Introduction

A number of ferritic steels are commercially available in a wide range of compositions; however it seems that none of them can fulfil all requirements for SOFC (Solid Oxide Fuel Cell) applications. Crofer 22APU steel has recently been developed for SOFC applications. Studies [15] of the behaviour of Crofer 22APU at high temperatures have proved that numerous factors influence the oxidation rate. These include the composition of the atmosphere, temperature, surface treatment, and the thickness of samples. The authors of the present paper report the results concerning the behaviour of Crofer 22APU steel in air atmospheres containing SO2. The purpose of these investigations was to verify the influence of various concentrations of SO2 on the oxidation rate of both Crofer 22APU steel and pre-oxidized Crofer 22APU steel. Previous work [6] presented the results of the morphology of the scale formed on Crofer 22APU steel oxidized in an atmosphere of air contaminated with SO2. The results of these studies indicated the presence of a trace amount of sulphur on the scale surface; thus the aim of the present paper is to determine the influence of various amounts of sulphur on the oxidation rate of the steel.

Materials and Methods

Commercial ferritic steel with the Crofer 22APU trade symbol was used for the research. The chemical composition of the steel is presented in Table 1. As follows from Table 1, chromium is the dominant alloy additive. The amounts of minor alloy additives of Al and Si are present because they improved the scale adhesion [5, 7].

Table 1 Chemical composition of Crofer 22APU (wt%) [57]

Samples of size 15 × 20 × 1.5 mm were cut from sheet metal 1.5 mm thick. A hole of φ = 1 mm for hanging the sample in the furnace was drilled in the middle, 1 mm from the top edge of the sample, and then the sample surface was ground with 800 grit abrasive paper. The samples were washed in an ultrasonic rinsing device and then degreased with ethanol prior to the experiments.

The samples were exposed in an apparatus for studying the oxidation kinetics of metallic materials at a high temperature [8].

Ground and degreased samples were hung on a quartz hook in the reaction chamber. Then, the reaction zone was flushed with argon and the furnace was heated to the desired temperature. When the appropriate temperature was achieved, the mixture of air + SO2 was introduced.

The oxidation rate measurements were carried out in the mixture of air + nSO2 (where n = 0.1%, 1.0%, and 10.0%, without of catalyst) using the periodic method. The rate of gas flow amounted to 10 dm3/h. The oxidation rate measurements were carried out within the temperature range of 873–1,173 K. After the given exposure time had elapsed, the samples were cooled down in the argon atmosphere. After the furnace temperature reached less than 323 K the sample together with the frame was removed from the furnace and placed for about half an hour in a desiccator until the sample reached room temperature. Then it was weighed with an accuracy of 0.0001 g. This procedure was repeated for each exposed sample for a given period of time.

Table 2 shows the partial pressures of oxygen and sulphur in the examined atmospheres at various temperatures. The values were determined by means of the program FactSage [9].

Table 2 Partial pressure of oxygen and sulfur in used atmospheres [6, 9]

Results and Discussion

SO2 as an impurity may occur in both the anode and the cathode zone of fuel cells, but the amount of SO2 in the first zone may be infinitely small.

It is assumed that at the inlet of the fuel cell anode zone, the gas (H2) may be contaminated with H2S. However, the gas content at the outlet may differ slightly quantitatively and qualitatively owing to the presence of oxygen in the anode zone diffusing through an electrolyte and reacting with hydrogen and contaminants.

The presence of H2S in the anode zone depends on the hydrogen’s source of origin. The reaction (1) of hydrogen obtained through electrolysis or the conversion of hydrocarbons is virtually unable to be contaminated with H2S due to the substrate’s purity (all \( \Updelta G_{T}^\circ \) for T = 1,073 K and p = 101,325 Pa values in this paper were calculated using FactSage with thermodynamic databases [9]).

$$ {\text{CH}}_{4} + {\text{H}}_{2} {\text{O}} \to {\text{CO}} + 3{\text{H}}_{2} ,\quad \Updelta G_{T}^\circ = + 215.043\,{\text{kJ/mol}} $$
(1)

The above reaction takes place in the presence of a nickel catalyst.

However the presence of H2S is possible if the process of gasification of sulphur-containing carbon is the source of hydrogen. The process of carbon gasification proceeds in accordance with the following reactions:

$$ 2{\text{C}} + 3{\text{H}}_{2} {\text{O}} \to {\text{CO}} + {\text{CO}}_{2} + 3{\text{H}}_{2} + {\text{Q}},\quad \Updelta G_{T}^\circ = - 1134.0833\,{\text{kJ/mol}} $$
(2)
$$ {\text{S}}_{2} + 2{\text{H}}_{2} \to 2{\text{H}}_{2} {\text{S}},\quad \Updelta G_{T}^\circ = -74.687\,{\text{kJ/mol}} $$
(3)
$$ 2{\text{S}}_{2} + 4{\text{H}}_{2} {\text{O}} \to 2{\text{H}}_{2} {\text{S}} + 2{\text{SO}}_{2} + 6{\text{H}}_{2} ,\quad \Updelta G_{T}^\circ = + 116.704\,{\text{kJ/mol}} $$
(3a)

Reaction (3a) is not possible \( \left( {\Updelta G_{T}^\circ > 0} \right) \) from the thermodynamics point of view. The presence of H2S results from the reaction of sulphur, arising from the contamination of carbon with organic and inorganic sulphur-containing compounds, with hydrogen.

As suggested in the literature [10], H2S can react with oxygen in the anode zone of SOFC according to the fallowing reactions:

$$ {\text{H}}_{2} {\text{S}} + 3{\text{O}}_{2} \to {\text{H}}_{2} {\text{O}} + {\text{SO}}_{2} ,\quad \Updelta G_{T}^\circ = -982.6528\,{\text{kJ/mol}} $$
(4)
$$ 2{\text{H}}_{2} {\text{S}} + {\text{O}}_{2} \to 2{\text{H}}_{2} {\text{O}} + {\text{S}}_{2} ,\quad \Updelta G_{T}^\circ = -179.800\,{\text{kJ/mol}} $$
(5)
$$ 2{\text{H}}_{2} {\text{S}} \to 2{\text{H}}_{2} + {\text{S}}_{2} ,\quad \Updelta G_{T}^\circ = + 191.533\,{\text{kJ/mol}} $$
(6)
$$ {\text{S}}_{2} + 2{\text{O}}_{2} \to 2{\text{SO}}_{2} ,\quad \Updelta G_{T}^\circ = -739.2389\,{\text{kJ/mol}} $$
(7)
$$ 2{\text{H}}_{2} + {\text{O}}_{2} \to 2{\text{H}}_{2} {\text{O}},\quad \Updelta G_{T}^\circ = -371.3332\,{\text{kJ/mol}} $$
(8)

ΔG T values were determined for the pressure of 101,325 Pa at a temperature of 1,073 K. Reactions (4) and (7) are the source of SO2, but reaction (5) is the source of sulphur formation which in turn may react (7) with oxygen, yielding SO2. Reaction (6) cannot proceed towards the dissociation of the H2S; in the H2/H2S mixture the reaction equilibrium is shifted to the left. A slight amount of H2S will react with oxygen according to reaction (5) with the formation of sulphur, which, reacting with oxygen, yields sulphur dioxide, SO2. However, sulphur dioxide, SO2, is more likely to be formed according to reaction (4).

Table 3 illustrates the contents of gas mixtures introduced into the inter-connector anode zone, where, reacting with oxygen diffusing through a stable electrolyte (ZrO2), they form a mixture of a different content at the outlet. The outlet gas content was calculated assuming that 30% of O2 diffused into the anode zone through the electrolyte. The calculations were made for a temperature of 1,073 K under pressure of 101,325 Pa and 0.6 and 6.0% H2S contents in the H2 atmosphere [9].

Table 3 The contents of gas mixtures introduced into the inter-connector anode zone and mixture of a different content at the output [9]

As the results of our calculation in Table 3 (very low concentration of SO2) show, that the amount of resulting SO2 is negligibly small. Negligible amount of SO2 form owing to the fact that only a slight amount of H2S can react with oxygen, which means that H2S is the prevailing impurity within the anode area.

Thus, sulphur occurs as an impurity in the form of H2S in the anode zone, but in the form of SO2 in the cathode area. In the cathode zone the probability of SO2 presence is significantly higher as its occurrence may result from the contamination of the air with this compound [6].

As can be concluded from the calculations (Table 2), the presence of slight amounts of SO2 in the air exerts practically no impact on oxygen partial pressure. Oxygen partial pressure changes with temperature only to a small degree. Yet in the case of sulphur, the values of its partial pressure change as a function of the concentration of SO2 in the gas by approximately three orders of magnitude for each temperature taken into consideration. However, as a function of temperature the values change by as much as ten orders of magnitude [6].

Figures 1, 2, 3, and 4 illustrate the oxidation kinetics of Crofer 22APU in atmospheres of varying SO2 content. Each oxidation process can be approximately described by a parabolic rate law, which means that in all cases the scale growth diffusion controlled.

Fig. 1
figure 1

Kinetic curves of Crofer 22APU oxidized at 873 K in air + nSO2. The total error was around 10−7 g2/cm4 and the errors bars are outside the scope of scale

Fig. 2
figure 2

Kinetic curves of Crofer 22APU oxidized at 973 K in air + nSO2

Fig. 3
figure 3

Kinetic curves of Crofer 22APU oxidized at 1,073 K in air + nSO2

Fig. 4
figure 4

Kinetic curves of Crofer 22APU oxidized at 1,173 K in air + nSO2

The registered differences in samples mass increments, especially at low temperatures, are within experimental errors. At higher temperatures mass increments are so large that the measurement error does not exert such an influence on the observed differences in mass increments for various concentrations of SO2.

The linear dependence of the parabolic rate constant on temperature indicates that the mechanism of oxidation within the studied range of temperatures is the same for all of the applied SO2 concentrations (Fig. 5).

Fig. 5
figure 5

Parabolic oxidation rate constant for Crofer 22APU steel as a function of temperature in nSO2 + air atmospheres (oxidation time: 100 h)

Figure 6 illustrates the values of the parabolic rate constant for Crofer 22APU steel as a function of atmospheric content change. The oxidation rate constants at a given temperature do not show distinctive differences, which means that the SO2 content exerts practically small influence on the Crofer 22APU steel oxidation rate within the studied time range. The steel oxidation rate in the air atmosphere is practically comparable with the values obtained in atmospheres containing SO2. Analysing the mass increment of samples oxidized in atmospheres with varying contents of SO2, it may be stated that only at a temperature of 873 K a slight influence of SO2 concentration on the mass increment is observed. At higher temperatures the difference in mass gain was comparable for all of the SO2 concentrations.

Fig. 6
figure 6

Parabolic oxidation rate constant for Crofer 22APU steel as a function of atmospheric content of nSO2 + air

Mass gain connected with the formation of MnS is greater than in the case of MnO but in the presence of SO2 taking part in the oxidation of steel it is very small and therefore practically unmeasurable. The reaction processes on the surface of the scale can be written as [11]:

$$ {\text{Mn}} + {\text{SO}}_{2} \to {\text{MnS}} + 2{\text{MnO}} $$
(9)
$$ {\text{MnO}} + {\text{Cr}}_{2} {\text{O}}_{3} \to {\text{MnCr}}_{2} {\text{O}}_{4} $$
(10)

The scale formed on Crofer has a good adherence to the metallic core (Fig. 7).

Fig. 7
figure 7

SEM cross section image of Crofer 22APU oxidized at 1173 K in a air + 0.1% SO2, b air + 1% SO2, and c air + 10% SO2

The results of the oxidation rate of the pre-oxidized sample are presented below (Fig. 8). A Crofer 22APU steel sample was pre-oxidized in an air atmosphere at a temperature of 1,073 K for 100 h. A 1.5–2.5 μm thick scale formed on the sample surface [5, 6]. The pre-oxidized sample was placed in a furnace and a mixture of gases, air + SO2, was introduced. Oxidation of preoxidized samples was carried out in air + SO2 gas mixture only at 1,073 K. These results have demonstrated that the preformed scale layer hindered the rate of further sample oxidation only to a slight degree (Fig. 8). Moreover, these results confirmed that the small amount of SO2 present in the atmosphere practically did not influence the oxidation rate.

Fig. 8
figure 8

Kinetic curves of pre-oxidized Crofer 22APU steel oxidized at 1,073 K in air + nSO2

Conclusions

On the basis of the conducted studies it may be established that:

  1. (1)

    The Crofer 22APU steel oxidation rate is practically independent of the oxidizing atmosphere content (nSO2 + air).

  2. (2)

    An influence of SO2 concentration on the oxidation rate practically was not observed.

  3. (3)

    The scale formed demonstrates good adherence to the steel.

  4. (4)

    Pre-oxidization of the samples lowers the rate of steel oxidation in atmospheres containing SO2 to a slight degree.