed TiO2 rutile nanowires processed at 250 °C. These TiO2 nanowires are hundreds of nm in width and several microns in length and are bundled together. The inset image of Fig. 3d shows the rutile TiO2 nanowires at a higher magnification.
O bonds, respectively.12,13 Using a high resolution spectra, chemical states of I 3d peaks are shown in Fig. 5c, in which evidence for the doped iodine is observed. The shift of I 3d 5/3 from 622 eV for HIO3 to 620 eV may arise from the energetically favorable substitution from Ti4+ (with radius of 0.64 nm) to I5+ (with radius of 0.62 nm).16 These iodine peaks only appear in samples at 150 °C as revealed by the XPS analysis. In terms of samples prepared at 250 °C, no high resolution iodine spectrum could be observed, which could be due to the promoted decomposition of iodine oxides to vaporized I2.
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| Fig. 5 XPS spectra of (a) survey spectrum, (b) C 1s calibration curves, and (c) I 3d spectra in 1-I/TiO2-150. | ||
The oxygen (O 1s) and titanium (Ti 2p) binding regions are shown in Fig. 6. It is worth noting that the peaks of the oxygen show different chemical states with different integrated areas in different samples. The two main O 1s peaks are attributed to O2− (528.2 eV–529.5 eV) and oxygen vacancies, O* (531.1–533.5 eV).36 Deconvolution of the peaks reveals that the number of oxygen vacancies (O* in TiO2−x around 531.1 eV–533.5 eV) increases as the hydrothermal temperature increases (Table 1).
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| Fig. 6 XPS spectra of O 1s spectrum in different samples: (a) 1-I/TiO2-150, (b) 1-I/TiO2-250, (c) 2-I/TiO2-150, and (d) 2-I/TiO2-250. The inset figure corresponds to the Ti 2p spectra of each sample. | ||
| Samples | O 1s (at. %) | Ti 2p (at. %) | |||||
|---|---|---|---|---|---|---|---|
| O* (TiO2−x) | O2− (TiO2) | O* (I2O5−x) | O2− (I2O5) | Ti3+ (TiO2−x) | Ti4+ (TiO2) | Ti3+ (I–O–Ti) | |
| 1-I/TiO2-150 | 20.90 | 30.05 | 32.21 | 16.83 | 56.35 | 11.62 | 32.03 |
| 2-I/TiO2-150 | 41.70 | 21.33 | 23.94 | 13.03 | 33.29 | 19.13 | 47.58 |
| 1-I/TiO2-250 | 55.58 | 41.88 | — | 2.54 | 28.02 | 71.98 | — |
| 2-I/TiO2-250 | 64.08 | 35.92 | — | — | 39.61 | 60.39 | — |
The residual iodine was present at samples synthesized at lower temperatures (Fig. 6a and c) and XPS analysis revealed iodine oxide deconvoluted peaks at 530 eV (O2− in I2O5) and 533 eV (O* in I2O5−x); no such peaks appear in Fig. 6b and d. In addition, the O* in I2O5−x has a binding energy ranging from 532.8 eV to 533.6 eV. This indicates the formation of I–O–Ti bonds in the TiO2 matrix from the substitution of I5+ with Ti4+.18 In the inset figures of Ti 2p XPS spectrum, the two peaks at 455.6 eV and 462.8 eV correspond to the different oxidation states of Ti, which are attributed to Ti3+ (458.1 eV) and Ti4+ (463.4 eV) sites. These Ti3+ species exist from the reduction of Ti4+ by the free electrons that are left from oxygen vacancies.11,37 Table 1 illustrates the detailed atomic percentage for each chemical state. By comparing the relative contents of both Ti3+ species and Ti4+ species under both synthesis processes (one-step and two-step), Ti3+ species were found in higher concentrations at 150 °C than at 250 °C.
| Ti4+ + 2O2− ↔ O2 + Ti3+ + 3e− | (1) |
![]() | (2) |
| Ti4+ + e− → Ti3+ | (3) |
The decomposition of iodic acid (HIO3) leads to the formation of I2O5. The amorphous phase in the samples contributes to surface oxygen defects or the adsorption of iodine oxides on the surface of TiO2 crystals.33 Oxygen vacancies were generated in the lattice of TiO2, which is mainly caused by the reduction of I5+ to lower multi-valance states. During the reduction reaction of I5+, free electrons were released and oxygen vacancies were generated in the lattice of TiO2; at the same time, the free electrons participate in the reduction of Ti4+ to Ti3+ (eqn 3). At 250 °C, the decomposition and reduction process of I2O5 consumes more free electrons from oxygen atoms, which produce more oxygen vacancies in TiO2 (eqn 2); this leads to less electrons being available that contribute to the generation of Ti3+ being restricted (eqn 3). The following reactions occur to iodine acid (HIO3):16
![]() | (4) |
![]() | (5) |
| I5+ + 2e− → I3+ | (6) |
| I5+ + 10e− → 5I2↑ | (7) |
The I5+ ions can act as electron acceptors when reducing to lower multi-valance states. The efficient electron scavenging by these multi-valance iodine ions contributes to the efficient separation of electron–hole pairs.19 Additionally, increased oxygen vacancies are generated (via eqn 2) through the reducing reaction with the accompaniment of increased substitution of I5+ for Ti4+ in I–O–Ti bonds. The equilibrium reaction between Ti4+ and O2− is restricted at high temperatures of 250 °C, and less Ti3+ sites are generated; however, more oxygen vacancies (by releasing electrons for the reduction of I2O5−x) are produced inside the TiO2 lattice than the relative contents produced at 150 °C.
| ln(C0/C) = Kapt, | (8) |
The surface area of each sample was characterized by the BET method (Table 2), since it is one of the important factors that influence the photocatalytic activity. According to literature, without considering other factors such as the choice of irradiation source, electronic properties, and optical absorption, large surface area nanomaterials tend to have increased degradation efficiency because of increased adsorption capacity and higher chemical reactivity. The change in surface area affects the photoactivity of the anatase samples. The anatase nanoparticle clusters (two-step) have larger surface areas compared to the anatase nanoparticles (one-step) and the rutile nanowires.
| Samples | Phase | Morphology | Specific surface area (m2 g−1) | Band gap (eV) | Degradation rated (%) | Kapc (10−3 min−1) |
|---|---|---|---|---|---|---|
| a A = anatase.b R = rutile.c Kap = apparent constant value.d Degradation of 0.03 mM methylene blue (MB) with catalysts dosage of 0.4 g L−1 for 1.5 h under visible irradiation (λ > 400 nm). | ||||||
| P25 | Aa + Rb | Nanoparticle | 52 | 3.05 | 3.6 | 0.387 |
| Pristine TiO2 | A | Nanowire | 21.52 | 3.16 | 3.8 | 0.418 |
| 1-I/TiO2-150 | A | Nanoparticle cluster | 189.37 | 3.08 | 21.7 | 2.71 |
| 1-I/TiO2-250 | R | Nanowire | 76.53 | 2.92 | 30.6 | 4.07 |
| 2-I/TiO2-150 | A | Nano sheet cluster | 321.44 | 3.16 | 39.9 | 5.50 |
| 2-I/TiO2-250 | R | Nanowire | 55.52 | 2.92 | 50.9 | 7.92 |
Visible light absorbance and a narrower bandgap in the TiO2 matrix are important factors in determining the visible light photoactivity as well as other electronic properties of the material, such as photoconductance.38 From Table 2, the iodine modified TiO2 have their bandgaps narrowed from 3.16 eV to up to 2.92 eV when compared to pristine TiO2. The bandgap narrowing improves the visible light degradation efficiency of MB. The 2-I/TiO2-250 sample had the highest degradation rate in which the MB degradation rate reaches 50.9% after 90 minutes (Kap = 7.92 × 10−3 min−1) under visible light irradiation. One of the reasons rutile presents better visible light photodegradation of MB, compared to similarly prepared anatase is the lower bandgap of rutile nanowire than that of the anatase nanoparticle cluster. The rutile nanowire product (2-I/TiO2-250), in particular, is capable of generating more electron–hole pairs under visible light due to the creation of both the Ti3+ sites, I–O–Ti and oxygen vacancies. With the bandgap further decreased by oxygen vacancies, better visible activated catalytic performance could be expected from rutile phase. The other reason lies in that rutile phase has higher photoconductance (photoconductance is related to the photoactivity) in the visible light region within the photon energy level of the bandgap, so there is greater electron and hole generation compared to anatase, even though the photoconductance is higher in anatase over the entire UV-Vis spectrum.38
The presence of excess Ti3+ sites contributes to the visible light absorption because of the formation of the 3d orbital of the Ti3+ ions in the bandgap just below the bottom of the CB.6,10 The existence of Ti3+ can form a defect that promotes charge transfer and suppress electron–hole recombination.6,38 The 3d states of Ti3+ below CB are due to the presence of oxygen vacancies in the TiO2 lattice. Additionally, the created oxygen vacancies also act as charge carriers of holes (positive effect) and benefit the separation of electron–hole pairs.39 Oxygen vacancies can efficiently transfer photo-induced electrons to reduce the recombination of electron–hole pairs and thus benefit the visible light photocatalytic activity. The creation of oxygen vacancies induce additional acceptor states above the valence band (VB) edge of TiO2, resulting in narrowing of the bandgap.35 However, according to previous studies,11,40 high concentrations of the 3d state Ti3+ sites associated with oxygen vacancies are considered as the electron–hole recombination centers (negative effect), which can also be verified in our case of low temperature (150 °C) samples. In the case of specimens at 250 °C, there are relatively low concentrations of 3d state Ti3+ sites and high content of oxygen vacancies that act as the charge carriers or electron donors, which decrease the recombination rate of photo-induced electron–hole pairs.40 The generation of low concentrations of 3d Ti3+ sites is controllable and high oxygen vacancies is the key to the enhanced photocatalytic performance of visible sensitized TiO2 nanomaterials.
From the above deductions and in conjunction with XPS analysis, we can conclude that the chemical reaction causes the reduction of high valance iodine ions to a lower valance by consuming oxygen atoms from pristine TiO2. Oxygen vacancies can be created with the increased formation of I–O–Ti bonds by the modification of iodine. The formation of 3d Ti3+ sites and oxygen vacancies narrows the absorption bandgap of TiO2. This bandgap narrowing allows TiO2 photocatalysts to be excited under visible light irradiation and generate electron–hole pairs, most of which are trapped or react in aqueous solutions producing reactive species such as O2−, ˙OH radicals, and H2O2.11 Photo-generated electrons transfer directly into the CB with the existence of oxygen vacancies and I–O–Ti bonding in the titania matrix. Interactions of these activity species account for the efficient degradation property of MB under visible light irradiation. These nanomaterial photocatalysts can be applied to the organic degradation of pollutants for water treatment using cheap solar irradiation, instead of an ultraviolet irradiation source.
Footnote |
| † Electronic supplementary information (ESI) available. See DOI: 10.1039/c4ra04768k |
| This journal is © The Royal Society of Chemistry 2014 |