Dongping
Sun
,
Jiazhi
Yang
and
Xin
Wang
*
Key Laboratory for Soft Chemistry and Functional Materials (Nanjing University of Science and Technology), Ministry of Education, Nanjing 210094, China. E-mail: wxin@public1.ptt.js.cn
First published on 11th November 2009
Bacterial cellulose (BC) nanofibers were biosynthesized by Acetobacter xylinum NUST5.2, and displayed a remarkable capability for orienting TiO2 nanoparticle arrays. Large quantities of uniform BC nanofibers coated with TiO2 nanoparticles can be easily prepared by surface hydrolysis with molecular precision, resulting in the formation of uniform and well-defined hybrid nanofiber structures. The mechanism of arraying spherical TiO2 nanoparticles on BC nanofibers and forming well-defined, narrow mesopores are discussed in this paper. The BC/TiO2 hybrid nanofibers were used as photocatalyst for methyl orange degradation under UV irradiation, and they showed higher efficiency than that of the commercial photocatalyst P25.
To improve photocatalytic activity, many researchers have attempted to decrease the particle size and increase the surface-to-volume ratio of anatase particles. Thus, the design and preparation of TiO2nanorods or nanofibers has attracted great attention during the last decade because of their potential for enhancing photocatalytic activity with high surface area.10,11 Using different methods, fibrous structures of TiO2, and TiO2-coated electrospunpolymernanofibers have been prepared. These one dimensional nanostructured TiO2 fibers have shown interesting results.12–14 With growing environmental problems caused by the end-of-life disposal of several organic polymeric matrices, hunting for renewable polymers to replace synthetic ones has become a hot topic.15
Bacterial cellulose (BC) fibers produced by Acetobacter xylinum were found to be superior, on many accounts, to plant fibers. The structure of BC is similar to that of plant cellulose but consists of microfibrillar ribbons with a width less than 100 nm, i.e. it is of nanoscale size and has an extremely developed specific surface.16,17 These fibers have a wide range of applications due to their mechanical properties and their stability towards chemicals and high temperatures.18,19 Recently BC membranes used as a kind of green matrix for palladium catalysts were studied, and results show that palladium catalysts have excellent catalytic activity. However, no reports have highlighted BC nanofiber’s unique structure and large specific surface area or its potential as a supporting catalyst.20,21 In the work reported here, bacterial cellulose (BC) was biosynthesized and used as a substrate for the fabrication of BC/TiO2 hybrid nanofibers. The hybrid nanofibers were prepared by a controlled surface hydrolysis method. Herein we put forward a plausible growth mechanism for the hybrid nanofibers, for verification we utilized scanning electron microscopy (SEM) and transmission electron microscopy (TEM). In addition, the structure was characterized by Fourier transform infrared (FTIR) spectroscopy.
![]() | ||
Fig. 1 SEM and TEM images of BC nanofibers. (a) A general view of the nanofibers. (b) A TEM image of the nanofibers. (c–d) TEM images of BC/TiO2 hybrid nanofibers. |
To evaluate the interactions between BC and TiO2 nanoparticles in hybrid fibers, FTIR was applied. The recorded spectra for pure BC and BC/TiO2 hybrid fibers are shown in Fig. 2. The peaks at around 1000–1300 cm−1 for BC/TiO2 hybrid fibers, due to C–OH stretching (1060 cm−1) and C–O–C bending vibrations (1163 cm−1), are weakened in comparison to the peaks in BC because the TiO2 nanoparticles grow on the surface of the BC.22 A characteristic IR band at 1642 cm−1 corresponding to the OC vibration of the BC moved slightly downfield as a result of the Ti–O–C vibration (from 1642 cm−1 to 1630 cm−1), which indicates that a strong interaction occurs at the interface of BC and TiO2 nanoparticles.23 A similar phenomenon was observed for the C–H stretching vibration (2910 cm−1). Due to coverage by thin layer of TiO2, this C–H in-plane stretching was blocked as result of steric hindrance (as shown in Fig. 2).
![]() | ||
Fig. 2 FTIR spectra of BC nanofibers and BC/TiO2 hybrid nanofibers. |
Based on the morphology results and FTIR spectra, we can state that the arrays of spherical TiO2 nanoparticles on BC nanofibers are produced through a surface hydrolysis process. Scheme 1 illustrates the entire procedure of the fabrication of BC/TiO2 hybrid nanofibers. Since it is widely accepted that ordered water molecules are always present in a cellulose–water system, a layer of water molecules covers the BC fibers via H-bonding,24 and the disordered water layers are located outside (Scheme 1a). BC nanofibers with an ordered water layer were prepared by solvent exchange (Scheme 1b) (as shown in section 2.2), and the BC nanofibers with an ordered water layer were then dispersed in a mixture of titanium butoxide (Ti(OBu)4) in an ethanol/urea solution. Ti(OBu)4 hydrolyzes at the ordered water layer of the BC nanofibers, as the reactivity of Ti(OBu)4 is mild upon exposure to moisture (Scheme 1c). With Ti(OH)4 dehydrating in the hydrothermal process, TiO2 nanoparticles with regulated size can be produced in situ (Scheme 1d).
![]() | ||
Scheme 1 Schematic illustration of the preparation of BC/TiO2 hybrid nanofibers. |
If the hypothesis of fabrication of BC/TiO2 hybrid nanofibers is accurate, the ordered interstice between the arrays of the TiO2 nanoparticles will be formed when Ti(OH)4 dehydrates in the hydrothermal process. The average diameter of the interstice can be calculated through plane of the closer-packing of spheres method (Scheme 2.) by using the following equation,
![]() | (1) |
![]() | ||
Scheme 2 Model of the close-packing of spheres. |
To confirm that pores of the hybrid fiber were formed, the BC fibers and the BC/TiO2 hybrid nanofibers were examined by N2 adsorption–desorption experiments and the isotherms are shown in Fig. 3a. The slope of the N2 adsorption–desorption isotherm together with the area of hysteresis increases significantly with the BC/TiO2 hybrid fibers, indicating an increase in the surface area and the total pore volume. On the other hand, the nitrogen uptake at low pressure also rises with the loading of TiO2, indicating an enhancement of the overall surface area. The corresponding quantitative data are summarized in Table 1. In comparison with the BC fibers, the BC/TiO2 hybrid fibers showed an increase in surface area of much as 156-fold and a 25-fold increase of pore volume. These values reached 208.17 m2g−1 and 0.151 cm3g−1 respectively. The pore size distribution plot was calculated using the Barrett–Joyner–Halenda (BJH) equation from the adsorption branch of the isotherm and is shown in Fig. 3b. For the BC fibers, a broad distribution of both mesopores and macropores is found (ranging from 2 to 100 nm). Interestingly, with the loading of TiO2, a relatively unique size distribution of the fibers is produced. Specifically, the BC/TiO2 hybrid fibers exhibit a well-defined, narrow mesopore population centered at 3.5 nm, which agrees quite well with the theoretical value of 3.3 nm.
Sample | S BET | Total pore volume/cm3g−1 | Mesopore volume (%) | Average pore diameter (nitrogen desorption)/nm |
---|---|---|---|---|
BC fibers | 1.37 | 0.006 | 63.1 | 35.4 |
BC/TiO2 fibers | 208.17 | 0.151 | 96.5 | 3.5 |
![]() | ||
Fig. 3 Nitrogen adsorption–desorption isotherms of BC nanofibers and BC/TiO2 hybrid nanofibers. (a) pore size distribution for the BC nanofibers and BC/TiO2 hybrid nanofibers (b) and (c) are the adsorption–desorption isotherms at 0–120 nm and 0–10 nm, respectively. |
It is well known that anatase-type TiO2 show better photocatalytic activities than the other types of TiO2. So insights on the nature of the formed TiO2 phases were obtained from the XRD diffraction pattern. As seen from the upper pattern (Fig. 4), the three characteristic peaks located at the 14.5, 16.6, and 22.5 can be assigned to the BC fiber. After the BC fiber is coated with TiO2, the intensities of the peaks mentioned above become weaker and inconspicuous. In addition, several new strong peaks at 25.3, 38.1, 47.8, 54.1, 62.2, 69.3 and 75.0 are observed. Comparing peak positions with crystallographic databases identifies the material as the anatase phase of TiO2. It is noted that the characteristic peaks of the TiO2 are broad, which is an indication of the small size of the TiO2 particles formed on the BC fibers. The crystallite size as calculated from the Debye–Scherrer equation is 7.2 nm which is in agreement with particle size estimates from TEM.
![]() | ||
Fig. 4 XRD patterns of BC and BC/TiO2 hybrid nanofibers. |
Fig. S1 of the ESI† displays the TG curves of pure BC and the BC/TiO2 hybrid nanofibers. A maximum degradation for both pure BC and BC/TiO2 hybrid nanofibers at around 300 °C is observed. With increasing emperature, pure BC degrades completely, leaving only minute amounts, while 75% of the sample still remains in BC/TiO2. White ashes were obtained after the measurement of BC/TiO2.
Fig. 5 displays the electronic absorption spectra of N-doped BC/TiO2 hybrid nanofibers and BC/TiO2 hybrid nanofibers. A clear shift of absorption in the visible light region can be observed for the N-doped BC/TiO2 hybrid nanofibers in comparison with BC/TiO2 hybrid nanofibers. The band gap energy (Eg) of these materials can be estimated by the formula:25Eg = 1240/λg, where λg is the wavelength corresponding to the intersection point of the vertical and horizontal parts of the spectrum. The calculated Eg of N-doped BC/TiO2 (2.99 eV) is lower than that of the BC/TiO2 (3.1 eV). This may be caused by the varying degree of N-doping in BC/TiO2 hybrid nanofibers. The N-doped BC/TiO2 hybrid nanofibers were examined by X-ray photoelectron spectroscopy (XPS). Fig. S2 of the ESI† shows the high-resolution XPS spectra of the N 1s region on the surface of N-doped BC/TiO2 hybrid nanofibers. The N 1s spectrum of N-doped BC/TiO2 hybrid nanofibers contains one peak at about 399 eV. It has been reported that a peak at about 400 eV is a sign of nitrogen doping in the lattice of the titanium, which can be attributed to N–O.26 It should be noted that a long absorption tail of (400–600 nm) is observed for both hybrid nanofibers (Fig. 5) and this may be attributed to the BC substrate.
![]() | ||
Fig. 5 UV–vis diffuse reflectance spectra of BC/TiO2 and N-doped BC/TiO2nanofibers. |
The photocatalytic activities of the N-doped BC/TiO2 and undoped BC/TiO2 hybrid nanofibers were evaluated by photocatalytic degradation of methyl orange under UV irradiation. As a control, the activity of the commercial photocatalyst P25 was also tested under the same conditions. Results of the photocatalytic evaluation are shown in Fig. 6. The photocatalytic activities of N-doped BC/TiO2 and BC/TiO2 hybrid nanofibers are much higher than that of P25, which may be attributed to their larger specific surface areas and smaller crystallite size. (The specific surface areas and crystallite size of P25 are usually about 50 m2g−1 and 30 nm, respectively.27). Recently A. Ghicov et al. reported that nitrogen-doped TiO2 nanotube layers increased the conversion efficiency in photocatalysis because of the combination of a high surface area with a photoresponse in visible light.9 This is also a suitable explanation for the higher photocatalytic activity of N-doped BC/TiO2 relative to BC/TiO2.
![]() | ||
Fig. 6 Comparison of the photocatalytic activity of BC/TiO2nanofibers, N-doped BC/TiO2 nanfibers, and P25. |
Footnote |
† Electronic supplementary information (ESI) available: Thermogravimetric analysis curves for BC and BC/TiO2 hybrid nanofibers and XPS spectrum of an N-doped BC/TiO2nanofiber sample. See DOI: 10.1039/b9nr00158a |
This journal is © The Royal Society of Chemistry 2010 |