Open Access Article
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Enhanced charge separation in TiO2/nanocarbon hybrid photocatalysts through coupling with short carbon nanotubes

Ahmed Al Mayyahia, Brian M. Everharta, Tej B. Shresthab, Tyson C. Backc and Placidus B. Amama*a
aTim Taylor Department of Chemical Engineering, Kansas State University, Manhattan, KS 66506, USA. E-mail: pamama@ksu.edu
bNanotechnology Innovation Center of Kansas State, Manhattan, KS 66506, USA
cMaterials and Manufacturing Directorate, Air Force Research Laboratory, Wright-Patterson AFB, OH 45433, USA

Received 4th January 2021 , Accepted 10th March 2021

First published on 22nd March 2021


Abstract

The interfacial contact between TiO2 and graphitic carbon in a hybrid composite plays a critical role in electron transfer behavior, and in turn, its photocatalytic efficiency. Herein, we report a new approach for improving the interfacial contact and delaying charge carrier recombination in the hybrid by wrapping short single-wall carbon nanotubes (SWCNTs) on TiO2 particles (100 nm) via a hydration-condensation technique. Short SWCNTs with an average length of 125 ± 90 nm were obtained from an ultrasonication-assisted cutting process of pristine SWCNTs (1–3 μm in length). In comparison to conventional TiO2–SWCNT composites synthesized from long SWCNTs (1.2 ± 0.7 μm), TiO2 wrapped with short SWCNTs showed longer lifetimes of photogenerated electrons and holes, as well as a superior photocatalytic activity in the gas-phase degradation of acetaldehyde. In addition, upon comparison with a TiO2–nanographene “quasi-core–shell” structure, TiO2-short SWCNT structures offer better electron-capturing efficiency and slightly higher photocatalytic performance, revealing the impact of the dimensions of graphitic structures on the interfacial transfer of electrons and light penetration to TiO2. The engineering of the TiO2–SWCNT structure is expected to benefit photocatalytic degradation of other volatile organic compounds, and provide alternative pathways to further improve the efficiency of other carbon-based photocatalysts.


1. Introduction

Rapid recombination of photogenerated electron–hole pairs is one of the major limitations of utilizing TiO2 photocatalysts in applications such as water treatment,1–3 air purification4–9 bacterial and viral inactivation,10,11 and self-cleaning glasses.12–14 Most of the photogenerated electron–hole pairs recombine within 10 picoseconds (ps), which is very short compared to the 100 ps typically required for redox reactions. As a result, only a small portion (∼10 percent) of the photogenerated charges, as revealed by time-resolved absorption spectroscopic studies, remain alive and able to participate in pollutant decomposition, resulting in limited photocatalytic activity.15,16 A number of studies have shown that inhibition of charge recombination and remarkable enhancement in photocatalytic efficiency of TiO2 can be achieved by coupling with carbon nanomaterials such as carbon nanotubes (CNTs), graphene, and fullerene.17–21 The coupling leads to formation of a Schottky barrier, through which electrons efficiently travel from TiO2 with a higher Fermi level to the carbon nanomaterial with a lower Fermi level until equilibrium is attained.22,23 In addition, the high electron-storage capacity of the graphitic structure (one electron per 32 carbon atoms) can serve as electron reservoirs or sinks, decreasing the recombination probability of the photogenerated charges in the hybrid material and enhancing photocatalytic activity.22

The improved charge separation in TiO2–nanocarbon hybrid structures depends largely on the quality of interfacial contact between TiO2 and the graphitic structure, and the structural and surface properties of the hybrid components.21,24–30 A knowledge gap that still exists is how the graphitic structures and their geometries affect the coupling and interfacial contacts of the components in the hybrid. The rate of electron transport and subsequent separation of photogenerated charges in conventional TiO2–nanocarbon composites are still hampered by nonuniform coating or poor dispersion induced by TiO2 aggregation on graphene sheets or CNT walls. Therefore, in light of the great promise shown by TiO2–nanocarbon hybrids in photocatalysis, research efforts have focused on tailoring the heterojunctions and schottky barriers to achieve efficient shuttling of electrons and promote electron–hole separation, as well as induce visible light excitation. It is well-established in the literature that charge recombination is inhibited on a variety of TiO2–CNT hybrids consisting of a thin, uniform TiO2 layer on individual multi-walled CNTs (MWCNTs) or TiO2 aggregates supported on CNTs.29,31–34 However, the trade-off relation between electron–hole concentration and separation efficiency in conventional TiO2-coated CNT composites remains a significant impediment to maximizing the photocatalytic activity.28 To this end, TiO2 wrapped with graphene has been considered as an alternative to the TiO2/CNT core–shell (or TiO2-coated CNT) structure, as the concentration of photogenerated charges can be optimized without sacrificing separation efficiency.19,35

Significant differences exist in hybrid structures formed with either CNTs or graphene. Graphene, a two-dimensional (2D) structure with several nanometers of width and high stacking tendency, can generate a “shell-like” structure consisting of several graphene layers on TiO2, preventing light penetration.36,37 Another complication associated with graphene is the unavoidable electron scattering that may reduce the electron transport rate and promote charge recombination.37 On the other hand, harnessing the one-dimensional (1D) single-wall CNT (SWCNT) structures in TiO2 hybrids not only provides well-defined routes for electron transport, but also their small size compared to MWCNTs and graphene sheets provide a degree of freedom for optimizing charge separation without compromising light absorption.38–42 A consensus from the aforementioned studies is that the structure of nanocarbons (i.e., the size of graphene or length of CNTs) is a crucial factor in controlling the quality of interfacial contact and subsequent charge separation. In particular, Kim et al.36 revealed a superior photocatalytic activity for TiO2 hybrids formed with nano-sized graphene (or nanographene) sheets in comparison to those formed with micro-sized graphene; the wrapping of nanographene on TiO2 particles in the former hybrid maximized the interfacial contact between the components, resulting in superior charge separation and photocatalytic activity. Similarly, we hypothesize that cutting long SWCNTs into high populations of open-ended tubes with high degrees of functionalization and density of active sites, as well as short lengths that can effectively wrap a large TiO2 particle (∼100 nm), can lead to enhanced interactions with TiO2 particles that will promote the photocatalytic process. Although many studies have investigated the influence of coupling SWCNTs with TiO2, all reported works employed SWCNTs with lengths in the micrometer range.

In this study, we report for the first time the wrapping of large TiO2 particles (∼100 nm) with short SWCNTs (125 ± 90 nm in length) obtained from an ultrasonication-assisted cutting process. The resulting TiO2–SWCNT hybrid photocatalyst exhibits enhanced interfacial contact and charge separation. The short, highly functionalized and dispersed SWCNTs, in the presence of TiO2, initiated formation of Ti–O–C bonds via intermolecular interactions, resulting in TiO2 nanoparticles or nanoparticle aggregates that are partially wrapped by SWCNTs. In comparison to conventional TiO2–SWCNT composites synthesized using long SWCNTs (1.2 ± 0.7 μm), TiO2 wrapped with short SWCNTs showed longer lifetimes of photogenerated electrons and holes, as well as a superior photocatalytic activity in the gas-phase degradation of acetaldehyde. In addition, upon comparison with a TiO2–nanographene “quasi-core–shell” structure, the novel TiO2–SWCNT composite offers superior electron-capturing efficiency and slightly higher photocatalytic performance, revealing the impact of the dimension of graphitic structures on the interfacial transfer of electrons and light penetration to TiO2.

2. Experimental section

2.1. Synthesis of TiO2–SWCNT composites

Purified SWCNTs (1–2 nm in diameter and 1–3 μm in length) were functionalized by refluxing with HNO3 (70%) at 150 °C for two hours. A known amount of functionalized SWCNTs were dispersed in ethanol and sonicated at 25 °C for four hours to produce the short SWCNTs. After the sonication-assisted cutting process, the resulting suspension was allowed to settle for 15 minutes and the supernatant was slowly added to the TiO2–ethanol dispersion (50 mg in 50 mL ethanol) under sonication, followed by robust stirring overnight at pH = 3.4. The sonicator (Branson, CPX5800H) operated at 100 W and 40 kHz. The TiO2 particles (anatase, 99.9%, 100 nm) were purchased from US Research Nanomaterials, Inc. The TiO2–SWCNT hybrid synthesized from short SWCNTs (hereafter referred to as TiO2-short SWCNT) was collected by filtration using a membrane with average pore size of 0.2 μm and dried at 60 °C. For TiO2–SWCNT hybrids synthesized from long SWCNTs, the same procedure was followed without subjecting the long SWCNTs to ultrasonication-assisted cutting; the resulting hybrid is hereafter referred to as TiO2-long SWCNT. Unless stated otherwise, the amount of SWCNTs used in the standard sample is 1 wt%.

2.2. Synthesis of TiO2–nanographene composites

The graphite powder was oxidized by the modified Hummer method.43–45 The graphene oxide (GO) produced was treated with a mixture of HCl and KMnO4 to produce the nanographene oxide. GO (0.05 g) was dispersed in 50 mL of concentrated HCl, and then 0.05 g of KMnO4 was slowly added under robust stirring. After one hour of stirring at 40 °C, the resulting slurry was cooled in an ice bath. Then, H2O2 solution (5 mL H2O2 and 95 mL distilled water) was slowly added with continued stirring for one hour, followed by sonication for 30 minutes to exfoliate the nanographene oxide. The final product was collected by filtration using similar conditions in Section 2.1 and oven-dried at 60 °C.

The TiO2–nanographene composite (0.7 wt% nanographene) was synthesized by dispersing a known amount of nanographene oxide in ethanol by sonication, and the resulting slurry was slowly added to the TiO2–ethanol dispersion (50 mg in 50 mL distilled water) under stirring at pH = 3.5, followed by robust stirring overnight. The brownish powder obtained was transferred to a Teflon-lined, hydrothermal synthesis autoclave reactor and heated at 120 °C for 24 hours to reduce the nanographene oxide. The final product (hereafter referred to as TiO2–nanographene) was washed repeatedly with 1 M HCl and distilled water, collected by filtration and dried at 60 °C.

2.3. Characterization methods

X-ray diffraction (XRD) patterns were collected on a Rigaku Miniex II X-ray diffractometer with Cu Kα radiation (λ = 1.5418 Å) at 40 kV and 40 mA. The Raman spectra were acquired via an iHR550 spectrometer with a laser excitation wavelength of 532 nm. Catalyst morphology was characterized by a field-emission scanning electron microscope (SEM, Hitachi S5200) equipped with energy-dispersive X-ray spectroscopy (EDS), and a transmission electron microscope (TEM, FEI Talos) operating at 200 kV. For TEM analysis, a small amount of the sample was dispersed in ethanol by sonication and dropped onto a copper microgrid coated with lacy carbon film. X-ray photoelectron spectroscopic (XPS) measurements were collected via a Kratos Ultra XPS system at 1.0 × 10−9 Torr. A monochromatic Al Kα source ( = 1486.6 eV) operating at 10 mA and 12 keV (120 W) was used to collect the spectra. The effect of charging was reduced by a charge neutralizer. Survey spectra were collected at 160 eV pass energy with 1 eV step and 100 ms contact time. For the high-resolution scans, spectra were collected at 20 eV pass energy with 0.1 eV step and 100 ms contact time. The photoluminescence (PL) spectra were acquired via a spectraMax i3x multi-mode microplate reader over the range of 400–700 nm using an excitation wavelength of 360 nm.

2.4. Evaluation of photocatalytic activity

The photocatalytic activity was tested by measuring the change in concentration of gas phase acetaldehyde as a function of irradiation time. The photocatalyst (100 mg) was placed in a 750 mL borosilicate batch reactor surrounded by light sources (two 25 W Sylvania 21703 (356 nm) bulbs and two 13 W ReptiSun 10.0 UV/B bulbs (280–320 nm) with intensity of 6.5 W m−2). One thousand ppmv of acetaldehyde gas was injected into the reactor via a syringe. After equilibrium between gaseous and adsorbed phases was attained, UV irradiation was started and the decrease in concentration was measured via an SRI 310C gas chromatograph equipped with a Restek silica gel column (8046-895, 6 ft length, 2 mm ID), on-column injection, and flame ionization detector (FID). According to the experimental data, acetaldehyde degradation by TiO2-short SWCNT, TiO2-long SWCNT and TiO2–nanographene fitted to a pseudo first-order reaction represented by eqn (1):
 
image file: d1ra00045d-t1.tif(1)
where k is the apparent constant of reaction rate, c is the concentration of acetaldehyde and t is the reaction time.

3. Results

3.1. Morphology, structure, composition, and interfacial properties

The SEM image in Fig. 1a reveals TiO2 particles are partially wrapped by short SWCNTs (TiO2-short SWCNT), a phenomenon that occurs uniformly over a large area on TiO2 particles. EDS mapping of TiO2-short SWCNT (Fig. 1b) reveals the co-existence of carbon, titanium, and oxygen, with atomic concentrations of 15.75%, 34.23%, and 32.62%, respectively. The partial wrapping of TiO2 particles by individual SWCNTs or SWCNT bundles is further confirmed by the TEM images in Fig. 1c and d while the low-magnification SEM image in Fig. S1 demonstrates the wrapping phenomenon occurs across a large area of the sample. The TEM images (Fig. 1c and d) show short SWCNTs of different lengths either as bundles or isolated nanotubes on a TiO2 particle. From SEM and TEM data, it is apparent intimate interactions between the SWCNTs and TiO2 exist. The high-resolution TEM images in Fig. S2 show the SWCNTs form a network on TiO2 particles. The small diameters of SWCNTs (∼1.5 nm) compared to that of TiO2 particles (∼100 nm) implies a large fraction of the incident light can participate in excitation of TiO2. In other words, the deposition of the short SWCNTs does not appear to lead to significant light scattering or prevent light absorption by TiO2. However, aggregation of the short SWCNTs was observed in photocatalyst samples with higher SWCNT concentrations as shown in the TiO2-short SWCNT sample with 3 wt% SWCNTs (Fig. S3).
image file: d1ra00045d-f1.tif
Fig. 1 (a) SEM image of TiO2-short SWCNT; (b) EDS mapping of TiO2-short SWCNT; (c) and (d) TEM images of (a) showing TiO2 particles decorated with short SWCNTs and SWCNT bundles with arrows showing interactions between a TiO2 particle and individual SWCNTs or bundles. (e) A zoom-in high-resolution TEM image of the region in (d) with a red square.

XRD patterns of short SWCNTs, TiO2, and TiO2-short SWCNT are shown in Fig. 2a. The peaks at 2θ = 55.1°, 54.0°, 48.1°, 37.9°, and 25.4° are respectively indexed to (211), (105), (200), (004), and (101) facets, typical for anatase TiO2. The sharp and intense peaks affirm the high crystallinity of the photocatalysts, whereas the absence of peaks associated with impurities is evidence of their high quality. The peaks at 26.8° and 42.8°, usually attributed to (002) and (100) crystal planes of SWCNTs, were not detected in TiO2-short SWCNT, due to the low SWCNT concentration (1 wt%). However, the addition of SWCNTs slightly reduced the relative intensity of TiO2 peaks, an observation consistent with other studies.46,47 Raman spectra (Fig. 2b) show the characteristic peaks of anatase TiO2 at 397, 515, and 639 cm−1.48 The characteristic anatase peaks (B1g, A1g + B1g, and Eg) were observed in TiO2-short SWCNT, accompanied by the disordered carbon-induced D-band at 1350 cm−1, and the G-band at 1583 cm−1 that represents sp2 carbon from SWCNTs. The slight shift in anatase modes observed in the Raman and XRD spectra generally correlates with the external perturbation by SWCNTs and the corresponding substitution of Ti4+ by C atoms, resulting in the formation of Ti–O–C bonds in the TiO2 lattice.49–52 However, band gaps of TiO2 and TiO2-short SWCNT (calculated from UV-Vis spectra in Fig. S4) are 3.22 and 3.19 eV, respectively, suggesting low-carbon doping in the composite.


image file: d1ra00045d-f2.tif
Fig. 2 (a) XRD profiles of TiO2, TiO2-short SWCNT, and short SWCNTs. (b) Raman spectra of TiO2, TiO2-short SWCNT, and short SWCNTs.

An XPS survey spectrum of TiO2-short SWCNT confirms the presence of Ti, O, and C (Fig. 3a). The high-resolution XPS spectrum of Ti 2p (Fig. 3b) shows two peaks located at 459.5 and 465.2 eV attributed to Ti 2p3/2 and Ti 2p1/2, respectively, which are typical binding energies of the Ti4+ valance state.53 The O 1s spectrum, shown in Fig. 3c, is fitted with three peak components. The component at 530.7 eV corresponds to Ti–O–Ti, while the peak at 531.6 eV is attributed to C[double bond, length as m-dash]O or C–OH.53 The peak at 532.8 eV is ascribed to Ti–O–C, and is an indication of the covalent interaction between TiO2 and SWCNTs.54 Based on density functional theory calculations,55 Ti–O–C bonds facilitate charge carrier separation due to their higher electrostatic density in comparison to the non-covalent interaction. As a consequence, the charge redistribution map predicts a higher rate of electron transport. The C 1s region, shown in Fig. 3d, is fitted with four peak components. The peak at 284.5 eV is assigned to sp2 carbon, while the peaks at 285.7, 287.7, and 289.8 eV are assigned to functional groups linked to the carbon atoms including C–O/C–O–Ti, C[double bond, length as m-dash]O, and O–C[double bond, length as m-dash]O, respectively.54,56 The various oxygen functional groups generate anchors for direct linking with TiO2. The absence of the Ti–C peak, typically located at 281 eV,57 confirms our claim regarding the absence of significant carbon doping in the composite.


image file: d1ra00045d-f3.tif
Fig. 3 XPS spectra of TiO2-short SWCNT. (a) XPS survey spectrum; deconvolution of high-resolution Ti 2p spectrum (b), O 1s spectrum (c), and C 1s spectrum (d).

3.2. Photocatalytic degradation of gaseous acetaldehyde by TiO2–SWCNT hybrids

To evaluate the photocatalytic activity of TiO2 wrapped with SWCNTs, the degradation of acetaldehyde was conducted under UV light. Fig. 4a shows the effect of SWCNT amount in the hybrid structure on photocatalytic activity expressed in terms of normalized acetaldehyde concentration after 60 minutes. Coupling of short SWCNTs with TiO2 markedly improves degradation of acetaldehyde. The photocatalytic degradation activity is sensitive to the amount of SWCNTs in the composite; our findings revealed the optimum amount to be 1 wt%. A schematic illustration of the proposed mechanism for photocatalytic degradation of gaseous acetaldehyde on TiO2-short SWCNT hybrid is depicted in Fig. 4b. Upon light illumination, photo-induced electron–hole pairs are produced by TiO2 (hv (<350 nm) → eCB+SWCNTs + h+); the electrons are promoted to the conduction band leaving holes in the valance band.58 The CB position of anatase is ∼4.21 eV using vacuum level (AVS) (−0.4 eV relative to reversible hydrogen electrode (RHE)), with a bandgap of about 3.2 eV. On the other hand, the work function of a SWCNT is known to be ∼−4.8 eV (AVS) (approximately 0.2 relative to RHE).59 Since the work function of SWCNTs is lower than the conduction band of TiO2, SWCNTs can act as electron sinks whereby a fraction of the photoelectrons flow to them.41,59 The holes in the valence band react with water molecules to generate hydroxyl radicals (˙OH) (H2O + h+ → ˙OH + H+), while the photoexcited electrons in SWCNTs and in the conduction band of TiO2 react with O2 to produce superoxide radicals (˙O2) (O2 + e CB+SWCNTs => ˙O2). The active radicals initiate decomposition of adsorbed gaseous acetaldehyde via two reaction pathways. ˙OH and ˙O2 could oxidize a portion of acetaldehyde to carbon dioxide and water (image file: d1ra00045d-t2.tif). The remaining acetaldehyde could be oxidized to acetic acid by ˙OH in the first step (image file: d1ra00045d-t3.tif) and subsequently converted to water and carbon dioxide by ˙O2 in a second step (image file: d1ra00045d-t4.tif).58,60–62 As shown in Fig. 4c, the relevant potential level of the acceptor species is located below the CB potential of TiO2. On the other hand, the potential level of the donor species is above the valence band position of TiO2, validating the generation of active radicals responsible for the degradation of gaseous acetaldehyde.63–69
image file: d1ra00045d-f4.tif
Fig. 4 (a) Photocatalytic degradation of gaseous acetaldehyde using TiO2 and TiO2-short SWCNT of different SWCNT loadings after 60 minutes. (b) Schematic illustration of the possible mechanism of photocatalytic degradation of gaseous acetaldehyde. (c) Band edge position of a TiO2–SWCNT hybrid relative to reversible hydrogen electrode (RHE) with approximated values of redox potentials of active radicals/compounds involved in degradation of gaseous acetaldehyde.

It is well known the photogenerated electron–hole pair participates in redox reactions on the catalyst surface to initiate degradation of adsorbed pollutant; however, the process is limited by rapid recombination of electrons and holes. As depicted in Fig. 4b, one of the roles of SWCNTs in TiO2–CNT composites is to inhibit electron–hole recombination.15,16 An increase in the amount of SWCNTs in the hybrid composite beyond 1 wt% has a negative effect on the photocatalytic performance, which we attribute to SWCNT aggregation and generation of large SWCNT bundles. Hsu and coworkers70–75 have provided further mechanistic insight into the effect of nanocarbon loading on photocatalytic performance. The overall charge separation efficiency in nanocarbon-semiconductor hybrids can be sacrificed when the amount of the electron sink (metal or nanocarbon) exceeds the optimum value. The observed trend in activity for the different TiO2–SWCNT ratios in our study is consistent with the results from these studies and can also be rationalized by the so called later-emerging electron–hole recombination that is induced across the interface. The formation of large-diameter bundles indicates SWCNTs at high concentration tend to interact with each other via Van der Waals forces rather than with TiO2. As a consequence, the quality of the interfacial contact (or degree of interaction) between TiO2 and SWCNTs is reduced. In addition, the coverage of thick SWCNT bundles on TiO2 particles has the potential of significantly decreasing light penetration to TiO2, thus reducing photoactivity as observed in other studies that involve wrapping of graphene on TiO2 or coupling graphene quantum dots with TiO2.41,76 Despite the decrease in photocatalytic activity upon SWCNT aggregation, the observed performance is still higher than pristine TiO2, indicating photon permeation is not completely blocked and the beneficial role of SWCNTs in photocatalytic enhancement, via charge separation, may still be partially maintained.

3.3. Effect of SWCNT length and graphitic dimensions on interfacial contact, charge separation, and photocatalytic activity of the hybrids

To probe the influence of SWCNT length on the interfacial contact and subsequent photocatalytic performance of TiO2–SWCNT hybrids, we synthesized another composite with long SWCNTs (TiO2-long SWCNT) using the same concentration of SWCNTs, but without subjecting the sample to the ultrasonication cutting step. Representative TEM images for long SWCNTs and short SWCNTs used for coupling with TiO2 are presented in Fig. S5 with corresponding box plots in Fig. 5 showing their length distributions; each box plot consists of 12 measurements of nanotubes from TEM images. The average length of short SWCNTs is 125 ± 90 nm while that of long SWCNTs is 1.2 ± 0.67 μm. The results clearly demonstrate the shear force generated by ultrasonication results in SWCNTs that are significantly shorter than those processed without ultrasonication. The use of ultrasonication as a nondestructive technique for cutting nanotubes is well established in processing nanomaterials. Shuba et al.77 showed that ultrasonication yields SWCNTs with low side-wall degradation and preserves the electronic properties of the nanotubes. Note that for SWCNTs to efficiently play the intended role of “electron sink” in hybrid structures during photocatalysis, preserving their structural integrity and exceptional electronic properties is critically important.
image file: d1ra00045d-f5.tif
Fig. 5 Box plots showing lengths of short SWCNTs and long SWCNTs. Each box plot consists of 12 measurements of nanotubes from TEM images.

The Raman spectra of pristine SWCNTs, short SWCNTs, and long SWCNTs in Fig. 6 provide further insight into the effect of the processing approach on the structure of SWCNTs. The ratio of G- to D-band intensities (IG/ID) from the Raman spectra, widely considered a quality or graphitization index for carbon-based materials,78–80 is 13.9 for pristine SWCNTs and decreases to 3.3 and 3.6 after acid treatment for long SWCNTs and short SWCNTs, respectively, due to the functionalization of SWCNTs. The IG/ID ratios for short and long SWCNTs are about the same, which indicates that the ultrasonication process did not degrade the nanotubes. As observed previously in Fig. 2b, the TiO2–SWCNT composite exhibited a slight decrease in IG/ID, suggesting the increase in defect after the coupling of TiO2 and SWCNTs,49 probably due to the low substitution of Ti4+ by carbon atoms. In addition, the characteristic phonon mode in SWCNTs occurring in the low frequency region (zoomed in the insets), the radial breathing mode (RBM), is clearly observed in pristine and processed SWCNTs. In fact, the same RBM peaks for pristine SWCNTs at ∼150 and 260 cm−1 are observed for long SWCNTs and short SWCNTs. This provides further evidence that the ultrasonication process did not destroy the nanotubes.


image file: d1ra00045d-f6.tif
Fig. 6 Raman spectra of pristine SWCNTs, long SWCNTs and short SWCNTs with insets showing zoom-in spectra of RBMs in the lower frequency region.

Next, we investigate the effect of SWCNT length and nanocarbon dimension on interfacial contact, charge separation, and photocatalytic activity of the hybrids. Electron microscopic images of the resulting hybrids formed with short SWCNTs, long SWCNTs and nanographene, along with corresponding EDS mapping for TiO2–nanographene, are shown in Fig. 7. The EDS mapping of TiO2–nanographene reveal a highly uniform distribution of titanium, carbon, and oxygen as observed for TiO2-short SWCNT (Fig. 1b). In contrast to TiO2-short SWCNT (Fig. 7a), bundles of large-diameter SWCNTs are apparent in TiO2-long SWCNT composites (Fig. 7b), with severe particle aggregation as shown in Fig. S6. These observations give credence to the assumption that ultrasonication not only reduces the length of SWCNTs, but also facilitates debundling of SWCNTs. Morphological characterization of micron-sized graphene, exfoliated nanographene, and non-exfoliated nanographene are summarized in Fig. S7. The average size the nanographene, as determined from TEM analysis and shown on the box plot (Fig. S7), is ∼125 ± 93 nm.


image file: d1ra00045d-f7.tif
Fig. 7 SEM images of TiO2-short SWCNT (a) and TiO2-long SWCNT (b). TEM image of TiO2–nanographene (c) and corresponding EDS mapping (d). TEM image of TiO2-short SWCNT (e).

Photocatalytic degradation of acetaldehyde by TiO2, TiO2-long SWCNT, TiO2–nanographene, and TiO2-short SWCNT, is shown in Fig. 8a along with the PL spectra of the photocatalysts in Fig. 8b. As depicted in Fig. 8a, TiO2-short SWCNT shows the highest performance; the rate constant of TiO2-short SWCNT is 0.015 min−1, while others are given as follows: pristine TiO2 (k = 0.0073 min−1), TiO2-long SWCNT (k = 0.0107 min−1), and TiO2–nanographene (k = 0.0125 min−1). TiO2-short SWCNT showed better performance compared with TiO2–nanographene, even though the quality of interfacial contact in the two heterostructures is somewhat similar, as evidenced by EDS mapping that reveals a highly uniform distribution of nanographene on TiO2 particles over a large area (Fig. 7d). The PL spectra (Fig. 8b) show lifetimes of charges on TiO2 coupled with short SWCNTs are longer than TiO2 coupled with nanographene, which explains the different photocatalytic activities observed as evidenced by their rate constants.


image file: d1ra00045d-f8.tif
Fig. 8 (a) Photocatalytic activity of TiO2, TiO2-short SWCNT and TiO2-long SWCNT during degradation of gaseous acetaldehyde based on a pseudo first-order kinetic model. (b) Photoluminescence (PL) spectra of TiO2, TiO2-long SWCNT, TiO2–nanographene, TiO2-short SWCNT, and short SWCNT.

4. Discussion

Based on our results, we present a schematic illustration of the interfacial contact between nanocarbon (short SWCNTs, long SWCNTs or nanographene) and TiO2, as well as the charge carrier movement in the hybrids in Fig. 7. We rationalize the superior performance of TiO2-short SWCNT to be due to the inhibition of charge recombination in the composite, which can be achieved in two ways. First, the increase in the number of interfacial contacts between each individual TiO2 and short SWCNTs provides more channels for electron transport that inhibits charge recombination. The short and well-exfoliated SWCNTs can have lower bending stiffness compared to the long and non-exfoliated SWCNTs. It has been shown that bending stiffness of SWCNTs is directly proportional to SWCNT diameter;81 therefore, we expect large-diameter SWCNT bundles to have larger persistence length compared to exfoliated SWCNTs (or small-diameter SWCNT bundles). Hence, short SWCNTs efficiently wrap a TiO2 particle (Fig. 9a). Consequently, a large fraction of TiO2 nanoparticles are in direct contact with short SWCNTs. In contrast, only a small fraction of TiO2 nanoparticles are in direct contact with the long SWCNTs (Fig. 9b). Second, the improved SWCNT debundling ensures a uniform distribution of SWCNTs over a large area on the TiO2 surface, and hence, the shuttling of electrons across the interface for enhanced charge separation is not restricted to a small portion of the composite as in the case of TiO2-long SWCNT hybrids. To test the above hypotheses, PL data presented in Fig. 8b provide valuable insight. In comparison to pristine TiO2, fluorescence quenching was observed in the TiO2–SWCNT hybrid structures, confirming the transfer of electrons from TiO2 to SWCNTs delayed charge recombination. It is clear from the PL results that the intensity of TiO2-short SWCNT hybrids is lower than that of TiO2-long SWCNT hybrids, and is substantially lower than pristine TiO2, confirming the efficient charge separation occurring in TiO2-short SWCNT hybrids.
image file: d1ra00045d-f9.tif
Fig. 9 Schematic illustrations of interfacial contact between nanocarbon and TiO2, and charge carrier movement in TiO2-short SWCNT (a), TiO2-long SWCNT (b), and TiO2–nanographene (c).

To rationalize the role of short SWCNTs (or oxygen-containing functionalities), we have to consider the synthesis steps, and in particular, the zeta potentials of SWCNTs and TiO2 particles in ethanol under the pH used. Factors such as type of solvent and pH of mixture can alter the surface charge of nanostructures. In our case, acid treatment lowers the zeta potential of SWCNTs due to the formation of oxygen functionalities as shown by Liu et al.82 These functional groups on the surface and tips of short SWCNTs imparts a strong negative charge and make them more easily dispersed. The negatively charged groups provide a strong electrostatic attraction toward positively charged species. Conversely, at low pH or high hydrogen ion activity, the surface of TiO2 acquires a positive charge due to the high zeta potential. In fact, Widegren and Bergström83 showed that the addition of a relatively small amount of acid or base is capable of introducing a relatively strong charge on TiO2 particles. In our synthesis experiment, TiO2 particles and functionalized SWCNTs were dispersed in ethanol at pH = 3.5 which creates an environment with a high hydrogen activity and a strong positive charge on TiO2. The strong positively charged TiO2 particles and negatively charged functionalized SWCNTs interact strongly via electrostatic attraction to form the hybrid structures with enhanced interfacial contact. In addition, opened and unblocked CNTs significantly increase the density of adsorption or anchoring sites.84 Cutting of long SWCNTs increases the number of open ends, and therefore, the short SWCNTs provide more “handles” or anchoring sites for interactions with TiO2 than long SWCNTs.

The dimension of the graphitic structure is another important factor that can affect charge separation. To understand the role of the dimension of the graphitic structure in the composite, we compared the performance of TiO2 quasi-wrapped by 1D SWCNTs (TiO2-short SWCNT) with the quasi-wrapped by 2D nanographene (TiO2–nanographene). The synthesis of the quasi-core–shell structure is adapted from a technique proposed by Kim et al.36 We hypothesize that random pathways in 2D graphene can significantly reduce the electron transport rate or may lead to electron escape from the graphene sheet (as schematically depicted in Fig. 9c), and thus promote charge carrier recombination. In contrast, the 1D SWCNTs offer efficient and short pathways for the transfer of vectorial electrons and, hence, enhanced charge separation. In addition, nanographene has a high stacking tendency and even after exfoliation, the number of layers cannot be easily controlled. During TEM analysis, we observed several TiO2 nanoparticles with thick graphitic shells, considerably thicker than SWCNT bundles (see Fig. 7c and e). This means significant portion of incident light is hindered from reaching TiO2 in a typical core–shell structure for TiO2–nanographene. On the other hand, SWCNTs, even in the case of bundles, due to their one-dimensional structure and small diameters, do not completely block light permeation to TiO2, as shown earlier for hybrid structures synthesized using high SWCNT concentrations. Nevertheless, coupling short SWCNTs or nanographene significantly improved electron–hole separation and photoreactivity of TiO2; the photoexcited electrons in the TiO2 core are efficiently transported into the nanocarbon due to the strong interfacial contact between the hybrid components.

5. Conclusions

TiO2 nanoparticles quasi-wrapped with short SWCNTs were successfully fabricated via an approach that involves the interaction between TiO2 and short SWCNTs in ethanol as a solvent. The presence of short SWCNTs resulted in enhanced photocatalytic activity and efficient charge separation. The improved interfacial contact, verified by electron microscopy, prolonged the lifetime of an electron–hole pair on TiO2 as demonstrated by photoluminescence spectroscopy. Unlike hybrid structures with long SWCNTs, higher photocatalytic performance in gas-phase degradation of acetaldehyde was achieved with TiO2-short SWCNT hybrids, confirming use of short SWCNTs in coupling with TiO2 as a better alternative. Investigations into the effect of nanocarbon dimensions on charge separation revealed TiO2-short SWCNT hybrids have slightly higher photocatalytic activity than TiO2–nanographene. We attribute the performance to electron scattering in 2D-nanographene, which may affect electron transport through the interface. The high stacking tendency of nanographene may form a thick graphitic layer on TiO2 that could hinder UV light penetration. Overall, this study provides rational new guidelines for maximizing electron–hole separation in TiO2–nanocarbon hybrids for improved photocatalytic performance.

Conflicts of interest

There are no conflicts to declare.

Acknowledgements

This study was financially supported by the National Science Foundation (Grant No. 1653527).

References

  1. S.-Y. Lee and S.-J. Park, TiO2 photocatalyst for water treatment applications, J. Ind. Eng. Chem., 2013, 19, 1761–1769 CrossRef CAS.
  2. A. Al Mayyahi, TiO2 Polyamide Thin Film Nanocomposite Reverses Osmosis Membrane for Water Desalination, Membranes, 2018, 8, 66 CrossRef PubMed.
  3. Y. Sheng, Z. Wei, H. Miao, W. Yao, H. Li and Y. Zhu, Enhanced organic pollutant photodegradation via adsorption/photocatalysis synergy using a 3D g-C3N4/TiO2 free-separation photocatalyst, Chem. Eng. J., 2019, 370, 287–294 CrossRef CAS.
  4. V. Puddu, H. Choi, D. D. Dionysiou and G. L. Puma, TiO2 photocatalyst for indoor air remediation: Influence of crystallinity, crystal phase, and UV radiation intensity on trichloroethylene degradation, Appl. Catal., B, 2010, 94, 211–218 CrossRef CAS.
  5. C. H. Ao and S. C. Lee, Indoor air purification by photocatalyst TiO2 immobilized on an activated carbon filter installed in an air cleaner, Chem. Eng. Sci., 2005, 60, 103–109 CrossRef CAS.
  6. P. B. Amama, K. Itoh and M. Murabayashi, Gas-phase photocatalytic degradation of trichloroethylene on pretreated TiO2, Appl. Catal., B, 2002, 37, 321–330 CrossRef CAS.
  7. P. B. Amama, K. Itoh and M. Murabayashi, Effect of RuO2 deposition on the activity of TiO2: Photocatalytic oxidation of trichloroethylene in aqueous phase, J. Mater. Sci., 2004, 39, 4349–4351 CrossRef CAS.
  8. P. B. Amama, K. Itoh and M. Murabayashi, Photocatalytic oxidation of trichloroethylene in humidified atmosphere, J. Mol. Catal. A: Chem., 2001, 176, 165–172 CrossRef CAS.
  9. P. B. Amama, K. Itoh and M. Murabayashi, Photocatalytic degradation of trichloroethylene in dry and humid atmospheres: role of gas-phase reactions, J. Mol. Catal. A: Chem., 2004, 217, 109–115 CrossRef CAS.
  10. V. Rodríguez-González, S. Obregón, O. A. Patrón-Soberano, C. Terashima and A. Fujishima, An approach to the photocatalytic mechanism in the TiO2-nanomaterials microorganism interface for the control of infectious processes, Appl. Catal., B, 2020, 270, 118853 CrossRef PubMed.
  11. P. Ganguly, C. Byrne, A. Breen and S. C. Pillai, Antimicrobial activity of photocatalysts: Fundamentals, mechanisms, kinetics and recent advances, Appl. Catal., B, 2018, 225, 51–75 CrossRef CAS.
  12. E. I. Cedillo-González, R. Riccò, M. Montorsi, M. Montorsi, P. Falcaro and C. Siligardi, Self-cleaning glass prepared from a commercial TiO2 nano-dispersion and its photocatalytic performance under common anthropogenic and atmospheric factors, Build Environ., 2014, 71, 7–14 CrossRef.
  13. Q. Yi, H. Wang, S. Cong, Y. Cao, Y. Wang, Y. Sun, Y. Lou, J. Zhao, J. Wu and G. Zou, Self-Cleaning Glass of Photocatalytic Anatase TiO2@Carbon Nanotubes Thin Film by Polymer-Assisted Approach, Nanoscale Res. Lett., 2016, 11, 457 CrossRef PubMed.
  14. T. Zhu, Y. Cheng, J. Huang, J. Xiong, M. Ge, J. Mao, Z. Liu, X. Dong, Z. Chen and Y. Lai, A transparent superhydrophobic coating with mechanochemical robustness for anti-icing, photocatalysis and self-cleaning, Chem. Eng. J., 2020, 399, 125746 CrossRef CAS.
  15. J. Schneider, M. Matsuoka, M. Takeuchi, J. Zhang, Y. Horiuchi, M. Anpo and D. W. Bahnemann, Understanding TiO2 Photocatalysis: Mechanisms and Materials, Chem. Rev., 2014, 114, 9919–9986 CrossRef CAS PubMed.
  16. K. Lee, H. Yoon, C. Ahn, J. Park and S. Jeon, Strategies to improve the photocatalytic activity of TiO2: 3D nanostructuring and heterostructuring with graphitic carbon nanomaterials, Nanoscale, 2019, 11, 7025–7040 RSC.
  17. X. Pan, Y. Zhao, S. Liu, C. L. Korzeniewski, S. Wang and Z. Fan, Comparing Graphene-TiO2 Nanowire and Graphene-TiO2 Nanoparticle Composite Photocatalysts, ACS Appl. Mater. Interfaces, 2012, 4, 3944–3950 CrossRef CAS PubMed.
  18. W. Wang, P. Serp, P. Kalck and J. L. Faria, Visible light photodegradation of phenol on MWNT-TiO2 composite catalysts prepared by a modified sol–gel method, J. Mol. Catal. A: Chem., 2005, 235, 194–199 CrossRef CAS.
  19. G. Lui, J.-Y. Liao, A. Duan, Z. Zhang, M. Fowler and A. Yu, Graphene-wrapped hierarchical TiO2 nanoflower composites with enhanced photocatalytic performance, J. Mater. Chem. A, 2013, 1, 12255–12262 RSC.
  20. X. Hao, Z. Jin, J. Xu, S. Min and G. Lu, Functionalization of TiO2 with graphene quantum dots for efficient photocatalytic hydrogen evolution, Superlattices Microstruct., 2016, 94, 237–244 CrossRef CAS.
  21. B. M. Everhart, M. Baker-Fales, B. McAuley, E. Banning, H. Almkhelfe, T. C. Back and P. B. Amama, Hydrothermal synthesis of carbon nanotube–titania composites for enhanced photocatalytic performance, J. Mater. Res., 2020, 35, 1451–1460 CrossRef CAS.
  22. K. Woan, G. Pyrgiotakis and W. Sigmund, Photocatalytic Carbon-Nanotube–TiO2 Composites, Adv. Mater., 2009, 21, 2233–2239 CrossRef CAS.
  23. M. Shaban, A. M. Ashraf and M. R. Abukhadra, TiO2 Nanoribbons/Carbon Nanotubes Composite with Enhanced Photocatalytic Activity; Fabrication, Characterization, and Application, Sci. Rep., 2018, 8, 781 CrossRef PubMed.
  24. V. Štengl, D. Popelková and P. Vláčil, TiO2–Graphene Nanocomposite as High Performance Photocatalysts, J. Phys. Chem. C, 2011, 115, 25209–25218 CrossRef.
  25. K. Zhou, Y. Zhu, X. Yang, X. Jiang and C. Li, Preparation of graphene–TiO2 composites with enhanced photocatalytic activity, New J. Chem., 2011, 35, 353–359 RSC.
  26. A. Miribangul, X. Ma, C. Zeng, H. Zou, Y. Wu, T. Fan and Z. Su, Synthesis of TiO2/CNT Composites and its Photocatalytic Activity Toward Sudan (I) Degradation, Photochem. Photobiol., 2016, 92, 523–527 CrossRef CAS PubMed.
  27. Y. Yang, L. Xu, H. Wang, W. Wang and L. Zhang, TiO2/graphene porous composite and its photocatalytic degradation of methylene blue, Mater. Design, 2016, 108, 632–639 CrossRef CAS.
  28. Z. Li, B. Gao, G. Z. Chen, R. Mokaya, S. Sotiropoulos and G. Li Puma, Carbon nanotube/titanium dioxide (CNT/TiO2) core–shell nanocomposites with tailored shell thickness, CNT content and photocatalytic/photoelectrocatalytic properties, Appl. Catal., B, 2011, 110, 50–57 CrossRef CAS.
  29. J. Yu, T. Ma and S. Liu, Enhanced photocatalytic activity of mesoporous TiO2 aggregates by embedding carbon nanotubes as electron-transfer channel, Phys. Chem. Chem. Phys., 2011, 13, 3491–3501 RSC.
  30. W. Yao, Y. Li, D. Yan, M. Ma, Z. He, S. Chai, X. Su, F. Chen and Q. Fu, Fabrication and photocatalysis of TiO2-graphene sandwich nanosheets with smooth surface and controlled thickness, Chem. Eng. J., 2013, 229, 569–576 CrossRef CAS.
  31. B. Gao, C. Peng, G. Z. Chen and G. Li Puma, Photo-electro-catalysis enhancement on carbon nanotubes/titanium dioxide (CNTs/TiO2) composite prepared by a novel surfactant wrapping sol–gel method, Appl. Catal., B, 2008, 85, 17–23 CrossRef CAS.
  32. X.-H. Xia, Z.-J. Jia, Y. Yu, Y. Liang, Z. Wang and L.-L. Ma, Preparation of multi-walled carbon nanotube supported TiO2 and its photocatalytic activity in the reduction of CO2 with H2O, Carbon, 2007, 45, 717–721 CrossRef CAS.
  33. W. Zhang, G. Li, H. Liu, J. Chen, S. Ma and T. An, Micro/nano-bubble assisted synthesis of Au/TiO2@CNTs composite photocatalyst for photocatalytic degradation of gaseous styrene and its enhanced catalytic mechanism, Environ. Sci.: Nano, 2019, 6, 948–958 RSC.
  34. B. Gao, G. Z. Chen and G. Li Puma, Carbon nanotubes/titanium dioxide (CNTs/TiO2) nanocomposites prepared by conventional and novel surfactant wrapping sol–gel methods exhibiting enhanced photocatalytic activity, Appl. Catal., B, 2009, 89, 503–509 CrossRef CAS.
  35. C. Wang, D. Meng, J. Sun, J. Memon, Y. Huang and J. Geng, Graphene Wrapped TiO2 Based Catalysts with Enhanced Photocatalytic Activity, Adv. Mater. Interfaces, 2014, 1, 1300150 CrossRef.
  36. H.-i. Kim, G.-h. Moon, D. Monllor-Satoca, Y. Park and W. Choi, Solar Photoconversion Using Graphene/TiO2 Composites: Nanographene Shell on TiO2 Core versus TiO2 Nanoparticles on Graphene Sheet, J. Phys. Chem. C, 2012, 116, 1535–1543 CrossRef CAS.
  37. Y. Dai, Y. Sun, J. Yao, D. Ling, Y. Wang, H. Long, X. Wang, B. Lin, T. H. Zeng and Y. Sun, Graphene-wrapped TiO2 nanofibers with effective interfacial coupling as ultrafast electron transfer bridges in novel photoanodes, J. Mater. Chem. A, 2014, 2, 1060–1067 RSC.
  38. H. R. Jafry, M. V. Liga, Q. Li and A. R. Barron, Single walled carbon nanotubes (SWNTs) as templates for the growth of TiO2: the effect of silicon in coverage and the positive and negative synergies for the photocatalytic degradation of Congo red dye, New J. Chem., 2011, 35, 400–406 RSC.
  39. L. Ling, C. Wang, M. Ni and C. Shang, Enhanced photocatalytic activity of TiO2/single-walled carbon nanotube (SWCNT) composites under UV-A irradiation, Sep. Purif. Technol., 2016, 169, 273–278 CrossRef.
  40. K. Dai, X. Zhang, K. Fan, T. Peng and B. Wei, Hydrothermal synthesis of single-walled carbon nanotube–TiO2 hybrid and its photocatalytic activity, Appl. Surf. Sci., 2013, 270, 238–244 CrossRef CAS.
  41. Y. Yao, G. Li, S. Ciston, R. M. Lueptow and K. A. Gray, Photoreactive TiO2/Carbon Nanotube Composites: Synthesis and Reactivity, Environ. Sci. Technol., 2008, 42, 4952–4957 CrossRef CAS PubMed.
  42. R. Seshadri, H. N. Aiyer, A. Govindaraj and C. N. R. Rao, Electron transport properties of carbon nanotubes, Solid State Commun., 1994, 91, 195–199 CrossRef CAS.
  43. W. S. Hummers and R. E. Offeman, Preparation of Graphitic Oxide, J. Am. Chem. Soc., 1958, 80, 1339 CrossRef CAS.
  44. W.-C. Hu, Y.-A. Chen, P.-Y. Hsieh, C.-W. Tsao, Y.-H. Chiu, T.-F. M. Chang, C.-Y. Chen, M. Sone and Y.-J. Hsu, Reduced graphene oxides-wrapped ZnO with notable photocatalytic property, J. Taiwan Inst. Chem. Eng., 2020, 112, 337–344 CrossRef CAS.
  45. K.-A. Tsai and Y.-J. Hsu, Graphene quantum dots mediated charge transfer of CdSe nanocrystals for enhancing photoelectrochemical hydrogen production, Appl. Catal., B, 2015, 164, 271–278 CrossRef CAS.
  46. Y. Huang, D. Chen, X. Hu, Y. Qian and D. Li, Preparation of TiO2/Carbon Nanotubes/Reduced Graphene Oxide Composites with Enhanced Photocatalytic Activity for the Degradation of Rhodamine B, Nanomaterials, 2018, 8, 431 CrossRef PubMed.
  47. Y. Li, Z. Wang and X.-J. Lv, N-doped TiO2 nanotubes/N-doped graphene nanosheets composites as high performance anode materials in lithium-ion battery, J. Mater. Chem. A, 2014, 2, 15473–15479 RSC.
  48. F. Wang and K. Zhang, Physicochemical and photocatalytic activities of self-assembling TiO2 nanoparticles on nanocarbons surface, Curr. Appl. Phys., 2012, 12, 346–352 CrossRef.
  49. B. Chai, T. Peng, X. Zhang, J. Mao, K. Li and X. Zhang, Synthesis of C60-decorated SWCNTs (C60-d-CNTs) and its TiO2-based nanocomposite with enhanced photocatalytic activity for hydrogen production, Dalton Trans., 2013, 42, 3402–3409 RSC.
  50. T. Appadurai, C. M. Subramaniyam, R. Kuppusamy, S. Karazhanov and B. Subramanian, Electrochemical Performance of Nitrogen-Doped TiO2 Nanotubes as Electrode Material for Supercapacitor and Li-Ion Battery, Molecules, 2019, 24, 2952 CrossRef CAS PubMed.
  51. W. Li, R. Liang, N. Y. Zhou and Z. Pan, Carbon Black-Doped Anatase TiO2 Nanorods for Solar Light-Induced Photocatalytic Degradation of Methylene Blue, ACS Omega, 2020, 5, 10042–10051 CrossRef CAS PubMed.
  52. R. Taziwa, E. L. Meyer and K. G. Chinyama, Raman temperature dependence analysis of carbon-doped titanium dioxide nanoparticles synthesized by ultrasonic spray pyrolysis technique, J. Mater. Sci., 2012, 47, 1531–1540 CrossRef CAS.
  53. G. An, W. Ma, Z. Sun, Z. Liu, B. Han, S. Miao, Z. Miao and K. Ding, Preparation of titania/carbon nanotube composites using supercritical ethanol and their photocatalytic activity for phenol degradation under visible light irradiation, Carbon, 2007, 45, 1795–1801 CrossRef CAS.
  54. W. Vallejo, A. Rueda, C. Díaz-Uribe, C. Grande and P. Quintana, Photocatalytic activity of graphene oxide–TiO2 thin films sensitized by natural dyes extracted from Bactris guineensis, R. Soc. Open Sci., 2019, 6, 181824 CrossRef CAS PubMed.
  55. S. Ayissi, P. A. Charpentier, K. Palotás, N. Farhangi, F. Schwarz and W. A. Hofer, Preferential Adsorption of TiO2 Nanostructures on Functionalized Single-Walled Carbon Nanotubes: A DFT Study, J. Phys. Chem. C, 2015, 119, 15085–15093 CrossRef CAS.
  56. Z. Hu, Y. Huang, S. Sun, W. Guan, Y. Yao, P. Tang and C. Li, Visible light driven photodynamic anticancer activity of graphene oxide/TiO2 hybrid, Carbon, 2012, 50, 994–1004 CrossRef CAS.
  57. H. Wu, J. Fan, E. Liu, X. Hu, Y. Ma, X. Fan, Y. Li and C. Tang, Facile hydrothermal synthesis of TiO2 nanospindles-reduced graphene oxide composite with a enhanced photocatalytic activity, J. Alloys Compd., 2015, 623, 298–303 CrossRef CAS.
  58. Q. Zeng, X. Xie, X. Wang, Y. Wang, G. Lu, D. Y. H. Pui and J. Sun, Enhanced photocatalytic performance of Ag@TiO2 for the gaseous acetaldehyde photodegradation under fluorescent lamp, Chem. Eng. J., 2018, 341, 83–92 CrossRef CAS.
  59. Y. Yao, G. Li, S. Ciston, R. M. Lueptow and K. A. Gray, Photoreactive TiO2/Carbon Nanotube Composites: Synthesis and Reactivity, Environ. Sci. Technol., 2008, 42, 4952–4957 CrossRef CAS PubMed.
  60. H. Hu, W.-j. Xiao, J. Yuan, J.-w. Shi, M.-x. Chen and W.-f. Shang Guan, Preparations of TiO2 film coated on foam nickel substrate by sol-gel processes and its photocatalytic activity for degradation of acetaldehyde, J. Environ. Sci., 2007, 19, 80–85 CrossRef CAS.
  61. X. Ye, D. Chen, J. Gossage and K. Li, Photocatalytic oxidation of aldehydes: Byproduct identification and reaction pathway, J. Photochem. Photobiol., A, 2006, 183, 35–40 CrossRef CAS.
  62. A. H. Mamaghani, F. Haghighat and C.-S. Lee, Photocatalytic oxidation technology for indoor environment air purification: The state-of-the-art, Appl. Catal., B, 2017, 203, 247–269 CrossRef CAS.
  63. H. Huang, B. Pradhan, J. Hofkens, M. B. J. Roeffaers and J. A. Steele, Solar-Driven Metal Halide Perovskite Photocatalysis: Design, Stability, and Performance, ACS Energy Lett., 2020, 5, 1107–1123 CrossRef CAS.
  64. X. Zhao, L. Du, B. You and Y. Sun, Integrated design for electrocatalytic carbon dioxide reduction, Catal. Sci. Technol., 2020, 10, 2711–2720 RSC.
  65. R. D. Feinman, Oxidation-reduction calculations in the biochemistry course, Biochem. Mol. Biol. Educ., 2004, 32, 161–166 CrossRef CAS PubMed.
  66. W. He, H.-K. Kim, W. G. Wamer, D. Melka, J. H. Callahan and J.-J. Yin, Photogenerated Charge Carriers and Reactive Oxygen Species in ZnO/Au Hybrid Nanostructures with Enhanced Photocatalytic and Antibacterial Activity, J. Am. Chem. Soc., 2014, 136, 750–757 CrossRef CAS PubMed.
  67. A. L. Linsebigler, G. Lu and J. T. Yates, Photocatalysis on TiO2 Surfaces: Principles, Mechanisms, and Selected Results, Chem. Rev., 1995, 95, 735–758 CrossRef CAS.
  68. M.-J. Fang, C.-W. Tsao and Y.-J. Hsu, Semiconductor nanoheterostructures for photoconversion applications, J. Phys. D: Appl. Phys., 2020, 53, 143001 CrossRef CAS.
  69. Y.-H. Chiu, T.-F. M. Chang, C.-Y. Chen, M. Sone and Y.-J. Hsu, Mechanistic Insights into Photodegradation of Organic Dyes Using Heterostructure Photocatalysts, Catalysts, 2019, 9, 430 CrossRef CAS.
  70. Y.-C. Chen, K.-i. Katsumata, Y.-H. Chiu, K. Okada, N. Matsushita and Y.-J. Hsu, ZnO–graphene composites as practical photocatalysts for gaseous acetaldehyde degradation and electrolytic water oxidation, Appl. Catal., A, 2015, 490, 1–9 CrossRef CAS.
  71. Y.-C. Chen, Y.-C. Pu and Y.-J. Hsu, Interfacial Charge Carrier Dynamics of the Three-Component In2O3–TiO2–Pt Heterojunction System, J. Phys. Chem. C, 2012, 116, 2967–2975 CrossRef CAS.
  72. Y.-H. Hsu, A. T. Nguyen, Y.-H. Chiu, J.-M. Li and Y.-J. Hsu, Au-decorated GaOOH nanorods enhanced the performance of direct methanol fuel cells under light illumination, Appl. Catal., B, 2016, 185, 133–140 CrossRef CAS.
  73. W.-H. Lin, Y.-H. Chiu, P.-W. Shao and Y.-J. Hsu, Metal-Particle-Decorated ZnO Nanocrystals: Photocatalysis and Charge Dynamics, ACS Appl. Mater. Interfaces, 2016, 8, 32754–32763 CrossRef CAS PubMed.
  74. Y.-F. Lin and Y.-J. Hsu, Interfacial charge carrier dynamics of type-II semiconductor nanoheterostructures, Appl. Catal., B, 2013, 130–131, 93–98 CrossRef CAS.
  75. Y.-C. Pu, H.-Y. Chou, W.-S. Kuo, K.-H. Wei and Y.-J. Hsu, Interfacial charge carrier dynamics of cuprous oxide-reduced graphene oxide (Cu2O-rGO) nanoheterostructures and their related visible-light-driven photocatalysis, Appl. Catal., B, 2017, 204, 21–32 CrossRef CAS.
  76. D. Pan, J. Jiao, Z. Li, Y. Guo, C. Feng, Y. Liu, L. Wang and M. Wu, Efficient Separation of Electron–Hole Pairs in Graphene Quantum Dots by TiO2 Heterojunctions for Dye Degradation, ACS Sustainable Chem. Eng., 2015, 3, 2405–2413 CrossRef CAS.
  77. M. V. Shuba, A. G. Paddubskaya, P. P. Kuzhir, S. A. Maksimenko, V. K. Ksenevich, G. Niaura, D. Seliuta, I. Kasalynas and G. Valusis, Soft cutting of single-wall carbon nanotubes by low temperature ultrasonication in a mixture of sulfuric and nitric acids, Nanotechnology, 2012, 23, 495714 CrossRef CAS PubMed.
  78. L. Bokobza, J.-L. Bruneel and M. Couzi, Raman Spectra of Carbon-Based Materials (from Graphite to Carbon Black) and of Some Silicone Composites, Carbon, 2015, 1, 77–94 Search PubMed.
  79. S. Santangelo, Controlled surface functionalization of carbon nanotubes by nitric acid vapors generated from sub-azeotropic solution, Surf. Interface Anal., 2016, 48, 17–25 CrossRef CAS.
  80. P. B. Amama, C. Lan, B. A. Cola, X. Xu, R. G. Reifenberger and T. S. Fisher, Electrical and Thermal Interface Conductance of Carbon Nanotubes Grown under Direct Current Bias Voltage, J. Phys. Chem. C, 2008, 112, 19727–19733 CrossRef CAS.
  81. N. Fakhri, D. A. Tsyboulski, L. Cognet, R. B. Weisman and M. Pasquali, Diameter-dependent bending dynamics of single-walled carbon nanotubes in liquids, Proc. Natl. Acad. Sci., 2009, 106, 14219 CrossRef CAS PubMed.
  82. Y. Liu, L. Gao, J. Sun and Y. Wang, Functionalization of carbon nanotubes for nanoparticle attachment, J. Ceram. Process. Res., 2010, 11, 120–122 Search PubMed.
  83. J. Widegren and L. Bergström, Electrostatic Stabilization of Ultrafine Titania in Ethanol, J. Am. Ceram. Soc., 2004, 85, 523–528 CrossRef.
  84. X. Ren, C. Chen, M. Nagatsu and X. Wang, Carbon nanotubes as adsorbents in environmental pollution management: A review, Chem. Eng. J., 2011, 170, 395–410 CrossRef CAS.

Footnote

Electronic supplementary information (ESI) available. See DOI: 10.1039/d1ra00045d

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