Rayhan Hossain*ab,
Jessica Hollowab,
Violet Chesterfieldab,
Daisy Langleyab and
Allen Apblett*ab
aDepartment of Natural Sciences, University of Michigan, 107 Science Faculty Center, Dearborn, MI 48128, USA. E-mail: rhossain@umich.edu; allen.apblett@okstate.edu
bDepartment of Chemistry, Oklahoma State University, 317 Physical Science, Stillwater, OK 74078, USA
First published on 4th August 2025
Anatase-phase TiO2 nanorods with diameters of approximately 3 ± 1 nm and lengths of 40 ± 10 nm were successfully synthesized using a solvothermal method, followed by metal doping through thermal diffusion of Fe2+ ions onto the nanocrystals. The dopant incorporation process led to a significant enhancement in the visible light absorption of TiO2, as observed from the red-shift in the UV-visible absorption spectra. This modification suggests a narrowing of the bandgap, making the material more suitable for photocatalytic applications under visible light. Specifically, Fe-doped TiO2 nanorods with 1.0% Fe2+ exhibited a 35% increase in photocatalytic hydrogen production under visible light illumination compared to pure TiO2. Electron microscopy and X-ray diffraction (XRD) analysis confirmed that the size and morphology of the nanocrystals remained unaffected by the doping process, retaining their anatase phase with no significant structural alteration. Additionally, UV-visible spectroscopy demonstrated a reduction in the bandgap energy of the TiO2 nanorods from 3.5 eV in pure TiO2 to a range of 3.14–3.34 eV for the Fe-doped samples. This decrease in bandgap energy is attributed to the introduction of iron ions into the TiO2 lattice, which facilitates enhanced light absorption and improved photocatalytic efficiency. The ability to precisely control the dopant concentration while preserving the structural integrity of the TiO2 nanocrystals is a key advantage of this method. The findings suggest that Fe-doped TiO2 nanorods, with their enhanced photocatalytic activity, could serve as efficient materials for various applications, including hydrogen production, solar cells, and environmental sensing. These findings highlight the potential of Fe-doped TiO2 nanorods as efficient materials for a range of clean energy technologies and environmental remediation processes.
To address this limitation and broaden its photoactive spectrum into the visible light range, various strategies have been explored, including doping TiO2 with transition metals, non-metals, and incorporating nano-structural modifications. Among these approaches, doping with transition metals, particularly iron (Fe), has garnered substantial interest. Transition metal doping introduces discrete energy states within the TiO2 bandgap, thereby lowering the material's bandgap and facilitating the absorption of photons with lower energy, thereby enabling TiO2 to be activated by visible light. This bandgap modulation not only enhances the photocatalytic efficiency of TiO2 under solar irradiation but also opens up new avenues for its application in environmental remediation, sustainable energy production, and antimicrobial treatments. The incorporation of iron (Fe) and other transition metals has demonstrated significant improvements in TiO2's photocatalytic performance, thereby expanding its potential for real-world applications in energy conversion and environmental purification under natural sunlight.15,16
Iron, being a first-row transition metal, has shown promise in tuning the electronic properties of TiO2. The successful incorporation of Fe into the TiO2 lattice modifies its electronic structure and can either enhance or inhibit the photocatalytic activity, depending on the oxidation state and doping concentration. Iron can exist in multiple oxidation states, including Fe2+ and Fe3+, with the most common form in TiO2 doping being Fe2+. Fe2+ ions substitute for Ti4+ in the lattice, generating defect states within the bandgap, facilitating the absorption of visible light.17
Furthermore, Fe doping also affects the surface properties and the ability of TiO2 to generate reactive oxygen species (ROS), which are key to its photocatalytic activity. Iron-doped TiO2 materials have shown improvements in the degradation of pollutants such as dyes, pesticides, and pharmaceuticals under visible light irradiation, a property that is invaluable for photocatalytic wastewater treatment.18–23 Additionally, Fe-doped TiO2 exhibits enhanced charge carrier separation and reduced recombination rates, which are crucial for improving the efficiency of photocatalytic reactions.24,25
Despite these advantages, the synthesis of Fe-doped TiO2 nanomaterials is highly sensitive to doping concentration, annealing conditions, and the method of preparation. Excessive doping can lead to the formation of undesirable phases, such as Fe2O3, which may reduce the photocatalytic activity. Therefore, achieving an optimal doping concentration is crucial to maximizing the photocatalytic performance of TiO2 while maintaining its stability.26
In addition to photocatalysis, Fe-doped TiO2 has been explored for other applications, such as solar cells, sensors, and magnetic materials. Due to the magnetic properties introduced by Fe, Fe-doped TiO2 also exhibits the potential for use in magnetic photocatalysis, where the material can be easily separated from the reaction medium, improving its reusability and cost-effectiveness. The combination of iron with titanium dioxide, especially in the form of nanocrystals, provides unique opportunities for the development of advanced materials that are both efficient and versatile. As such, Fe-doped TiO2 nanocrystals continue to be a subject of extensive research in the fields of material science and environmental engineering.27,28
Transition metal doping in TiO2 leads to the introduction of new energy levels in the bandgap. These energy levels can either serve as electron traps or act as intermediates for the transfer of charge carriers. Iron (Fe) has several oxidation states, with Fe2+ and Fe3+ being the most common in TiO2 doping. Fe2+ is typically incorporated into the TiO2 lattice, substituting for Ti4+, while Fe3+ may exist as an impurity or interact with oxygen vacancies within the TiO2 matrix.29
The introduction of Fe2+ into the TiO2 lattice creates defect states that are located below the conduction band. These defect states facilitate electron excitation under visible light, allowing TiO2 to absorb light in the visible spectrum rather than just the UV region.30 Additionally, Fe2+ doping can generate oxygen vacancies and enhance the mobility of photogenerated charge carriers, leading to improved photocatalytic activity. Fe3+, on the other hand, can act as an electron trap, increasing the separation of charge carriers and further enhancing the photocatalytic efficiency of Fe-doped TiO2 under visible light.31,32
Fe-doped TiO2 also benefits from the creation of oxygen vacancies, which are critical for improving photocatalytic performance. These vacancies act as active sites for photocatalytic reactions, improving the material's ability to degrade pollutants. However, excessive doping of Fe can lead to the formation of recombination centers, where the photogenerated electrons and holes recombine, reducing the overall photocatalytic efficiency. Therefore, the optimal doping concentration of Fe is crucial for maximizing the performance of TiO2.33
The physical and chemical properties of Fe-doped TiO2 are significantly altered compared to pure TiO2, influencing its photocatalytic performance and other functional characteristics. Doping TiO2 with Fe reduces the bandgap, shifting the absorption edge from the UV to the visible light region, typically between 2.4 and 2.8 eV. This reduction in bandgap enhances the material's ability to absorb visible light and, consequently, improves its photocatalytic activity under visible light irradiation. Additionally, the incorporation of Fe into the TiO2 lattice causes local distortion due to the difference in ionic radii between Ti4+ (0.605 Å) and Fe2+ (0.769 Å), leading to the formation of oxygen vacancies.34 These structural defects are essential for improving photocatalytic activity, as they provide additional active sites for reactions and enhance charge separation.
Fe-doped TiO2 nanocrystals have shown significantly improved photocatalytic performance compared to pure TiO2, particularly in the degradation of organic pollutants and dyes under visible light. This improvement is due to the reduced bandgap, the presence of defect states, and the enhanced charge carrier separation, which minimizes electron–hole recombination. Furthermore, at low doping concentrations, Fe-doped TiO2 can exhibit weak magnetic properties. This feature is valuable for applications that require magnetic separability, such as in photocatalytic water treatment, where the catalyst can be easily recovered and reused. Lastly, the creation of oxygen vacancies and defect states through Fe doping improves photocatalytic efficiency by promoting electron–hole pair generation and reducing recombination. These defects also enhance the material's ability to participate in redox reactions during photocatalysis.35
The synthesis of Fe-doped TiO2 nanocrystals involves various methods that determine the morphology, crystal structure, and doping concentration of the final product. The sol–gel method is a widely used and cost-effective technique for synthesizing Fe-doped TiO2 nanocrystals. This method offers precise control over the doping concentration and particle size by adjusting the reaction conditions. The sol–gel process involves the hydrolysis and condensation of titanium alkoxides, followed by doping with iron salts. Hydrothermal and solvothermal methods involve the use of high temperature and pressure to synthesize TiO2 nanoparticles.36,37 These techniques result in highly crystalline TiO2 with controlled particle sizes and doping levels. The solvothermal method allows for greater flexibility in terms of solvent choice, which can influence the crystallinity and morphology of the nanocrystals.
Co-precipitation is a widely employed method for doping titanium dioxide (TiO2) with transition metals, including iron. This technique involves the precipitation of TiO2 from an aqueous solution in the presence of an iron precursor, followed by thermal treatment to crystallize the TiO2 structure. The co-precipitation method is advantageous due to its simplicity and scalability, rendering it suitable for large-scale production of Fe-doped TiO2. However, for more precise control over doping levels, chemical vapor deposition (CVD) is an alternative approach, though less commonly employed due to its inherent complexity and high cost. CVD involves the deposition of titanium and iron precursors onto a heated substrate, facilitating fine control over doping concentrations and the formation of films with uniform characteristics. Despite these advantages, the method is generally less favored for large-scale synthesis owing to its technical demands and economic constraints. Additionally, ion implantation offers a physical doping strategy that allows for highly controlled depth and concentration profiles. In this technique, Fe ions are accelerated and implanted into the TiO2 surface, resulting in a shallow doping profile. Ion implantation is particularly beneficial for specialized applications requiring highly tailored doping characteristics, though its application is often restricted to advanced research settings.38–40
TiO2-based photocatalysts have long been studied for their potential in environmental remediation, but they face inherent limitations, such as low photocatalytic activity under visible light and rapid charge carrier recombination. To address these challenges, doping TiO2 with transition metals like Fe(II) has gained attention, as it can introduce semi-Fenton-like properties that enhance photocatalytic efficiency. However, this process critically depends on solution pH, and traditional Fenton processes often suffer from issues like the need for acidic conditions and the degradation of catalysts over time due to the generation of reactive oxygen species. Recent studies on photocatalysts such as Z-scheme silver iodide/tungstate binary nano photocatalysts and FeO–clinoptilolite nanoparticles have highlighted alternative approaches to improve photocatalytic activity.41,42 In our work, we design Fe(II)-doped TiO2 nanorods, which not only improve photocatalytic activity under visible light but also mitigate the pH-dependent drawbacks of the semi-Fenton process, offering enhanced stability and efficiency across a broader pH range.
Incorporating the effects of anion vacancies, particularly sulfur, nitrogen, carbon, halogen, and oxygen vacancies, has been extensively explored in the context of photocatalysis and water splitting. Numerous recent reviews, including those focusing on the boosted effects of these vacancies in photocatalytic degradation and photoelectrochemical processes, have demonstrated their significant role in enhancing photocatalytic efficiency. The introduction of vacancies, such as oxygen vacancies, can significantly alter the electronic structure, increase charge carrier separation, and improve the reactivity of the photocatalyst. For instance, vacancies in g-C3N4, especially carbon and nitrogen vacancies, have been shown to enhance photocatalytic solar water splitting, providing insights into how tailored defects can optimize the material's performance.43–46
The novelty of the present work lies in the development of a precise and methodical two-step process for doping anatase-phase, rod-shaped TiO2 nanocrystals with iron, which integrates surface metalation followed by thermal diffusion. This approach distinguishes itself from conventional doping techniques by offering unparalleled control over the dopant concentration. In contrast to existing methods that may lack such precision, this study innovatively combines the loading of metal ions onto the surface of TiO2 nanocrystals with a subsequent thermal diffusion step. This method ensures the controlled incorporation of Fe2+ ions into the TiO2 nanorods without altering their size, morphology, or crystalline structure, as evidenced by electron microscopy and powder X-ray diffraction analyses. The precise doping achieved through this process addresses a significant gap in the preparation of doped TiO2 materials, enabling tailored manipulation of visible light absorption properties and facilitating enhanced photocatalytic performance.47,48 The proposed methodology offers a robust platform for advancing TiO2-based photocatalytic applications and other domains by harnessing the enhanced material properties afforded through meticulous doping.49–53 This innovation represents a significant advancement in the field of materials science, providing new avenues for the development of high-performance TiO2-based systems.
The synthesis yielded samples of Fe-doped TiO2 nanorods with varying iron contents, including 1.5 mol%, 3.0 mol%, and 5.0 mol%, which contain both surface-bound and doped iron ions. The following section details the protocol to selectively remove the surface iron ions, leaving behind only the doped iron within the TiO2 matrix, thereby isolating the doped nanocrystals for further characterization and application.
At higher magnification, as depicted in Fig. 1, clear lattice fringes with a spacing of 0.35 nm were observed, corresponding to the {101} lattice planes (d-spacing = 0.351 nm; JCPDS file 21-1272). The nanocrystals, when viewed along the [100] zone axis, reveal the intersection of lattice fringes from the (011) and (01−1) planes, meeting at an angle of 43°, consistent with theoretical predictions. Additionally, less pronounced lattice fringes associated with the (004) planes were also discernible through fast Fourier transform (FFT) analysis, further confirming the crystalline nature of the nanorods.
The phase purity and crystallinity of both pure and doped TiO2 samples were evaluated using PXRD analysis, as illustrated in Fig. 2. The PXRD patterns of both pure and Fe-doped TiO2 consistently show the presence of the anatase phase, with no detectable peaks corresponding to additional phases associated with metal or metal oxide impurities. This confirms the retention of the anatase crystal structure. The peak at 25.3° (2θ), associated with the (101) plane of anatase-phase TiO2, further corroborates the phase identity, with observed values matching the standard reference (JCPDS file 21-1272).
After collection of PXRD data, structural refinements were performed using the Rietveld method. The analysis of the PXRD data was carried out employing the whole pattern powder fitting (WPPF) feature of the Rigaku PDXL software. The refined structural parameters for both TiO2 nanorods and iron doped TiO2 nanorods are presented in Table 1. These data provide detailed insights into the crystallographic characteristics and structural integrity of the synthesized materials.
Sample | Crystallinity | Crystallite size (Å)a (Scherrer) | Crystallite | Anatase d101 FWHM | Anatase d004 | Anatase d004 FWHM | Lattice parameter a = b (Å)b | Lattice parameter c (Å)b | Unit cell volume (Å)3 | |
---|---|---|---|---|---|---|---|---|---|---|
Size (Å)a (W–H) | Anatase d101 | |||||||||
Undoped_TiO2 | 98 | 27.87 | 27.90 | 3.538 | 2.76 | 2.481 | 0.44 | 3.734 | 9.467 | 139.4 |
0.25% Fe_dTiO2 | 100 | 32.49 | 32.34 | 3.529 | 2.56 | 2.371 | 0.56 | 3.649 | 9.544 | 138.9 |
0.5% Fe_dTiO2 | 100 | 32.41 | 32.10 | 3.521 | 2.53 | 2.369 | 0.89 | 3.834 | 9.472 | 137.4 |
1.0% Fe_dTiO2 | 98 | 32.12 | 31.98 | 3.516 | 2.69 | 2.359 | 0.74 | 3.894 | 9.646 | 138.4 |
1.5% Fe_dTiO2 | 99 | 31.42 | 31.35 | 3.512 | 2.59 | 2.344 | 0.64 | 3.414 | 9.498 | 137.7 |
2.5% Fe_dTiO2 | 100 | 33.69 | 32.20 | 3.509 | 2.68 | 2.336 | 0.45 | 3.810 | 9.483 | 136.9 |
3.0% Fe_dTiO2 | 98 | 32.29 | 32.15 | 3.507 | 2.48 | 2.324 | 0.49 | 3.829 | 9.474 | 138.9 |
5.0% Fe_dTiO2 | 99 | 32.94 | 32.60 | 3.504 | 2.67 | 2.314 | 0.94 | 3.624 | 9.464 | 140.4 |
In addition to the Rietveld refinement, we also estimated the crystallite size of the final catalyst using two common methods: the Scherrer equation and the Williamson–Hall (W–H) model. Both models provide complementary information, allowing us to evaluate the effects of size and strain on the crystallites. The comparison of crystallite sizes derived from both models reveals that while the Scherrer equation provides an estimate of the size assuming no strain effects, the W–H model accounts for strain, which can significantly affect the peak broadening, especially at higher dopant concentrations. For instance, the crystallite sizes obtained using the Scherrer equation were slightly larger than those obtained from the W–H model, indicating the influence of strain in the doped samples. The microstrain values were found to be higher in Fe-doped samples, reflecting the distortion of the crystal lattice due to the incorporation of Fe2+ ions.
The lattice parameters were determined using the (WPPF) method, while crystallite sizes were evaluated through the Williamson–Hall approach. The samples exhibit a high degree of crystallinity, ranging from 97% to 100%, with crystallite sizes spanning 27 to 34 Å. Analysis of the d-spacing for the (101) and (004) facets reveal a reduction in d-spacing with increasing iron dopant concentration. This trend is also evident in the unit cell parameters. The observed decrease in both d-spacing and unit cell dimensions suggests that the incorporation of Fe2+ ions is accompanied by the removal of Ti4+ and O2− ions, thereby maintaining charge neutrality within the nanocrystalline structure. Fluctuations in the cell volume, however, do not exhibit a clear trend, which may be attributed to the presence of mixed oxidation states of Fe, further complicating the structural behavior.
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Fig. 3 UV-visible absorption spectra of (A) synthesized TiO2 and (B) 1.5% Fe(doped)2+–TiO2 nanorods dispersed in hexane. |
Furthermore, a distinct absorption feature centered around 400 nm emerges in the spectra of iron doped TiO2 samples. This extended absorption in the visible region can be attributed to the excitation of 3d electrons from the iron dopant ions to the conduction band, corresponding to the energy levels of the Fe ions, which suggests a metal-to-conduction band charge transfer (MCT) process. The O 2p → Ti 3d ligand-to-metal charge transfer (LMCT) transition continues to dominate the absorption below 350 nm, contributing significantly to the strong ultraviolet absorbance observed. Notably, the absorption feature associated with the iron dopant states exhibits greater intensity compared to the d–d transition originating from Fe2+ ions, underscoring the enhanced optical response due to the iron doping.
The SEM and EDS analyses reveal consistent morphological patterns, suggesting a homogeneous distribution of elements within the particles. Ti Kα mapping indicates a uniform spatial distribution of titanium (Ti) throughout the sample, while Fe Kα analysis confirms the even dispersion of iron (Fe) within the sample. Notably, there are no regions exhibiting significant variation in the concentration of Fe, further supporting the uniformity of the elemental distribution.
The elemental composition of the Fe(doped)2+–TiO2 samples was measured by EDS. EDS spectra of doped samples (comparatively larger ionic radii metal dopant Ti4+ = 0.605 Å; Fe2+ = 0.769 Å) displayed no apparent signals directly related to metal dopants. These results indicate that the incorporation of metal ions into the TiO2 lattice was promising.
According to the theoretical model, both Fe3+ and Fe2+ ions were present within the lattice of the 1.5% Fe–TiO2 sample. The ionic radius of Fe3+ (0.645 Å) is comparable to that of Ti4+ (0.605 Å), facilitating the incorporation of Fe3+ into the TiO2 lattice, thereby forming Ti–O–Fe bonds. It is plausible that the XPS technique primarily detected Fe2+ due to the reduction of Fe3+ to Fe2+ during the XPS measurement, which occurs under the vacuum conditions commonly used in such analyses.
The coexistence of Fe(II) and Fe(III) species is critical in influencing the photocatalytic behavior of Fe-doped TiO2. Fe3+ ions, with an ionic radius similar to Ti4+, can substitute into the TiO2 lattice and contribute to the formation of Ti–O–Fe linkages, which are known to facilitate charge carrier transport. Additionally, the redox couple Fe3+/Fe2+ may engage in reversible electron exchange processes under light irradiation. Specifically, Fe3+ can act as an efficient electron trap, accepting photogenerated electrons and subsequently reducing to Fe2+. This can then be reoxidized by surface-adsorbed oxygen or reactive species, thus promoting continuous electron shuttling and suppressing charge recombination.
Moreover, Fe2+ species themselves may also serve as temporary electron reservoirs, extending the lifetime of conduction band electrons. The synergistic behavior of both oxidation states enhances charge separation and transfer dynamics, ultimately boosting photocatalytic efficiency. It is worth noting that the relatively higher signal of Fe2+ observed in our XPS data may also be partially attributed to in situ reduction of Fe3+ to Fe2+ under vacuum conditions during measurement.
In the case of TiO2 nanorods, doping with Fe leads to a marked reduction in PL emission intensity, as shown in Fig. 6. With increasing concentrations of Fe3+ ions, the PL intensity diminishes further. The Fe3+ dopants, possessing a 3d5 electron configuration, can interact with photogenerated holes, resulting in the formation of more stable Fe2+ species. This interaction suppresses the recombination process, thereby leading to a decrease in PL emission intensity. Both in the case of pure TiO2 and Fe-doped TiO2, the excitation energy exceeds the band gap of TiO2, yet the PL spectra are distinct, suggesting the presence of different energy levels in the metal's density of states. These additional energy states enable the promotion of valence band electrons to discrete states within the metal's electronic structure, depending on the excitation energy. Consequently, the excited electrons can relax back to the valence band through multiple pathways, resulting in variations in the PL emission spectra.
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Fig. 6 PL spectra of undoped and Fe(doped)2+–TiO2 nanocrystals with different dopant concentrations. PL spectra measured with the excitation wavelength at 290 nm (left) and 350 nm (right). |
This complex behavior highlights that the PL emission mechanisms in semiconductor nanorods are intricate and multifaceted. However, despite these variations, the peak positions of the PL signals remain consistent, indicating the existence of several relatively stable energy levels associated with excitons and surface states.
The PL spectra was measured with two different excitation wavelengths 290 nm and 350 nm. It is important to note that the PL emission intensity and spectral features differ between these wavelengths. Excitation at 290 nm provides more energy, which is closer to the band gap of TiO2 and leads to the generation of photogenerated carriers (electrons and holes) that interact with the material's defect states and oxygen vacancies. In contrast, excitation at 350 nm is farther from the band gap, resulting in different photogenerated carrier dynamics. These variations could highlight the influence of defect states and dopant levels on the PL emissions.
The Rayleigh scattering effect can impact the PL spectra, particularly at lower excitation wavelengths. Rayleigh scattering involves the elastic scattering of light by the particles, which could contribute to the observed PL intensity at certain wavelengths. This effect must be considered in the analysis of the PL data to distinguish between intrinsic PL signals and scattering contributions. The decrease in PL intensity with higher Fe doping concentrations might be influenced by the Rayleigh scattering effect, which could mask or alter the true intensity of recombination events. Careful consideration of this scattering effect is essential for accurate interpretation of the results.
The reduction in PL intensity observed with increasing Fe doping can also be related to the photocatalytic activity of the materials. The suppression of PL intensity suggests that Fe dopants may enhance charge separation by trapping photogenerated electrons, reducing recombination. This behavior is consistent with improved photocatalytic performance, as efficient charge separation is critical for photocatalysis. The Fe2+ species formed from the Fe3+ dopants likely act as effective charge carriers, facilitating electron transfer and enhancing photocatalytic reactions, particularly in processes like degradation of organic pollutants or water splitting.
The samples contain a weak absorption feature centered around 500–600 nm that is due to d–d transition of the surface Fe2+ centers. In addition, there is a new absorption feature centered around 400 nm. The extended absorption feature observed for the TiO2 samples doped with Fe in the visible region, can be explained by the excitation of 3d electrons of the dopant ion to the conduction band according to their respective energy levels (i.e., a metal to conduction band charge transfer).
For Fe-doped TiO2, the Tauc plot typically exhibits a well-defined linear region, which corresponds to the onset of absorption, known as the absorption edge. By extrapolating the linear portion of the plot to the x-axis (hν), the optical bandgap energy (Eg) can be extracted. The data presented (see Fig. 7) reveal a bandgap range between 3.14 eV and 3.34 eV for Fe-doped TiO2, indicating a clear narrowing of the bandgap relative to undoped TiO2. This reduction in the bandgap is attributed to the introduction of localized electronic states within the bandgap, induced by the substitutional doping of iron ions (Fe2+). These states serve as intermediate energy levels that facilitate electron transitions at lower photon energies, thereby promoting enhanced visible light absorption.
The bandgap narrowing observed in Fe-doped TiO2 is of significant interest for a range of optoelectronic applications. Specifically, the reduced bandgap renders the material more responsive to visible light, thereby enhancing its potential in photocatalysis, solar energy harvesting, and other devices that capitalize on semiconducting materials with improved light absorption properties. Consequently, Fe-doped TiO2 holds promise for advancing the performance and efficiency of next-generation energy conversion and environmental remediation technologies.
To strengthen this analysis, we considered similar methodologies reported in the literature for other doped and composite photocatalysts. Recent studies have employed various forms of the Tauc equation, choosing different values of n to explore both direct and indirect transitions in systems such as BiVO4/WO3, AgBr/g-C3N4, and CdS–PbS.54–58 Including a range of Tauc formulations, as done in those studies, enables a more nuanced understanding of the optical behavior in semiconducting materials. We have highlighted this context to guide readers on the proper selection of transition models in bandgap estimation.
Based on these sources, we have expanded the theoretical background of the Kubelka–Munk function
F(R) = (1 − R)2/2R, |
(F(R)·hν)n = A(hν − Eg), |
Fe-doped TiO2 thin films exhibit a progressive increase in resistance with increasing film thickness, following an approximately exponential trend. This behavior is attributed to enhanced electron scattering and an extended electrical conduction pathway in thicker films. The incorporation of Fe ions introduces localized energy states within the TiO2 bandgap, which facilitates carrier mobility and results in a lower resistance compared to undoped TiO2 films. Furthermore, doping with Fe improves intergranular conductivity by reducing potential barriers at grain boundaries, a feature that becomes particularly advantageous in decreasing resistance for thinner films.
Conversely, undoped TiO2 thin films display significantly higher resistance than their Fe-doped counterparts, with a more pronounced increase in resistance as film thickness increases. This trend is attributable to the intrinsic semiconducting properties of TiO2, which is characterized by a low carrier concentration and high resistivity (see Fig. 8). The absence of Fe doping leads to reduced charge carrier mobility, impeding electron transport across the film thickness and resulting in less efficient electrical conduction. The steeper increase in resistance with film thickness for undoped TiO2 reflects the lack of doping-induced enhancement of conductivity.
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Fig. 8 Resistance versus film thickness plot for thin-film samples of TiO2 and Fe-doped TiO2 on ITO-coated glass substrate. |
This plot illustrates the relationship between film thickness and resistance for undoped TiO2, 3% Fe-doped TiO2, and 1.5% Fe-doped TiO2 films. Resistance increases linearly with film thickness across all samples, which is expected because a thicker film provides a longer conduction path, increasing resistance. Among the materials, undoped TiO2 has the highest resistance due to a lack of free charge carriers, which limits its electrical conductivity. In contrast, 1.5% Fe-doped TiO2 shows the lowest resistance, indicating an optimal doping level where conductivity is maximized. The 3% Fe-doped TiO2 has an intermediate resistance, suggesting that excessive doping introduces scattering or defects, which reduce carrier mobility despite the higher carrier density.
The enhanced conductivity in Fe-doped TiO2 films is due to Fe ions acting as shallow donors, which introduce additional free electrons into the conduction band, lowering resistivity. At 1.5% doping, this effect is most pronounced, providing an optimal balance between increasing carrier density and maintaining carrier mobility. However, at 3% doping, further Fe incorporation may create more lattice distortions or defect sites, leading to scattering and reduced mobility, which partially offsets the gains in conductivity. These findings highlight the critical role of doping concentration in tailoring the electrical properties of TiO2 films. The superior performance of 1.5% Fe-doped TiO2 makes it a promising candidate for applications requiring low-resistance thin films, such as transparent electrodes, sensors, and photocatalytic devices.
The utilization of an ITO-coated glass substrate is pivotal in facilitating accurate resistance measurements. ITO provides a highly conductive foundation, thereby establishing a shorter electrical conduction path through the thin film, which is essential for reliable four-point probe measurements. In contrast, films deposited on bare glass substrates exhibit excessively high resistance, rendering such measurements impractical. The incorporation of Fe into TiO2 significantly enhances its electrical properties, rendering the material more suitable for applications that demand improved conductivity, such as optoelectronics and photocatalysis. The observed linear relationship between film thickness and resistance highlights the critical role of thickness optimization in achieving the desired electrical performance for device fabrication. The comparison presented in this analysis underscores the complex interplay between doping, film thickness, and substrate selection, providing valuable insights into the customization of thin-film properties for targeted technological applications.
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Fig. 9 Time-dependent photocatalytic hydrogen production. Rate of hydrogen generation using 200 W Xe Arc lamp as light source. |
The hydrogen generation rate appears to accelerate in the early hours (0 to 2 h), with production doubling from 8 μmol to 16 μmol. This initial rapid increase can be attributed to the early activation of the photocatalyst, where the photogenerated electron–hole pairs facilitate the reduction of protons to hydrogen. After the initial phase, the rate of hydrogen production slows down slightly, but still exhibits a consistent increase, suggesting that the catalyst remains active and efficient throughout the 6 h period.
The nearly linear trend up to 6 h may indicate that the photocatalytic process is not yet limited by factors such as reactant depletion, catalyst deactivation, or photon absorption saturation. This could suggest that the system has achieved a steady-state level of photocatalytic efficiency under the given experimental conditions.
The rate of hydrogen generation can be further analyzed using the Hinshelwood model, a concentration-dependent model often applied in photocatalytic processes. The rate constant (k-value) is a critical factor in determining the efficiency of photocatalytic reactions. When comparing the k-value for the 1.5% Fe2+-doped TiO2 nanocrystals with those reported in the literature, we can gain insights into the relative performance of our catalyst.
For example, the study on the photocatalytic degradation of dimethyldisulfide by zeolite A containing nano-CdS reported a k-value of 0.054 min−1, indicating a moderate reaction rate for the photocatalyst.59 Similarly, the co-precipitation synthesized Zn(II)/Ni(II) ferrite for the degradation of metronidazole exhibited a k-value of 0.1 min−1.60 In contrast, the degradation of sulfasalazine by Cu2O/CdS nanoparticles reported a higher k-value of 0.15 min−1.61
When we calculate the k-value for the 1.5% Fe2+-doped TiO2 system based on the observed hydrogen production rates, we find that it is approximately 0.12 min−1. This places it in a competitive range relative to the aforementioned systems, particularly when compared to the Zn(II)/Ni(II) ferrite and Cu2O/CdS systems, which exhibit slightly higher k-values. This suggests that the Fe2+-doped TiO2 catalyst performs similarly to these established systems, with the added advantage of being a more stable and easily synthesized material. Long-term stability and multi-cycle reusability of the Fe2+-doped TiO2 catalyst will be evaluated in future studies to further assess its practical applicability.
These ROS are highly reactive and play a key role in attacking and degrading the organic molecules, breaking them down into simpler, non-toxic compounds, and eventually mineralizing them into carbon dioxide (CO2) and water (H2O).
To gain mechanistic insight into the photodegradation process, we have used electron paramagnetic resonance (EPR) spectroscopy, which is particularly useful for detecting paramagnetic species like ROS. EPR can directly identify hydroxyl radicals (˙OH) and superoxide anions (O2˙−), which are crucial intermediates in the reaction. By utilizing spin-trapping agents like DMPO (which reacts with ˙OH) and TEMP (which reacts with O2˙−), we can capture stable adducts that are detectable by EPR. The resulting EPR spectra provides distinct signals that help identify and quantify these radical species in real-time during the photocatalytic reaction. The intensity of the EPR signals can be correlated with the rate of degradation, offering valuable insights into the efficiency of radical generation and the overall photocatalytic process. This additional discussion not only clarifies the mechanism behind the photodegradation but also emphasizes the importance of EPR in providing direct evidence of the reactive species involved.
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Fig. 11 BET adsorption isotherm for hydrogen, which shows the volume of gas adsorbed as a function of relative pressure (P/P0). |
The Brunauer–Emmett–Teller (BET) adsorption isotherm for hydrogen was used to determine the specific surface area of the synthesized material. The isotherm plots the volume of hydrogen gas adsorbed as a function of relative pressure (P/P0), where P is the equilibrium pressure and P0 is the saturation vapor pressure of hydrogen at the measurement temperature. In the low to mid relative pressure region (typically P/P0 ≈ 0.05–0.3), a linear relationship is observed, which is characteristic of monolayer adsorption and suitable for BET analysis. From the slope and intercept of this linear region, the BET surface area was calculated using the BET equation. The estimated surface area of the sample is approximately 498.67 m2 g−1, indicating a high surface area that is favorable for applications involving gas adsorption, catalysis, or surface-dependent reactivity.
The undoped TiO2 sample exhibits a high real impedance of approximately 50 Ω, indicating a significant resistance to charge transport within the material. In contrast, the Fe-doped TiO2 sample shows a substantially reduced real impedance, around 10 Ω, suggesting improved electrical conductivity and more efficient charge carrier mobility. The imaginary part of the impedance in both samples remains relatively low, indicating limited capacitive behavior and suggesting that charge transfer resistance dominates the overall impedance response.
The dramatic decrease in impedance upon Fe doping can be attributed to the introduction of Fe2+/Fe3+ states within the TiO2 lattice. These dopant states likely act as shallow donors, increasing free carrier density and enhancing electrical conductivity. Moreover, the incorporation of Fe ions may reduce recombination losses by facilitating charge separation and transport, consistent with prior reports on transition metal doping in metal oxides. These findings confirm that Fe doping at 1.5% significantly enhances the electronic properties of TiO2, rendering it more suitable for applications such as photocatalysis, photoelectrochemical water splitting, and optoelectronic devices.
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Fig. 13 Photocurrent decay profiles of undoped TiO2 and 1.5% Fe-doped TiO2 samples under continuous illumination. |
Both samples exhibit an initial photocurrent of ∼1.0 A at time zero, indicating comparable initial charge carrier generation upon light exposure. However, a pronounced difference in photocurrent stability is observed over the 1-second measurement interval. The undoped TiO2 sample (red curve) shows a relatively slower decay, maintaining approximately 60% of its initial photocurrent. In contrast, the 1.5% Fe-doped TiO2 sample (blue curve) exhibits a more rapid decline, retaining only about 13% of its initial value. This accelerated photocurrent decay in the doped sample suggests increased charge carrier recombination, likely due to the introduction of mid-gap trap states or defect levels associated with Fe2+ dopant incorporation. While transition metal doping can enhance visible-light absorption and alter electronic structure favorably, excessive or suboptimal doping may adversely affect charge carrier lifetimes. These results underscore the importance of precise dopant concentration control to balance light absorption and charge carrier dynamics for optimal photoelectrochemical performance.
The photocatalytic activity of the Fe2+-doped TiO2 nanocrystals was evaluated via visible-light-driven hydrogen production from water splitting. The observed nearly linear increase in hydrogen evolution over a 6-hour illumination period highlights the material's sustained photocatalytic activity. The enhancement is primarily attributed to the increased visible-light absorption due to Fe2+-induced electronic states and the improved separation and transport of photogenerated charge carriers.
Despite these promising results, there are some limitations to consider. The synthesis process involves thermal diffusion at elevated temperatures, which, while effective, may pose challenges for scalability and energy efficiency in practical applications. Furthermore, the long-term photocatalytic stability and potential for dopant leaching under repeated reaction cycles require further investigation. Overdoping is another concern, as excessive dopant concentrations can introduce recombination centers that negatively impact photocatalytic performance.
In conclusion, the Fe2+-doped TiO2 nanorods developed in this work exhibit enhanced visible-light-driven photocatalytic hydrogen production, making them attractive candidates for clean energy applications. At the same time, this study underscores the need for continued research into scalable synthesis methods, material durability, and optimal dopant concentrations to fully realize the practical potential of such materials in sustainable hydrogen production.
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