Feng Caoa,
Duanyang Lia,
Ruiping Dengb,
Lijian Huangb,
Daocheng Panb,
Jianmin Wanga,
Song Lia and
Gaowu Qin*a
aKey Laboratory for Anisotropy and Texture of Materials (Ministry of Education), Northeastern University, Shenyang 110819, China. E-mail: qingw@smm.neu.edu.cn; Tel: +86-24-83691565
bState Key Laboratory of Rare Earth Resource Utilization, Changchun Institute of Applied Chemistry, Chinese Academy of Sciences, Changchun 130022, China
First published on 17th September 2015
It is of great importance to develop humidity-buffering materials and thus to improve indoor environments. Uniform Fe2O3 nanocubes with an average pore size distribution of 8.48 nm exhibit superior water adsorption–desorption ability, arising from the appropriate pore size distribution around the condensation critical radius. This finding can provide a novel strategy to design and prepare new humidity-buffering nanomaterials.
As is well known, small-sized inorganic nanocrystals with large specific surface areas have got extensive research interests owing to the possibility of tuning their optical, chemical and electronic property on a large scale, which can cause the tunable multi-functionalities.4 α-Fe2O3, as the most stable iron oxide under ambient atmosphere, has sparked increasing interest over the past few decades because of its low cost, high corrosion resistance, abundant and eco-friendly properties.5 To our knowledge, the potential application of α-Fe2O3 porous nanomaterials as a stand-alone material for adsorbents has not been studied yet. Herein, preparation and water vapour adsorption–desorption property of the well-dispersed α-Fe2O3 nanocubes in a narrow size distribution and large specific surface area are our main objectives. Nanoparticles exhibit properties different from those of their bulk counterparts, which can be exploited to obtain new functionalities.6
In this work, we presented a facile and simple one-pot hydrothermal approach to prepare α-Fe2O3 nanocubes with an average pore size distribution of 8.48 nm. The size of the nanocube is around 40–50 nm. The uniform ordered cube-like Fe2O3 nanomaterial showed an excellent humidity-buffering ability, due to adsorption and desorption of water vapour by utilizing the intra- and inter-granular pores and large specific surface areas. Specifically, the Fe2O3 nanocubes has a much higher water adsorption capacity compared with bulk Fe2O3 counterparts and porous Fe2O3 nanofibers. Further comparison with the conventional humidity-buffering materials (raw diatomite and calcined diatomite) was conducted. Results show that the significantly enhanced water adsorption capacity of Fe2O3 nanocubes mainly arises from the appropriate pore size distribution nearby condensation critical radius.
The structure and composition of the as-prepared powder samples was characterized by XRD analysis, as shown in Fig. 1. All the diffraction peaks can be identified to the Fe2O3 phase (JCPDS card no. 33-0664). No other characteristic peaks from the other crystalline impurities were detected, thus indicating formation of the pure Fe2O3 products. The morphology and size of the as-prepared Fe2O3 products were visualized by SEM. The low-magnification SEM image (Fig. 2A) shows that the product is composed of uniform ordered nanocubes. The high-magnification SEM image (Fig. 2B) clearly reveal that, the cube-like shape have a narrow size distribution of 40–50 nm. Additionally, the chemical composition of these nanocubes is further investigated by energy-dispersive spectroscopy (EDS, inset in Fig. 2A). The strong peaks of Fe and O are observed in the EDS result, and the atomic percentage ratio is about 2:
3, which is close to the stoichiometry of Fe2O3. For comparison, bulk counterpart Fe2O3 powder and Fe2O3 porous nanofibers were also measured.7 The structure and morphology results were shown in Fig. S1.† Pure Fe2O3 crystalline phases (JCPDS card no. 33-0664) were identified. The morphology of commercial Fe2O3 powder was nanocables with particles, of which average particle size was about 100 nm. The morphology of uniform Fe2O3 porous nanofibers can be observed obviously.
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Fig. 2 (A) Low-magnification SEM image of the Fe2O3 nanocubes, and the EDS pattern (inset); (B) enlarged SEM image of the Fe2O3 nanocubes. |
Further insight into the microstructure and morphology of cube like Fe2O3 nanoarchitecture was obtained through TEM and HR-TEM. Fig. 3A shows the low-magnification TEM images of the Fe2O3 nanostructures, uniform ordered small-sized nanocubes can be observed clearly, in accordance with the SEM results (such as Fig. 2B). The high-magnification TEM images in inset of Fig. 3A and B reveal the presence of mesopores in the nanocubes. The HR-TEM image (Fig. 3C), SAED (inset) and FFT pattern (Fig. 3D) exhibit the high-crystalline characterization with a lattice spacing of 0.37 nm, which can be indexed readily to (101) plane of Fe2O3 nanocubes.
The specific surface area and porosity of the Fe2O3 samples were investigated. Fig. 4 shows the N2 adsorption/desorption isotherms and Barrett–Joyner–Halenda (BJH) pore size distribution curve of the as-obtained Fe2O3 nanocubes, nanofibers and bulk Fe2O3 counterpart powder. Results show that the isotherm of Fe2O3 nanocubes can be categorized as type IV, with the distinct hysteresis loop observed in the range of 0.5–1.0 p/p0 on the basis of IUPAC classification. Evidently, the pore size distribution is relatively narrow, with an average size of 8.48 nm. This result coincides with that of the TEM (Fig. 3A and B). The BET surface area and pore volume of Fe2O3 nanocubes are calculated to be 50.91 m2 g−1 and 0.17 cm3 g−1 respectively, which are much higher than that of bulk Fe2O3 counterpart powder (8.79 m2 g−1, 0.02 cm3 g−1) and porous Fe2O3 nanofibers (13.4 m2 g−1, 0.15 cm3 g−1).
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Fig. 4 N2 adsorption–desorption isotherm for (A) the Fe2O3 nanocubes, bulk Fe2O3 and (B) Fe2O3 nanofibers. The inset shows BJH pore size distributions of the samples. |
Such a high specific surface area is believed to benefit from the synthesis process of nanocubes.8 Control experiments were carried out to determine the synthesis parameters that may affect the formation of Fe2O3 nanocubes. We found that the addition of urea and DEG has strong effects on the formation of nanocubes. Fig. S2† shows SEM images of the samples obtained when different amounts of urea are introduced into the reaction system. Without using urea, microrods with lengths of about 10 μm are the dominant products in the batch solution. Increasing the amount of urea, more and more nanocubes appear in the product together with a decreased amount of rod-like microstructures. The major role of urea can be assigned to provide OH− ion supply in aqueous solution through CO(NH2)2 hydrolysis.9 Fig. S3† gives SEM images of the products obtained when EG and PEG 400 replace DEG while keeping the other conditions unchanged. It is obvious that nanocubes can be fabricated only under the presence of DEG. As reported in literature, DEG with its high boiling point and viscosity property has been widely used in the polyol method to fabricate a series of monodisperse nanostructured materials.10
Comparative experiments were carried out to examine the effect of Fe2O3 nanomaterials on the water vapour adsorption–desorption. As shown in Fig. 5, the adsorption capacity of water vapour at both low and high humidity ranges follows the order of bulk Fe2O3 < Fe2O3 nanofibers < Fe2O3 nanocubes. This result is consistent with the trend of pore size, pore volume and surface area of Fe2O3 nanomaterials. In addition, conventional humidity-buffering materials (raw diatomite and calcined diatomite) were prepared and used as control samples. Their N2 sorption isotherm, BJH pore size distribution and water sorption kinetic are shown in Fig. S4 and S5.† The results of BET surface areas, BJH average pore sizes, pore volumes values and the maximum adsorption capacity of water vapor of the Fe2O3 nanocubes, Fe2O3 porous nanofibers, bulk Fe2O3 counterparts, raw diatomite and calcined diatomite samples were summarized in Table 1. The adsorption capacity of the Fe2O3 nanocubes was higher than that of the raw and calcined diatomites adsorbents. More interesting, similar BET surface areas were observed between the Fe2O3 nanocubes and calcined diatomite sample, but the water adsorption capacity of Fe2O3 nanocubes was found to be much higher than that of calcined diatomites adsorbent. In general, BET surface area is one of the most critical influences on water vapour adsorption performance.11 Our experimental results demonstrate that there are some other influences on the water vapor adsorption efficiency, besides BET surface area in this system.12 Considering the samples with different pore structure, pore size may be another big factors influencing their water vapour adsorption performance. For Fe2O3 nanocubes, the largest increase in uptake takes place in the range of medium RHs when the filling of micropores starts, and follows at the higher RHs by capillary condensation in the mesopores. At the relatively low water vapour pressure, the water is preferentially adsorbed on the highly hydrophilic sites, formed monolayer adsorption.13 At the relatively higher pressure, multilayer adsorption occurs, followed by capillary condensation in the porous channels.14
Sample | Surface area (m2 g−1) | Pore size (nm) | Pore size (cm3 g−1) | Max water sorption capacity (%) |
---|---|---|---|---|
Fe2O3 nanocubes | 50.91 | 8.48 | 0.17 | 14 |
Fe2O3 nanofibers | 13.4 | 35.2 | 0.15 | 0.8 |
Bulk Fe2O3 | 8.79 | 6.78 | 0.02 | 0.4 |
Raw diatomite | 71.57 | 9.32 | 0.10 | 10 |
Calcined diatomite | 52.45 | 6.75 | 0.09 | 64 |
For the capillary condensation phenomena, Kelvin equation can be used. At the higher RH, the pore diameter, where capillary condensation takes place, can be calculated via Kelvin equation:
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Fig. 6 Cycling runs for the water vapour adsorption–desorption over Fe2O3 nanocubes at room temperature. |
Footnote |
† Electronic supplementary information (ESI) available: Details of experimental procedures; XRD and SEM image of the bulk Fe2O3 powder and porous Fe2O3 nanofibers; SEM images of the Fe2O3 samples with different amounts of urea; SEM images of products prepared under similar conditions but with DEG replaced by EG, and PEG 400; N2 adsorption–desorption isotherm for the conventional samples (raw diatomite and calcined diatomite). The inset shows BJH pore size distributions of the samples; water sorption kinetics of the conventional samples (raw diatomite and calcined diatomite) equilibrated for a fixed time at room temperature. See DOI: 10.1039/c5ra12456e |
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