Detection of H2S, SO2, and NO2 using electrostatic sprayed tungsten oxide films

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Abstract

This paper presents the electrostatic spray deposition of tungsten oxide (WO3) films for the detection of different pollutant gases. The influence of several types of precursors on the structure and morphology of the films was studied by means of X-ray diffraction (XRD) and scanning electron microscopy (SEM) techniques. This preliminary study allowed to select the proper precursor for the preparation of pure and porous WO3 films which offer high gas response (Rair/Rgas=1200) to low concentrations of H2S (10 ppm) at low operating temperature (200 °C). The gas response to NO2 and SO2 is low at this temperature suggesting no possible interference with these two gases during the H2S detection. Furthermore, the films are able to detect very low concentrations of NO2 (less than 1 ppm) at 150 °C.

Introduction

Due to its negative impacts on the health and on the environment a great attention has been paid to the air pollution caused by different pollutant gases released from industrial processes and vehicles. Usually, conventional techniques like chromatography or electrochemistry are used to detect and monitor these gases. To overcome their disadvantages in terms of high price, large volume and time consuming, semiconductor metal oxide gas sensors can be employed.

The tungsten trioxide gas sensor was first reported by Shaver [1], who observed the modification of the WO3 film resistance upon hydrogen exposure. Over the time, WO3 proved to be an attractive material for gas sensor applications, mainly used for the detection of NO2 [2], [3], [4] but also employed for the detection of other gases, such as H2S [5], SO2 [6], O2 [7], etc.

Teoh et al. [8] prepared mesoporous WO3 films which showed very high gas response at low concentration of NO2 and at low operating temperature. The authors suggested that WO3 excellent sensing properties are due to its high surface area which allows high quantities of gas to be adsorbed. Tamaki et al. [9] found a correlation between NO2 gas response and the thickness of the WO3 films and that of the electrodes: when the film thickness is higher than the electrode one, the gas response improves with the film thickness decrease. Furthermore, when the film thickness is lower than the substrate one, the gas response proved to be independent of the film thickness. The influence of the annealing atmosphere on the WO3 gas response has been studied by Lozzi et al. [10]. They showed that the vacuum treated films have a lower gas response to NO2 comparing with those annealed in air. Hence, the decrease in the gas response was explained by the decrease in the film oxygen concentration.

The film substrate can have an influence on the gas response as showed by Lee et al. [11]. The authors found that the substrates with high degree of surface roughness induce the formation of highly porous films with small particle size, increasing in this way the gas response. Several authors have improved the gas sensor properties by doping with different kinds of metals or metal oxides. The most employed dopant to increase the WO3 gas response to NO2 is TiO2, and, this improvement is usually correlated with the inhibition of the WO3 grain growth during the doping process [12], [13].

Concerning the H2S detection, Barrett et al. [14] was one of the first authors who investigated the gas response of WO3 to H2S. Solis et al. [5] detected H2S with a very high gas response (four orders of magnitude) at room temperature and this remarkable performance was related to the formation of tetragonal WO3 phase. The inconvenience of these sensors was the resistance recovery obtained only by applying a heat treatment at 250 °C. Noble metals as activator layers or dopants were also used to improve the gas response to H2S. Tao et al. [15] have chosen Pt as an activator layer to improve the gas response to H2S and the selectivity to other reducing gases like CH4, CO, and H2. Stankova et al. [16] studied the influence of the electrode geometry on the WO3 gas response to H2S. It was found that smaller the gap between the electrodes is, higher the sensor gas response is. Hoel et al. [17] have detected H2S at room temperature using Al doped WO3 films. The films proved to detect H2S, NO2 and CO at different operating temperatures (i.e., 400, 525, and 700 K). The use of a sensor array operating at different temperatures was proposed to improve the selectivity.

It is obvious that various methods have been used to improve the gas response of WO3, including especially the modification of the morphology and the microstructure (i.e., grain size, film thickness, phase) by using different deposition techniques [18], [19], [20], [21], by doping with different compounds [12], [13], [22], [23] or by modifying the sensor geometry [16], [24].

Until now, the deposition of WO3 films has been done by several techniques as chemical vapour deposition [25], sol–gel [2], [26], sputtering [18], [27], and spray pyrolysis [19], [20]. In this work the electrostatic spray deposition technique is selected for the preparation of WO3 films considering that it allows an easy control of the morphology and the composition of the films. Firstly, the influence of the precursor solution on the structure and the morphology of the films are presented. Secondly, the performance of WO3 films in the detection of different pollutant gases (H2S, SO2, and NO2) is evaluated as a function of the operating temperature, and also as a function of the gas concentration.

Section snippets

Sensor fabrication

For the fabrication of the sensors, alumina pellets (99.7%, Gimex Technische Keramiek B.V., The Netherlands), with a dimension of 10×20 mm2 and a thickness of 1 mm were used. Platinum electrodes (1–5 μm in thickness) were applied by coating a platinum paste (Engelhard Clal, model 6082A) followed by a thermal treatment at 800 °C for 2 h in air. A distance of 1 mm was maintained between the two electrodes. Then the WO3 sensing film was deposited on this Pt-coated alumina substrate using a stainless

Gas-sensing measurements

The experimental set-up used to evaluate the WO3 gas sensing performances is described in Fig. 1. The films were placed in a closed quartz tube furnace where the measurements were carried out at different operating temperatures (50–300 °C). The temperature was measured using a K type thermocouple (placed close to the sensor) which was controlled by a PID temperature regulator (JUMO dTRON 16.1). The resistance of the films was measured with an electrometer (KEITHLEY 6514) by using Pt wires and

Structure and morphology characterization

The relevant parameters influencing the sensor performance are mainly connected with their morphology and their microstructure. The porous structure is preferable because it enhances the adsorption of the gas molecules improving in this way the gas response. In the same way, the small particle size also plays a very important role for a gas response improvement. Hence, tailoring these parameters is of great interest.

The structure of the films prepared using different types of precursors has

Conclusions

In this paper it is demonstrated that a simple and cost-effective deposition technique, i.e., electrostatic spray deposition can be used for the fabrication of WO3 sensors which are able to detect different pollutant gases. The films are obtained with different types of precursors and the most convenient one (tungsten ethoxide) has been selected for the fabrication of good quality films in terms of microstructure and morphology.

The films are able to detect very small quantities of NO2 (less

References (53)

  • P. Nelli et al.

    Sub-ppm NO2 sensors based on nanosized thin films of titanium–tungsten oxides

    Sensors Actuators B

    (1996)
  • W.-H. Tao et al.

    H2S sensing properties of noble metal doped WO3 thin film sensors fabricated by micromachining

    Sensors Actuators B

    (2002)
  • M. Stankova et al.

    Detection of SO2 and H2S in CO2 stream by means of WO3-based micro-hotplate sensors

    Sensors Actuators B

    (2004)
  • A. Hoel et al.

    Nanomaterials for environmental applications: novel WO3-based gas sensors made by advanced gas deposition

    Curr Appl Phys

    (2004)
  • C. Lemire et al.

    Magnetron sputtering deposition of WO3 thin films

    Sensors Actuators B

    (2002)
  • P.S. Patil et al.

    Influence of substrate temperature on properties of sprayed WO3 thin films

    Mater Chem Phys

    (2001)
  • R. Sivakumar et al.

    Preparation and characterization of spray deposited n-type WO3 thin films for electrochromic devices

    Mater Res Bull

    (2004)
  • H. Xia et al.

    Au-doped WO3-based sensor for NO2 detection at low operating temperatures

    Sensors Actuators B

    (2008)
  • C. Zamani et al.

    Detection of amines with chromium-doped WO3 mesoporous material

    Sensors Actuators B

    (2009)
  • S. Vallejos et al.

    Micro-machined WO3-based sensors selective to oxidizing gases

    Sensors Actuators B

    (2008)
  • P. Tägtström et al.

    Chemical vapour deposition of epitaxial WO3 films

    Thin Solid Films

    (1999)
  • A. Patra et al.

    Sol–gel electrochromic WO3 coatings on glass

    Mater Lett

    (2004)
  • M. Stankova et al.

    Influence of the annealing and operating temperatures on the gas-sensing properties of rf sputtered WO3 thin-film sensors

    Sensors Actuators B

    (2005)
  • E. Ozkan et al.

    Electrochromic and optical properties of mesoporous tungsten oxide films

    Solid State Ionics

    (2002)
  • A.P. Baker et al.

    Production of tungsten oxide coatings, via sol–gel processing of tungsten anion solutions

    Surf Coat Technol

    (2002)
  • K. Nishio et al.

    Electrochromic thin films prepared by sol–gel process

    Sol Energy Mater Sol Cells

    (2001)
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