X. H. Yanga,
H. Xiea,
H. T. Fu*a,
X. Z. An*a,
X. C. Jiangb and
A. B. Yub
aSchool of Metallurgy, Northeastern University, Shenyang 110819, China. E-mail: fuht@smm.neu.edu.cn
bDepartment of Chemical Engineering, Monash University, Clayton, VIC 3800, Australia
First published on 6th September 2016
Hierarchical three-dimensional nanosheet-assembled vanadium pentoxide (V2O5) microflowers are successfully synthesized by a hydrothermal method, followed by a high-temperature sintering treatment. Several advanced techniques are used to characterize the morphology and composition of the resulting nanostructures, such as TEM, HRTEM, SEM, XRD, and BET. The HRTEM image shows that the microflowers are assembled from the nanosheets with highly exposed {010} facets, as confirmed by selected area electron diffraction (SAED). According to N2 sorption isothermal studies, the as-prepared V2O5 microflowers show high specific surface area of 61.5 m2 g−1. The formation of the microflowers with assistance of NaHCO3, which may play a critical role in the self-assembly process, may be attributed to a “reproduction mechanism”. The gas sensing performances of both the V2O5 microflowers and the V2O5 nanosheets were evaluated towards several volatile organic compounds (VOCs), such as 1-butylamine, ethanol, acetone, and formaldehyde. The results show that the flower-like structure exhibits a superior sensing response and selectivity towards amines compared to that of the sheet-like structure at an optimum working temperature of ∼300 °C. The high selectivity towards 1-butylamine can be ascribed to the selective oxidation mechanism. This work will help explore vanadium oxides as gas sensors toward volatile organic compounds with high performance.
Vanadium oxides, especially vanadium pentoxide (V2O5, an n-type semiconductor), have been intensively studied as sensing materials recently due to their high chemical stability, low manufacturing cost, and high resistance to corrosion. These advantages make V2O5 high potentials for drunken driving tests, indoor gas detection, and disease diagnosis.11–13 These materials are highly shape-dependent on sensing performance towards some volatile organic compounds (VOCs), such as acetone,8 organic ammine,9 and ethanol.10 V2O5 nanostructures with all kinds of morphologies, such as 1D (nanotubes,11 wires,9 belts,12 rods13), 2D (nanosheets),14 and 3D structures (urchin-like,8 flower-like,15 hollow spheres16) have been synthesized to improve their sensing and electrical performance. For example, Liu et al. demonstrated that V2O5 nanobelts prepared by a hydrothermal method, having width and length in the ranges of 20–30 nm and 0.2–1 μm, show short response/recovery times of 30–50 s and a low detection limit (5 ppm) towards ethanol at 200 °C.10 Recently, we have reported nanorod-assembled urchin-like microstructures with good sensitivity toward acetone.8 However, there still exists a great challenge to control nano/microstructures with desirable morphologies for excellent sensing performance towards volatile gases.
Organic amines (e.g., 1-butylamine) are widely applied in polymer industries, rubber production, and manufacturing of dyes, pharmaceuticals and textiles.17 However, the 1-butylamine is toxic and easily absorbed through skin. Direct exposure of 1-butylamine vapor can lead to eye, skin and upper respiratory tract irritation.18 Therefore, it is necessary to properly detect and alert for those exposed to such gases. Currently, atmospheric 1-butylamine has been quantified by several advanced techniques, such as liquid chromatogram, fluorescence and other optical spectrum, which require expensive apparatuses and are not suitable for portable carrier.19 Resis-chemical sensors are proposed as a low-cost and high efficient tool to detect organic amines. Thus, the sensing materials become vital to the devices.
In this area, some metal oxide nanoparticles (V2O5, In2O3, ZnO and MoO3) have been investigated for detection of organic amines.20–24 For instance, the black rice pigment sensitized TiO2 thin film can be used as sensing layer to detect biogenic amines at room temperature.25 It is reported that ZnO nanoparticles films present a good sensing performance towards some volatile amines at room temperature, and the detection limit could reach to 162 ppm.26 Cao et al. reported that the three dimensional In2O3 nanosheets with a high surface area composed of ultrathin nanosheets show excellent amine sensing performance at room temperature. The 3D structure takes advantage of avoiding aggregation and facilitating the diffusion of the target gas.27 V2O5 nanowires, prepared by a sol–gel method, exhibit a very low detection limit of 30 ppb toward 1-butylamine.9 Shah et al. reported that V2O5/In2O3 core–shell nanorods, prepared by a combination of solid solution and hydrothermal methods, can be used for sensing n-propylamine with high selectivity and sensitivity (S = Ra/Rg, S = ∼14), but suffering from long response (48 s) and recovery time (121 s).28 Furthermore, our study shows that silver vanadate nanoparticles can be used for sensing organic amines and exhibit moderate response with sensitivity (S = 4.5 for Ag2V4O11) towards 100 ppm of 1-butylamine at 260 °C.19,29 Despite of the efforts above, the responses of these sensing materials toward 1-butylamine are not satisfactory for practical use, and still requires further enhancement.
Herein, we report a simple and effective hydrothermal method for the synthesis of nanosheet self-assembled V2O5 microflowers with large surface areas for sensing organic amines. The composition and morphology of such structures will be characterized with several analytical techniques, such as transmission electron microscopy (TEM), high-resolution transmission electron microscopy (HRTEM), scanning electron microscopy (SEM), X-ray diffraction (XRD), and Brunauer–Emmett–Teller (BET) surface area. The gas sensing performance (e.g., sensitivity, selectivity, and stability) of the as-prepared V2O5 microparticles toward several VOCs (including 1-butylamine) will be measured and evaluated. Finally, the possible mechanisms for achieving high sensing performance of such nanostructures will be discussed.
Before the measurement, a Ni–Cr resistor was inserted into the ceramic tube as a heater, which is used to control the operating temperature by adjusting the heating voltage (Vheating). A reference resistor was placed in series with the sensor to form a complete measurement circuit. The change of the voltage at the two end of the reference resistor (Rreference) can be monitored by the computer. The target gas (e.g., 1-butylamine) was injected into the testing chamber using a microsyringe. The response (S) of n-type semiconductors can be defined as the ratio of the resistances measured in air (Ra) and in the tested gas atmosphere (Rg): S = Ra/Rg. The output voltage was set at 5 V and the gas-sensing measurements were conducted at a relative humidity of 55–65%.
To further confirm the composition of the precursor and investigate the transformation from precursor to V2O5 particles, FT-IR was used to characterize the precursor and the sintered product. Fig. 2a shows the FT-IR spectra of the precursor and V2O5 microflowers. In the curve of precursor, the peaks concentrated at ∼3444 and 1637 cm−1 corresponds to the O–H stretching bond, which may generates from VOOH species. The small peaks located at ∼2973 and 2925 cm−1 represent CH2O– group, probably originated from VEG. The peak centered at ∼991 cm−1 can be assigned to VO stretching bond, while those centered at 638 and 617 cm−1 are attributed to the V–O–V bending mode and coupled bending vibration of V–O. From the FT-IR spectra, it can be confirmed that the VEG and VOOH species exist in the precursor, in good agreement with the deduction from the XRD pattern. The black curves in Fig. 2a shows a typical FT-IR spectrum of V2O5, in which the V
O stretching bond appears at ∼1014 cm−1. While the peak at 522 cm−1 is assigned to the V–O–V stretching bond. The V–O stretching bond and the coupled vibration between V
O and V–O–V bonds can be found at 664 and 848 cm−1, respectively.8,30
To identify the phase transformation of the precursor, TGA/DSC technique was also used to monitor the transformation process of the precursor in air, as shown in Fig. 2b. Considering the melting point of V2O5 (690 °C), the testing temperature ranges from room temperature to 600 °C. From the TGA curve (black solid line), there is a weight gain of ∼10% at ∼300 °C, corresponding to the transformation from low valence vanadium compounds to V2O5. Due to the complicated composition of the precursor, the weight gain does not exactly follow the theoretical value (∼21% from pure V2O3 to V2O5). The gain stops before ∼600 °C, which means the oxidation has completed. The DSC curve (blue dot line) indicates the oxidizing reaction is a exothermic reaction, while the reaction temperature can be determined as precise as 328.2 °C. Fig. 2c and d show the elemental EDS spectra of the precursor and sintered V2O5 products, respectively. The EDS spectrum of precursor clearly indicates the existence of carbon, due to the presence of VEG; while the peak corresponding to carbon (C) vanishes in the EDS spectrum of V2O5. The element of aluminium (Al) is generated from sample holders, while Au is attributed to Au spin-coating for SEM observation.
A few of pertinent parameters (including reaction temperatures, concentration of vanadium, reaction time, pH and molar ratio of vanadium to bicarbonate) have been optimized to investigate their effects on the morphologies. It is found that pH heavily affects the morphologies (Fig. 4), when other conditions are fixed at 0.75 mM (vanadium concentration), 260 °C, and 48 h. The effect of other parameters (e.g., concentration of vanadium, temperature, and reaction time) on the morphology can be found in Fig. S1–3.† Fig. 4 shows the effect of pH on the morphology of the precursor. The pH adjustment was achieved by HNO3 and NaHCO3. It can be observed that the sheet-like structure can form with wide range of pH, from 1 to 8. The self-assembled microflowers appear at pH 10. Due to the buffer properties of bicarbonate, the continuing addition of the amount of bicarbonate cannot increase the pH of the system. Therefore, the effect of the molar ratio of vanadium to bicarbonate needs to be investigated. The SEM images are shown in Fig. S4.† It can be found that the morphology of the precursors is not heavily changed at the molar ratio from 1:
1 to 1
:
2 (Fig. S4a and b†). Continuously increasing the molar ratio to 1
:
3 and 1
:
4, the microflowers trend to aggregate with each other and form larger microparticles (Fig. S4c and d†). Meanwhile, we also tried other bases (e.g., NaOH) to adjust high pH (≥10). However, no self-assembled microflowers are observed.
The mechanism for the formation of the nanosheet-assembled microflowers can be attributed to so-called “reproduction mechanism”. In the initial process of growth, the sheet-like particles might form at the low molar ratio of vanadium to bicarbonate. With the ratio increase, the concentration of H+ released from bicarbonate will ascent, leading to the incomplete nanosheets under the reducing conditions. The incomplete nanosheets agglomerate to form a new growth point. As a result, these new points further grow to form random nanosheet self-assembled microflowers.32 This mechanism can be confirmed by the aggregation of microflowers at high molar ratio of vanadium to bicarbonate.
Surface area is one key factor affecting the gas sensing performance.34 The surface areas of the as-prepared precursors and the corresponding V2O5 microstructure were measured by the BET method via N2 sorption isotherms. The isotherms of the sheet-like precursor and the corresponding V2O5 nanosheets are displayed in Fig. 5a and b. The BET surface area of the V2O5 nanosheets is ∼56.4 m2 g−1, much higher than that of the precursor (24.6 m2 g−1). While the isotherms of the nanosheet-assembled precursors and the corresponding V2O5 microflowers are shown in Fig. 6c and d. It can be seen that sintering can significantly increase the surface area of the particles (29.9 to 61.5 m2 g−1). It is also noted that the nanosheet-assembled microflowers show higher surface area than that of nanosheets. This may be the reason that the V2O5 microflower show higher sensing performance than that of V2O5 nanosheets. The microflowers may provide more sites for the adsorption of O2 molecules, which play an important role in the sensing mechanism. The pore sizes distributions (Fig. 5c and d) derived from both adsorption and desorption branches of the isotherms using the BJH method indicate the difference in porosity for the two materials.
The diffusion rates of gas molecules are dependent on temperatures, thus the working temperature significantly may affect both the response and the sensitivity. Fig. 6a displays the response of the sensors made from the nanosheet-assembled V2O5 microflowers, the V2O5 nanosheets and the commercial V2O5 particles toward 100 ppm of 1-butylamine with increasing working temperature from 240–340 °C. All V2O5 microflower-based sensors exhibit an optimum working temperature of 300 °C with S = 3.3 toward 100 ppm of 1-butylamine. In comparison, other two V2O5 based sensors (the V2O5 nanosheets and the commercial V2O5 particles) show the same optimum working temperatures, but the responses are lower than that of V2O5 microflowers.
The dynamic response–recovery transients of the V2O5-based sensors are shown in Fig. 6b. It is obvious that the output voltages of the sensors increase when the 1-butylamine is input, and decrease with the removal of the gas. Fig. 6c depicts the responses of three V2O5 based sensors toward different concentrations of 1-butylamine at 300 °C. It can be seen that the flower-like V2O5 particles show much higher response (∼3 times) towards 1-butylamine than the commercial V2O5 particles. The response of the sheet-like V2O5 particles is between those of the microflowers and the commercial V2O5 particles, however, the former exhibit ∼2 times higher response than the latter.
Selectivity is another critical characteristic in gas sensing, which needs to be evaluated to ensure an accurate detection of a single gas in a mixer with a higher response. The response of the sensors based on the flower-like, the sheet-like and the commercial V2O5 particles towards 100 ppm of different gases (e.g., 1-butylamine, acetone, pyridine, formaldehyde and alcohols) were measured at the working temperature of 300 °C, as displayed in Fig. 6d. It is noted that the flower-like V2O5 exhibit excellent selectivity to 1-butylamine, with much higher response than that of other gases. In comparison, the high selectivity towards 1-butylamine is observed on the sensors based on the sheet-like V2O5 particles, while the selectivity of the commercial V2O5 particles is not ideal. This indicates that the morphology of the V2O5 particles could highly affect the selectivity.
Recover time is also a key criterion to judge gas sensing performance of nanoparticles. Fig. 7a and b show the response/recovery time of the flower-like and sheet-like V2O5 particles, respectively. The response time is defined as the time required to 90% of the final equilibrium value, following exposure to 1-butylamine vapor. Inversely, the recovery time is defined as the time needed by the sensor to return to 10% of the original conductance in air, with removal of 1-butylamine vapor. It can be observed that the response time of the flower-like V2O5 particles (Fig. 7a) upon exposure to 5–100 ppm of 1-butylamine differs from 10–25 s, whereas the recovery time is 3–14 s. For the sheet-like V2O5 particles (Fig. 7b), the response time and recovery time vary from 10–17 s and 5–14 s, respectively. Furthermore, we also observed that the response/recovery time increases with gas concentration, probably due to the low vapor and diffusion rate of 1-butylamine in the gas chamber at high concentration. The above results show that the response speed of the flower-like V2O5 particles is slower than that of the sheet-like V2O5 particles. It can be concluded that the nanosheet assembly can enhance the sensitivity and selectivity to 1-butylamine of V2O5 particles, however, the response speed slightly decreased.
Repeatability is one of important parameters of a sensing material, related to long-term reliability of the sensor. As shown in Fig. 7c, the repeatabilities of the samples (the flower-like, the sheet-like, and commercial V2O5 particles) were evaluated by testing the response towards 100 ppm of 1-butylamine at 300 °C by repeating 10 times. It can be found that the response of the sensing materials remains constant during 10 tests, suggesting the excellent potential of the flower-like V2O5 as a sensitive, selective and stable sensing material for detection of 1-butylamine. In the case of sensing 1-butylamine, the nanosheet-assembled V2O5 microflowers show superior sensitivity and selectivity to Ag2V4O11 (ref. 29), Ag0.35V2O5 (ref. 19), VOx/Ag nanobelts,29 and V2O5 nanofibers.9
Regarding the gas sensing mechanisms of V2O5 nanoparticles, the general surface absorbed redox mechanism is usually used for fundamental understanding. However, the sensing mechanism toward amines is slightly different. When exposed to amines, the sensing material (V2O5) interacts with the chemisorbed oxygen species on the surface to form CO2, H2O, and NOx, and then release the trapped electrons to the oxide particles.19 The superior sensing response of the flower-like V2O5 particles to the nanosheets can be attributed to the higher surface area and the unique hierarchical structure. For the microflower structures, the radial and non-aggregated sheets may allow more gas molecules to contact. In contrast, the nanosheets may pack more densely than the microflowers. Hence the contact area with gases would be smaller than the microflowers. On the other hand, the highly selectivity of the V2O5 microflower sensor toward 1-butylamine is attributed to the selective oxidation of 1-butylamine. It is accepted that the selective oxidation of primary amines is favorable in the presence of vanadic acids.35 The V2O5 particles may exhibit vanadic acids-like behavior under sensing condition because of reaction between the surface defect and water.36,37 However, we need to point that the as-prepared V2O5 microflowers still show relatively low sensitivity compared with the Au doped ZnO nanoflakes.38 The reason may be due to the difference of work functions between metal oxides (4.65 eV for ZnO,38 4.5 eV for SnO2 (ref. 2) and 7 eV for V2O5 (ref. 28)). It is well-accepted that modifying by noble metal can improve the sensing performance, especially for the improvement of sensing performance by decoration of Au nanoparticles on the metal oxides (∼5.1 eV for Au).2,38,39 Therefore, the future work will focus on the modification of Au nanoparticles on the surface of V2O5 microflowers for achieving high sensing performance.
(i) Unique microflower structures. The sheet-like V2O5 particles have been obtained under the reported conditions, especially for the self-assembled microflower structures with diameter of ∼5 μm, composed of numerous polycrystalline nanosheets, leading to a high surface area up to 61.5 m2 g−1. The formation and growth was dependent on high pH at high molar ratio of vanadium to bicarbonate.
(ii) Excellent gas sensing performance. The sheet-like and flower-like V2O5 particles have been used for sensing detection of ethanol, 1-butylamine, acetone, pyridine, methanol, isopropanol, formaldehyde and 1-butanol. The flower-like V2O5 particles show a low detection limit to 5 ppm and a significant high selectivity toward 1-butylamine among the tested particles, at the optimum working temperature of 300 °C. Furthermore, the flower-like and sheet-like particles show short response (10–25 s for microflowers, 10–17 s for nanosheets) and recovery time (3–14 s for microflowers, 5–14 s for nanosheets) at the concentration range from 5–100 ppm under the reported conditions.
The results in this work ascertain the potential use of vanadium oxide nanoparticles for industrial and environmental applications in the future.
Footnote |
† Electronic supplementary information (ESI) available. See DOI: 10.1039/c6ra18848f |
This journal is © The Royal Society of Chemistry 2016 |