D. M. Tobaldi*a,
M. P. Seabraa,
G. Otero-Iruruetab,
Y. R. de Miguelc,
R. J. Balld,
M. K. Singhb,
R. C. Pullara and
J. A. Labrinchaa
aDepartment of Materials and Ceramic Engineering, CICECO – Aveiro Institute of Materials, University of Aveiro, Campus Universitário de Santiago, 3810-193 Aveiro, Portugal. E-mail: david.tobaldi@ua.pt; david@davidtobaldi.org; Tel: +351 234 370 041
bCenter for Mechanical Technology and Automation – TEMA, Department of Mechanical Engineering, University of Aveiro, Campus Universitário de Santiago, 3810-193 Aveiro, Portugal
cTECNALIA, Parque Tecnológico de Bizkaia, C/Geldo, Edificio 700, E-48160 Derio, Bizkaia, Spain
dBRE Centre for Innovative Construction Materials, Department of Architecture and Civil Engineering, University of Bath, Claverton Down, BA2 7AY, Bath, UK
First published on 26th November 2015
Carbon-modified commercial anatase (KRONOClean 7000®) was quantitatively characterised with XRD for the first time – full phase composition (both crystalline and amorphous content) and microstructure. The material was found to be bimodal anatase, mostly ∼4 nm diameter, but with a small amount of a larger fraction between ∼12 and 15 nm. Absorption in the visible range was confirmed by UV-Vis analysis, whilst XPS showed that an aromatic carbon compound is at the origin of that absorption. Also, the photocatalytic activity of this commercial nano-TiO2 was assessed, monitoring the abatement of NOx using a white LED lamp, irradiating exclusively in the visible region. Experiments simulated an indoor environment, highlighting the potential of this nano-TiO2 for adoption as a standard for visible-light photocatalytic activity, i.e. applications for innovative interior eco-building materials.
For this reason, in this work we report a fully quantitative X-ray characterisation (the crystalline and amorphous content, as well as the crystalline domain shape, size and size distribution), of the commercially available carbon-modified nano-anatase KRONOClean 7000® (K7000), with a view to assessing its ability as a visible-light active photocatalyst for indoor use. Furthermore, the PCA in gas–solid phase was assessed monitoring the degradation of NOx (NO & NO2) using exclusively visible-light irradiation.
Optical properties of the specimen were analysed via diffuse reflectance spectroscopy (DRS), performed using a Shimadzu UV 3100 (JP) spectrometer, equipped with a BaSO4 integrating sphere. Spectra of the samples were acquired in the UV-Vis range (250–750 nm) with 0.2 nm resolution, with BaSO4 as reference. Raman spectroscopy was also assessed; spectra were acquired in the 50–1000 cm−1 wavenumber range, with 4 cm−1 resolution, on a Bruker RFS 100/S (DE), equipped with a Nd:YAG laser (1064 nm) as the excitation source. FT-IR was performed with the aim of detecting the occurrence of OH groups and/or water adsorbed on the photocatalyst surface. This was carried out on a Bruker Tensor 27 (DE) spectrometer. The measurements were carried out over the wavenumber range of 4000–350 cm−1, in attenuated total reflectance (ATR) mode.
X-ray photoelectron spectroscopy (XPS) was used to characterise the elemental composition of the sample and the chemical state of the titanium, oxygen and carbon species. XPS spectra were acquired in an Ultra High Vacuum (UHV) system with a base pressure of 2 × 10−10 mbar. The system is equipped with a hemispherical electron energy analyser (SPECS Phoibos 150), a delay-line detector and a monochromatic AlKα (1486.74 eV) X-ray source. High resolution spectra were recorded at normal emission take-off angle and with a pass-energy of 20 eV, which provides an overall instrumental peak broadening slightly better than 0.5 eV. For XPS measurements the sample was diluted in Milli-Q water and a thin film was deposited on silicon by drop coating. Ar+ ion sputtering at 2 kV was used to remove the surface adsorbed species and access to the subsurface region for comparison. The resulting XPS spectra were calibrated in binding energy by referencing to the C 1s peak from contamination at 284.8 eV.
PCA tests were assessed in the gas–solid phase, monitoring the degradation of NOx. The reactor used has been described in detail elsewhere.10,22,23 The initial concentration of NOx (kept stable throughout the experiments, and prepared using synthetic air and NOx gas) was 0.2 ppm. Two mass flow controllers were used to prepare the mixture of air with the desired concentration of NOx, with a flow rate of 1 L min−1; this initial step was necessary to ensure the sample saturation, and ensuring that during the test, measurement of NOx is exclusively due to the photocatalytic process (i.e. no absorption from the sample, nor from the reactor walls).24 The outlet concentration of NOx was measured using a chemiluminescence analyser (AC-30 M, Environment SA, FR).
Samples were prepared in the form of a thin layer of powder, with a constant mass (∼0.10 g), and thus approximately constant thickness, in a 6 cm diameter Petri dish. Tests were performed at 18.1 ± 1 °C (temperature inside the reactor) with a relative humidity of 31%. These parameters, controlled by means of a thermocouple that was placed inside the chamber, and a humidity sensor placed in the inlet pipe, remained stable throughout the tests. The light source employed was a LED white light, irradiating only in the visible region (Philips LED Bulb Warm white), placed 28 cm from the photocatalyst, and the light intensity reaching the photocatalyst was 7 W m−2 in the visible range – being nil in the UVA (its emission spectrum being reported in the ESI, Fig. S1†). Once the desired concentration of NOx was attained, the window glass was uncovered, the LED white-lamp turned on, and the PCA reaction started. PCA tests were repeated in triplicate, using the very same sample and with the same protocol of the first test, so as to check the repeatability, recyclability and photostability of the K7000 batches.
K7000, batch | No of variables | Agreement factors | Phase composition (wt%) | |||
---|---|---|---|---|---|---|
R(F2) (%) | Rwp (%) | χ2 | Anatase | Amorphous | ||
a Note: there were 2285 observations; the number of anatase reflections in the data set was 32. | ||||||
1 | 15 | 3.74 | 4.79 | 2.24 | 91.9 ± 1.3 | 8.1 ± 1.3 |
2 | 15 | 3.56 | 4.31 | 1.98 | 93.5 ± 1.1 | 6.5 ± 1.1 |
3 | 15 | 3.56 | 4.66 | 2.18 | 93.1 ± 1.2 | 6.9 ± 1.2 |
Individual microstructural analysis and size distribution for the anatase phase present in the three batches of K7000 are shown in Fig. 1a–c and Table 2; a graphical output of the WPPM modelling is shown in Fig. 1a. From this novel XRD analysis, the anatase average crystalline domain diameters were found to be in the range of 2.3–3.3 nm (with a very narrow size distribution for all three batches, the mode being 2.0 nm in all cases, cf. Table 2). Moreover, in all three probability distributions, the right-hand tail is longer than the left, implying that those distributions are skewed to the right (i.e. positive skewness). Thus – assuming a unimodal model for the lognormal size distribution – all the three batches exhibited very similar microstructural characteristics. However, as can be seen in Fig. 1a, in assuming a unimodal model we do not obtain a perfect fit: some features are still present in the difference curve (continuous blue line in Fig. 1a), likely due to a non-ideal distribution of crystalline domains. For this reason, HR-TEM analysis was carried out, to obtain evidence endorsing this suspected non-ideal domain size distribution, cf. Fig. 2a–d. As can be clearly seen in Fig. 2a–d, K7000 shows the simultaneous presence of small and large domains – the small crystalline domains being much more strongly aggregated, cf. Fig. 2a and b. Therefore, the WPPM analysis was performed a second time, considering a bimodal size distribution for anatase. As can be seen in Fig. 1a, the bimodal model led to an almost perfect fit, the resulting difference curve virtually being a straight line (continuous dark grey line in Fig. 1a). Quantitative results of the bimodal size distribution model are depicted in Table 3; introducing a second fraction does not change the unit cell parameter results (sizes and volume are unaltered). As for the domain size, we observe the appearance of a small quantity of a second, larger-sized fraction of anatase (11.9–15.5 nm, Fig. 2c and d), co-existing with the smaller 3.8–4.4 nm domains. Hence, this extra fraction of material is able to explain the presence of the long tail in the actual distribution leading towards anatase larger sizes.
K7000, batch | Agreement factors | Unit cell parameters | Mean crystalline domain diameter (nm) | Skewness of the size distribution (nm) | ||||
---|---|---|---|---|---|---|---|---|
Rwp (%) | Rexp (%) | χ2 | a = b (nm) | c (nm) | V (nm3) | |||
1 | 4.04 | 2.33 | 1.74 | 0.3793(1) | 0.9524(1) | 0.137(1) | 3.3 ± 0.1 | 2.1 ± 0.1 |
2 | 4.87 | 2.28 | 2.15 | 0.3792(1) | 0.9519(1) | 0.137(1) | 2.3 ± 0.1 | 2.5 ± 0.1 |
3 | 3.82 | 2.27 | 1.68 | 0.3792(1) | 0.9526(1) | 0.137(1) | 3.3 ± 0.1 | 2.1 ± 0.1 |
K7000, batch | Agreement factors | Anatase 1 | Anatase 2 | ||||
---|---|---|---|---|---|---|---|
Rwp (%) | Rexp (%) | χ2 | Volume (nm3) | Average size (nm) | Volume (nm3) | Average size (nm) | |
1 | 3.08 | 2.28 | 1.35 | 0.137(1) | 4.4 ± 0.3 | 0.136(1) | 11.9 ± 0.6 |
2 | 3.98 | 2.23 | 1.78 | 0.137(1) | 3.8 ± 0.1 | 0.137(1) | 13.6 ± 0.5 |
3 | 4.24 | 2.23 | 1.90 | 0.137(1) | 4.0 ± 0.2 | 0.136(1) | 15.5 ± 0.8 |
Data obtained are thus only partially consistent with those reported by Quesada-Cabrera et al., who stated that K7000 had a “crystallite” size of around 15 nm, obtained using the Scherrer equation, and with a titania content of roughly 95% (though they did not specify whether that remaining 5% was amorphous or not).25 Consequently, they neglected the fraction of the small anatase crystalline domains below 5 nm diameter. In this regard, it is noteworthy that diffraction is sensitive to the volume, therefore to the fraction in that volume, which is the dominant one. A “crystallite” size of ∼15 nm is also given in the data sheet of K7000 manufacturer, though they state a TiO2 content of >87.5%.26
Raman spectroscopy confirmed the XRD results: only Raman modes assignable to anatase were detected in the K7000 spectrum (Fig. S3†). Moreover, the smaller crystalline domain size of anatase in K7000, compared to that in P25, is also confirmed by analysing and comparing the position and full width at half maximum (FWHM) of the symmetric vibrational Eg (O–Ti–O) Raman mode of anatase in K7000 versus P25. The obtained position of the Raman Eg mode in K7000 (147.7 cm−1) is obviously blue shifted compared to that of anatase in P25 (142.7 cm−1, dotted line in the inset of Fig. S3†); the FWHM of K7000 Raman Eg mode (18.7 cm−1) is broader than that of anatase in P25 (11.5 cm−1). This confirms not only the smaller crystalline domain size of K7000 vs. P25, but also its higher disorder.30
An FT-IR spectrum is reported in Fig. S4.† The huge broad band, centred at approximately 3425 cm−1, is assigned to surface-adsorbed hydroxyl groups (this being an advantage for PCA),31 whilst the peak at around 1630 cm−1 corresponds to the bending vibrations of O–H; the band in the range of 400–600 cm−1 clearly belongs to Ti–O–Ti vibrations.
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Fig. 4 High resolution XPS of Ti 2p (a), O 1s (b) and C 1s (c) core levels of the as received samples (bottom spectra in black) and after ion etching (upper spectra in red). |
Two main features dominate the Ti 2p spectrum, appearing at binding energies (BE) of (458.8 ± 0.1) eV and (464.6 ± 0.1) eV, that correspond to Ti 2p3/2 and Ti 2p1/2, respectively. These values are in good agreement with previously reported BEs for TiO2 NPs.32 Consequently, a main component is observed in the O 1s region at (530.1 ± 0.1) eV and ascribed to the oxygen atoms of the TiO2 NPs.32 The relatively small component that appears at (531.3 ± 0.1) eV is usually assigned to adsorbed surface species such as hydroxyl groups,33 and/or carbonate-like species in carbon-doped TiO2 samples. On the other hand, in the case of the C 1s core level, three components were necessary for the fitting of the spectrum. The first component is centred at a BE of (284.8 ± 0.1) eV and is usually ascribed to the graphitic-like C–C bond, while the other two components, at (286.3 ± 0.1) and (288.9 ± 0.1) eV, are ascribed to C–O and CO bonds, respectively.33 Our XPS data for the C 1s core level are very close to those reported in the literature for carbon-doped TiO2 NPs,33–35 in which the peaks ascribed to C–O and C
O bonds were assigned to an arylcarboxylate group, whilst the peak centred at 286.3 eV was assigned to a bidentately-bound arylcarboxylate. Thus, by analogy with those literature reports, we assigned the C 1s core level to an aromatic carbon compound.
Moreover, Zhang et al.33 recently performed ion etching on similar samples in order to remove the adsorbed surface species, and access the bulk composition. XPS spectra obtained after having followed the same approach on our samples are presented in the upper panel of Fig. 4 (red spectra). The O 1s core level is very similar to the spectrum obtained before the ion etching, but an important change appears in the Ti 2p3/2 core level. In this peak, the main component is still related to the Ti4+ atoms of TiO2 (see Fig. 4a), while the new small and broad component near 457.1 eV is ascribed to Ti3+ from the formation of oxygen vacancies induced by the ion bombardment.33 Likewise, the C 1s core level was fitted by the same three components discussed above but, interestingly, the intensity of the signal significantly diminished. Furthermore, Fig. S5† shows a comparison of the normalised C 1s spectra before and after the ion etching. The shape, BEs and relative intensities of the main features are virtually the same before and after the erosion with argon ions. This indicates that, even after having partially cleaned the surface of the NPs, “new” carbon species inside the bulk of the TiO2 NPs do not appear. Thus, this effect suggests a preferential covering of the surface of the NPs with carbon species, rather than their accommodation inside the TiO2 lattice (neither interstitial nor substitutional).
TiO2 + hν → eCB− + hVB+ | (1) |
hVB+ + H2O(ads) → OH˙ + H+ | (2) |
eCB− + O2 → O2˙− | (3) |
NO + OH˙ → NO2 + H+ | (4) |
NO + O2˙− → NO3− | (5) |
NO2 + OH˙ → NO3− + H+ → HNO3 | (6) |
Such HNO3 is produced on the surface of the catalyst, and might act as a physical barrier, inhibiting the photocatalytic reaction. As a consequence, a plateau is generally observed in the NOx abatement vs. time curve.36,37 This explains why the PCA tests were carried out for up to 20 min visible-light irradiation time. Nevertheless, a test up to 100 min visible-light irradiation time was assessed, and is depicted in Fig. S6.† In this, it is shown that the photocatalytic NOx abatement is attenuated at ∼40 min reaction time, and after this the photocatalytic reaction proceeds slowly. This likely means that the product of the photocatalytic NOx reaction is insufficient to act as a barrier that can “deactivate” the photocatalyst – in any case, the formed HNO3 can be easily eluted from TiO2 into water.38
NOx abatement PCA results are shown in Fig. 5. It is seen that, in the first photocatalytic run, after 20 min reaction time the NOx degradation by all the three batches is in the range of 20–23%. Furthermore, these PCA tests with K7000 were shown to be repeatable, the PCA in the second and third tests being approximately the same as in the first run. This clearly shows that a complete reuse cycle is possible for K7000, which proved to be very stable after three consecutive photocatalytic runs for all the three batches used, and suitable for continued reuse. Also, K7000 was shown to possess a considerably higher PCA (∼30% higher) compared to the well-known P25, under white (visible-only) indoor light (Fig. 5).
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Fig. 5 Photocatalytic NOx abatement test in triplicate of the three K7000 batches, and P25 as comparison, using the white LED lamp. |
Such a superior, and very stable, PCA under white-light exposure in K7000 has been attributed to the presence of an organic sensitiser (i.e. aryl carboxylate species), cf. spectroscopic and XPS sections, as suggested in the literature.33–35 Interestingly, these species clearly seem to be photostable, and thus resistant to photodegradation, which explains the stability and reusability of K7000 (in all the three batches) when using white-light. Also, the much higher specific surface area (SSA) of K7000 compared to that of P25 (229.2 versus ∼50 m2 g−1, respectively) and, consequently, its smaller crystalline domain size, could account for its higher PCA with regards to that of P25 – high SSA is actually connected to a high number of active centres on the photocatalyst's surface.39 Furthermore, although we do not have any experimental evidence that upon visible-light irradiation K7000 exhibits a better charge separation/transfer, it has been recently reported that carbon-modified TiO2 shows improved charge separation and transfer ability.40,41 These findings would make K7000 a more consistent commercial standard for comparing the indoor PCA of materials made only of the anatase TiO2 phase.
PCA of the commercial material (in three batches) was assessed against NOx abatement, simulating an indoor environment (pollutant concentration, and intensity of the white-light entering the reactor). It was found that the K7000 photocatalyst showed a higher PCA (∼30% higher) compared to that of the well-known P25. Furthermore, K7000 exhibited a very stable PCA after three consecutive photocatalytic runs, and proved suitable for reuse. K7000 is highlighted as a promising commercial anatase standard for indoor (visible-light) PCA applications.
Footnote |
† Electronic supplementary information (ESI) available: Emission spectrum of the lamp used for the photocatalytic experiments; graphical output of Rietveld–RIR QPA refinement; Raman and FT-IR spectra; normalised XPS C 1s core level spectra; PCA up to 100 min visible-light irradiation time. See DOI: 10.1039/c5ra22816f |
This journal is © The Royal Society of Chemistry 2015 |