1 Introduction

Atmospheric-pressure nonthermal plasma (NTP) offers unique chemical environment for the removal of dilute air pollutants. Electrical energy is converted into chemically reactive species in the plasma. On the other hand, extensive studies during the last two decades pointed out several limitations of the plasma alone processes for the extended practical use in industry. These include large energy consumption, low selectivity, and formation of unwanted byproducts. Combination of nonthermal plasma with heterogeneous catalyst is currently considered as a possible way to overcome these problems. Two types of combination, single-stage and two-stage, are currently being studied to improve the process performance. Single-stage process is more complex compared to two-stage process, and little knowledge is presently available on the interaction between plasma and catalyst. Nevertheless, this complementary combination has been experimentally proved to provide better selectivity for plasma and lower working temperature for catalyst [13]. For example, it has been reported that the combination of dielectric barrier discharge plasma and manganese catalyst enhances TCE decomposition and CO2 selectivity [4, 5]. The loading of active metals not only enhance CO2 selectivity for various VOCs [68], but also extend plasma area over the surface of catalyst [9]. The important role of oxygen was confirmed by varying O2 content in gas mixtures. The larger the oxygen content, the higher the decomposition efficiency of VOC and the CO2 selectivity [10, 11].

Fundamental research works are under progress for a better understanding of the interaction between plasma and catalyst. Roland et al. experimentally studied the stabilization of plasma-formed oxidants on the surface of LaCoO3 [12]. When CO/N2 mixture was fed to the plasma pretreated LaCoO3 catalyst, the profiles of outlet CO concentration exhibited different patterns according to the plasma pretreatment time. As the plasma treatment time increased, the recovery of outlet CO concentration became slower. Although the profile of CO2 was not given, the authors tentatively explained the difference of CO profile due to the oxidation induced by surface atomic oxygen fixed by the plasma. Holzer et al. also studied the interaction between nonthermal plasma and catalysts for both single-stage and two-stage configuration [13]. They also consider the role of porosity and the possible adsorption of atomic oxygen (or ozone) on the surface of the catalyst. More recently, Guaitella et al. have shown that the plasma pretreated TiO2 with O2 or air can remove C2H2 even in the absence of plasma and UV activation [14]. The adsorbed oxygen species were considered to play a key role in those experiments.

Experiments with stable isotopes and mass spectrometric analysis provide a powerful tool to study the mechanism of chemical reactions. Isotopically-labeled chemicals have been used in the gas-phase chemistry of nonthermal plasma and electron-beam irradiation. Locke et al. studied the nonthermal plasma decomposition of NOx in 15NO-N2 mixture [15]. Martin et al. studied the decomposition mechanism of toluene in a point-plane type barrier discharge using 18O2 and deuterium-labeled toluene (C6H6-CD3) [16]. Material balance of nitrogen oxides in electron-beam processing of simulated flue gas was studied using 15N labeled NO [17, 18]. Oxygen isotope (18O2) has been used in many catalytic reactions to understand the mechanism involving oxygen. Calla and Davis used 18O2 to study the CO oxidation over titania- and alumina-supported Au nanoparticles [19]. The behavior of oxygen under discharge plasma over catalyst has been investigated using 18O2 at atmospheric pressure and room temperature. Measured data of reaction products provides a direct evidence for the plasma induced fixation of oxygen on the catalyst surface and its subsequent involvement in the oxidation of VOC.

In this work, we measured the profile of isotope oxygen species in plasma-driven catalyst reactor packed with four catalysts, TiO2, Ag/TiO2, Ag/γ-Al2O3 and Ag/MS-13X. The chemical change by the plasma was evaluated based on the stoichiometric ratio between reactants and products.

2 Experimental

Figure 1 shows the experimental setup used in this study. A barrier type plasma reactor packed with catalysts was used. The effective length and inner diameter were 40 and 8 mm, respectively. The coil electrode (stainless steel with 0.45 mm diameter) was set at the inner surface of the quartz tube, which served as a corona electrode. Silver paste was painted on the outer surface as a ground electrode. Three different catalysts either in pellet or bead were tested. Gamma alumina (Mizusawa Chemical Co.) and anatase type of TiO2 (Sakai Chemicals Co.) were spherical beads with average diameter of about 1.8 and 2.0 mm, respectively. Molecular sieve-13X (MS-13X, Sigma-Aldirch Co.) was pellet with 1.6 mm diameter and 2 mm length. The MS-13X has the specific surface area of 540 m2 g−1, and followed by γ-Al2O3 (210 m2 g−1) and TiO2 (60 m2 g−1). Silver was impregnated on the surface of catalyst using AgNO3 as a precursor. The resulting catalysts were dried using a rotary evaporater, and then calcined at 500 °C in air for 10 h.

Fig. 1
figure 1

Experimental setup

The plasma-catalyst reactor was energized by an AC power supply (Trek, Model 20/20B). Frequency and applied voltage were fixed at 200 Hz and 24 kVpk–pk, respectively. Applied voltage was measured by a high voltage probe (Tektronix, P6015A) and an oscilloscope (Tektronix, TDS3034B). Discharge power was measured by using a V-Q Lissajous figure program (Insight Co. Version 1.72) [20]. The typical discharge power in the catalyst-packed plasma reactor was in the range of 2.1–2.4 W.

The gas components were measured by an on-line mass spectrometer (MKS Residual Gas Analyzer Microvision-IP) equipped with a quadrupole mass analyzer and a Faraday cup or a multiplier as detector (MKS Instruments). In the present experiments the multiplier was used preferentially as it offered higher sensitivity. The mass range was set from m/z 4 to 80 according to the gas mixtures of reactants and products. The isotope-labelled oxygen (18O2) with purity of 99.9% was supplied from Cambridge Isotope Laboratories, Inc and it was diluted with high purity He (99.999% purity, Takachiho Co.). The purity of normal oxygen (16O2) was 99.999%. For the convenience of experiment, oxygen concentration was set at 2.5% for 18O2/He or 16O2/He. The 16O18O can be formed in the ionizer of the mass spectrometer when 16O2 and 18O2 were coexisted in sample gas mixture. The intensity of 16O18O was found to be about 3–5% of the inlet oxygen molecules (16O2 + 18O2). In the experimental conditions of this study, 18O2 and 16O2 did not coexist so the formation of 16O18O in the mass spectrometer ionizer can be neglected. Benzene was supplied by bubbling liquid benzene with 10 mL min−1 He flow. The gas flow rate was regulated using mass flow controllers (KOFLOC, FCC-3000). Reaction temperature was in the range of 293–300 K at atmospheric pressure. Total gas flow rate was 0.2 L min−1 at standard conditions (273 K, 0.1 MPa). All experiments were conducted at dry conditions. Humidity was less than about 80 ppmv, as measured by a dew point hygrometer (General Eastern, Hygro-M4 Model).

Figure 2 shows the experimental scheme for the isotope exchange experiment. In the first step, 2.5% 18O2 in He was fed to the reactor and, after a few minutes, the discharge plasma was turned on. After 10 min the plasma was turned off, the gas flow was switched from 18O2/He to 16O2/He and kept for about 30 min. The benzene flow was then started and after about 3 min the plasma was turned on again. In this second step of plasma application, oxidation products of benzene, especially those containing 18O, were measured together with the isotope-exchange product, 18O16O.

Fig. 2
figure 2

Experimental procedure flow-chart

Table 1 summarizes mass number of oxygen-containing species, which could be detected in this study. In the case of nitrogen dilution, some of mass number overlaps with isotope-exchanged species. For example, C18O and N16O have the same mass number (m/z 30). To indentify the mass signals of oxygen species more correctly, helium was used in stead of N2 as dilution gas.

Table 1 Mass to charge ratios (m/z) for the isotope exchange reactions

3 Results and Discussions

Figure 3 shows the profiles of oxygen species in the plasma reactors packed with four different catalysts. The catalytic activity in VOC decomposition and the some physical-, electrical properties of these catalysts have been reported elsewhere [9, 11, 20]. The signal of normal oxygen, 16O2, was observed as an impurity in the 18O2/He flow. Since the MS signal intensity was linearly proportional to oxygen concentration up to about 3% within reasonable error limits, the impurity level of 16O2 was estimated to be about 400–500 ppm. Interestingly, some isotope-exchanged oxygen 16O18O was observed as the 18O2 feeding started even in the absence of plasma application. The intensity of 16O18O was larger than that of the impurity 16O2. This result indicates that the heterogeneous catalytic reaction is the main reason for the 16O18O signal without plasma ON. Application of plasma caused a sharp increase of the 16O18O signal, which was estimated to reach a concentration around 2000–2500 ppm. Electrical discharge is known as an effective way to achieve the gas-phase isotope exchange equilibrium [21]. It should be noted that formation of 16O18O requires the consumption of equal amounts of 16O2 and 18O2. If we assume that the impurity 16O2 is the only source of 16O and that 16O18O can only form by the gas-phase Reaction R1, then the ratio of 16O18O formation to 18O2 consumption should be no larger than two.

$$ {}^{16}{\text{O}}_{ 2} + {}^{ 1 8}{\text{O}}_{ 2} \to 2^{ 1 6} {\text{O}}^{ 1 8} {\text{O}} $$
(R1)
Fig. 3
figure 3

Evolution of reaction products from 18O2/He mixture; a TiO2 catalyst, b 4% Ag/TiO2 catalyst, c 5% Ag/γ-Al2O3 catalyst, and d 5% Ag/MS-13X catalyst. Plasma was applied for 10 min

However, the ratio of 16O18O to the initial 16O2 ranged from 3.3 to 4.6 indicating that considerable amounts of 16O were supplied by sources other than gas-phase 16O2. Catalyst surface is expected to be a probable source of 16O, because oxygen is fixed on the surface in various forms. The presence of surface oxygen radical anions (O, O2−, O2 ), metal oxide and lattice oxygen have been measured by various techniques such as ESR (electron spin resonance), temperature-programmed desorption (TPD), x-ray photoelectron spectroscopy (XPS) etc. [22, 23]. The involvement of surface oxygen can be further validated by the ratio of the 16O18O increase to the 16O2 decrease by a plasma application. These values were in the range of 2.8–7.5, indicating more 16O18O formation than the consumption of impurity 16O2 in the gas-phase. Mass spectrometric measurements of isotope oxygen species provided clear evidence that the atmospheric-pressure plasma can activate surface oxygen species fixed on catalysts. On the other hand, the signal of 18O2 slightly decreased in the presence of discharge plasma. This value went back to its initial value after the plasma was turned off. These trends are common to all tested catalysts. The contribution of silver (Ag) can be seen from the comparison between (a) TiO2 and (b) 4% Ag/TiO2. The produced amount of 16O18O was larger with 4% Ag/TiO2 than with TiO2 alone. The signal of ozone was not detected.

The gas flow was then switched from 18O2/He to 16O2/He and kept for about 30 min, and then eventually set to C6H6/16O2/He. Figure 4 shows the time-lapse changes for the intensity of relevant ion signals observed in the presence of different catalysts. It should be noticed that the outlet benzene concentration was always below the detection limits because the adsorption equilibrium requires much longer time than the measurement time-scale. The profiles of benzene decomposition products (CO and CO2) are also not in steady state. Because of the high purity of 16O2, the 18O2 signal was kept to decrease with time after switching the gas line. Nevertheless, as already indicated in Fig. 3, a constant 16O18O signal was observed even in the absence of plasma. This observation provides even more convincing evidence of the heterogeneous pathway for the 16O18O formation. When the plasma was turned on again with benzene/16O2/He flow, several reaction products containing 18O were observed. The most abundant one was 16O18O. Despite the same reaction conditions, the increase of 16O18O by the plasma was more significant than that observed with all catalysts in the absence of benzene (Fig. 3). One possible reason for this discrepancy is the isotope effect in the reaction rate. Reaction rate coefficients of isotopically-labeled oxygen (18O2) differ from normal oxygen (16O2). Two well-known examples are the ozone formation [24, 25] and isotope-exchange reaction [26, 27]. Thus, the reaction rate coefficient of k R2 is known to be 50% larger than k R3 [28, 29].

Fig. 4
figure 4

Evolution of reaction products from 16O2/He mixture containing benzene; a TiO2 catalyst, b 4% Ag/TiO2 catalyst, c 5% Ag/γ-Al2O3 catalyst, and d 5% Ag/MS-13X catalyst. Catalysts were pretreated in 18O2/He mixture for 10 min (see Fig. 3)

$$ {}^{16}{\text{O}} + {}^{16}{\text{O}}_{ 2} + {\text{M}} \to^{ 1 6} {\text{O}}_{ 3} + {\text{M}} $$
(R2)
$$ {}^{18}{\text{O}} + {}^{16}{\text{O}}_{ 2} + {\text{M}} \to^{ 1 8} {\text{O}}^{ 1 6} {\text{O}}_{ 2} + {\text{M}} $$
(R3)
$$ {}^{16}{\text{O}} + {}^{18}{\text{O}}_{ 2} \to^{ 1 6} {\text{O}}^{ 1 8} {\text{O}} + {}^{18}{\text{O}} $$
(R4)
$$ {}^{18}{\text{O}} + {}^{16}{\text{O}}_{ 2} \to^{ 1 8} {\text{O}}^{ 1 6} {\text{O}} + {}^{16}{\text{O}} $$
(R5)

Similarly, the reaction rate coefficient k R5 is 1.25 times larger than k R4. If we assume that surface 18Os reacts more easily than surface 16Os, then the observed data can be well explained. It is interesting to note that the 18O containing products decreased with time in the case of TiO2, whereas the C16O2 kept increasing. On the other hand, Ag loaded catalysts exhibited constant levels of 18O containing products. These observations suggest that the Ag nanoparticles play an important role as oxygen (18O2 in this case) reservoirs. It has been well-known that active metals are capable of adsorbing oxygen on their surface. Oxygen adsorption on silver has also been the object of intensive study because of its peculiar activity toward ethylene partial oxidation to ethylene oxide [30, 31]. For example, Busser et al. studied the temperature-programmed desorption (TPD) of O2 from Ag/Al2O3 catalyst in a microreactor [32]. Bukhtiyarov et al. reported that the size of silver particles substantially changed the oxygen adsorption pattern [31, 33]. Recently, enhanced interaction of plasma with silver nanoparticle loaded zeolites has been demonstrated by the microscope-ICCD camera measurement [9]. Regardless of the type of surface oxygen species, it is evident that the 18O was supplied from the surface of catalysts, which was fixed by discharge plasma in 18O2/He flow. The most prominent decomposition product of benzene was C16O2 and followed by C16O18O and C18O2. This order was the same for all tested catalysts in this study. In the case of benzene/16O2/He mixture, the signal changes of 16O2 were less significant compared to those of 18O2/He mixture. Although the detailed reason for this is not clear at this stage, unknown behavior of oxygen isotope could be a reason. Weston pointed out that significant kinetic isotope effects are found in the electron impact dissociation of molecular oxygen, R6 [34].

$$ {\text{O}}_{ 2} + {\text{e}} \to {\text{O}}\left( {^{ 1} {\text{D}}} \right) + {\text{O}}\left( {^{ 3} {\text{P}}} \right) + {\text{e}} $$
(R6)

Thus, the reaction rates for the electron impact dissociation of 17O16O and 18O16O are two times faster than that of 16O2. Within our literature survey, there is no previous report on the reaction rate of R6 for 18O2. If 18O2 dissociates more easily than 16O2, similarly to 17O16O and 18O16O, then the different profile of oxygen (18O2 and 16O2) in 18O2/He and 16O2/He can be rationalized. In conclusion, although, the nature of the kinetically active oxygen species in these systems is still uncertain, it was found that nonthermal plasma can induce fixation of oxygen on the surface of catalyst and chemical reaction as well. Remaining open questions are what are the surface oxygen species fixed by a discharge plasma and how do they interact with discharge plasma which leads to catalytic reaction on the surface. These will be further investigated in future studies.

4 Summary

The role of oxygen in plasma-driven catalysis has been investigated using isotopically-labeled molecular oxygen (18O2). It was found that oxygen is fixed onto the surface of the catalyst by the action of atmospheric-pressure nonthermal discharge plasma, and can survive in such a state for about 30 min. In turn, the adsorbed 18O-labeled oxygen species are easily activated by discharge plasma, and react with 16O2 and benzene to produce 18O16O and 18O-containing CO x , respectively. The Ag nanoparticles supported on catalysts served as oxygen reservoirs.

5 Acknowledgment

This research was partly supported by the Environmental Research and Technology Development Fund (S2-01) of the Ministry of the Environment, Japan.