Next Article in Journal
Influence of Absorber Contents and Temperatures on the Dielectric Properties and Microwave Absorbing Performances of C@TiC/SiO2 Composites
Previous Article in Journal
Designing and Optimizing Electrode Materials for Energy Harvesting in CAPMIX Cells
Previous Article in Special Issue
Palladium-Functionalized Nanostructured Nickel–Cobalt Oxide as Alternative Catalyst for Hydrogen Sensing Using Pellistors
 
 
Search for Articles:
Title / Keyword
Author / Affiliation / Email
Journal
Article Type
 
 
Advanced Search
 
Section
Special Issue
Volume
Issue
Number
Page
 
Journals
Nanomaterials
Volume 14
Issue 24
10.3390/nano14242032
nanomaterials-logo
Submit to this Journal Review for this Journal Propose a Special Issue
► Article Menu

Article Menu

share Share announcement Help format_quote Cite question_answer Discuss in SciProfiles
first_page
settings
Order Article Reprints
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Oxygenated VOC Detection Using SnO2 Nanoparticles with Uniformly Dispersed Bi2O3

by
Haoyue Yang
1,
Koichi Suematsu
2,*,
Felipe Hiroshi Mashiba
1,
Ken Watanabe
2 and
Kengo Shimanoe
2,*
1
Interdisciplinary Graduate School of Engineering Sciences, Kyushu University, Kasuga 816-8580, Fukuoka, Japan
2
Department of Advanced Materials Science and Engineering, Faculty of Engineering Sciences, Kyushu University, Kasuga 816-8580, Fukuoka, Japan
*
Authors to whom correspondence should be addressed.
Nanomaterials 2024, 14(24), 2032; https://doi.org/10.3390/nano14242032
Submission received: 29 November 2024 / Revised: 11 December 2024 / Accepted: 16 December 2024 / Published: 18 December 2024
(This article belongs to the Special Issue Nanostructured Materials in Gas Sensing Applications)
Browse Figures
Versions Notes

Abstract

:
Bi2O3 particles are introduced as foreign additives onto SnO2 nanoparticles (NPs) surfaces for the efficient detection of oxygenated volatile organic compounds (VOCs). Bi2O3-loaded SnO2 materials are prepared via the impregnation method followed by calcination treatment. The abundant Bi2O3/SnO2 interfaces are constructed by the uniform dispersion of Bi2O3 particles on the SnO2 surface. The results of oxygen temperature-programmed desorption suggest that Bi2O3-loaded SnO2 samples display improved surface oxygen ions than neat-SnO2 NPs. As a result, the gas sensor based on 1 mol% Bi2O3-loaded SnO2 (1Bi-L-SnO2) composites shows significantly higher sensitivity and a faster response speed toward various oxygenated VOCs compared with SnO2, especially at 200 °C and 250 °C. The results of catalytic combustion and temperature-programmed reaction measurements reveal the dominant role of adsorption and partial oxidation during ethanol combustion on SnO2 and 1Bi-L-SnO2 surfaces. In this case, the improvement in the sensing performance of the 1Bi-L-SnO2 sensor can be associated with the increase in surface oxygen ions at Bi2O3/SnO2 interfaces. The results confirm the significant role of surface functionalization for sensing materials. The obtained outstanding sensing performance provides the potential application for the simultaneous detection of total oxygenated VOCs in practice.

1. Introduction

As an important group of volatile organic compounds (VOCs), oxygenated VOCs (including organic alcohols, aldehydes, and ketones, etc.) are widespread in the atmosphere derived from various human activities and biogenic emissions, such as the oxidation of hydrocarbons, emission of oxygenated fuels in industrial application, burning of biomass, etc. [1,2,3]. The various oxygenated VOCs lead to the formation of ozone and secondary organic aerosols, resulting in the threat to environmental pollution and human health [4,5]. In addition, many kinds of oxygenated VOCs are concomitant and interconvertible during the chemical reactions [6,7]. Hence, the importance and necessity of achieving simultaneous detection of total oxygenated VOCs in the atmosphere is noticeable. Chemiresistive-type gas sensors using semiconductor metal oxides (SMOs) like SnO2, ZnO, WO3, and In2O3 have garnered many outstanding performances for various gas detection in various applications including air quality monitoring, industrial safety, and so on [8,9,10,11,12]. In particular, SnO2 has been considered as one of the most sensitive materials by continuous research for decades [13,14,15]. At present, researchers have proposed various types of SnO2-based gas sensors for the efficient detection of specific oxygenated VOCs, such as ethanol, acetone, formaldehyde, and so on [16,17,18]. However, it is still insufficient for the detection of total oxygenated VOCs in the practical application. This highlights the importance of exploring sensing material to detect total oxygenated VOCs.
The basic understanding of the sensing mechanism is crucial for the research of gas sensors. It is normally recognized that the sensitivities of SnO2-based resistive-type gas sensors to fundamental gases such as CO and H2 are evaluated by the change in electrical resistances arising from the combustion reaction between gas molecules and adsorbed oxygen ions to form CO2 and H2O on the surface of materials. However, many studies indicate the complete combustion of oxygenated VOCs on the surfaces of metal oxides tends to occur under high operating temperatures (almost above 300 °C), and considerable intermediates will be produced during the combustion reaction [19,20,21]. Interestingly, the reported research has indicated the considerable sensitivity of SnO2-based gas sensors to ethanol at 250 °C [22]. In this case, the detection mechanism for oxygenated VOCs at temperatures below 300 °C may be different from high temperatures. Therefore, it is necessary to investigate the basic reaction process during oxygenated VOC combustion on SnO2-based gas sensors at various temperatures.
According to reported research, the sensing performance of SnO2-based gas sensors can be further improved after surface functionalization by introducing foreign additives, such as metal oxides and noble metals [9,23,24,25,26]. Generally, the functionalized surface properties of SnO2 by foreign additives mainly include the modulation of active oxygen ions, acidic sites, etc. The former parameter is directly responsible for the activity of the oxidation reaction of target gas molecules. The surface acid–base property concerns the specific adsorption and selective conversion of target gas molecules on the material surface [27,28,29]. Thus, the sensing properties of SnO2-based gas sensors to oxygenated VOCs may be further improved by modulating the surface properties using foreign additives. α-Bi2O3 particles have stood out for their high stability and environmental promise, conducing to the application as a photocatalyst, selective oxidation catalyst, sensing material, etc. [30,31,32]. In particular, the Bi atoms in Bi2O3 contribute to the electrical conductivity due to the hybridization between the O 2p orbital and Bi 6s or 6p orbitals [33]. Several studies have confirmed the facilitation of the sensing performance of SMOs-based gas sensors by employing Bi2O3 particles as foreign additives [34,35,36]. Moreover, it is possible that Bi2O3 shows different acid–base properties with SnO2 due to the different electronegativity of Bi3+ (13.3) than Sn4+ (16.2) [37]. Consequently, Bi2O3 may be a promising candidate as a foreign additive to improve the sensing properties of SnO2-based gas sensors to oxygenated VOCs.
Herein, in order to improve the selectivity to typical oxygenated VOCs, we employed Bi2O3 particles as foreign additives on a SnO2-based gas sensor. Bi2O3-loaded SnO2 materials were synthesized, and Bi2O3 was uniformly dispersed on the surface of SnO2 nanoparticles (NPs). Bi2O3-loaded SnO2 materials showed increased surface oxygen ions than SnO2 NPs. As a result, the gas sensor based on 1 mol% Bi2O3-loaded SnO2 nanoparticles showed excellent sensitivities toward various oxygenated VOCs, especially at 200 °C and 250 °C. Meanwhile, catalytic combustion and temperature-programmed reaction measurements revealed that the adsorption–desorption, dissociation, and partial oxidation of oxygenated VOCs were dominant at temperatures lower than 300 °C. In conclusion, the improvement in sensing properties of the SnO2 sensor by Bi2O3-loading could be ascribed to the increased surface oxygen ions at the contact interfaces between Bi2O3 and SnO2 accelerated the adsorption and partial combustion of oxygenated VOCs. This research provided the basic insight into the reaction mechanism of oxygenated VOCs at low temperatures (below 300 °C). Meanwhile, the results indicated the uniform dispersion of foreign additives played an active role in the sensing properties of gas sensors.

2. Materials and Methods

2.1. Materials Synthesis

The synthesis of pure SnO2 NPs. SnO2 NPs were synthesized via hydrothermal synthesis accompanied by calcination. Firstly, 1 M of SnCl4·5H2O (98.0%, special grade; FUJIFILM Wako Pure Chemical Corporation, Osaka, Japan) solution was dropwise added into 1 M of NH4HCO3 (99.0%, special grade; FUJIFILM Wako Pure Chemical Corporation, Osaka, Japan) solution under stirring. Next, the obtained stannic acid gel was washed to remove Cl− and then mixed with deionized water. After adjusting the PH to 10.5 by tetramethylammonium hydroxide (15%, special grade, FUJIFILM Wako Pure Chemical Corporation, Osaka, Japan) solution, the mixture was heated in a 100 mL stainless steel reactor with Teflon inner cylinder at 200 °C for 10 h in an oven. Subsequently, the obtained transparent sol was dried at 120 °C and annealed at 600 °C for 3 h under O2 flow to prepare SnO2 NPs.
The synthesis of Bi2O3-mixed SnO2 samples. Firstly, Bi2O3 particles were obtained by calcining the Bi(NO3)3·5H2O (99.5 %, special grade, KISHIDA Chemical Co. Ltd., Osaka, Japan) at 550 °C for 3 h under O2 flow. Next, 1.5 g SnO2 NPs and a stoichiometric amount of Bi2O3 powders were mixed and ground manually for 15 min. Then the particles were calcined at 530 °C for 3 h under O2 flow to obtain Bi2O3-mixed SnO2 materials, which were labeled as 1Bi-M-SnO2 and 3Bi-M-SnO2 according to the concentration of Bi2O3 (the atomic ratio of Bi to Sn was 1/100 and 3/100, respectively).
The synthesis of Bi2O3-loaded SnO2 samples. Bi2O3-loaded SnO2 samples with various Bi contents were synthesized by a simple impregnation method. 1.5 g SnO2 NPs dissolved in 20 mL deionized water was impregnated on an aqueous solution of a stoichiometric amount of Bi(NO3)3·5H2O with stirring for 24 h at room temperature. The resulting precipitates were washed by centrifugation, dried at 100 °C, and calcined at 550 °C for 3 h under O2 flow. The obtained samples were referred to hereafter as 1Bi-L-SnO2 and 3Bi-L-SnO2 (the atomic ratio of Bi to Sn was 1/100 and 3/100, respectively).

2.2. Material Characterization

Wavelength-dispersive X-ray fluorescence spectroscopy (WDX, Supermini 200, Rigaku, Tokyo, Japan) was used to evaluate the content of Bi ions in Bi2O3-loaded SnO2 materials. The crystal structures of as-synthesized SnO2, Bi2O3-mixed SnO2, and Bi2O3-loaded SnO2 samples were investigated by X-ray diffractometry (XRD; MiniFlex, Rigaku, Tokyo, Japan) with CuKα radiation. The specific surface reaction and pore volume of materials were respectively evaluated by N2 adsorption/desorption analyzer (BELSORP-mini II, MicrotracBEL Corp., Osaka, Japan), and calculated by Brunauer–Emmett–Teller (BET) method and Barrett–Joyner–Halenda (BJH) method, respectively. The distribution of Bi2O3 on the surface of SnO2 was investigated by scanning electron microscopy (SEM; JCM-7000, JEOL, Tokyo, Japan) equipped with an energy-dispersive X-ray spectroscopy (EDS) attachment.
Temperature-programmed desorption of oxygen and ammonia (O2-TPD and NH3-TPD) measurements were expected to estimate the adsorption–desorption of oxygen and NH3 on sample surfaces using a catalyst analyzer (BELCAT II, MicrotracBEL Corp., Osaka, Japan) equipped with a thermal conductivity (TCD) detector. The system is also linked with a quadrupole mass spectrometer (QMS, BELMASS II, MicrotracBEL Corp., Osaka, Japan) to analyze the desorbed products emitted from the material surface. The gas adsorption–desorption on the materials’ surfaces was analyzed using temperature-programmed reaction (TPR) measurement. The TPR system consisted of a gas mixing system, a reaction chamber, and a gas detector with a quadrupole mass spectrometer (QMS; PrismaPlus QMG220, PFEIFFER, Hessen, Germany). The catalytic combustion measurement was employed to monitor the consumption of gas molecules and production of intermediates caused by gas combustion on material surfaces using a self-assembled system consisting of a gas mixing system, reaction chamber, and gas chromatography (GC-4000 Plus, GL Science Inc., Tokyo, Japan) equipped with a flame ionization detector and a methanizer (MT221), followed by the connection with series to 2 m of Porapak Q and Porapak N columns (GL Science Inc., Tokyo, Japan). The details of measuring processes were described in Supporting Information.

2.3. Sensor Fabrication and Measurement

The gas sensors were fabricated by screen printing method. Firstly, Au electrodes were screen-printed on an alumina substrate (9 × 13 × 0.38 mm3) followed by heat-treated at 850 °C for 3 h (line width: 180 μm, distance between lines: 90 μm, sensing area: 64 mm2). Next, the samples were mixed with α-terpineol to form paste, and then screen-printed on the alumina substrate with Au electrodes. The resulting devices were calcined at 500 °C for 3 h in the air to remove the organic binder. The obtained gas sensors were placed in an electric furnace combined with a gas flow apparatus under the total flow rate of 100 cm3/min controlled by mass flow controllers. The operating temperatures of gas sensors were modulated at 200 °C, 250 °C, 300 °C, and 350 °C. Each sensor was connected in series to a standard resistor and applied a DC voltage of 4 V. An electrometer (2701; Keithley Instruments, Solon, OH, USA) was employed to measure the electrical resistances by evaluating the voltage across the standard resistor. The sensor response was evaluated by the change in electrical resistances in synthesis air and target gas atmospheres (S = Ra/Rg). The response time was considered as the time required for the sensor to be 90% of maximum response change [38]. The target gases were diluted by N2 with 21% O2 to obtain the tested concentration (5 ppm) under a gas mixture system.

3. Results and Discussion

3.1. Materials Characteristics

The actual concentration of Bi ions in Bi2O3-loaded SnO2 materials was evaluated by WDX analysis using the calibration results of Bi2O3-mixed SnO2 materials. The calculated amounts of Bi ions in 1Bi-L-SnO2 and 3Bi-L-SnO2 materials were 1.1 mol% and 2.8 mol%, respectively. The results indicated the comparable content of Bi ions in Bi2O3-loaded SnO2 and Bi2O3-mixed SnO2 materials. The XRD patterns of SnO2, Bi2O3-loaded SnO2, and Bi2O3-mixed SnO2 materials (Figure 1) showed diffraction peaks matched well with tetragonal rutile structure SnO2 with the space group of P42/mnm (JCPDS: 41-1445), indicating all as-synthesized materials had the same SnO2 crystal phase. Meanwhile, the obtained Bi2O3 particles were assigned to monoclinic α-Bi2O3 with the space group of P21/c (JCPDS: 41-1449). The diffraction peak appeared at about 27.15° of Bi2O3-mixed SnO2 samples could be assigned to the (111) plane of α-Bi2O3, proving that α-Bi2O3 particles were successfully complexed on the surface of SnO2. No diffraction peak of Bi2O3 was observed on Bi2O3-loaded SnO2 samples, which might be caused by the well-dispersion of Bi2O3 particles. In addition, the average crystallite sizes of SnO2 in as-prepared materials were calculated by the Scherrer formula, as shown in Table S1. The results indicated the nanostructure of obtained SnO2 powders. There was no obvious change in crystallite size after Bi2O3-mixing and Bi2O3-loading on SnO2 NPs.
To investigate the distribution of Bi2O3 on the SnO2 surface, we detected the SEM-EDS elemental mapping images of Sn and Bi in Bi2O3-mixed and Bi2O3-loaded SnO2 materials, as shown in Figure 2 and Figure S2. For Bi2O3-mixed SnO2 materials (Figure 2a and Figure S2a), Sn was observed almost across the whole imaged area, while Bi was exhibited only in localized regions. Meanwhile, there was little overlapping area between Bi and Sn, proving the separate distribution of Bi2O3 and SnO2 particles with little contact interfaces in Bi2O3-mixed SnO2 materials. In contrast, Figure 2b and Figure S2b revealed the uniform distribution of Sn and Bi elements in Bi2O3-loaded SnO2 materials, indicating Bi2O3 particles were homogeneously dispersed on the surface of SnO2 NPs. As a result, abundant contact interfaces at Bi2O3/SnO2 were constructed in Bi2O3-loaded SnO2 materials, while major Bi2O3 particles were agglomerated and physically mixed with SnO2 NPs in Bi2O3-mixed SnO2 materials. The specific surface area and average pore volume of Bi2O3-mixed SnO2 materials were comparable to those of Bi2O3-loaded SnO2 and slightly larger than that of neat-SnO2 (Table S1). The indistinctive impact on the surface area and porosity of SnO2 NPs after introducing Bi2O3 particles might be associated with the low concentration of Bi2O3 particles, and the observed slight increase in neat-SnO2 might be ascribed to the difference during the sample preparation process.

3.2. Gas Sensing Properties

Figure S3 showed the electrical resistance in synthetic air (Ra) of neat-SnO2, Bi2O3-mixed SnO2, and Bi2O3-loaded SnO2 gas sensors at 200 °C, 250 °C, 300 °C, and 350 °C. It was difficult to detect the sensing performance of the 3Bi-L-SnO2 sensor at 200 °C due to the excessively high electrical resistance exceeding system limits. The Ra of Bi2O3-loaded SnO2 sensors were larger than that of neat-SnO2 and Bi2O3-mixed SnO2 sensors at all detected temperatures, confirming the effect of uniform dispersion of Bi2O3 particles on the conductivity of SnO2-based sensor. We investigated the sensitivities of gas sensors to 5 ppm of various VOCs (CH3CH2OH, CH3OH, CH3COCH3, CH3CHO, C2H4, and C7H8) at 200–350 °C. As displayed in Figure 3, the gas sensors based on Bi2O3-mixed SnO2 samples showed similar responses to tested oxygenated VOCs (CH3CH2OH, CH3OH, CH3COCH3, CH3CHO) with neat-SnO2 sensor, indicating the agglomerated Bi2O3 particles exhibited little effect on the reactivity of SnO2 for oxygenated VOCs detection. Meanwhile, the 1Bi-L-SnO2 sensor showed dramatically improved sensitivities to tested oxygenated VOCs at all detected operating temperatures (especially at 200 °C and 250 °C). The phenomenon confirmed the uniform dispersion of Bi2O3 particles on the SnO2 surface during the Bi2O3-loading process played a vital role in the adsorption and combustion of oxygenated VOCs. However, the responses of the 3Bi-L-SnO2 sensor to oxygenated VOCs were lower than that of the 1Bi-L-SnO2 sensor, which might be attributed to the excessive dispersion of Bi2O3 particles prevented the diffusion of gas molecules into the sensing layer of SnO2 [39]. Besides, the neat-SnO2 sensor showed clearly higher responses to C2H4 and C7H8 than Bi2O3-loaded SnO2 and Bi2O3-mixed SnO2 sensors. In conclusion, the 1Bi-L-SnO2 sensor showed excellent sensitivity and selectivity to oxygenated VOCs, especially at 200 °C and 250 °C. Additionally, the responses toward oxygenated VOCs were decreased with the increase in temperature.
The response curve is a crucial parameter to estimate the sensing performance of gas sensors. The dynamic time-dependence response curves of obtained gas sensors based on SnO2 and Bi2O3-loaded SnO2 materials toward ethanol as the representative of tested oxygenated VOCs at 200–350 °C are shown in Figure 4. The corresponding response time required for the sensors to 90% of response changes are calculated in Table S2. Figures S4–S7 exhibited the dynamic response curves of all the obtained gas sensors toward tested oxygenated VOCs at 200–350 °C. Clearly, the responses of all sensors were rapidly increased during the initial period under the target gases’ atmosphere. Generally, the initial rapid increase in response could be associated with the consumption of adsorbed oxygen ions on the surface of sensing materials. Bi2O3-loaded SnO2 sensors showed an obviously improved increasing tendency at the initial period compared to neat-SnO2 sensors. Moreover, the response time of SnO2 to ethanol was decreased with the rising Bi2O3-loading content. In this case, the improved response speed of Bi2O3-loaded SnO2 sensors to ethanol might be assigned to the improved amount of surface oxygen ions of Bi2O3-loaded SnO2 surfaces. The response speeds of all sensors were increased with the rising temperature, corresponding to the enhanced reactivity of surface oxygen ions of sensing materials. Consequently, the rapid response and outstanding sensitivity to oxygenated VOCs combined with weak responses to C2H4 and C7H8 of the 1Bi-L-SnO2 sensor proved the potential for sensitive and selective oxygenated VOCs detection. Additionally, the results indicated the different distribution of Bi2O3 particles on the SnO2 surface caused by Bi2O3-mixing and Bi2O3-loading processes showed various sensing performances, the abundant Bi2O3/SnO2 interfaces formed by the uniform dispersion of Bi2O3 particles might be the crucial parameter improving the sensing properties.

3.3. Catalytic Combustion Measurement

Generally, the combustion of gas molecules on material surfaces plays a vital role in the sensing performance of gas sensors. As one of the typical oxygenated VOCs, the combustion of ethanol on neat-SnO2 and 1Bi-L-SnO2 surfaces under 200–350 °C was investigated, as shown in Figure 5. It was observed that the consumption of ethanol gradually increased from 200 °C and approximately reached 100% at 350 °C. Simultaneously, a number of CH3CHO and a little of C2H4 were produced during 200–350 °C, which were caused by the dehydrogenation and dehydration of ethanol, respectively. Noteworthy, no CO2 was detected at 200 °C and 250 °C, indicating the absence of complete combustion of ethanol. Hence, ethanol molecules were initially adsorbed on material surfaces and then converted to CH3CHO combined with a little C2H4. Subsequently, CH3CHO molecules were oxidized to intermediates (CH3COOH, CO, etc.) [40,41]. With the further increase in temperature, CO2 was gradually produced by the complete combustion of ethanol. Meanwhile, the production of CO2 was about 27% and 61% at 300 °C and 350 °C, revealing the presence of both partial and complete combustion of ethanol on the SnO2 surface. Besides, the productions of CO2 and C2H4 on 1Bi-L-SnO2 were smaller than those on the SnO2 surface, as demonstrated in Figure S8. As reported previously, ethanol molecules could be converted to CH3CHO and C2H4 on basic and acid material surfaces, respectively [19]. Hence, the almost disappeared yield of C2H4 on the 1Bi-L-SnO2 surface might be ascribed to the reduced surface acidity. Furthermore, the decreased CO2 production corresponded to the declined complete combustion of ethanol. Consequently, the complete combustion of ethanol to CO2 on the SnO2 surface was weakened after Bi2O3-loading, and CH3CHO became the main intermediate combined with the reduced production of C2H4. As a result, partial combustion was dominant during the combustion of ethanol and CH3CHO on the surface of 1Bi-L-SnO2 material below 300 °C. In addition, the combustion of acetone on SnO2 and 1Bi-L-SnO2 surfaces was investigated in Figure S9. It was obvious that no acetone consumption and CO2 yields were detected at 200 °C and 250 °C, suggesting little combustion of acetone occurred on material surfaces. As the temperature increased to 300 °C and 350 °C, part of the acetone was combusted to CO2, a little CH3CHO, and other intermediates. Similarly, neat-SnO2 showed a higher amount of acetone consumption and CO2 production than 1Bi-L-SnO2, indicating the improvement in partial combustion of acetone after Bi2O3-loading. As a result, the combustion of acetone on the 1Bi-L-SnO2 surface exhibited a similar phenomenon to that of ethanol, which was mainly in accordance with partial combustion.

3.4. TPD and TPR Measurements

The desorption of oxygen on the surfaces of SnO2, 3Bi-M-SnO2, and 1Bi-L-SnO2 materials was evaluated by O2-TPD combined with a mass spectrometer monitored at m/z 32, as depicted in Figure 6. Obviously, the desorption signal of SnO2 gradually increased from approximately 450 °C, corresponding to the desorption of surface lattice oxygen (O2−) of SnO2 [16,42]. 3Bi-M-SnO2 sample showed a similar phenomenon with neat-SnO2, indicating the agglomerated Bi2O3 showed little effect on the desorption of oxygen of SnO2. For 1Bi-L-SnO2, the temperature-dependent desorption signal could be roughly categorized as 100–400 °C and 400–550 °C. The former signal was assigned to the desorption of active oxygen ions (such as O2−, O−, and O2−) [43,44]. The desorption at higher temperatures was caused by the desorption of O2 arising from the surface lattice oxygen of SnO2. Consequently, the Bi2O3-loading onto the SnO2 surface facilitated the desorption of surface oxygen ions during 100–400 °C, which might be attributed to the abundant Bi2O3/SnO2 interfaces. Additionally, the effect of Bi2O3 particles on the surface acidity of SnO2 NPs was investigated by NH3-TPD measurements. As demonstrated in Figure S10, the desorption amount of NH3 on the SnO2 surface was decreased after Bi2O3-mixing and Bi2O3-loading processes, suggesting the exposure of acid sites on the surface of SnO2 was declined by the introduction of Bi2O3 particles. In this case, neat-SnO2 showed the highest responses to C2H4 and C7H8 than other sensors, consistent with the amount of surface acidity. The result indicated that surface acidic sites might play a more vital role in the combustion of C2H4 and C7H8 than surface oxygen ions [45].
The desorption signals on SnO2 and 1Bi-L-SnO2 surfaces after ethanol adsorption were investigated by ethanol-TPR measurements. Initially, ethanol molecules were respectively adsorbed on the materials at various temperatures (200 °C, 250 °C, 300 °C, and 350 °C) and then heated to 500 °C under Ar flow containing 21% of O2. The desorption signals at mass numbers 44 (the fragment of CH3CHO and CO2), 2 (H2), and 17 (H2O) were monitored during the heating period, as shown in Figure 7. Roughly, SnO2 and 1Bi-L-SnO2 materials showed similar TPR spectra. When ethanol was exposed at 200 °C, m/z 44 and m/z 2 exhibited distinct desorption peaks during 200–300 °C. According to the catalytic combustion result, no CO2 was produced at 200 °C and 250 °C, indicating the peak at m/z 44 was probably mainly caused by the desorption of CH3CHO. The peak at m/z 2 was assigned to the production of H2 arising from the deprotonation or dehydrogenation of ethanol. The phenomenon suggested that ethanol molecules could be dissociated to CH3CHO accompanied by the release of protons on SnO2 and 1Bi-L-SnO2 surfaces. When the materials adsorbed ethanol above 250 °C, m/z 44 and m/z 17 exhibited desorption peaks while no H2 was produced during the heating process, indicating ethanol molecules were further oxidized. As a result, ethanol molecules on SnO2 and 1Bi-L-SnO2 surfaces were mainly followed by dissociation and partial oxidation at 200 °C and 250 °C. Besides, the desorption amount at m/z 44 was drastically decreased when ethanol was exposed at 300 °C and 350 °C, illustrating ethanol molecules were easily oxidized and desorbed from the material surface at high temperatures.

3.5. Sensing Mechanism

Based on the above discussions, we proposed the possible sensing mechanism of SnO2 and Bi2O3-loaded SnO2 gas sensors. Firstly, the reaction pathway of ethanol combustion on the SnO2 surface was investigated as the representative of oxygenated VOCs. For neat-SnO2, at 200 °C and 250 °C, ethanol molecules were initially adsorbed and then partially dissociated to ethoxides or CH3CHO via deprotonation or dehydrogenation, respectively. Meanwhile, the dissociated protons could remain on the SnO2 surface by bonding with oxygen ions. Next, part of the ethoxides and CH3CHO molecules were further oxidized to CO2 and intermediates (CH3COOH, CO, etc.) by combustion reaction as the increase in temperature (300 °C and 350 °C). On the other hand, a small amount of ethanol molecules was converted to C2H4 and H2O by dehydration at the acidic sites of SnO2. In this case, the dissociation and partial oxidation of ethanol exhibited a significant effect on the sensitivities especially at 200 °C and 250 °C. According to the results of O2-TPD measurements, the surface lattice oxygen of SnO2 tended to be active at higher temperatures. Hence, the surface oxygen ions were major active species for ethanol adsorption.
Figure 8 shows the reaction pathway of ethanol combustion on the 1Bi-L-SnO2 surface. 1Bi-L-SnO2 sensor showed a larger amount of surface oxygen ions, as demonstrated in O2-TPD profiles. At 200 °C and 250 °C, the increased basic oxygen ions (mainly O−) could attract the adsorption of ethanol molecules by promoting the cleavage of acidic α-H and O-H bonding. Subsequently, the ethoxides and CH3CHO were partially oxidized with the increase in temperature, which was similar to neat-SnO2. Additionally, the catalytic combustion results indicated 1Bi-L-SnO2 showed a declined production of CO2 than neat-SnO2 material, revealing the improvement in surface oxygen ions improved the partial combustion of ethanol. In this context, the construction of Bi2O3/SnO2 interfaces mainly improved the initial adsorption, dissociation, and partial combustion of ethanol molecules. As a result, the 1Bi-L-SnO2 sensor showed higher sensitivity and faster response speed to ethanol than neat-SnO2, particularly at 200 °C and 250 °C. Furthermore, oxygen vacancies would be exposed after consuming the surface oxygen ions, especially at high temperatures, accelerating the adsorption of oxygen and gas molecules. In addition, catalytic combustion and TPR measurements confirmed the active combustion and desorption of ethanol on material surfaces at 300–350 °C, leading to a smaller change in the electrical resistance than at 200–250 °C. Hence, the SnO2 and 1Bi-L-SnO2 sensors showed fast response speeds but weak sensitivities to ethanol at high temperatures. Moreover, the production of C2H4 almost disappeared due to the declined exposure of surface acidic sites by the Bi2O3-loading process. With the increasing concentration of Bi2O3 (3Bi-L-SnO2 sensor), the amount of surface oxygen ions was further increased, while the excessively dispersed Bi2O3 particles on the SnO2 surface disturbed the adsorption of gas molecules on SnO2, suppressing the further oxidation. Therefore, the 3Bi-L-SnO2 sensor showed a higher response speed but lower sensitivity to oxygenated VOCs than the 1Bi-L-SnO2 sensor.
As the major intermediate during ethanol combustion, the oxidation of CH3CHO might show similar productions with that of ethanol combustion, such as CH3COOH and CO. In addition, the reaction pathway of methanol combustion frequently consisted with ethanol due to the same functional group. For example, CH3OH molecules can be dissociated to HCHO by dehydrogenation and further oxidized to HCOOH, CO, and CO2. For acetone combustion, we could not observe the main intermediates by catalytic combustion measurement except a little CH3CHO at 300 °C and 350 °C. However, the acidic α-H bonding of acetone might be cleavage by the basic adsorption ions to form CH3COCH2− and protons. Subsequently, CH3CHO and CH3COOH might be produced during acetone combustion like ethanol combustion [46,47]. In addition, the catalytic combustion results confirmed the combustion of acetone on the 1Bi-L-SnO2 surface exhibited a similar phenomenon to that of ethanol, which was mainly in accordance with the adsorption–desorption and partial combustion. As a result, 1Bi-L-SnO2 showed outstanding sensitivity and selectivity to oxygenated VOCs due to the improvement in surface oxygen ions.

4. Conclusions

In this experiment, Bi2O3-mixed SnO2 and Bi2O3-loaded SnO2 materials were synthesized for fabricating efficient gas sensors toward multiple oxygenated VOCs. Bi2O3 particles were uniformly dispersed on the SnO2 surface for Bi2O3-loaded SnO2 materials, leading to the construction of abundant Bi2O3/SnO2 interfaces. While agglomerated Bi2O3 particles were physically mixed with SnO2 NPs in Bi2O3-mixed SnO2 samples. O2-TPD spectra revealed the increased surface oxygen ions of Bi2O3-loaded SnO2 materials than that of SnO2 and Bi2O3-mixed SnO2 materials. 1Bi-L-SnO2 sensor showed improved sensitivity and selectivity to tested oxygenated VOCs, particularly at 200 °C and 250 °C. While the Bi2O3-mixed SnO2 sensor exhibited similar sensing properties to the SnO2 sensor. According to the results of catalytic combustion and TPR measurements, the detected sensitivities to ethanol of SnO2 and 1Bi-L-SnO2 sensors were primarily caused by the adsorption and partial oxidation of ethanol molecules. Meanwhile, the Bi2O3-loading process improved the partial combustion of ethanol on the SnO2 surface. The phenomenon indicated the effect of different distributions of Bi2O3 on the sensing performance of SnO2-based sensors. The abundant Bi2O3/SnO2 interfaces formed by the uniform dispersion of Bi2O3 particles were responsible for the enhancement of surface oxygen ions and sensing properties. The research provided a promising application for achieving sensitive and selective gas sensors for total oxygenated VOC detection by modulating the surface properties of sensing materials using foreign additives.

Supplementary Materials

The following supporting information can be downloaded at: https://www.mdpi.com/article/10.3390/nano14242032/s1, Figure S1: Explanation of operating processes during (a) O2-TPD-MS (b) NH3-TPD-MS. Figure S2. SEM-EDS mapping images of Sn and Bi elements for (a) 3Bi-M-SnO2 and (b) 3Bi-L-SnO2 samples. Figure S3. The electrical resistances in synthetic air of as-fabricated gas sensors at 200 °C, 250 °C, 300 °C, and 350 °C. Figure S4: Dynamic time-dependence response curves of gas sensors to 5 ppm of (a) CH3CH2OH, (b) CH3CHO, (c) CH3COCH3, (d) CH3OH at 200 °C. Figure S5: Dynamic time-dependence response curves of gas sensors to 5 ppm of (a) CH3CH2OH, (b) CH3CHO, (c) CH3COCH3, (d) CH3OH at 250 °C. Figure S6: Dynamic time-dependence response curves of gas sensors to 5 ppm of (a) CH3CH2OH, (b) CH3CHO, (c) CH3COCH3, (d) CH3OH at 300 °C. Figure S7: Dynamic time-dependence response curves of gas sensors to 5 ppm of (a) CH3CH2OH, (b) CH3CHO, (c) CH3COCH3, (d) CH3OH at 350 °C. Figure S8. The temperature-dependence of (a) CH3CH2OH consumption, (b) CO2, (c) CH3CHO, and (d) C2H4 yields during ethanol combustion on the surfaces of SnO2 and 1Bi-L-SnO2 particles from 200 °C to 350 °C. Figure S9. The temperature-dependence of (a) CH3COCH3 consumption, (b) CO2, and (c) CH3CHO yields during acetone combustion on the surfaces of SnO2 and 1Bi-L-SnO2 particles from 200 °C to 350 °C. Figure S10. (a) NH3-TPD profiles of as-prepared materials; NH3-TPD combined with mass spectrometer spectra of (b) SnO2, (c) 1Bi-M-SnO2, (d) 3Bi-M-SnO2, (e) 1Bi-L-SnO2 and (f) 3Bi-L-SnO2 materials. Table S1. Average crystallite size, BET, and BJH results of SnO2, 1Bi-M-SnO2, 3Bi-M-SnO2, 1Bi-L-SnO2, 3Bi-L-SnO2 materials. Table S2. Response time of SnO2 and Bi2O3-loaded sensors to 5 ppm of ethanol at 200–350 °C.

Author Contributions

Conceptualization: H.Y., K.S. (Koichi Suematsu), and K.S. (Kengo Shimanoe); Experimental: H.Y. and F.H.M.; Writing—original draft: H.Y.; Writing—review and editing: K.S. (Koichi Suematsu), K.W. and K.S. (Kengo Shimanoe); Funding acquisition: K.S. (Koichi Suematsu) and K.S. (Kengo Shimanoe). All authors have read and agreed to the published version of the manuscript.

Funding

This work was funded by the Japan Society for the Promotion of Science (JSPS) KAKENHI grant numbers JP23K26740 and JP23K26383. This work was supported by JKA and its promotion funds from AUTORACE to K. Suematsu. It was also supported by the Chinese Scholarship Council (CSC) scholarship to Haoyue Yang.

Data Availability Statement

The original contributions presented in the study are included in the article and Supplementary Materials. Further inquiries can be directed to the corresponding author.

Acknowledgments

The authors sincerely thank to Transdisciplinary Research and Education Center for Green Technologies, Kyushu University.

Conflicts of Interest

The authors declare no competing financial interests.

References

  1. Wang, W.; Yan, Y.; Fang, H.; Li, J.; Zha, S.; Wu, T. Volatile organic compound emissions from typical industries: Implications for the importance of oxygenated volatile organic compounds. Atmos. Pollut. Res. 2023, 14, 101640. [Google Scholar] [CrossRef]
  2. Gilman, J.B.; Lerner, B.M.; Kuster, W.C.; Goldan, P.D.; Warneke, C.; Veres, P.R.; Roberts, J.M.; Gouw, J.A.; Burling, I.R.; Yokelson, R.J. Biomass burning emissions and potential air quality impacts of volatile organic compounds and other trace gases from fuels common in the US. Atmos. Chem. Phys. 2015, 15, 13915–13938. [Google Scholar] [CrossRef]
  3. Mellouki, A.; Wallington, T.J.; Chen, J. Atmospheric chemistry of oxygenated volatile organic compounds: Impacts on air quality and climate. Chem. Rev. 2015, 115, 3984–4014. [Google Scholar] [CrossRef]
  4. Ran, L.; Zhao, C.S.; Xu, W.Y.; Lu, X.Q.; Han, M.; Lin, W.L.; Yan, P.; Xu, X.B.; Deng, Z.Z.; Ma, N.; et al. VOC reactivity and its effect on ozone production during the HaChi summer campaign. Atmos. Chem. Phys. 2011, 11, 4657–4667. [Google Scholar] [CrossRef]
  5. Wang, F.; Ho, S.S.H.; Man, C.L.; Qu, L.; Wang, Z.; Ning, Z.; Ho, K.F. Characteristics and sources of oxygenated VOCs in Hong Kong: Implications for ozone formation. Sci. Total Environ. 2024, 912, 169156. [Google Scholar] [CrossRef] [PubMed]
  6. Matheus, C.R.V.; Aguiar, E.F.S. The role of MPV reaction in the synthesis of propene from ethanol through the acetone route. Catal. Commun. 2020, 145, 106096. [Google Scholar] [CrossRef]
  7. Sun, Y.; Zhang, X.; Li, N.; Xing, X.; Yang, H.; Zhang, F.; Cheng, J.; Zhang, Z.; Hao, Z. Surface properties enhanced MnxAlO oxide catalysts derived from MnxAl layered double hydroxides for acetone catalytic oxidation at low temperature. Appl. Catal. B-Environ. Energy 2019, 251, 295–304. [Google Scholar] [CrossRef]
  8. Lee, J.; Jung, Y.; Sung, S.H.; Lee, G.; Kim, J.; Seong, J.; Shim, Y.S.; Jun, S.C.; Jeon, S. High-performance gas sensor array for indoor air quality monitoring: The role of Au nanoparticles on WO3, SnO2, and NiO-based gas sensors. J. Mater. Chem. A 2021, 9, 1159–1167. [Google Scholar] [CrossRef]
  9. Li, C.; Kim, K.; Fuchigami, T.; Asaka, T.; Kakimoto, K.I.; Masuda, Y. Acetone gas sensor based on Nb2O5@SnO2 hybrid structure with high selectivity and ppt-level sensitivity. Sens. Actuators B Chem. 2023, 393, 134144. [Google Scholar] [CrossRef]
  10. Sui, N.; Zhang, P.; Zhou, T.T.; Zhang, T. Selective ppb-level ozone gas sensor based on hierarchical branch-like In2O3 nanostructure. Sens. Actuators B Chem. 2021, 336, 129612. [Google Scholar] [CrossRef]
  11. Xu, H.; Gong, Z.X.; Huo, L.Z.; Guo, C.F.; Yang, X.J.; Wang, Y.X.; Luo, X.P. Zinc Oxide-Loaded Cellulose-Based Carbon Gas Sensor for Selective Detection of Ammonia. Nanomaterials 2023, 13, 3151. [Google Scholar] [CrossRef] [PubMed]
  12. Suematsu, K.; Harano, W.; Yamasaki, S.; Watanabe, K.; Shimanoe, K. One-trillionth level toluene detection using a dual-designed semiconductor gas sensor: Material and sensor-driven designs. ACS Appl. Electron. Mater. 2020, 2, 4122–4126. [Google Scholar] [CrossRef]
  13. Maekawa, T.; Tamaki, J.; Miura, N.; Yamazoe, N.; Matsushima, S. Development of SnO2-based ethanol gas sensor. Sens. Actuators B Chem. 1992, 9, 63–69. [Google Scholar] [CrossRef]
  14. Ren, H.; Zhao, W.; Wang, L.; Ryu, S.O.; Gu, C. Preparation of porous flower-like SnO2 micro/nano structures and their enhanced gas sensing property. J. Alloys Compd. 2015, 653, 611–618. [Google Scholar] [CrossRef]
  15. Zhang, S.; Pu, Y.; Cao, S.; Zhu, D. SnO2 nanoparticles derived from metal–organic precursors as an acetaldehyde gas sensor with ppb-level detection limit. ACS Appl. Nano Mater. 2023, 6, 13177–13187. [Google Scholar] [CrossRef]
  16. Suematsu, K.; Hiroyama, Y.; Watanabe, K.; Shimanoe, K. Amplifying the receptor function on Ba0.9La0.1FeO3-SnO2 composite particle surface for high sensitivity toward ethanol gas sensing. Sens. Actuators B Chem. 2022, 354, 131256. [Google Scholar] [CrossRef]
  17. Zhu, X.; Cao, P.; Li, P.; Yu, Y.; Guo, R.; Li, Y.; Yang, H. Bimetallic PtAu-Decorated SnO2 Nanospheres Exhibiting Enhanced Gas Sensitivity for Ppb-Level Acetone Detection. Nanomaterials 2024, 14, 1097. [Google Scholar] [CrossRef]
  18. Zong, S.; Zhang, Y.; Cao, J.; Qin, C.; Bala, H.; Wang, Y. Hydrothermal Synthesis of SnO2 with Different Morphologies as Sensing Materials for HCHO Detection. Langmuir 2024, 40, 10814–10824. [Google Scholar] [CrossRef]
  19. Jinkawa, T.; Sakai, G.; Tamaki, J.; Miura, N.; Yamazoe, N. Relationship between ethanol gas sensitivity and surface catalytic property of tin oxide sensors modified with acidic or basic oxides. J. Mol. Catal. A-Chem. 2000, 155, 193–200. [Google Scholar] [CrossRef]
  20. Torai, S.; Ueda, T.; Kamada, K.; Hyodo, T.; Shimizu, Y. Effects of addition of CuxO to porous SnO2 microspheres prepared by ultrasonic spray pyrolysis on sensing properties to volatile organic compounds. Chemosensors 2023, 11, 59. [Google Scholar] [CrossRef]
  21. Kumar, A.; Mukasyan, A.S.; Wolf, E.E. Combustion synthesis of Ni, Fe and Cu multi-component catalysts for hydrogen production from ethanol reforming. Appl. Catal. A-Gen. 2011, 401, 20–28. [Google Scholar] [CrossRef]
  22. Suematsu, K.; Ma, N.; Yuasa, M.; Kida, T.; Shimanoe, K. Surface-modification of SnO2 nanoparticles by incorporation of Al for the detection of combustible gases in a humid atmosphere. RSC Adv. 2015, 5, 86347–86354. [Google Scholar] [CrossRef]
  23. Suematsu, K.; Shin, Y.; Ma, N.; Oyama, T.; Sasaki, M.; Yuasa, M.; Kida, T.; Shimanoe, K. Pulse-driven micro gas sensor fitted with clustered Pd/SnO2 nanoparticles. Anal. Chem. 2015, 87, 8407–8415. [Google Scholar] [CrossRef] [PubMed]
  24. Zhang, H.; Guo, S.; Zheng, W.; Wang, H.; Li, H.Y.; Yu, M.H.; Chang, Z.; Bu, X.H.; Liu, H. Facile engineering of metal–organic framework derived SnO2-ZnO composite based gas sensor toward superior acetone sensing performance. Chem. Eng. J. 2023, 469, 143927. [Google Scholar] [CrossRef]
  25. Dong, Z.M.; Xia, Q.; Ren, H.; Shang, X.; Lu, X.; Joo, S.W.; Huang, J. Preparation of hollow SnO2/ZnO cubes for the high-performance detection of VOCs. Ceram. Int. 2023, 49, 4650–4658. [Google Scholar] [CrossRef]
  26. Acharyya, S.; Bhowmick, P.K.; Guha, P.K. Selective identification and quantification of VOCs using metal nanoparticles decorated SnO2 hollow-spheres based sensor array and machine learning. J. Alloys Compd. 2023, 968, 171891. [Google Scholar] [CrossRef]
  27. Niwa, M.; Igarashi, J.Y. Role of the solid acidity on the MoO3 loaded on SnO2 in the methanol oxidation into formaldehyde. Catal. Today 1999, 52, 71–81. [Google Scholar] [CrossRef]
  28. Yan, H.; Liu, T.; Lv, Y.; Xu, X.; Xu, J.; Fang, X.; Wang, X. Doping SnO2 with metal ions of varying valence states: Discerning the importance of active surface oxygen species vs. acid sites for C3H8 and CO oxidation. Phys. Chem. Chem. Phys. 2024, 26, 3950–3962. [Google Scholar] [CrossRef] [PubMed]
  29. Lu, B.; Ma, S.; Liang, S.; Wang, Z.; Liu, Y.; Mao, S.; Ban, H.; Wang, L.; Wang, Y. Efficient Conversion of Ethanol to 1-Butanol over Adjacent Acid–Base Dual Sites via Enhanced C–H Activation. ACS Catal. 2023, 13, 4866–4872. [Google Scholar] [CrossRef]
  30. Chauhan, A.; Verma, R.; Dhatwalia, J.; Kumari, A.; Dutta, V.; Chandrasekaran, G.; Ghotekar, S.; Kaur, M.; Vignesh, J.; Thakur, S. Phyto-mediated synthesis of pure phase α-Bi2O3 nanostructures using Rubus ellipticus plant extract: Photocatalytic activity and antimicrobial efficacy. Biomass Convers. Biorefinery 2024, 14, 25103–25122. [Google Scholar] [CrossRef]
  31. Dai, W.; Wang, P.; Long, J.; Xu, Y.; Zhang, M.; Yang, L.; Zou, J.; Luo, X.; Luo, S. Constructing robust Bi active sites in situ on α-Bi2O3 for efficient and selective photoreduction of CO2 to CH4 via directional transfer of electrons. ACS Catal. 2023, 13, 2513–2522. [Google Scholar] [CrossRef]
  32. Moumen, A.; Zappa, D.; Poli, N.; Comini, E. Catalyst–Assisted vapor liquid solid growth of α-Bi2O3 nanowires for acetone and ethanol detection. Sens. Actuators B Chem. 2021, 346, 130432. [Google Scholar] [CrossRef]
  33. Jiang, S.; Wang, L.; Hao, W.; Li, W.; Xin, H.; Wang, W.; Wang, T. Visible-light photocatalytic activity of S-doped α-Bi2O3. J. Phys. Chem. C 2015, 119, 14094–14101. [Google Scholar] [CrossRef]
  34. Park, S.; Kim, S.; Sun, G.J.; Lee, C. Synthesis, structure, and ethanol gas sensing properties of In2O3 nanorods decorated with Bi2O3 nanoparticles. ACS Appl. Mater. Interfaces 2015, 7, 8138–8146. [Google Scholar] [CrossRef]
  35. Cheng, L.; Li, Y.; Sun, G.; Cao, J.; Wang, Y. Modification of Bi2O3 on ZnO porous nanosheets-assembled architecture for ultrafast detection of TEA with high sensitivity. Sens. Actuators B Chem. 2023, 376, 132986. [Google Scholar] [CrossRef]
  36. Zhang, M.; Liu, K.; Zhang, X.; Wang, B.; Xu, X.; Du, X.; Yang, C.; Zhang, K. Interfacial energy barrier tuning of hierarchical Bi2O3/WO3 heterojunctions for advanced triethylamine sensor. J. Adv. Ceram. 2022, 11, 1860–1872. [Google Scholar] [CrossRef]
  37. Tanaka, K.I.; Ozaki, A. Acid-base properties and catalytic activity of solid surfaces. J. Catal. 1967, 8, 1–7. [Google Scholar] [CrossRef]
  38. Guo, Y.; Liu, B.; Duan, Z.; Yuan, Z.; Jiang, Y.; Tai, H. Batch fabrication of H2S sensors based on evaporated Pd/WO3 film with ppb-level detection limit. Mater. Chem. Phys. 2023, 302, 127768. [Google Scholar] [CrossRef]
  39. Suematsu, K.; Watanabe, K.; Tou, A.; Sun, Y.; Shimanoe, K. Ultraselective toluene-gas sensor: Nanosized gold loaded on zinc oxide nanoparticles. Anal. Chem. 2018, 90, 1959–1966. [Google Scholar] [CrossRef] [PubMed]
  40. Gonçalves, F.; Medeiros, P.R.; Eon, J.G.; Appel, L.G. Active sites for ethanol oxidation over SnO2-supported molybdenum oxides. Appl. Catal. A-Gen. 2000, 193, 195–202. [Google Scholar] [CrossRef]
  41. Sun, J.; Wang, Y. Recent advances in catalytic conversion of ethanol to chemicals. ACS Catal. 2014, 4, 1078–1090. [Google Scholar] [CrossRef]
  42. Yamazoe, N.; Fuchigami, J.; Kishikawa, M.; Seiyama, T. Interactions of tin oxide surface with O2, H2O and H2. Surf. Sci. 1979, 86, 335–344. [Google Scholar] [CrossRef]
  43. Guo, Y.; Liang, J.; Liu, Y.; Liu, Y.; Xu, X.; Fang, X.; Zhong, W.; Wang, X. Identifying surface active sites of SnO2: Roles of surface O2−, O22− anions and acidic species played for toluene deep oxidation. Ind. Eng. Chem. Res. 2019, 58, 18569–18581. [Google Scholar] [CrossRef]
  44. Yan, L.; Liu, Y.; Zha, K.; Li, H.; Shi, L.; Zhang, D. Deep insight into the structure–activity relationship of Nb modified SnO2–CeO2 catalysts for low-temperature selective catalytic reduction of NO by NH3. Catal. Sci. Technol. 2017, 7, 502–514. [Google Scholar] [CrossRef]
  45. Liu, Y.; Guo, Y.; Liu, Y.; Xu, X.; Peng, H.; Fang, X.; Wang, X. SnO2 nano-rods promoted by In, Cr and Al cations for toluene total oxidation: The impact of oxygen property and surface acidity on the catalytic activity. Appl. Surf. Sci. 2017, 420, 186–195. [Google Scholar] [CrossRef]
  46. Meziane, I.; Fenard, Y.; Delort, N.; Herbinet, O.; Bourgalais, J.; Ramalingam, A.; Heufer, K.A.; Battin-Leclerc, F. Experimental and modeling study of acetone combustion. Combust. Flame 2023, 257, 112416. [Google Scholar] [CrossRef]
  47. Zaki, M.I.; Hasan, M.A.; Pasupulety, L. Surface reactions of acetone on Al2O3, TiO2, ZrO2, and CeO2: IR spectroscopic assessment of impacts of the surface acid-base properties. Langmuir 2001, 17, 768–774. [Google Scholar] [CrossRef]
Nanomaterials 14 02032 g001
Figure 1. (a) XRD patterns of SnO2, 1Bi-M-SnO2, 3Bi-M-SnO2, 1Bi-L-SnO2, 3Bi-L-SnO2; (b) the corresponding magnified region at 22–30°.
Figure 1. (a) XRD patterns of SnO2, 1Bi-M-SnO2, 3Bi-M-SnO2, 1Bi-L-SnO2, 3Bi-L-SnO2; (b) the corresponding magnified region at 22–30°.
Nanomaterials 14 02032 g001
Nanomaterials 14 02032 g002
Figure 2. SEM-EDS elemental mapping images of Sn and Bi for (a) 1Bi-M-SnO2 and (b) 1Bi-L-SnO2 samples.
Figure 2. SEM-EDS elemental mapping images of Sn and Bi for (a) 1Bi-M-SnO2 and (b) 1Bi-L-SnO2 samples.
Nanomaterials 14 02032 g002
Nanomaterials 14 02032 g003
Figure 3. The responses of as-fabricated gas sensors to 5 ppm various VOCs at (a) 200 °C, (b) 250 °C, (c) 300 °C, and (d) 350 °C.
Figure 3. The responses of as-fabricated gas sensors to 5 ppm various VOCs at (a) 200 °C, (b) 250 °C, (c) 300 °C, and (d) 350 °C.
Nanomaterials 14 02032 g003
Nanomaterials 14 02032 g004
Figure 4. Dynamic time-dependence response curves of SnO2 and Bi2O3-loaded SnO2 sensors to 5 ppm of ethanol at (a) 200 °C, (b) 250 °C, (c) 300 °C, and (d) 350 °C.
Figure 4. Dynamic time-dependence response curves of SnO2 and Bi2O3-loaded SnO2 sensors to 5 ppm of ethanol at (a) 200 °C, (b) 250 °C, (c) 300 °C, and (d) 350 °C.
Nanomaterials 14 02032 g004
Nanomaterials 14 02032 g005
Figure 5. The temperature-dependence consumption of CH3CH2OH and the yields of products (CO2, CH3CHO, and C2H4) during ethanol combustion on the surfaces of (a) SnO2 and (b) 1Bi-L-SnO2 particles from 200 °C to 350 °C.
Figure 5. The temperature-dependence consumption of CH3CH2OH and the yields of products (CO2, CH3CHO, and C2H4) during ethanol combustion on the surfaces of (a) SnO2 and (b) 1Bi-L-SnO2 particles from 200 °C to 350 °C.
Nanomaterials 14 02032 g005
Nanomaterials 14 02032 g006
Figure 6. O2-TPD combined with mass spectrometer monitored at m/z 32 of SnO2, 3Bi-M-SnO2, and 1Bi-L-SnO2 materials.
Figure 6. O2-TPD combined with mass spectrometer monitored at m/z 32 of SnO2, 3Bi-M-SnO2, and 1Bi-L-SnO2 materials.
Nanomaterials 14 02032 g006
Nanomaterials 14 02032 g007
Figure 7. TPR spectra of (a) SnO2 and (b) 1Bi-L-SnO2 under O2/Ar flow after exposing 100 ppm ethanol/Ar during heating period from 200 °C, 250 °C, 300 °C, 350 °C, to 500 °C at mass numbers 44, 2, and 17.
Figure 7. TPR spectra of (a) SnO2 and (b) 1Bi-L-SnO2 under O2/Ar flow after exposing 100 ppm ethanol/Ar during heating period from 200 °C, 250 °C, 300 °C, 350 °C, to 500 °C at mass numbers 44, 2, and 17.
Nanomaterials 14 02032 g007
Nanomaterials 14 02032 g008
Figure 8. Schematic illustration of ethanol oxidation route on the 1Bi-L-SnO2 material surface.
Figure 8. Schematic illustration of ethanol oxidation route on the 1Bi-L-SnO2 material surface.
Nanomaterials 14 02032 g008
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Yang, H.; Suematsu, K.; Mashiba, F.H.; Watanabe, K.; Shimanoe, K. Oxygenated VOC Detection Using SnO2 Nanoparticles with Uniformly Dispersed Bi2O3. Nanomaterials 2024, 14, 2032. https://doi.org/10.3390/nano14242032

AMA Style

Yang H, Suematsu K, Mashiba FH, Watanabe K, Shimanoe K. Oxygenated VOC Detection Using SnO2 Nanoparticles with Uniformly Dispersed Bi2O3. Nanomaterials. 2024; 14(24):2032. https://doi.org/10.3390/nano14242032

Chicago/Turabian Style

Yang, Haoyue, Koichi Suematsu, Felipe Hiroshi Mashiba, Ken Watanabe, and Kengo Shimanoe. 2024. "Oxygenated VOC Detection Using SnO2 Nanoparticles with Uniformly Dispersed Bi2O3" Nanomaterials 14, no. 24: 2032. https://doi.org/10.3390/nano14242032

APA Style

Yang, H., Suematsu, K., Mashiba, F. H., Watanabe, K., & Shimanoe, K. (2024). Oxygenated VOC Detection Using SnO2 Nanoparticles with Uniformly Dispersed Bi2O3. Nanomaterials, 14(24), 2032. https://doi.org/10.3390/nano14242032

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop