Introduction
Bi-layer functionally gradient thick film semiconducting butane sensors
S. Shrivastava1, R. Biswal2, S. Chakraborty3, I. Roy3, A. K. Halder3, A. Sen3,*
Abstract
Gas sensors based on metal oxide semiconductors like tin dioxide are widely used for the detection of toxic and combustible gases like carbon monoxide, methane and butane. One of the problems of such sensors is their lack of sensitivity, which to some extent, can be circumvented by using different catalysts. However, highly reactive volatile organic compounds (VOC) coming from different industrial and domestic products (e.g. paints, lacquers, varnishes etc) can play havoc on such sensors and can give rise to false alarms. Any attempt to adsorb such VOCs results in sorption of the detecting gases (e.g. butane) too. To get round the problem, bi-layer sensors have been developed. Such tin oxide based functionally gradient bi-layer sensors have different compositions at the top (high resistance in the order of M? range) and bottom layers (low resistance in the order of K?). Here, instead of adsorbing the VOCs, they are allowed to interact and are consumed on the top layer of the sensors and a combustible gas like butane being less reactive, penetrates the top layer and interacts with the bottom layer and the electrical signal generated at the bottom layer from the combustible gas is collected. Such functionally gradient sensors, being very reliable, can find applications in domestic, industrial and strategic sectors. The processing steps for the fabrication of such sensors are also simple and cost-effective.
1. Introduction:
With increasing world-wide distribution of gas sensors for different applications, the demand of sensors fulfilling specific standards is growing in leaps and bounds1-2. Incidentally, volatile organic compounds are posing as a menace for satisfactory sensor performance because they come out from many industrial and domestic products like paints, lacquers, varnishes, cosmetics and automobile exhausts and being highly reactive, they tend to interfere with the sensor operation. In this regard, a particular concern is to avoid VOC cross-sensitivity with the detecting gases as VOCs being highly reactive, can give rise to false alarm. So far, primarily two techniques have been tried to get around the problem. One of the techniques to avoid interference from unwanted vapours is to use charcoal filters3. Such sensors are satisfactory for detection of CO in presence of VOCs. The disadvantage of this method lies in the fact that charcoal filters also adsorb most of the combustible gases and hence cannot be used satisfactorily to detect combustible gases like methane, propane, CNG and LPG in presence of VOCs. The other technique is to use uncoated/coated (with Pt, Pd etc.) filters of Al2O3, SiO2, WO3 etc on SnO2 coatings4-5. Such protecting filters can, to some extent, check specifically alcohol cross-sensitivity. The second method also has drawbacks because VOCs, in general, are either not affected by such filters or, the overall sensitivity of the sensors towards the detecting gases dramatically goes down. In this study we prepare a functionally graded tin dioxide based composition for gas sensors capable of detecting combustible gases in presence of volatile organic compounds.
2. Experimental
A precursor powder (SnO2+0.25 Sb2O3+ 5Pd+0.1B) for the bottom layer was prepared by the following steps6-7. Firstly, reagent grade stannous chloride (SnCl2, 2H2O) was dissolved in 200 mL of hot distilled water containing 20 drops of HCl with continuous stirring. Secondly, reagent grade Sb2O3 was dissolved in 50 mL distilled water (at 80oC) containing 5 drops of HCl. In the next step, reagent grade PdCl2 was taken in 100 mL distilled water containing 10 drops of HNO3 and PdCl2 was slowly dissolved by heating the mixture at 80oC under constant stirring for 1 h. The three solutions were mixed and added to ammonia solution under sonication (ultrasonic processor, vibronics, 25 kHz, 250 W) and the pH of the solution has maintained at 9. The precipitate was centrifuged and dried at 100oC for 10 h. Then calculated amount boric acid solution was added into the precursor powder and again dried into a mortar pestle. Finally, the dries powder was calcined at 900oC for 2 h.
To prepare the precursor powder (SnO2+ 10 Pd+ Al2O3 (varying amount 10 to 30 wt% with respect to tin dioxide based composition)) for the top layer, again stannous chloride and PdCl2 were dissolved in distilled water following the above procedure. Reagent grade alumina powder was then mixed with the calcined powder in the different ratio by weight using an agate mortar and a pestle.
A thick paste of the powder formulation for the bottom coating was made by mixing the prepared powder for the bottom layer with dilute alumina gel and cured at 600oC for 1 h. A thick paste of the powder formulation for the top coating was made by mixing the prepared powder for the top layer with dilute alumina gel and cured at 500oC for 30 min. Gold electrodes and platinum lead wires were attached at the ends of the tubes (by curing at a higher temperature) before applying the paste. Kanthal heating coils were placed inside the tubes and the leads were bonded to nickel pins. The electrical resistance and butane (500 ppm) sensitivity of the coatings were measured at 350°C by using a digital multimeter (Solartron), a constant voltage/current source (Keithley 228A) and X–Y recorder (Yokogawa). All the fired samples were initially preheated at 350°C for 72 h to achieve the desired stability before the measurements.
3. Results and discussion
The X-ray diffractogram of calcined tin dioxide powder (SnO2+0.25Sb2O3+ 5Pd+ 0.1B) is depicted in figure 1, which indicates complete SnO2 phase formation after firing at 900°C. The crystallite size of the SnO2 based powder is calculated by scherrer formula and the value is around 27 nm.
From this spectrum a strong band associated with the anti-symmetric Sn–O–Sn stretching mode of the surface binding oxide can be observed apparently at 600 cm-1.
The percent response (S) of SnO2 based sensors in different gases at 350°C has been calculated by
S = (RA – RG)/RA × 100%
RA and RG being the sensor resistance in air and gas at the same temperature. The measurement temperature, 350°C, was selected for our studies because C4H10 sensitivity is maximum around this temperature.
It is shown that the double coated sensors (30 wt% Al2O3 doped) prepared in this way showed an average sensitivity of around 90% in 500 ppm butane at 350oC. Incidentally, the sensors show a low sensitivity of around 30% or even less when kept inside a container containing standard paint thinner (a source of conc. VOCs) or acetone or alcohol etc. whereas, under the same condition, the sensitivity in such conc. VOCs can be as high as 75%, when the sensor is singly coated, i.e., the top coating of the sensor is absent. Hence, by properly designing the electronic circuit, the double coated sensors can be made selective to the detecting gases even in the presence of VOCs. The basic mechanism besides that the top layer of the functionally gradient bi-layer sensor contains tin dioxide, palladium and alumina. Alumina raises the resistance of the top coating to the order of 10–100 MW at the operating temperature. Such increase in resistance can be explained by considering the electronic interaction between semiconducting tin dioxide grains in close contact with the Lewis acid sites (electron acceptor) of alumina grains. Whereas, the bottom coating is devoid of alumina and contains antimony resulting in the resistance value of the order of 10–100 kW at the operating temperature. The VOCs being highly reactive, interact with adsorbed oxygen on the top layer releasing free electrons. However, due to three orders of higher resistance of the top coating with respect to that of the bottom coating, the top coating always remains shunted to the bottom coating. Less reactive gases like methane penetrate the top layer and interacts with the bottom layer of adsorbed oxygen and the change in resistance is picked up by the electrical leads at the bottom.
4. Conclusions
By modifying the chemical compositions of the top and bottom layers, novel functionally gradient bi-layer tin dioxide based sensors have been developed, which show excellent sensitivity towards methane with negligible cross-sensitivity towards volatile organic compounds. The processing steps for the fabrication of such sensors are also simple and cost-effective.
References
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