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Article

Effects of Base Materials (α-Alumina and/or γ-Alumina) on Volatile Organic Compounds (VOCs)-Sensing Properties of Adsorption/Combustion-Type Microsensors

1
Graduate School of Integrated Science and Technology, Nagasaki University, 1-14 Bunkyo-machi, Nagasaki 852-8521, Nagasaki, Japan
2
Graduate School of Engineering, Nagasaki University, 1-14 Bunkyo-machi, Nagasaki 852-8521, Nagasaki, Japan
3
Gas Equipment R&D Center, Yazaki Energy System Corporation, 23 Minami Kajama, Futamata-cho, Tenryu-ku, Hamamatsu-shi 431-3393, Shizuoka, Japan
*
Author to whom correspondence should be addressed.
Chemosensors 2025, 13(1), 9; https://doi.org/10.3390/chemosensors13010009
Submission received: 13 December 2024 / Revised: 5 January 2025 / Accepted: 6 January 2025 / Published: 7 January 2025
(This article belongs to the Special Issue Advanced Chemical Sensors for Gas Detection)

Abstract

:
The sensing properties of adsorption/combustion-type microsensors using 5 wt% Pt-loaded aluminas, which consist of two kinds of alumina (α-Al2O3 and γ-Al2O3), as sensing (catalytic) materials for ethanol and toluene, were investigated in air, and the mixing effects of α-Al2O3 with γ-Al2O3 on the dynamic and static responses of the sensors were discussed in this study. The mixing of 50 wt% α-Al2O3 with γ-Al2O3 was the most effective in enhancing the dynamic responses to ethanol, which originated from the flash combustion behavior of ethanol and/or their partially decomposed products adsorbed on the sensing films from 150 °C to 450 °C, while further mixing of α-Al2O3 with γ-Al2O3 tended to increase the dynamic responses to toluene. On the other hand, the static responses to both ethanol and toluene, which arise from their catalytic combustion at elevated temperatures (450 °C), mainly increased with an increase in the addition of α-Al2O3 in the 5 wt% Pt-loaded aluminas. These results indicate that the synergistic effects of the catalytic activity and the thermal conductivity of the 5 wt% Pt-loaded aluminas are the most important for the sensing properties of these sensors to ethanol and toluene.

1. Introduction

The large number of volatile organic compounds (VOCs) generated from various building materials, such as paints, adhesives, and resins, has been a serious problem for a long time, and it is widely recognized that these substances have a variety of adverse effects on human health [1,2,3]. In order to reduce these symptoms, so-called “sick house syndrome” and “chemical sensitivity”, it is essential to develop specific VOC-sensing devices that can detect VOCs in indoor environments with high sensitivity. On the other hand, various kinds of VOCs are also contained in human biogases, such as exhaled breath and skin gas, and monitoring changes in their concentrations can help determine the health status and presence or absence of disease [4,5,6]. For example, acetone has been reported to be a biomarker for diabetes and metabolic activity, isoprene and pentane for heart disease, and toluene and 1-nonanal for lung cancer [7,8,9,10,11], and the development of a wearable device that can sensitively and selectively detect these VOCs is significantly attractive in the healthcare and medical fields. Recently, various gas sensors have been developed for the sensitive and selective detection of different types of VOCs [12,13,14,15,16,17,18,19,20,21,22,23,24]. Our group has developed adsorption/combustion-type gas sensors that combine the functions of “VOC adsorption” and “flash VOC combustion” for many years, by dynamically operating kinds of catalytic combustion-type gas sensors, in order to detect such ultra-trace amounts of VOCs [25,26]. After VOCs are adsorbed on the surface of the catalytic materials of the sensors at low temperatures, they are burned by flash heating and the large amount of combustion heat generated becomes output as a sensor signal. We previously reported that the VOC response of adsorption/combustion-type gas sensors was drastically improved by impregnating Pd and Au nanoparticles in an optimal ratio on γ-alumina (γ-Al2O3) or by highly dispersing core/shell (Au/Pd) nanoparticles by ultrasonic reduction on γ-Al2O3 [27,28]. We also confirmed that the VOC response was improved by co-loading Pt and a metal oxide on γ-Al2O3 and that the VOC-sensing characteristics were highly dependent on the type of metal oxide [29,30]. In the process of clarifying the VOC-response mechanism of adsorption/combustion-type gas sensors while closely investigating the VOC oxidation activity and adsorption/desorption characteristics, it was suggested that the thermal conductivity of the catalytic material also had a significant effect on the VOC-response characteristics [31]. In fact, our previous research revealed that the VOC-response characteristics of the sensor were improved when α-alumina (α-Al2O3), which has a small specific surface area but high crystallinity, was mixed with γ-Al2O3 and that they were loaded with Pd and Au [26]. In this case, it was inferred that the higher thermal conductivity of α-Al2O3 compared with γ-Al2O3 contributed to the improved VOC-response characteristics. In this study, therefore, we focused on Pt nanoparticles as a noble-metal catalyst for efficient VOC combustion and aimed to clarify the effect of mixing α-Al2O3 with γ-Al2O3 as the base material of the sensing film on the VOC-sensing properties of adsorption/combustion-type microsensors for two kinds of VOCs, ethanol and toluene.

2. Experimental Section

2.1. Preparation of Sensing Materials and Characterization

γ-Al2O3 powder (JGC Catalysts and Chemicals Ltd., Kanagawa, Japan) and α-Al2O3 powder (TM-DA, Taimei Chemical Chemicals Co., Ltd., Tokyo, Japan) were mechanically mixed in an agate mortar, and then Pt particles were loaded onto their surfaces by general impregnation with hydrogen hexachloroplatinate(IV) hexahydrate (FUJIFILM Wako Pure Chem. Corp., Osaka, Japan), followed by heat treatment at 500 °C for 1 h. The obtained powder is denoted as nPt/γ(r)α(t)-Al2O3 [n: the amount of Pt loaded (wt%), r: the weight ratio of γ-Al2O3 to all aluminas (wt%), t: the weight ratio of α-Al2O3 to all aluminas (wt%)], and nPt/γ(100)α(0)-Al2O3 and nPt/γ(0)α(100)-Al2O3 are abbreviated and simply expressed as nPt/γ-Al2O3 and nPt/α-Al2O3, respectively. The pore size distribution and the specific surface area (SSA) of the obtained powders were measured by Barrett-Joyner-Halenda (BJH) and Brunauer-Emmett-Teller (BET) methods using nitrogen adsorption-desorption isotherms (TriStar 3000, Micromeritics Inst. Corp., Norcross, GA, USA), respectively [32,33,34]. The crystal phases of the powders were characterized by X-ray diffraction analysis (XRD; Minflex 600-DX, Rigaku Corp., Tokyo, Japan) using Cu Kα radiation (40 kV, 40 mA), and their crystallite sizes were calculated by using the Scherrer equation. The chemical states of Al, O, and Pt on the surface of the representative powders were characterized by X-ray photoelectron spectroscopy using Al Kα radiation (XPS; ACIS-TLATRA DLD, Kratos Analytical, Manchester, UK). The binding energy was calibrated using the C 1s level (285.0 eV) of the usual contamination.
The dispersibility, surface area, and average particle size of the Pt nanoparticles on the surface of typical 5Pt/γ(r)α(t)-Al2O3 powders were calculated using the CO-pulse method (BELCAT II, MicrotracBEL Corp., Osaka, Japan). The nanostructure of the typical 5Pt/γ(r)α(t)-Al2O3 powder was observed by transmission electron microscopy (TEM; JEM-ARM200F, JEOL Ltd., Tokyo, Japan), and scanning transmission electron microscopy with energy dispersive X-ray spectroscopy for elemental mapping (STEM-EDS; JEM-ARM200F and JED-2300T, JEOL Ltd., Tokyo, Japan). The thermal conductivity of representative nPt/γ(r)α(t)-Al2O3 powders was measured by using a modified transient plane source sensor (TRIDENT, C-Therm Technologies, Fredericton, NB, Canada). The nPt/γ(r)α(t)-Al2O3 powders were pelletized by compressing at 1000 kg for 8 min, followed by annealing at 500 °C for 2 h in ambient air, and the obtained disks with a diameter of ca. 2 cm and a thickness of ca. 1 mm were used for the thermal conductivity measurement. The heat treatment condition was the same as that of the sensor fabrication described in the following section. The catalytic combustion behavior of ethanol and toluene over typical 5Pt/γ(r)α(t)-Al2O3 powders was measured using a handmade catalytic activity evaluation system. The 5Pt/γ(r)α(t)-Al2O3 powders were pelletized by compressing at 1000 kg for 8 min, followed by annealing at 500 °C for 2 h in ambient air, and the obtained disks with a diameter of ca. 1 cm were crushed to obtain irregularly shaped agglomerates with a size of 250–850 μm. They were packed into the region of ca. 12 mm in width in the center of a fixed bed reactor with an inner diameter of 2.0 cm, and the oxidation activity of ethanol and toluene over the typical nPt/γ(r)α(t)-Al2O3 powders was measured in synthetic air at a flow rate of 20 cm3 min−1 (space velocity: 8159 h−1) and in compressed air at a flow rate of 20 cm3 min−1 (space velocity: 40,795 h−1).

2.2. Fabrication of Sensors and Measurement of Sensing Properties to Ethanol and Toluene

Figure 1a shows a stereomicroscope photograph of a microsensor platform with a couple of Pt microheaters, which was fabricated by MEMS technology, and Figure 1b shows a SEM photograph of a Pt microheater, which was covered with a thin alumina film, on a thin insulating substrate (ca. 70 × 70 μm2) with a diaphragm structure. The Pt microheater also served as a detector. The microsensor platform, which was recently downsized from the previous one [16,17,18,19,20,21,22,23], was designed by Yazaki Energy System Corp. The nPt/γ(r)α(t)-Al2O3 and unloaded γ(r)α(t)-Al2O3 powders were used as the sensing and reference materials, respectively. They were mixed with an appropriate amount of an organic vehicle consisting of polyvinyl butyral resin (mean polymerization degree: 700)], di-n-butyl phthalate, and terpineol by ball milling for 30 min. The obtained nPt/γ(r)α(t)-Al2O3 and unloaded γ(r)α(t)-Al2O3 pastes were applied over both the Pt microheaters, as a sensing film or a reference film, respectively, by drop coating employing an air-pulse fluid dispenser (MS-10DX, Musashi Eng., Inc., Tokyo, Japan) with a suitable syringe. The microsensor chips attached to these films were then heat-treated at 500 °C for 2 h in ambient air. The obtained sensors were referred to as sensing materials (nPt/γ(r)α(t)-Al2O3). Figure 1c shows the SEM photographs of a typical sensing 5Pt/γ(r)α(t)-Al2O3 film on a substrate with a Pt microheater. The thickness at the center of the film was approximately 30–40 μm, and the thickness gradually decreased toward the edge of the film. In addition, the surface of the film was relatively smooth, and the morphology of the film was formed with relatively good reproducibility.

2.3. Measurement of Sensing Properties to Ethanol and Toluene

The sensing properties of ethanol and toluene were measured in an acrylic chamber (internal volume: approximately 50 dm3) in which 10, 100, and 1000 ppm of ethanol or toluene were vaporized just on a compact ceramic heater. The nPt/γ(r)α(t)-Al2O3 sensors consist of sensing (nPt/γ(r)α(t)-Al2O3) and reference (γ(r)α(t)-Al2O3) films with Pt microheaters, and these films were assembled into a bridge circuit, as shown in Figure S1a. All sensors were consecutively pulse-heated during a cycle of 10 s from low temperature (LT, 150 °C, 9.6 s) to high temperature (HT, 450 °C, 0.4 s) in this study. A typical signal profile of the sensor is shown in Figure S1b. Ethanol, toluene, and their related components (intermediates), which are produced by partial oxidation and/or condensation, are adsorbed on the oxide surfaces of both films at 150 °C in the target gas. These adsorbates burn mainly on the oxide surface of the sensing film the moment the sensor is heated to 450 °C. At that time, the sensor-signal profile typically has one dynamic signal originating from the flash catalytic combustion of all the adsorbates mainly on the oxide surface of the sensing film. A static signal originating from the general catalytic combustion of ethanol or toluene mainly on the oxide surface of the sensing film is constantly confirmed after the instantaneous dynamic signal disappears during pulse heating at 450 °C. The magnitude of the general response (ΔVMAX) was defined as the largest difference between the output voltage in air containing ethanol or toluene and that in air (ΔV). Two responses, which were calculated by integrating the dynamic and static signals of the sensor-signal profiles, were defined as the integrated dynamic response (IDR) and integrated static response (ISR), respectively (see Figure S1b).

3. Results and Discussion

3.1. Characterization of Sensor Materials

Figure S2 shows the nitrogen adsorption/desorption isotherms and pore size distributions of all the 5Pt/γ(r)α(t)-Al2O3 powders. Figure 2 shows the dependence of the SSA of the 5Pt/γ(r)α(t)-Al2O3 powders on the amount of α-Al2O3 (t). The amount of nitrogen adsorbed on the 5Pt/γ-Al2O3 powder was the largest among all the 5Pt/γ(r)α(t)-Al2O3 powders, and thus both the pore volume and the SSA (ca. 219 m2 g−1) of the 5Pt/γ-Al2O3 powder were also the largest among them. In addition, the large hysteresis of the nitrogen adsorption-desorption isotherms was clearly confirmed under a relative pressure of 0.6–1.0, indicating that they were classified mainly as type-IV isotherms in the models of IUPAC [32]. Thus, the mesopore distribution arising from nitrogen adsorption was significantly different from that of nitrogen desorption. The SSA monotonically decreased with an increase in the amount of α-Al2O3, as shown in Figure 2, and the ratio of the small mesopores (diameter: ≤ca. 5 nm) to large mesopores (diameter: ≥ca. 5 nm) gradually increased with the decrease in the SSA. The SSA of the 5Pt/α-Al2O3 powder was the smallest among them (ca. 12 m2 g−1), while the adsorption and desorption isotherms had little hysteresis and the diameters of the mesopores were mainly less than 5 nm. Figure S3 shows the XRD spectra of all the 5Pt/γ(r)α(t)-Al2O3 powders, and Figure 3 shows the dependence of the ratio of the normalized integral intensity of the (400) peak of γ-Al2O3 to that of the (116) peak of α-Al2O3 (I400,γ/I116,α) on the amount of α-Al2O3 in the 5Pt/γ(r)α(t)-Al2O3 powders. All the peaks of the 5Pt/γ-Al2O3 powder were assigned to γ-Al2O3 (JCPDS No. 10-0425), while all the peaks of the 5Pt/α-Al2O3 powder were assigned to either Pt (JCPDS No. 04-0802) or α-Al2O3 (JCPDS No. 71-1123). In addition, the peaks of both γ-Al2O3 and α-Al2O3 were confirmed in the XRD spectra of the other 5Pt/γ(r)α(t)-Al2O3 powders. On the other hand, the small peaks of Pt were detected only in the 5Pt/γ(75)α(25)-Al2O3 powder among them, which indicates that the crystallinity and/or crystallite size of Pt nanoparticles loaded to the γ(r)α(t)-Al2O3 powders increased with an increase in the amount of α-Al2O3 in the 5Pt/γ(r)α(t)-Al2O3 powders. Furthermore, the I400,γ/I116,α value monotonically decreased with an increase in the amount of α-Al2O3 in 5Pt/γ(r)α(t)-Al2O3. The dependences of both SSA (Figure 2) and I400,γ/I116,α (Figure 3) values on the amount of α-Al2O3 in the 5Pt/γ(r)α(t)-Al2O3 obviously show that α-Al2O3 was uniformly mixed with γ-Al2O3 in the 5Pt/γ(r)α(t)-Al2O3 powders.
Figures S4 and S5 show the XPS spectra of Pt 4f, Al 2s, and O 1s of all 5Pt/γ(r)α(t)-Al2O3 powders, and variations in the ratio of Pt or Al to all Pt and Al species and the ratio of each Pt component to all Pt species with the amount of α-Al2O3 in the 5Pt/γ(r)α(t)-Al2O3 powders are shown in Figure 4. All the ratios were calculated by the deconvolution of their XPS spectra. The half-widths of both the Al 2s and O 1s spectra gradually narrowed with an increase in the amount of α-Al2O3 (“from ca. 2.7 eV to ca. 2.0 eV” and “from ca. 2.8 eV to ca. 1.8 eV”, respectively). In addition, the binding energy of the Al 2s spectra was hardly dependent on the amount of α-Al2O3, whereas the binding energy of the O 1s spectra was negatively shifted with an increase in the amount of α-Al2O3. On the other hand, the amount of Pt0 (Pt metal) increased and the amount of Pt2+ (such as PtO) decreased with the amount of α-Al2O3, while the amount of Pt4+ (such as PtO2) remained almost unchanged. Nevertheless, the binding energy of Pt positively shifted with the amount of α-Al2O3, while the amount of Pt2+ was much larger than those of Pt0 and Pt4+. These results indicate that the electron density in all the Pt components decreased with an increase in the amount of α-Al2O3 and that the electrons were transferred to the oxygen species of the Al2O3-components due to the interaction between Pt and Al2O3. Moreover, the ratio of Pt to all Pt and Al species on the 5Pt/γ(r)α(t)-Al2O3 surface increased with an increase in the amount of α-Al2O3, even though the amount of Pt loaded onto the mixed aluminas was only 5 wt% for all 5Pt/γ(r)α(t)-Al2O3 powders. In other words, the amount of Pt loaded per unit SSA increased with an increase in the amount of α-Al2O3 because the SSA of α-Al2O3 was much smaller than that of γ-Al2O3, as shown in Figure 2.
The dispersibility, surface area, and average particle size of Pt loaded onto the aluminas of representative 5Pt/γ(r)α(t)-Al2O3 (5Pt/γ-Al2O3, 5Pt/γ(50)α(50)-Al2O3, and 5Pt/α-Al2O3) powders were estimated from the CO adsorption/desorption properties, as shown in Table 1. The dispersibility and surface area of the Pt nanoparticles decreased and then the average particle size of Pt increased with an increase in the amount of α-Al2O3. These results indicate that the Pt nanoparticles, which were smaller than those on the surface of α-Al2O3, were loaded in a highly dispersed state on the surface of γ-Al2O3. The dispersibility and surface area of 5Pt/γ(50)α(50)-Al2O3 were relatively close to the average values of α-Al2O3 and γ-Al2O3 (dispersibility: ca. 31%, surface area: ca. 76 m2 g−1-Pt). This suggests that the Pt nanoparticles loaded on the surface of α-Al2O3 and γ-Al2O3 of 5Pt/γ(50)α(50)-Al2O3 existed in a relatively similar state to the Pt nanoparticles loaded on the surface of α-Al2O3 and γ-Al2O3 alone. Therefore, the average particle size of the Pt nanoparticles of 5Pt/γ(50)α(50)-Al2O3 calculated from the CO adsorption/desorption properties is not very meaningful when discussing the loading state. However, just the value is also very reasonable because it lies between the Pt nanoparticles on the 5Pt/γ-Al2O3 surface, which has a small average particle size, and the Pt nanoparticles on the 5Pt/α-Al2O3 surface, which has a large average particle size.
Figure 5 shows TEM photographs of representative 5Pt/γ(r)α(t)-Al2O3 (5Pt/γ-Al2O3, 5Pt/γ(50)α(50)-Al2O3, and 5Pt/α-Al2O3) powders. The γ-Al2O3 powder consisted of very fine particles, which were quite aggregated. In contrast, the α-Al2O3 powder was formed from particles with a diameter of approximately 200 nm. Furthermore, it was confirmed that the particles of both γ-Al2O3 and α-Al2O3 powders were uniformly mixed in the TEM photograph of 5Pt/γ(50)α(50)-Al2O3. Many Pt nanoparticles were confirmed with both γ-Al2O3 and α-Al2O3 particles in all highly magnified TEM photographs. The sizes of the Pt nanoparticles in the 5Pt/γ-Al2O3 and 5Pt/γ(50)α(50)-Al2O3 powders were smaller than those of the Pt nanoparticles in the 5Pt/α-Al2O3 powder, but their sizes seem to be comparatively smaller than the average sizes of the Pt nanoparticles, which were calculated from the amount of CO adsorption (Table 1).
Figure S6 shows the annular dark-field (ADF)-STEM images and EDS maps (Al K and Pt M) of representative 5Pt/γ(r)α(t)-Al2O3 (5Pt/γ-Al2O3, 5Pt/γ(50)α(50)-Al2O3, and 5Pt/α-Al2O3) powders, together with their TEM photographs. In all the samples, the EDS signal of Al K almost overlapped with the morphology of the alumina particles, as confirmed in the TEM photographs. The EDS signal of Pt M was also observed at almost the same location as the EDS signal of Al M in the TEM and ADF-STEM images of 5Pt/γ-Al2O3 and 5Pt/γ(50)α(50)-Al2O3, which indicates that Pt nanoparticles were uniformly loaded on both γ-Al2O3 and α-Al2O3 particles in these samples. On the other hand, on the basis of the ADF-STEM images and the EDS maps of the Pt M signal, it was confirmed that not only Pt nanoparticles randomly loaded on the surface of the α-Al2O3 particles, but also that a large amount of Pt nanoparticles was agglomerated at the interfaces (grain boundaries) of the α-Al2O3 particles. The large average size of the Pt nanoparticles in the 5Pt/α-Al2O3 powder (Table 2), which was calculated from the amount of CO adsorbed, probably originates from their agglomeration. Such agglomeration of Pt nanoparticles was not observed in the 5Pt/γ(50)α(50)-Al2O3 powder, because the γ-Al2O3 particles were well mixed with the α-Al2O3 particles and the γ-Al2O3 particles were well inserted among the α-Al2O3 particles, as shown in the TEM and ADF-STEM images. The amounts of Pt nanoparticles loaded in 5Pt/γ-Al2O3, 5Pt/γ(50)α(50)-Al2O3, and 5Pt/α-Al2O3, which were evaluated by EDS analysis, were ca. 5.1 wt%, ca. 4.7 wt%, and ca. 4.9 wt%, respectively, and these values were almost the same as the amount of Pt added during the preparation process.
The thermal conductivity of the sensing materials is one of the most important factors for adsorption/combustion-type gas sensors, because the thermal energy generated by the oxidation of VOCs on the catalyst surface needs to be effectively transferred to the Pt microheater (detector) to enhance the magnitude of the VOC response. Table 2 shows the thermal conductivities of representative sample disks fabricated under the same conditions as the sensor manufacturing conditions (heat treatment at 500 °C for 2 h in ambient air). The thermal conductivity of the γ-Al2O3 disk was small, and the thermal conductivity largely increased with an increase in the amount of α-Al2O3 added to γ-Al2O3 and the thermal conductivity of the α-Al2O3 disk was very large. On the other hand, the thermal conductivity of the nPt/γ-Al2O3 disks also tended to increase with an increase in the amount of Pt loaded, but the increase ratio was small in the range of 0–10 wt%. These results indicate that the addition of α-Al2O3 is effective in increasing the thermal conductivity of the sensing film.

3.2. Catalytic Activities

Figure 6a shows the catalytic combustion behavior of 100 ppm ethanol and 100 ppm toluene over representative 5Pt/γ(r)α(t)-Al2O3 (5Pt/γ-Al2O3, 5Pt/γ(50)α(50)-Al2O3, and 5Pt/α-Al2O3) powders in dry air at a flow rate of 20 cm3 min−1. The oxidation activities of 5Pt/γ-Al2O3 and 5Pt/γ(50)α(50)-Al2O3 for ethanol were extremely high, achieving nearly 100% ethanol conversion even at room temperature. However, there was a large difference in the amount of acetaldehyde produced as an intermediate product, and the amount of acetaldehyde produced over 5Pt/γ-Al2O3 was clearly smaller than that over 5Pt/γ(50)α(50)-Al2O3. The amount of CO2 produced over both samples did not increase until relatively high temperatures were reached, and the CO2 concentration reached 200 ppm, which is the concentration produced when ethanol is completely oxidized, at 250 °C. This was because other partially decomposed products except for acetaldehyde were produced over both samples. In fact, previous studies confirmed the production of ethylene and diethyl ether as partially decomposed products at incomplete medium temperatures for ethanol oxidation [22]. No partially decomposed products other than acetaldehyde were confirmed because of the low ethanol concentration used in this study. The catalytic combustion behavior of 100 ppm ethanol over representative 5Pt/γ(r)α(t)-Al2O3 (5Pt/γ-Al2O3, 5Pt/γ(50)α(50)-Al2O3, and 5Pt/α-Al2O3) powders in dry air was also investigated at a higher flow rate of 100 cm3 min−1, as shown in Figure S7a. It was not possible to quantify the amount of CO2 produced in this experiment because compressed air was used as the base gas. Increasing the gas flow rate obviously clarified that the oxidation activity of 5Pt/α-Al2O3 for ethanol was higher than that of 5Pt/γ(50)α(50)-Al2O3. These results confirmed that the ethanol oxidation activity decreased with increasing amounts of α-Al2O3 added to 5Pt/γ(r)α(t)-Al2O3, owing to the large specific surface area of 5Pt/γ-Al2O3, as well as the high dispersibility of Pt nanoparticles and the large Pt surface area.
Figure 6b shows the catalytic combustion behavior of 100 ppm toluene over representative 5Pt/γ(r)α(t)-Al2O3 (5Pt/γ-Al2O3, 5Pt/γ(50)α(50)-Al2O3, and 5Pt/α-Al2O3) powders in dry air at a flow rate of 20 cm3 min−1. The toluene conversion property of 5Pt/γ(50)α(50)-Al2O3 was the highest among them, but 5Pt/α-Al2O3 also showed a relatively high toluene conversion property. The amount of CO2 generated, which is an indicator of complete oxidation, over 5Pt/α-Al2O3 was larger than that over 5Pt/γ(50)α(50)-Al2O3, even at low temperatures, confirming that partially decomposed products of toluene are not easily generated on the surface of 5Pt/α-Al2O3. On the other hand, the oxidation activity of 5Pt/γ-Al2O3 for toluene was much lower than that of the others, whereas the oxidation activity of 5Pt/γ-Al2O3 was comparable to that of the others only at lower temperatures. The catalytic combustion behavior of 100 ppm toluene over representative 5Pt/γ(r)α(t)-Al2O3 (5Pt/γ-Al2O3, 5Pt/γ(50)α(50)-Al2O3, and 5Pt/α-Al2O3) powders in dry air was also investigated at a higher flow rate of 100 cm3 min−1, as shown in Figure S7b. The amount of CO2 produced was not able to be monitored in this experiment, too. The difference in the catalytic activity between 5Pt/γ(50)α(50)-Al2O3 and 5Pt/α-Al2O3 was clarified by increasing the gas flow rate, and it was confirmed that the toluene oxidation activity of 5Pt/γ(50)α(50)-Al2O3 was higher than that of 5Pt/α-Al2O3. It is also noteworthy that the oxidation activity of 5Pt/γ-Al2O3 for toluene became comparable to that of 5Pt/α-Al2O3 when the gas flow rate increased from 20 cm3 min−1 to 100 cm3 min−1, which means that the gas flow rate (the rate at which toluene is supplied to the catalyst surface) is one of the most important factors for the relative comparison of the oxidation activities of the samples.

3.3. VOC-Sensing Properties

Figure 7 shows the sensor-signal profiles of representative 5Pt/γ(r)α(t)-Al2O3 (5Pt/γ-Al2O3, 5Pt/γ(50)α(50)-Al2O3, and 5Pt/α-Al2O3) sensors to ethanol and toluene in ambient air. These sensor-signal profiles largely depended on the kind of VOCs and their concentration, as well as the composition of the aluminas, that is, the amount of α-Al2O3, in the 5Pt/γ(r)α(t)-Al2O3 powders. The 5Pt/γ-Al2O3 sensor shows “medium dynamic responses and relatively small static responses to ethanol” and “quite small dynamic responses and medium static responses to toluene”. The 5Pt/γ(50)α(50)-Al2O3 sensor showed “quite large dynamic responses and relatively small static responses to ethanol” and “small dynamic response and medium static response to toluene”, but the dynamic responses of the 5Pt/γ(50)α(50)-Al2O3 sensor to toluene were much larger than those of the 5Pt/γ-Al2O3 sensor. On the other hand, the 5Pt/α-Al2O3 sensor showed small dynamic responses and large static responses to both gases. As mentioned above, the mixing of α-Al2O3 with γ-Al2O3 can significantly change the sensor-signal profiles to ethanol and toluene. Figure 8 summarizes the composition dependencies of the three kinds of responses of all the 5Pt/γ(r)α(t)-Al2O3 sensors to ethanol and toluene. The general response, ΔVMAX, and integrated dynamic response, IDR, to ethanol were the largest when the amount of α-Al2O3 was 50 wt%, irrespective of the concentration of ethanol, while the maximum of ΔVMAX and IDR to toluene tended to shift toward a larger amount of α-Al2O3. Therefore, the magnitudes of ΔVMAX and IDR to ethanol were basically larger than those of toluene, but the differences were relatively smaller when the amount of α-Al2O3 was larger. The integrated static response, ISR, to 1000 ppm ethanol increased with an increase in the amount of α-Al2O3, while those to 10 and 100 ppm ethanol seemed to be the largest at the amount of α-Al2O3 of 50 wt%, as with their ΔVMAX and IDR. On the other hand, the ISR to toluene increased with an increase in the amount of α-Al2O3 in all toluene concentration ranges. In addition, the magnitude of ISR to ethanol was smaller than that of toluene, irrespective of the toluene concentration and the amount of α-Al2O3.
Figure 9 summarizes the concentration dependencies of the three kinds of responses of all 5Pt/γ(r)α(t)-Al2O3 sensors to ethanol and toluene. The ΔVMAX and IDR, especially the IDR to both ethanol and toluene, tend to be saturated with an increase in their concentration, which indicates that ethanol, toluene, and their partially decomposed products produced during the low-temperature period (150 °C) were adsorbed on the sensing-material surface and they burned during the flash heating-up period from 150 °C to 450 °C. On the other hand, the ISR to both ethanol and toluene increased approximately linearly with an increase in their concentration. This is because ethanol and toluene directly burned over the sensing-material surface during the static operation at 450 °C, and thus the ISR behavior of these sensors is quite similar to the behavior of general catalytic combustion-type gas sensors.
The variations in the three kinds of responses with the amount of α-Al2O3 seem to be influenced by the various characteristics of 5Pt/γ(r)α(t)-Al2O3. The ethanol oxidation activity decreased with an increase in the amount of α-Al2O3. In addition, the amount of ethanol and/or the partially decomposed products generally decreases with an increase in the amount of α-Al2O3, because the specific surface area of 5Pt/γ(r)α(t)-Al2O3 powder drastically decreased with an increase in the amount of α-Al2O3. However, the thermal conductivity increased significantly with an increase in the amount of α-Al2O3. The synergetic effects of these factors must determine the largest ΔVMAX and IDR to ethanol when the amount of α-Al2O3 was 50 wt%. The shift of the largest ΔVMAX and IDR to toluene toward a larger amount of α-Al2O3 in comparison with those to ethanol probably arises from the largest toluene oxidation activity of 5Pt/γ(50)α(50)-Al2O3. On the other hand, ISRs to both ethanol and toluene increased with an increase in the amount of α-Al2O3, which was almost the same as the dependence of thermal conductivity on the amount of α-Al2O3. The highly thermally conductive α-Al2O3 effectively transfers the thermal energy generated by the oxidation of ethanol and toluene toward the Pt microheater of the 5Pt/γ(r)α(t)-Al2O3 sensors during the high-temperature period.
As mentioned above, the 5Pt/γ(r)α(t)-Al2O3 sensors have two important sensing-output information in one signal: dynamic response and static response. Therefore, we expect that these attractive characteristics of adsorption/combustion-type VOC sensors will bring great benefits to highly sensitive and selective VOC detection through accurate analysis using adequate computing technologies, such as machine learning and AI technology.

4. Conclusions

The sensing properties of adsorption/combustion-type 5Pt/γ(r)α(t)-Al2O3 sensors to ethanol and toluene were investigated in ambient air, and the effects of mixing α-Al2O3 and γ-Al2O3 as the base material of the sensing film on the sensing properties were discussed in this study. The α-Al2O3 powder was well mixed with the γ-Al2O3 powder, and the Pt nanoparticles were basically dispersed on the surface of these aluminas (some of the Pt nanoparticles were agglomerated at the grain boundaries only in the γ-Al2O3 powder), which was confirmed by the evaluation of the adsorption/desorption characteristics of N2 and CO, as well as by the analyses using XRD, XPS, TEM, and STEM-EDS. The mixing of 50 wt% α-Al2O3 with γ-Al2O3 was the most effective in enhancing both ΔVMAX and IDR to ethanol, while the maximum ΔVMAX and IDR to toluene tended to shift toward a larger amount of α-Al2O3. The ethanol oxidation activity of 5Pt/γ(r)α(t)-Al2O3 decreased with an increase in the amount of α-Al2O3, whereas the thermal conductivity increased with an increase in the amount of α-Al2O3. These results indicate that the synergistic effects of catalytic activity and thermal conductivity of 5Pt/γ(r)α(t)-Al2O3 are quite important in enhancing the ethanol-sensing properties of the sensors. On the other hand, the ISR to both ethanol and toluene mainly increased with an increase in the addition of α-Al2O3 in 5Pt/γ(r)α(t)-Al2O3, even though the oxidation activities of α-Al2O3 for ethanol and toluene were lower than those of the other samples. Therefore, the relatively high thermal conductivity of α-Al2O3 must be of great importance in the effective transfer of thermal energy generated by the oxidation of ethanol and toluene toward the Pt microheater of the 5Pt/γ(r)α(t)-Al2O3 sensors during the high-temperature period.

Supplementary Materials

The following supporting information can be downloaded at https://www.mdpi.com/article/10.3390/chemosensors13010009/s1, Figure S1: Measurement circuit and typical sensor-signal profile with definition of three kinds of responses; Figure S2: Nitrogen adsorption-desorption isotherms and pore size distributions of all 5Pt/γ(r)α(t)-Al2O3 powders; Figure S3: XRD spectra of all 5Pt/γ(r)α(t)-Al2O3 powders; Figure S4: XPS spectra of Pt 4f of all 5Pt/γ(r)α(t)-Al2O3 powders; Figure S5: XPS spectra of Al 2s and O 1s of all 5Pt/γ(r)α(t)-Al2O3 powders; Figure S6: (i) TEM photographs, (ii) ADF-STEM images, and EDS maps of (iii) Al K and Pt M of representative 5Pt/γ(r)α(t)-Al2O3 (5Pt/γ-Al2O3, 5Pt/γ(50)α(50)-Al2O3, and 5Pt/α-Al2O3) powders; Figure S7: Catalytic combustion behavior of (a) 100 ppm ethanol and (b) 100 ppm toluene over representative 5Pt/γ(r)α(t)-Al2O3 powders in dry air (flow rate: 100 cm3 min−1).

Author Contributions

Conceptualization, T.H., T.S. and Y.S.; methodology, T.H.; software, T.S.; validation, T.H. and T.U.; investigation, Y.M., G.I. and T.U.; data curation, T.H. and T.U.; writing—original draft preparation, T.H.; writing—review, and editing, T.H. and T.U.; supervision, T.H., Y.S. and T.U.; project administration, T.H. and T.S.; funding acquisition, T.H. and T.S. All authors have read and agreed to the published version of the manuscript.

Funding

This research was partly funded by JSPS KAKENHI, grant number JP21H01626 and The Murata Science Foundation, grant number H31-076.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

The data that support the findings of this study are available from the corresponding author upon reasonable request.

Conflicts of Interest

The author, Takahiko Sasahara, was employed by the Gas Equipment R&D Center, Yazaki Energy System Corporation. The remaining authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as potential conflicts of interest.

References

  1. Rumchev, K.; Brouwn, H.; Spickett, J. Volatile Organic Compounds: Do they present a risk to our health? Rev. Environ. Health 2007, 22, 67–82. [Google Scholar] [CrossRef] [PubMed]
  2. Bhoonah, R.; Maury-Micolier, A.; Jolliet, O. Integrated empirical and modelled determination of the human health impacts of building material VOCs. Build. Environ. 2023, 242, 110523. [Google Scholar] [CrossRef]
  3. Haug, H.; Klein, L.; Sauerwald, T.; Poelke, B.; Beauchamp, J.; Alexander, R. Sampling Volatile organic compound emissions from consumer products: A review. Crit. Rev. Anal. Chem. 2024, 54, 1895–1916. [Google Scholar] [CrossRef] [PubMed]
  4. Sekine, Y.; Kimura, K.; Umezawa, K. What does human skin gas analysis work for? J. Jpn. Assoc. Odor Environ. 2017, 48, 410–417. [Google Scholar] [CrossRef]
  5. Moura, P.C.; Raposo, M.; Vassilenko, V. Breath volatile organic compounds (VOCs) as biomarkers for the diagnosis of pathological conditions: A review. Biomed. J. 2023, 46, 10623. [Google Scholar] [CrossRef]
  6. Kim, C.; Kang, M.S.; Raja, I.S.; Oh, J.-W.; Joung, Y.K.; Han, D.-W. Current issues and perspectives in nanosensors-based artificial olfactory systems for breath diagnostics and environmental exposure monitoring. Trends Anal. Chem. 2024, 174, 117656. [Google Scholar] [CrossRef]
  7. Tassopoulos, C.N.; Barnett, D.; Russell Fraseer, T. Breath-acetone and blood-sugar measurements in diabetes. Lancet 1969, 28, 1282–1286. [Google Scholar] [CrossRef]
  8. Hunt, J.; Gaston, B. Airway nitrogen oxide measurements in asthma and other pediatric respiratory diseases. J. Pediatr. 2000, 137, 14–20. [Google Scholar] [CrossRef]
  9. Cikach, F.S., Jr.; Dweik, R.A. Cardiovascular biomarkers in exhaled breath. Prog. Cardiovasc. Dis. 2012, 55, 34–43. [Google Scholar] [CrossRef]
  10. Choueiry, F.; Barham, A.; Zhu, J. Analyses of lung cancer-derived volatiles in exhaled breath and in vitro models. Exp. Biol. Med. 2022, 247, 1179–1190. [Google Scholar] [CrossRef]
  11. Schmidt, F.; Kohlbrenner, D.; Malesevic, S.; Huang, A.; Klein, S.D.; Puhan, M.A.; Kohler, M. Mapping the landscape of lung cancer breath analysis: A scoping review. Lung Cancer 2023, 175, 131–140. [Google Scholar] [CrossRef] [PubMed]
  12. Güntner, A.T.; Weber, I.C.; Schon, S.; Pratsinis, S.E.; Gerber, P.A. Monitoring rapid metabolic changes in health and type-1 diabetes with breath acetone sensors. Sens. Actuators B 2022, 367, 132182. [Google Scholar] [CrossRef]
  13. Mori, M.; Itagaki, Y.; Sadaoka, Y. VOC detection by potentiometric oxygen sensor based on YSZ and modified Pt electrodes. Sens. Actuators B 2012, 161, 471–479. [Google Scholar] [CrossRef]
  14. Itoh, T.; Nakashima, T.; Akamatsu, T.; Izu, N.; Shin, W. Nonanal gas sensing properties of platinum, palladium, and gold-loaded tin oxide VOCs sensors. Sens. Actuators B 2013, 187, 135–141. [Google Scholar] [CrossRef]
  15. Kim, N.-H.; Choi, S.-J.; Yang, D.-J.; Bae, J.; Park, J.; Kim, I.-D. Highly sensitive and selective hydrogen sulfide and toluene sensors using Pd functionalized WO3 nanofibers for potential diagnosis of halitosis and lung cancer. Sens. Actuators B 2014, 193, 574–581. [Google Scholar] [CrossRef]
  16. Ye, M.; Chien, P.-J.; Toma, K.; Arakawa, T.; Mitsubayashi, K. An acetone bio-sniffer (gas phase biosensor) enabling assessment of lipid metabolism from exhaled breath. Biosens. Bioelectron. 2015, 73, 208–213. [Google Scholar] [CrossRef]
  17. Hyodo, T.; Kaino, T.; Ueda, T.; Izawa, K.; Shimizu, Y. Acetone-sensing properties of WO3-based gas sensors operated in dynamic temperature modulation mode —Effects of loading of noble metal and/or NiO onto WO3. Sens. Mater. 2016, 28, 1179–1189. [Google Scholar]
  18. Suematsu, K.; Harano, W.; Oyama, T.; Shin, Y.; Watanabe, K.; Shimanoe, K. Pulse-driven semiconductor gas sensors toward ppt level toluene detection. Anal. Chem. 2018, 90, 11219–11223. [Google Scholar] [CrossRef]
  19. Choi, H.-J.; Chung, J.-H.; Yoon, J.-W.; Lee, J.-H. Highly selective, sensitive, and rapidly responding acetone sensor using ferroelectric ε-WO3 spheres doped with Nb for monitoring ketogenic diet efficiency. Sens. Actuators B 2021, 338, 129823. [Google Scholar] [CrossRef]
  20. Sun, Y.; Zhao, Z.; Suematsu, K.; Zhang, W.; Zhang, W.; Zhuiykov, S.; Shimanoe, K.; Hu, J. MOF-derived Au-NiO/In2O3 for selective and fast detection of toluene at ppb-level in high humid environments. Sens. Actuators B 2022, 360, 131631. [Google Scholar] [CrossRef]
  21. Shinkai, T.; Masumoto, K.; Iwai, M.; Inomata, Y.; Kida, T. Study on sensing mechanism of volatile organic compounds using Pt-loaded ZnO nanocrystals. Sensors 2022, 22, 6277. [Google Scholar] [CrossRef] [PubMed]
  22. Ueda, T.; Oide, N.; Kamada, K.; Hyodo, T.; Shimizu, Y. Improved toluene response of mixed-potential type YSZ-based gas sensors using CeO2-added Au electrodes. ECS Sens. Plus 2022, 1, 013604. [Google Scholar] [CrossRef]
  23. Minami, K.; Zhou, Y.; Imamura, G.; Shiba, K.; Yoshikawa, G. Sorption kinetic parameters from nanomechanical sensing for discrimination of 2-nonenal from saturated aldehydes. ACS Sens. 2024, 9, 689–698. [Google Scholar] [CrossRef] [PubMed]
  24. Schmitt, E.A.; Krott, M.; Epifani, M.; Suematsu, K.; Weimar, U.; Barsan, N. Volatile organic compound sensing with WO3-based gas sensors: Surface chemistry basics. J. Phys. Chem. C 2024, 128, 1633–1643. [Google Scholar] [CrossRef]
  25. Sasahara, T.; Kido, A.; Sunayama, T.; Uematsu, S.; Egashira, M. Identification and quantification of alcohol by a micro gas sensor based on adsorption and combustion. Sens. Actuators B 2004, 99, 532–538. [Google Scholar] [CrossRef]
  26. Hyodo, T.; Shimizu, Y. Adsorption/combustion-type micro gas sensors: Typical VOC-sensing properties and material-design approach for highly sensitive and selective VOC detection. Anal. Sci. 2020, 36, 401–411. [Google Scholar] [CrossRef]
  27. Yuzuriha, Y.; Hyodo, T.; Sasahara, T.; Shimizu, Y.; Egashira, M. Mesoporous Al2O3 co-loaded with Pd and Au as a combustion catalyst for adsorption/combustion-type gas sensors. Sens. Lett. 2011, 9, 409–413. [Google Scholar] [CrossRef]
  28. Hyodo, T.; Yuzuriha, Y.; Nakgoe, O.; Sasahara, T.; Tanabe, S.; Shimizu, Y. Adsorption/combustion-type gas sensors employing mesoporous γ-alumina loaded with core(Au)/shell(Pd) nanoparticles synthesized reduction by sonochemical reduction. Sens. Actuators B 2014, 202, 748–757. [Google Scholar] [CrossRef]
  29. Hyodo, T.; Hashimoto, T.; Ueda, T.; Nakgoe, O.; Sasahara, T.; Tanabe, S.; Shimizu, Y. Adsorption/combustion-type VOC sensors employing mesoporous γ-alumina co-loaded with noble-metal and oxide. Sens. Actuators B 2015, 220, 1091–1104. [Google Scholar] [CrossRef]
  30. Hyodo, T.; Nagae, K.; Ueda, T.; Sasahara, T.; Shimizu, Y. Sensing behavior of adsorption/combustion-type gas microsensors to various alcoholic vapors. Sens. Mater. 2023, 35, 3851–3861. [Google Scholar] [CrossRef]
  31. Hyodo, T.; Hiura, T.; Nagae, K.; Ueda, T.; Shimizu, Y. Effects of catalytic combustion behavior and adsorption/desorption properties on ethanol-sensing characteristics of adsorption/combustion-type gas sensors. J. Asian Ceram. Soc. 2021, 9, 1015–1030. [Google Scholar] [CrossRef]
  32. Sing, K.S.W. Reporting physisorption data for gas/solid systems. Pure Appl. Chem. 1982, 54, 2201–2218. [Google Scholar] [CrossRef]
  33. Brunauer, S.; Emmett, P.H.; Teller, E. Adsorption of gases in multimolecular layers. J. Am. Chem. Soc. 1938, 60, 309–319. [Google Scholar] [CrossRef]
  34. Barrett, E.P.; Joyner, L.G.; Halenda, P.H. The determination of pore volume and area distributions in porous substances. I. Computations from nitrogen isotherms. J. Am. Chem. Soc. 1951, 73, 373–380. [Google Scholar] [CrossRef]
Figure 1. (a) Stereomicroscope photograph of microsensor platform with a couple of Pt microheaters, and SEM photographs of (b) Pt microheater and detector at diaphragm and (c) typical sensing film (5Pt/γ-Al2O3).
Figure 1. (a) Stereomicroscope photograph of microsensor platform with a couple of Pt microheaters, and SEM photographs of (b) Pt microheater and detector at diaphragm and (c) typical sensing film (5Pt/γ-Al2O3).
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Figure 2. Dependence of specific surface area (SSA) of 5Pt/γ(r)α(t)-Al2O3 powders on the amount of α-Al2O3 (t).
Figure 2. Dependence of specific surface area (SSA) of 5Pt/γ(r)α(t)-Al2O3 powders on the amount of α-Al2O3 (t).
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Figure 3. Dependence of the ratio of normalized integral intensity of (400) peak of γ-Al2O3 to that of (116) peak of α-Al2O3 (I400,γ/I116,α) on the amount of α-Al2O3 (t) in 5Pt/γ(r)α(t)-Al2O3 powders.
Figure 3. Dependence of the ratio of normalized integral intensity of (400) peak of γ-Al2O3 to that of (116) peak of α-Al2O3 (I400,γ/I116,α) on the amount of α-Al2O3 (t) in 5Pt/γ(r)α(t)-Al2O3 powders.
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Figure 4. Variations in the ratio of Pt or Al to all Pt and Al species and the ratio of each Pt component to all Pt species with the amount of α-Al2O3 in 5Pt/γ(r)α(t)-Al2O3 powders.
Figure 4. Variations in the ratio of Pt or Al to all Pt and Al species and the ratio of each Pt component to all Pt species with the amount of α-Al2O3 in 5Pt/γ(r)α(t)-Al2O3 powders.
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Figure 5. TEM photographs of representative 5Pt/γ(r)α(t)-Al2O3 powders. Black and white arrows show Pt nanoparticles.
Figure 5. TEM photographs of representative 5Pt/γ(r)α(t)-Al2O3 powders. Black and white arrows show Pt nanoparticles.
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Figure 6. Catalytic combustion behavior of (a) 100 ppm ethanol and (b) 100 ppm toluene over representative 5Pt/γ(r)α(t)-Al2O3 powders in dry air (flow rate: 20 cm3 min−1).
Figure 6. Catalytic combustion behavior of (a) 100 ppm ethanol and (b) 100 ppm toluene over representative 5Pt/γ(r)α(t)-Al2O3 powders in dry air (flow rate: 20 cm3 min−1).
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Figure 7. Sensor-signal profiles of (a) 5Pt/γ-Al2O3, (b) 5Pt/γ(50)α(50)-Al2O3, and (c) 5Pt/α-Al2O3 sensors to ethanol and toluene in ambient air.
Figure 7. Sensor-signal profiles of (a) 5Pt/γ-Al2O3, (b) 5Pt/γ(50)α(50)-Al2O3, and (c) 5Pt/α-Al2O3 sensors to ethanol and toluene in ambient air.
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Figure 8. Composition dependencies of three kinds of responses of all 5Pt/γ(r)α(t)-Al2O3 sensors to (a) ethanol and (b) toluene.
Figure 8. Composition dependencies of three kinds of responses of all 5Pt/γ(r)α(t)-Al2O3 sensors to (a) ethanol and (b) toluene.
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Figure 9. Concentration dependencies of three kinds of responses of all 5Pt/γ(r)α(t)-Al2O3 sensors to (a) ethanol and (b) toluene.
Figure 9. Concentration dependencies of three kinds of responses of all 5Pt/γ(r)α(t)-Al2O3 sensors to (a) ethanol and (b) toluene.
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Table 1. Dispersibility, surface area, and average particle size of Pt loaded onto the aluminas of typical 5Pt/γ(r)α(t)-Al2O3 powders.
Table 1. Dispersibility, surface area, and average particle size of Pt loaded onto the aluminas of typical 5Pt/γ(r)α(t)-Al2O3 powders.
Sample5Pt/γ-Al2O35Pt/γ(50)α(50)-Al2O35Pt/α-Al2O3
Dispersibility/%47.832.014.0
Surface area/m2 g−1-Pt11880.034.5
Average particle size/nm2.373.558.12
Table 2. Thermal conductivities of typical samples.
Table 2. Thermal conductivities of typical samples.
SampleThermal Conductivity/10−2 W m−1 K−1
γ-Al2O39.32
5Pt/γ-Al2O39.63
10Pt/γ-Al2O39.97
γ(50)α(50)-Al2O314.9
α-Al2O337.7
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Hyodo, T.; Matsuura, Y.; Inao, G.; Sasahara, T.; Shimizu, Y.; Ueda, T. Effects of Base Materials (α-Alumina and/or γ-Alumina) on Volatile Organic Compounds (VOCs)-Sensing Properties of Adsorption/Combustion-Type Microsensors. Chemosensors 2025, 13, 9. https://doi.org/10.3390/chemosensors13010009

AMA Style

Hyodo T, Matsuura Y, Inao G, Sasahara T, Shimizu Y, Ueda T. Effects of Base Materials (α-Alumina and/or γ-Alumina) on Volatile Organic Compounds (VOCs)-Sensing Properties of Adsorption/Combustion-Type Microsensors. Chemosensors. 2025; 13(1):9. https://doi.org/10.3390/chemosensors13010009

Chicago/Turabian Style

Hyodo, Takeo, Yuma Matsuura, Genki Inao, Takahiko Sasahara, Yasuhiro Shimizu, and Taro Ueda. 2025. "Effects of Base Materials (α-Alumina and/or γ-Alumina) on Volatile Organic Compounds (VOCs)-Sensing Properties of Adsorption/Combustion-Type Microsensors" Chemosensors 13, no. 1: 9. https://doi.org/10.3390/chemosensors13010009

APA Style

Hyodo, T., Matsuura, Y., Inao, G., Sasahara, T., Shimizu, Y., & Ueda, T. (2025). Effects of Base Materials (α-Alumina and/or γ-Alumina) on Volatile Organic Compounds (VOCs)-Sensing Properties of Adsorption/Combustion-Type Microsensors. Chemosensors, 13(1), 9. https://doi.org/10.3390/chemosensors13010009

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