Xueying Zhanga,
Muhammad Ikrama,
Zhi Liua,
Lei Tenga,
Jialing Xuea,
Di Wanga,
Li Li*ab and
Keying Shi*ac
aKey Laboratory of Functional Inorganic Material Chemistry, Ministry of Education, School of Chemistry and Material Science, Heilongjiang University, Harbin 150080, PR China. E-mail: shikeying2008@163.com; lili1993036@hlju.edu.cn
bKey Laboratory of Chemical Engineering Process & Technology for High-efficiency Conversion, School of Chemistry and Material Science, Heilongjiang University, Harbin 150080, PR China
cKey Laboratory for Photonic and Electronic, Ministry of Education, Modern Experiment Center, Harbin Normal University, Harbin 150025, PR China
First published on 18th March 2019
To develop an ultra-sensitive and selective NOx gas sensor with an ultra-low detection limit, expanded graphite/NiAl layered double hydroxide (EG/NA) nanowires were synthesized by using hydrothermal method with EG as a template and adjusting the amount of urea in the reaction. X-ray diffraction and transmission electron microscopy showed EG/NA3 nanowires with a diameter of 5–10 nm and a length greater than 100 nm uniformly dispersed on the expanded graphite nanosheet (>8 layers). The synergy between NiAl layered double hydroxide (NiAl-LDH) and expanded graphite (EG) improved the gas sensing properties of the composites. As expected, gas sensing tests showed that EG/NA composites have superior performance over pristine NiAl-LDH. In particular, the EG/NA3 nanowire material exhibited an ultra-high response (Ra/Rg = 17.65) with ultra-fast response time (about 2 s) to 100 ppm NOx, an ultra-low detection limit (10 ppb) and good selectivity at room temperature (RT, 24 ± 2 °C), which could meet a variety of application needs. Furthermore, the enhancement of the sensing response was attributed to the nanowire structure formed by NiAl-LDH in the EG interlayer and the conductive nanonetwork of interwoven nanowires.
In the past few decades, sensors using electronic signals for NOx gas detection based on various materials, such as metal oxides,3 polymers,4 MoS25 and carbon materials,6,7 have been reported. In particular, due to their excellent physical and electrical properties, carbon materials, such as carbon nanotubes (CNTs), carbon black (CB), graphene (GN), and carbon nitride (g-C3N4) nanomaterials, have received great attention as gas sensor materials.8 Seekaew et al.9 obtained 3D TiO2/graphene–carbon nanotube (TiO2/G-CNT) composites by chemical vapor deposition and sparking. It was found that 3D TiO2/G-CNT composites with optimum spark time of 60 s at RT showed high response to toluene (500 ppm, ∼42%). Chu et al.10 synthesized three-dimensional (3D) α-Ni(OH)2/carbon black composites (NiCB) by a simple reflux method. It was found that NiCB composites with 20 mg carbon black had excellent response to NO2 gas at RT (100 ppm, ∼62.45%). Ye et al.11 obtained graphene nanoplate (GN)-polyaniline (PANI) composites through in situ polymerization, which exhibited good sensor response for 100 ppm NH3 at RT (15 ppm, ∼1.5%). Gong et al.12 successfully synthesized a g-C3N4 modified ball-flower like Co3O4 composite (Co3O4/pCNH) by a simple hydrothermal method. It was found that the Co3O4/pCNH composites exhibited a very high response to ethanol gas at 210 °C (500 ppm, ∼30.2%). However, due to the high curvature of 0D carbon spheres and 1D CNTs, nanomaterials are not easily grown on their surfaces. EG and g-C3N4 are ideal atomic thickness 2D substrates for anchoring nanomaterials.12,13 In our previous work, EG was used as a substrate to synthesize CeO2/graphene nanoflower composites. The sensitivity of CeO2/graphene composites for 100 ppm NOx was 10.39% at RT.14 However, due to its sluggish response, it is not well suited for commercial application.
Among the most promising materials, LDH materials have been widely used for catalysts,15 anion exchange,16 magnetic elements17 and oxide precursors, owing to their versatility in both chemical composition and structural morphology.18–20 Recently, LDHs have received great attention as gas sensitive materials due to their high specific surface area and short carrier transport diffusion length.21–23 However, application of pristine LDHs has been hindered due to their low electrical conductivity and tendency to stack easily in the solid state.24
To overcome these problems, in the present work, EG and LDHs were combined to synthesize a nanomaterial with the advantages of enhanced gas sensitivity, ultra-low detection limit, and improved response and response time, all of which were beneficial for practical and commercial application of composite materials.25 The EG/NiAl-LDH composites were synthesized by using EG and varying the amount of urea in the hydrothermal reaction. The entire process is illustrated in Scheme 1. The process begins with activated EG and then synthesizes EG/NA nanowires by vacuum impregnation and hydrothermal methods. During vacuum impregnation, the EG interlayer was opened and the NiAl-LDH precursor solution was pumped into the interlayers of EG. Subsequently, EG was used in the hydrothermal process for (i) its functional surface, which served as a template for NiAl-LDH nucleation and provided anchor sites for LDH nanosheets; (ii) its conductivity in EG/NA composites.26 At the same time, by using EG and changing the concentration of urea in the precursor solution, the morphology of the obtained NiAl hydrotalcite was tuned from a three-dimensional (3D) flower structure to EG-loaded NiAl-LDH nanosheets, especially EG/NA nanowires. It is worth noting that EG/NA nanowires exhibited superior performance for NOx gas compared to other forms of NiAl-LDH materials such as nanosheets and nanoparticles.
When urea loading increased to 1 mmol, there was a large number of particles and a small amount of nanowire attached to the EG surface (EG/NA2, Fig. 1d). When urea loading was further increased to 2 mmol and 3 mmol, the morphology of nanowires became well developed (EG/NA3 and EG/NA4, Fig. 1e and f). By comparing the morphologies of pristine NiAl-LDH and EG-loaded NiAl-LDH, it could be concluded that EG played an important role in synthesising EG/NA nanowires: the electrostatic interaction between the EG plate and NiAl-LDH nanosheets prevented aggregation of the obtained NiAl-LDH.27 In summary, TEM results showed that the addition of EG and the change of urea loading in the hydrothermal reaction changed the morphology of NiAl-LDH.
X-ray diffraction (XRD) measurements were taken to confirm the phases and structures of the composite materials. Fig. 2a showed that the EG/NA composites had an XRD pattern similar to NiAl-LDH. The peak at 26.5° was attributed to the (002) plane of the hexagonal graphite structure; the lower strong diffraction peaks at 11.7°, 35.2°, 38.4° and 61.1° correspond to the (003), (012), (104) and (110) atomic surface reflections, respectively, of the LDH phase (JCPDS card no. 15-0087). This indicated that the presence of EG did not affect the crystal structure of the synthesized NiAl-LDH. However, compared to the Bragg reflection intensity of NiAl-LDH, EG/NA1 exhibited weaker (003), (006) and (009) Bragg reactions, indicating there was less ordered stacking of LDH nanosheets. This might be attributed to the polar surface of the EG plate interfering with the orderly stacking of LDH nanosheets by electrostatic interaction.28,29 As the amount of urea increased, the peak intensity of EG/NA2 further weakened, indicating the ordered stacking of LDH nanosheets was further reduced, and nanoparticles began to appear. EG/NA3 and EG/NA4 nanowires presented nearly identical XRD patterns, indicating that they had nearly identical nanowire compositions.
Fig. 2 (a) XRD patterns of NiAl-LDH and EG/NA composites; (b and c) TEM images of the EG/NA3 nanowires; (d–f) HRTEM images of the EG/NA3 nanowires. |
To further investigate the morphology and structure of the EG/NA3 nanowires, TEM/HRTEM were carried out (Fig. 2b–f). Fig. 2b shows that a large number of nanowires were grown on the EG plate; the EG/NA3 nanowires with large specific surface area had a diameter of 5–10 nm and length greater than 100 nm, as shown in Fig. 2c and d. The large specific surface area was confirmed by the N2 adsorption/desorption isotherms (Fig. 3). The specific surface area (107.3 m2 g−1) of EG/NA3 was 2.4 times that of NiAl-LDH (45.4 m2 g−1). The nanowires with large specific surface area shorten the diffusion distance of carriers, which facilitates efficient and rapid delivery of gases to active sites for quick adsorption and desorption.30,31 This network of ultra-thin nanowires also ensured a maximum exposure of active metal ions to gas.32 In addition, the interlayer of multi-layer expanded graphite could accommodate large volume changes of nanowires, avoiding collapse or deformation during repeated adsorption and desorption.33 HRTEM images of EG/NA3 displayed in Fig. 2d–f indicate that the nanowires were formed by nano-sized crystals and the lattice spacings 0.751 and 0.252 nm correspond to the (003) and (012) planes of the NiAl-LDH nanocrystal, respectively; 0.21 nm corresponds to the (002) plane of EG. These results were in good agreement with XRD results.
Fig. 3 N2 adsorption–desorption isotherms of nanocomposites (inset is the pore diameter distribution curve of the corresponding sample): (a) NiAl-LDH; (b) EG/NA3. |
The FT-IR and Raman spectra of the prepared samples are shown in Fig. 4. In Fig. 4a, EG/NA3 had similar infrared characteristic peaks as NiAl-LDH. The broad band in the range of 3000–3500 cm−1 corresponds to the stretching mode of O–H from the brucite-like layer and interlayer water molecules.34 The interlayer H2O could also be observed close to 1600 cm−1.35 The strong vibration band near 1379 cm−1 was attributed to interlayer carbonate36,37 and M–O–C (M: metal atom) was recorded at 1065 cm−1.38 A small peak near 430 cm−1 confirmed the presence of nickel hydroxide. Since it was difficult to observe the characteristic stretching vibration peaks of EG, Raman testing was performed for EG and EG/NA3.39 In the Raman spectra, there were two strong peaks around 1383 and 1592 cm−1 in both EG and EG/NA3 composites (Fig. 4b) which could be assigned to the D and G bands of carbon material, respectively.40 The Raman spectrum of the EG/NA3 nanowires contained peaks characteristic of graphene.41 This indicated the coexistence of EG and NiAl-LDH in EG/NA3 composites. Furthermore, the intensity ratio of the D band to the G band in the EG/NA3 complex increased compared to a pure EG sample, indicating that doping with NiAl-LDH may result in a more disordered structure. This is ascribed to the reduction of the size of the sp2 region in the EG plane during the hydrothermal reaction, unrepaired topological defects, and carbon vacancies caused by the removal of oxygen functional groups from EG during NiAl-LDH growth.42 The defect sites in the EG/NA3 composites were similar to the oxygen-containing functional groups, adsorbing metal ions and serving as anchoring centers for metal ion dispersion support.43
Fig. 4 (a) FT-IR spectra of NiAl-LDH and EG/NA3; (b) Raman spectra of EG and EG/NA3; (c) XPS survey spectra of EG and EG/NA3; (d) C 1s XPS spectra of EG and EG/NA3. |
XPS studies further proved the chemical structures of EG and EG/NA3. EG contained only C and O elements, namely C 1s and O 1s at 282 eV and 530 eV, respectively (Fig. 4c). Compared with pure EG, the XPS spectrum of EG/NA3 nanowires exhibited Al 2p and Ni 2p peaks, in addition to C 1s and O 1s peaks. This result further confirmed the presence of NiAl-LDH in EG/NA3 nanowires. Fig. 4d depicts the C 1s XPS spectra of EG and EG/NA3. The C 1s region of EG was deconvoluted into three peaks. The peaks at 284.6, 286.6 and 288.2 eV were assigned to C–C, C–O and OC–O.27,44 The peaks located at 286.6 and 288.2 eV were associated with oxygen-containing functional groups, which effectively generate anchoring sites for adsorption of inorganic nanomaterials during the hydrothermal reaction.45 In addition, for EG/NA3 composites, the peak intensities of 286.6 and 288.2 eV decreased, indicating that the number of oxygen-containing functional groups decreased during hydrothermal reaction.46,47
In this work, NOx (the concentration ratio of NO2 and NO was 17:5) was selected as the target analyte to evaluate the sensing performance of the obtained EG/NA3 at RT. Fig. 5a and b show the dynamic response of gas in EG/NA3 composite film sensor during cyclic exposure, with NOx concentrations ranging from 100 ppm to 0.01 ppm. Fig. 5a shows the typical response–recovery cycle curve for a sensor with lower NOx concentration. After injection of NOx gas, the resistance of the thin film sensor dropped sharply. After stabilization, the NOx was pumped out (injected into fresh air) and the resistance returned to the initial value, showing p-type semiconductor behavior. When the NOx concentration was 100 ppm, the response was as high as 17.65% and the response time was 2 s. It was found that the response gradually decreased as NOx concentration decreased, but response time was maintained within 6.6 s. In addition, the gas response and response time of EG/NA synthesized with different urea amounts were also investigated at RT, as shown in Fig. 5b, S2 and Table S1.† As expected, the EG/NA3 sensor exhibited an enhanced response to each NOx concentration in a given region compared to the other samples. For 100 ppm NOx, the response of the EG/NA3 sensor was 3.9, 3.4 and 2.6 times those of EG/NA1, EG/NA2 and EG/NA4, respectively (Fig. 5b). It can be seen more intuitively in the column chart in Fig. 4c. The reproducibility and reliability of EG/NA3 were further explored at the same NOx concentration. Fig. 5d shows a stable response to 100 ppm NOx for 10 cycles at RT. The response and recovery time exhibited no change after 10 consecutive cycles. These results strongly demonstrated that EG/NA3 nanocomposites are promising candidates for gas sensing applications.
In order to be well applied in practice and industrially, selectivity and stability are two important factors to consider when preparing gas sensors.49,50 As shown in Fig. 5e, the selectivity of the prepared EG/NA3 sensor was tested by H2, CO, CH4 and NH3 gases. The measured response for 100 ppm NOx (17.65) was much higher than that for 100 ppm NH3 (1.4), while the sensor was almost unresponsive to H2, CO and CH4 at the same concentration. The sensor's gas response to NOx was much higher than several other gases, mainly because NOx reacts with absorbed oxygen (O2−) at RT.51,52 The sensor was placed in air at RT for 72 h to verify the stability of the EG/NA3. The resistance of the EG/NA3 sensor was then tested for 100, 5, and 0.5 ppm NOx gas every 10 days at RT (Fig. 5f). The results showed that the EG/NA3 composite was stable to NOx gas and could be stable for up to 100 days at any concentration. Based on the above analysis, we believe that the EG/NA3 nanowire sensor may be suitable for detection of NOx in real life environments.
In addition, the sensing properties of EG, NiAl-LDH and EG/NA3 samples were investigated. In Fig. 6 and Table S2,† the EG/NA3 composite sensor shows faster response to different concentrations of NOx and a faster response/recovery time compared to the other two sensors. For 100 ppm NOx, the response of the EG/NA3 sensor was approximately 8 times that of EG and NiAl-LDH. The EG/NA3 sensor also had faster response–recovery times of 2 s and 9.3 s, respectively (see Table S2†). The enhanced of response was due to the synergy between EG and NiAl-LDH (NiAl-LDH nanowires and assembly network of EG). Therefore, the electrical properties of the three samples were further studied.
Nd = (−2/e0εε0)[d(1/C2)/dV]−1 | (1) |
It has been well known that the resistance of materials plays a crucial role in their sensing process; appropriate resistance and electron transport in air result in better gas sensitivity.56 Therefore, EIS of the EG, NiAl-LDH and EG/NA3 composites was carried out, as shown in Fig. 7b. Here, RΩ denotes the uncompensated bulk resistance of the electrolyte, separator and electrode. Rct was attributed to the charge transfer resistance at the interface of the active material; C is a long phase angle element, involving double layer capacitance. The semicircle in the high frequency range was related to the surface properties of the electrode, corresponding to Rct. The impedance of the EG/NA3 electrode was between pure EG and NiAl-LDH (see Table S3†). This result was consistent with MS analysis. Therefore, according to MS and EIS analysis, an improvement in sensing performance was expected due to an improvement in carrier density of the EG/NA3 composites.
The proposed gas sensing mechanism is illustrated in Scheme 2A–D. The gas sensing mechanism of the EG/NA3 sensor should follow the surface charge model, as explained by the change in resistance of EG/NA3 sensor when exposed to different gas environments.46 Oxygen adsorption played an important role in charge transport of EG/NA3. To the best of our knowledge, semiconductors typically react with O2 during semiconductor sensor operation, resulting in the formation of oxygen species (such as O2−) on their surfaces and grain boundaries under an air atmosphere.59 These adsorbates formed a space charge region inside the semiconductor and formed an electron depletion layer due to electron transfer onto the surface-adsorbed oxygen.
When EG/NA3 was exposed to air, O2 could easily capture free electrons from the conduction band or donor level of EG/NA3 to form an oxygen adsorbate (O2−), which could improve the performance of NOx sensors (reaction (2)). When exposed to NOx, NOx was directly adsorbed on EG/NA3 and reacted with O2− to form NO2− (reaction (3)–(5)). As the interaction time prolonged, NO2− became partially NO3− in reaction (6). This process captured electrons from the conduction band or donor level of NiAl-LDH, resulted in a decrease in electron density, and finally increased the hole carrier density on the semiconductor surface due to electron loss.60 From the results of electrochemical tests and gas sensitivity tests, we learned that EG/NA3 exhibited p-type semiconductor behavior. The increase in hole density caused a decrease in semiconductor resistance, which eventually led to a rapid decline in resistance (see Fig. 5).
O2 + e− → O2− | (2) |
NO2 + e− → NO2− | (3) |
NO2 + O2− → NO2− + 2O | (4) |
NO + O2− → NO2− + O | (5) |
NO2− + O → NO3− | (6) |
The gas sensing mechanism was primarily due to the direct charge transfer between the NOx molecule and the sensing material, once the target gas was absorbed by the sensor. Since EG behaved as a typical p-type semiconductor and the oxidized NOx acted as an electron acceptor, NOx absorption resulted in an increase in hole density and an increase in conductivity. In summary, the high performance of the EG/NA3 gas sensor for NOx could be attributed to three factors. First, in addition to improving the conductivity of the sensor element, the multilayer EG substrate also produced an effective Schottky contact at the interface with NiAl-LDH, which greatly enhanced the gas sensing performance.61,62 Second, the slit holes between the parallel layers of multilayer EG and the pores formed by the interdigitated NiAl-LDH nanowires in the EG interlayer might enhance gas sensing performance. The slit holes and pores could act as channels for gas diffusion, thus providing more active sites for the reaction of NOx with surface adsorbed oxygen species. Third, the NiAl-LDH nanowires shortened the gas transport path and resulted in a higher surface area for the EG/NA3 composites. Therefore, they increased the number of active adsorption sites and enhanced the interaction between the NOx molecule and EG/NA3.
Footnote |
† Electronic supplementary information (ESI) available. See DOI: 10.1039/c9ra00526a |
This journal is © The Royal Society of Chemistry 2019 |