A New Approach to Determine Gas Diffusion Coefficients in Porous Solids by EIS: Application for NH<sub>3</sub> and CO<sub>2</sub> Adsorption on Zirconia and Zeolite Type 5A

Nguyen, Tien-Quang; Glorius, Maja; Breitkopf, Cornelia

doi:https://doi.org/10.1155/2018/5462659

Advances in Mathematical Physics

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Abstract Introduction Experimental Results and Discussion Conclusion Data Availability Conflicts of Interest Acknowledgments References Copyright Related Articles

Research Article | Open Access

Volume 2018 | Article ID 5462659 | https://doi.org/10.1155/2018/5462659

A New Approach to Determine Gas Diffusion Coefficients in Porous Solids by EIS: Application for NH₃ and CO₂ Adsorption on Zirconia and Zeolite Type 5A

Tien-Quang Nguyen,¹Maja Glorius,¹and Cornelia Breitkopf¹

Academic Editor: Ivan Giorgio

Received06 Jul 2018

Revised12 Sept 2018

Accepted18 Sept 2018

Published04 Oct 2018

Abstract

A new theoretical approach has been established to define transport coefficients of charge and mass transport in porous materials directly from impedance data; thus four transport coefficients could be determined. In case of ammonia adsorption on sulfated zirconia, the diffusion coefficient was figured out to be approximately the mobility diffusion coefficient of ammonium ions: 1.2 x 10^-7cm²/s. The transport of carbon dioxide was examined for samples of zeolite type 5A in different hydration states. By impedance spectroscopy measurements, the diffusion coefficient of water vapor at 373 K is estimated to be about 7 x 10^-6cm²/s. The influence of carbon dioxide adsorption on diffusion coefficients is studied based on two pellet types of zeolite 5A. The difference between polar and non-polar gas adsorption in porous solids is considered as changed characteristic of impedance.

1. Introduction

Gas transport in porous material plays a significant role in industrial applications, especially in electrocatalysis, batteries, and gas sensor research. Zeolites and zirconias are ionic conducting materials used as gas sensor [1–6] at high temperatures and are proton conducting at low temperatures [7]. Diffusion of gases in these catalysts has been published, i.e., in zeolite [5, 6, 8, 9] and in sulfated zirconia [1, 3, 10, 11]. However, it has not been measured by EIS so far.

Electrochemical impedance spectroscopy (EIS) has proven to be a powerful tool to investigate mass and charge transfer processes [3, 6, 12, 13]. The gas phase adsorption on porous solid has been studied by impedance spectroscopy of pure gases regarding the change of capacitance [14], electrical conductivity [5, 6, 10], and impedance at low frequencies depending on gas concentration [4]. In the meantime, many models of gas phase diffusion have been built by using EIS for fuel cells such as the stagnant gas layer above electrodes [1, 3], gas diffusion electrodes [15], and mass transport contribution in diffusion limitation [12].

Ammonia is a well-known probe gas to investigate acid property of porous catalysts thanks to the high selectivity of small molecules. Accordingly, various types of ammonia sensor have been developed from sensing materials like proton conductor, semiconductor, and polymers. Recently, Satsuma and coworkers [10] have reported a good response of ammonia sensing on thick film tungstated-zirconia. They indicated from results of impedance spectroscopy method that ammonia plays a significant role in increasing the conductivity of tungstated-zirconia. Previously, this had been pointed out in case of NH₃ adsorption on zeolites [5, 6]. They suggested the sensing mechanism of proton diffusion by hopping in zeolites, which was then modified by Satsuma [10] that surface adsorbed species such as ammonia play a part in the solvation-supported proton transport. However, there has not been any evaluation of ammonia diffusion in sensing porous materials despite its important effect on the performance of sensors. Therefore, ammonia diffusivity is very worth concerning as diffusion process takes place slowly in porous materials. Transport coefficients of ammonia in different porous media have been reported in numerous experimental methods, i.e., the isothermal transient ionic current method [16], NMR [17, 18], and vacuum-TPD [13, 19]. So far, it has not been measured by EIS method.

Carbon dioxide through zeolite type A is an interesting issue due to their selective cation exchangers in numerous applications, such as air separation and gas separation of CO₂ from waste gas emissions [2, 20, 21]. Investigation of this diffusion phenomenon seems to be restricted regarding the number of experimental methods. The diffusion coefficient of CO₂ on zeolite 5A has been measured by NMR [8], frequency response [22], gas chromatography [23], and gravimetric method [9].

In principle, the transport diffusion for mass in impedance spectroscopy method is described by Fick’s law which lays the foundation for the Warburg impedance [24]. In addition, the diffusion coefficient of mobile charge is also defined by impedance spectroscopy based on the Nernst-Einstein relation [25]. In comparison with other experimental methods, with respect to the diffusivity of proton/water in FAU-type zeolite [26], the diffusivities are measured by quasi-elastic-neutron (QENS) based on the concentration of water molecules in zeolite. Meanwhile, the diffusivities of CO₂ in zeolite (including LTA) were found to follow Arrhenius law [27].

In this study, transport coefficients of gas phases in porous pellets are obtained by means of impedance spectroscopy. These parameters are calculated directly from experimental data based on available models in literature and new proposed approaches in case of gas phase effect. Diffusion coefficients are determined by separate calculations of net ionic mobility and gas phases. IR spectroscopy data are combined in analyses with respect to mechanism and position of gases on the surface of porous catalysts.

2. Experimental

2.1. Material

Sulfated zirconia (SZ) based on zirconium hydroxide XZO 1720 with 10 wt.-% SO₃ from MEL Chemicals is used to study the transport of ammonia. Zeolite type 5A provided by Chemiewerk Bad Köstritz GmbH (Germany) as molecular sieve Köstrolith® 5AK/ABFK is applied for carbon dioxide adsorption and transport. Powder is sieved with grain diameters smaller than 0.1 μm before they are utilized for the experiments.

2.2. Preparation and Pretreatment Sample

2.2.1. Sulfated Zirconia Pellets

The MEL precursor was calcined at 873 K for 3 h in air flow of 0.03 NL/min. After being cooled to room temperature, about 150 mg of the dried powder was pressed (3 Ton) into a pellet with a diameter of 13 mm. The pellet was then contacted with silver paste (by Sigma Aldrich) on both faces. After that, the sample was placed into the EIS-chamber and heated at 383 K for 2 h in ambient atmosphere before the measurement. The thickness of the sample is 0.8 mm.

2.2.2. Zeolite 5A Pellets

Zeolite type 5A was pressed (4 Ton) into a pellet with a diameter of 13 mm. Two types of pellets with different thicknesses (0.65 mm and 0.35 mm) have been prepared. The pellets were contacted with silver paste (by Sigma Aldrich) on both faces and the silver layer had been dried at room temperature before the next thermal treatment was carried out.

For the first sample with thickness 0.65 mm (Z5A-1), they were heated at 573 K for 2 h in air flow of 0.03 NL/min and cooled to room temperature before being located into the cell chamber. The second sample (Z5A-2) was directly put into the closed chamber and heated at 473 K for 30 min. Then it was reduced to 373 K and held at this temperature until the first measurement in the closed chamber.

2.3. Impedance Measurement

The measurements by EIS were carried out before and after gas loading (i.e., NH₃ through sulfated zirconia and CO₂ through zeolite 5A) at the same temperature. In principle, the sample was maintained at the desired temperature for at least 30 min before the first measurement. The sample is kept between two copper surfaces which are connected to Autolab PGSTAT302N (EcoChemie, Netherlands). Electrochemical impedance measurements were conducted by two electrodes without reference electrode in a frequency range from 0.01 Hz to 100 kHz. The silver paste is used to improve electrode/electrolyte contact. The influence of the silver paste layer can be ignored at low temperatures. Electrical linearity of the sample response has been examined in a voltage amplitude range of 10-250 mV. In order to obtain the best current resolution, a measuring voltage of 250 mV is chosen so that the responses are found to be linear, which obeys Ohm’s law. The impedance data are analyzed by fitting with equivalents circuit by NOVA integrated into Autolab PGSTAT 302N.

3. New Theoretical Approach to Evaluate Transport Parameters

3.1. Diffusion Coefficients of Mobile Species

A model of ionic concentration polarization between two blocking electrodes is applied for the macroscopic space-charge polarization by Coelho [28]. The equivalent circuit of this model includes RC parallel for electrolyte series doulbe-layer capaciatance and for interface of electrode/electrolyte. In non-Debye relaxation, capacitance elements will be replaced by constant phase element (CPE). From the analysis of the effective complex permittivity, Bandara and Mellander [25] suggested the diffusion coefficient of ionic mobile species as the following: where τ₂ is the characteristic time constant which corresponds to the peak point on the loss tangent (Figures 1(a) and 1(b)). Parameters at the peak are given as at

(a)

(b)

The Debye length is calculated as the ratio of a sample thickness, d with the dimension-less, δ:This model assumes that the dimensionless δ >>1. According to Coelho [28], the good approximation is typically applied for δ ≥ 10.

3.2. Chemical Diffusion Coefficient

This value originates from the fitting of a finite-length Warburg element with impedance data at low frequencies. with j being imaginary unit

In this paper, the Warburg impedance is separated into the real and imaginary part. Diffusion parameters, i.e., and , are obtained by fitting imaginary data with the imaginary part of the Warburg element. The results will refer to the fitting outcome of programs such as NOVA, Zview from corresponding equivalent circuits. In fact, the fitting value by an equivalent circuit is likely to have a significant deviation in the appearance of Warburg element due to the number of noisy points by mass transport at low frequencies. Then, the chemical diffusion coefficient is defined as an equation, if the diffusion length is known. Under the condition of incomplete diffusion limitation, this diffusion coefficient has a significant contribution from mass transport [12]. By that means, the diffusion length is bigger than the Debye length, which is computed based on the assumption of the electron lifetime [29] and equals the summit frequency.

3.3. Effective Diffusion Coefficient

The effective diffusion coefficient is estimated by (7) via the stagnant gas layer model [3], where is the diffusion time constant and is the thickness of the stagnant gas layer.

In electrochemical systems, the diffusion coefficient of the bulk gas in a stagnant gas layer above the electrode surface relates to the effective diffusion coefficient which is described by the finite-length Warburg component [1, 3, 12]. Most electrochemical systems have this diffusivity which is caused by the mass exchange between a species source or the sink location and surface electrodes [1]. The stagnant gas layer is calculated based on the summit frequency, , that is the maximum frequency of a pseudo-RC parallel circuit. This circuit replaces the finite-length Warburg element because of increasing capacitance of the double-layer by gas phase diffusion and the binary diffusion coefficient. It is computed as (8) [3]:In (8), the binary diffusion coefficient D₁₂ is determined by the Chapman-Enskog model:where T is absolute temperature in Kelvin, p is pressure in Pascal, M is molar weight of the gases, and σ₁₂ and are parameters of gases calculation from Lennard-Jones potentials.

3.4. Diffusion Coefficient by Jumping between Two Neighboring Sites

In some cases of solid materials such as zeolites, the capacitance of the pellet reaches high values at low temperatures. As a result, the loss tangent at the peak is small due to the high value of . In these cases, the dimensionless δ is smaller than 10 and the Bandara-Mellander model cannot be employed. The average distance jump of mobility by the hopping model will replace the Debye-length in (1). Hence, the diffusion coefficient by jumping is explained by where τ₂ is the time constant at the peak on the loss tangent. The characteristic time constant is minimal (10⁻³ - 10⁻⁵ s). At that time, the average distance jump can be followed by the model of Rolling et al. [30] and Dygas [31].

The square of the average distance jump is defined bywhere , , , and are onset frequency, relaxation frequency, permittivity of vacuum, and dc conductivity, respectively. The parameter Γ is interpreted as an average length or element jump distance of relative charge shift, caused by local rearrangements of hopping carriers [31]. The dimensionless P or the Barton-Nakajima-Namikawa relation provides valuable information about unit jump length and units of average time between jumps of a hopping carrier [31].

4. Results and Discussion

4.1. Ammonia on Sulfated Zirconia

4.1.1. Influence of Ammonia Adsorption on Impedance

Figure 2 shows the Nyquist plots for sulfated zirconia samples before and after ammonia is loaded. It includes a semicircle at high frequencies and a tail at low frequencies. The semicircle is characterized by the grain and grain boundary geometry. The profiles of impedance spectra indicate that the characterization of the grain or grain boundary can be interpreted in terms of a RC parallel equivalent circuit. In solid electrochemistry, the surface roughness is one of the factors which has a significant contribution to frequency dispersion. Such behavior is generally analyzed by replacing a capacitor by a constant phase element (CPE) [32]. At low frequencies, the appearance of a tail is attributed to gas phase diffusion in diffusion limitation condition. From EIS point of views, the low-frequency dispersion is interpreted in terms of the Warburg impedance by a diffusion process [33]. On the contrary, owing to the contribution of bulk gas diffusion, the double-layer capacitance increases. As a consequence, the spectra at low frequencies will form a semicircle fitted by R-CPE parallel, which is proposed by the studies in [3, 12]. The equivalent circuit and fitted curves are illustrated in Figure 3.

The semicircle decreases significantly after ammonia adsorption (Figure 2), which implies that the electrical conductivity of the sample increases. The ionic conductivity is described by the number of ions present and their respective mobility was ascribed for adsorbed -ions [5, 6, 10]. Fundamentally, ammonia molecules act on Brønsted acid sites at the surface of sulfated zirconia via H-bonding. Protons from OH-groups will transfer to ammonia molecules to generate ammonium ions. During that time, ammonia acts as a solvation-supported proton transport, which is similar to the Grotthuss mechanism. The dependence of proton diffusion on the temperature resembles the description in [34]. Therefore, the electrical conductivity σ depends on the mobility of migrating species μ and the concentration of ions, as follows:where F and z are the Faraday constant and the number of charged species, respectively.

4.1.2. Diffusion Coefficients

The diffusion coefficient of mobile ions is calculated by the peak point on the loss tangent plot at low frequencies (see Figure 4 and Section 3.1). Meanwhile, the diffusion coefficient of ammonia is extracted from the finite-length Warburg (see (4)). In order to estimate the summit frequency, the equivalent circuit is extended to the broad frequency range from 0.001 Hz to 100 kHz. A summary of diffusion parameters of ammonia adsorption on sulfated zirconia is illustrated in Table 1.

The diffusion coefficient of mobility increases slightly in the measurement. It shows that the conductivity of the sample grows with the time. By that means, it is suggested that the adsorption of ammonia is still occurring at other OH-groups on the surface of sulfated zirconia. Similarly, the chemical diffusion coefficient which is assumed by fitting data with the finite-length Warburg element also rises after 20 min of adsorption. In fact, the chemical diffusion coefficient has contributed to the bulk gas and charged species concentration [12]. However, the average value of mobility and chemical diffusion coefficients are determined to be about 1.2 x 10^-7cm²/s. Therefore, it is recommended that most of ammonia gas promotes the formation of ammonium ions on the surface of sulfated zirconia. As a result, the diffusion coefficient of ammonia in sulfated zirconia equals the chemical diffusion coefficient, = (0.9 -1.5) x 10^-7cm²/s.

About the diffusion mechanism of mobile species, this phenomenon can be interpreted by proton hopping mechanism suggested by Franke and Simon [5, 6]. Accordingly, the presence of adsorbed ammonia acts as solvation-supported proton transfer via the Grotthuss mechanism at low temperatures. In particular, the adsorption of ammonia on sulfated zirconia was observed with - ions on surface acidic OH groups, i.e., the Brønsted acid sites. In fact, the water has not been fully eliminated at measurement conditions at low temperatures. However, in the presence of ammonia, the electrostatic attraction between free water and negative charged lattices of OH-groups decreases significantly, which produces a new ammonium ion. This excess proton can be delivered to a new unoccupied site or another NH₃ molecule [5]. Consequently, the mobility of ionic charges increases, resulting in an enhanced conductivity which is mainly proportional to the concentration of -ions. The diffusion coefficient of mobile charged species is primarily given by -ions motion.

In literature, similar data are reported for ammonium ion diffusion in a cylindrical pellet of (NH₄)₄Fe(CN)₆·1.5H₂O by Gawad and Bhat [16] using the isothermal transient ionic current method, D = 3.87 x 10^-7cm²/s. Their discovered value lies in the same range as for the investigated sulfated zirconia in this research, because the identical phenomenon of diffusion in a cylindrical pellet and the experimental method is also applied by electrochemical system. Moreover, the diffusion coefficient of ammonia in Table 1 can be compatible with the self-diffusion coefficient of ammonia in some porous solids: in silica from 300 to 500 K by QENS (2.5 x 10⁻⁶ to 2.0 x 10^-5cm²/s) and by PFG NMR (3 x10⁻⁷ to 1.5 x10^-6cm²/s) [18]; in H-ZSM5 in range from 1 x10⁻⁷ to 2 x10^-5cm²/s [17]. Its value depends on the concentration of ammonia on the surface and ignores the hopping diffusion of proton transport in NH₃ phase via in the channel.

The effective diffusion coefficient of mixed gases above electrodes illustrated in Table 2 was previously calculated by (7)-(9). The experimental system is assumed to contain three gas phases: ammonia, water, and helium at 2 bar pressure and 383 K. In this case, the lowest binary gas mixture is used to determine the stagnant gas layer as (8). Accordingly, the binary diffusion coefficient of NH₃/H₂O is defined as the lowest, and its value is based on the Lennard-Jones characteristic lengths in [35]. It can be seen that the effective diffusion coefficient during measurement is nearly constant. Their values are higher than the lowest binary diffusion coefficient nevertheless, which may be caused by Knudsen diffusion in pores [1]. Particularly, the increase of the stagnant gas layer can be explained by the decrease of ammonia concentration according to Nakajima [12]. In other words, ammonia gas above electrodes will continue to be adsorbed on the surface of sulfated zirconia.

4.2. Carbon Dioxide in Zeolite 5A

In order to obtain transport coefficients of carbon dioxide by means of EIS method, two different samples (Z5A-1 and Z5A-2) which correspond to high- and low-temperature treatment are investigated with adsorbed CO₂ gas.

4.2.1. Effect of on Impedance at 433 K in Sample Z5A-1

Figure 5(a) displays the comparison of the impedance spectrum for zeolite Z5A-1 before and after carbon dioxide adsorption. It can be realized that the impedance of the sample decreases substantially after carbon dioxide is adsorbed. However, the impedance spectrum after carbon dioxide adsorption has been formed as similarly as in the absence of carbon dioxide. In specific, the impedance spectra of both cases consist of two semicircles which are attributed to the grain and grain boundary at high and low frequencies. The equivalent circuit includes two series of R-CPE parallel.

(a)

(b)

On the other hand, the relaxation distribution of ions on broad frequency ranges is more useful to display results as the modulus loss (Figure 5(b)). It is extracted from the impedance by the expression

Only one peak appears at medium frequencies before carbon dioxide is loaded, which suggests only single species relaxation. This maximum corresponds to the dipolar relaxation of Ca²⁺- ion in α-cage since the activation energy of relaxation for this sample below 573 K is estimated to be about 86 kJ/mol (data from activation energy measurement of a similar sample). Besides, the simulated result by Demontis [36] showed that the activation energy ranging from 51 to 97 kJ/mol was not likely to enable cations Ca²⁺ and Na⁺ jumping diffusion in zeolite 5A. Thus, the ion conduction can be assumed by protons. Actually, the proton presence on the surface of zeolite 5A can be observed by IR spectroscopy by two bridging OH-groups on super-cages (band at 3650 cm⁻¹) and sodalite-cages (band at 3512 cm⁻¹); see Figure 6. This result is in agreement with [20]. Moreover, a strong band at 3567 cm⁻¹ is attributed to nonacid [Ca(OH)]⁺ in the measurement temperature; this band is at 3555 cm⁻¹ in [20]. The strong band appearance of Ca(OH)⁺ in zeolite 5A can be interpreted by the hydroxylation of Ca²⁺ cations with even very small tracers of water [8]:This reaction takes place leading to the replacement of one divalent cation by two monovalent cations. In this case, proton motion is likely to happen between two neighboring cations.

After CO₂ adsorption, the impedance spectrum reduces significantly at low frequencies, which corresponds to an increasing conductivity; see Figure 7(a). The relaxation peak on the modulus shifts towards higher frequencies, which implies that the conductivity relaxation mode of proton rises after CO₂ is loaded. Theoretically, the adsorption of carbon dioxide on zeolite can be modeled by the change of electric capacitance or electrical conductivity [4, 14, 37]. The growth of electrical capacitance as well as the dielectric constant after carbon dioxide had been adsorbed in a zeolite sample was supported by the theory of Kurzweil et al. [37] and Staudt et al. [14]. Accordingly, the raising capacitance of the capacitor causes an increase in the dielectric constant; see Figure 7(b).

(a)

(b)

The diffusion coefficients were first estimated via the Bandara-Mellander model based on the peak on the loss tangent plot (Figure 8). Regarding Table 3, the dimensionless δ is smaller than 10; hence the Bandara-Mellander model will not be employed in this case. The proton diffusion coefficient is calculated as in Section 3.3 in which the Debye length is replaced by the average length distance, Γ, as (11). Diffusion parameters of protons in Z5A-1 under the influence of carbon dioxide are defined in Table 4.

The proton diffusion coefficient increases slightly after carbon dioxide adsorption. From the viewpoint of the mechanism of CO₂ adsorption on zeolite 5A, it is assumed that this growth originates from the perturbation of carbon dioxide molecules to residual [Ca(OH)]⁺ groups and cations Ca⁺⁺ and Na⁺ in order to generate OCO-Ca²⁺ and OCO-Na⁺ ions. Furthermore, a minority of CO₂ adsorption on zeolite 5A is chemisorbed to form carbonate species because carbon dioxide does not interact with nonacidic OH groups on Ca(OH)⁺ [20]. The interaction between carbon dioxide and acidic OH-groups only happens on zeolite protonic centers, i.e., Si-OH-Al bridging OH groups. Thus, the bonding of protons on oxygen atom becomes weak and the interaction of protons with neighboring sites rises more strongly than that. The minor growth of proton mobility diffusion coefficient reflects the perturbation but does not belong to the diffusion coefficient of carbon dioxide gas phase.

Theoretically, the proton mobility diffusion coefficients from OH groups are given from 10⁻¹³ to 10^-11cm²/s in the temperature range 373 to 473 K in HNaY [38]. Similarly, Fripiat et al. [39] figured out the diffusion coefficients of proton jump in faujasite zeolite (X, Y) in temperature between 373 and 673 K about 3.4 x 10⁻¹⁴ to 3.1 x 10^-9cm²/s with the jump distance of 4.4 Å. Therefore, the calculated value by EIS is appropriate to the proton diffusion coefficient.

4.2.2. Effect of Diffusing in Sample Z5A-2

Figures 9(a) and 9(b) show impedance spectra and the fitted data curves of sample Z5A-2 before and after CO₂ loading. In both cases, the impedance can be analyzed with three semicircles. They are attributed to the grain at high frequencies, grain boundaries at intermediate frequencies, and interface at low frequencies (usually less than 10 Hz). The equivalent circuit model is fitted by an equivalent circuit with three series of R-CPE parallel (see Figure 9(b)). After CO₂ is loaded, the impedance increases primarily in the second and third arc at intermediate and low frequencies owing to the gas effect at low frequencies [4]. The impedance growth is caused by the reduction of the electrical conductivity. Therefore, there is no difference of impedance compositions for the sample with/without CO₂.

(a)

(b)

The electrical conductivity in the sample depends on the concentration of hydroxonium ions on the surface; see (12). In fact, the sample is heated in the closed chamber at low temperatures; the free water inside is desorbed to generate the water vapor pressure in the chamber. It is assumed that the mobility of this sample is caused by the hydroxonium ion H₃O⁺ of hydrogen-bonding H₂O···OH. Additionally, the hydroxonium concentration also arises from hydroxylation process of Ca²⁺ cations with moderate water as (14). At 373 K, water molecules play a role in supporting proton motion between zeolite lattices via the Grotthuss mechanism [34]. After carbon dioxide is loaded, the concentration of H₃O⁺ ions drops immediately because of the weak bonding between H₂O⋯OH. Therefore, the relaxation peak on the modulus and the loss tangent graphs is shifted backward lower frequency after CO₂ loading (Figures 10(a) and 10(b)).

(a)

(b)

Regarding diffusion process occurring at low frequencies, the impedance can be fitted by finite-length Warburg element as (4). However, due to the influence of gas phase diffusion (i.e., water vapor or CO₂), the impedance spectra have the shape of a semicircle which is represented by a parallel R-CPE. Before CO₂ adsorption, this semicircle is attributed to the water vapor diffusion in high voltage condition. The characterization is still right in case CO₂ is loaded. The presence of CO₂ does not give identification for its diffusivity; carbon dioxide in this case just impacts the diffusivity of water vapor and ionic mobility.

Two diffusion coefficients (, ) exhibited in Table 5 are diffusion coefficient of ionic mobility H₃O⁺ ions and the self-diffusion coefficient of water vapor in zeolite, respectively. Both decrease slightly after CO₂ loading. In comparison, diffusion coefficient of proton mobility was reported in range of (2.5 – 5.0) x10^-6cm²/s at 373 K in hydrated zeolite NaY [40] and 7 x10^-5cm²/s at room temperature in Nafion/ZrO₂- [41]. Meanwhile, the diffusion coefficient of water vapor was also given as 4.7 x10^-5cm²/s at 363 K [41]. Although the estimated values differ slightly compared with results in literature due to some conditions, they are in the same order of magnitude. The mechanism of hydroxonium ions transfer can be assumed via the Grotthuss mechanism and/or vehicle mechanism [34] under the effect of temperatures and the electric force. Water molecules play a part in promoting and supporting hydroxonium ions transfer between two sites. After carbon dioxide is introduced into the closed chamber, the gradient of the bulk gas influences the removal of a few water molecules on the chain, which encourages hydroxonium ions transfer between two sites. It can interact with weak hydrogen bonded H₃O⁺-ion on the surface to generate water molecules. Consequently, three diffusion coefficients in Tables 5 and 6 become a little bit smaller after carbon dioxide flows into the chamber. In comparison with sample Z5A-1, the diffusion coefficient of proton increases after the presence of CO₂. The difference is caused by the strong bond of proton on acid sites; carbon dioxide only helps to enhance the relaxation but cannot remove protons out of the surface.

5. Conclusion

The new proposed approach was effectively applied to compute transport coefficients of gas adsorption in porous solids derived from EIS data. Four transport coefficients can be defined by this method. In case of ammonia adsorption, the mobility diffusion coefficient depends on the concentration of ammonium ions at the interface, which results in an increase of the electrical conductivity. The diffusion coefficient of ammonia in sulfated zirconia is estimated to be approximately the mobility diffusion coefficient of ammonium ions. In the event of carbon dioxide adsorption, proton and hydroxonium ions in two types of samples are charged carriers. The diffusion coefficient of carbon dioxide cannot be directly calculated from the impedance data. It can be only evaluated by its effect on diffusion coefficient of proton mobility, the self-diffusion coefficient of water vapor in the zeolite pellet, and the effective diffusion coefficient above electrodes.

Data Availability

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

Conflicts of Interest

The authors declare that they have no conflicts of interest.

Acknowledgments

The authors thankfully acknowledge the financial support provided by DAAD (A/10/75442), Graduate Academy-Technical University of Dresden, and The Ministry of Education and Training (MoET), Vietnam.

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Copyright © 2018 Tien-Quang Nguyen et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

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Advances in Mathematical Physics

A New Approach to Determine Gas Diffusion Coefficients in Porous Solids by EIS: Application for NH3 and CO2 Adsorption on Zirconia and Zeolite Type 5A

Abstract

1. Introduction

2. Experimental

2.1. Material

2.2. Preparation and Pretreatment Sample

2.2.1. Sulfated Zirconia Pellets

2.2.2. Zeolite 5A Pellets

2.3. Impedance Measurement

3. New Theoretical Approach to Evaluate Transport Parameters

3.1. Diffusion Coefficients of Mobile Species

3.2. Chemical Diffusion Coefficient

3.3. Effective Diffusion Coefficient

3.4. Diffusion Coefficient by Jumping between Two Neighboring Sites

4. Results and Discussion

4.1. Ammonia on Sulfated Zirconia

4.1.1. Influence of Ammonia Adsorption on Impedance

4.1.2. Diffusion Coefficients

4.2. Carbon Dioxide in Zeolite 5A

4.2.1. Effect of on Impedance at 433 K in Sample Z5A-1

4.2.2. Effect of Diffusing in Sample Z5A-2

5. Conclusion

Data Availability

Conflicts of Interest

Acknowledgments

References

Copyright

A New Approach to Determine Gas Diffusion Coefficients in Porous Solids by EIS: Application for NH₃ and CO₂ Adsorption on Zirconia and Zeolite Type 5A