Pulsed corona discharge induced hydroxyl radical transfer through the gas-liquid interface

ABSTRACT The highly energetic electrons in non-thermal plasma generated by gas phase pulsed corona discharge (PCD) produce hydroxyl (OH) radicals via collision reactions with water

molecules. Previous work has established that OH radicals are formed at the plasma-liquid interface, making it an important location for the oxidation of aqueous pollutants. Here, by

contacting water as aerosol with PCD plasma, it is shown that OH radicals are produced on the gas side of the interface, and not in the liquid phase. It is also demonstrated that the

gas-liquid interfacial boundary poses a barrier for the OH radicals, one they need to cross for reactive affinity with dissolved components, and that this process requires a gaseous atomic H

scavenger. For gaseous oxidation, a scavenger, oxygen in common cases, is an advantage but not a requirement. OH radical efficiency in liquid phase reactions is strongly temperature

dependent as radical termination reaction rates increase with temperature. SIMILAR CONTENT BEING VIEWED BY OTHERS RESONANT DUAL-PULSE LASER IGNITION TECHNIQUE BASED ON OXYGEN REMPI

PRE-IONIZATION Article Open access 16 November 2020 A WATER COOLED, HIGH POWER, DIELECTRIC BARRIER DISCHARGE REACTOR FOR CO2 PLASMA DISSOCIATION AND VALORIZATION STUDIES Article Open access

06 May 2023 OBSERVATION AND RATIONALIZATION OF NITROGEN OXIDATION ENABLED ONLY BY COUPLED PLASMA AND CATALYST Article Open access 20 January 2022 INTRODUCTION Atmospheric pressure

non-thermal plasma technologies have been an on-going focus of research in water treatment over the last two decades. The most common laboratory-scale studies have included investigation of

dielectric barrier discharge (DBD) and pulsed corona discharge (PCD), the latter forming the subject of discussion in this paper. Plasma treatment of water is chemically similar with

traditional ozonation, as several oxidants are formed in plasma reactions from oxygen and water, including ozone O3, hydroxyl radical OH, hydrogen peroxide H2O2, atomic oxygen O(3P) and

singlet oxygen O2(1Δg). Of these, O3 and OH are specially recognized as the major oxidants in plasma water treatment1,2,3,4,5. The latter is largely produced via inelastic electron

collisions with water as in Eq. (1)3: $${{\rm{H}}}_{2}{\rm{O}}+{e}^{-}\to {\rm{OH}}+{\rm{H}}+{e}^{-}$$ (1) For water treatment purposes, the gas-liquid interface where the OH radicals are

formed is a crucial environment and the plasma-liquid contact surface area thus makes an important variable4,5,6. In earlier work, a vertical PCD reactor in which the treated solution is

allowed to shower through a perforated plate positioned above the plasma zone was employed to generate a large plasma-liquid contact surface area6. Increasing this contact surface improves

the oxidation energy efficiency mainly due to the enhanced action of superficial OH radicals4,6. Although OH radical activity at the plasma-liquid interface is evident, it is extinguished in

complete absence of O2 4. So far this property, however, seems only observed with the present configuration; several other types of non-thermal plasmas applied in oxidation of aqueous

organic compounds seem to have effect also in the absence of molecular O2 7,8,9,10,11, suggesting that these processes include various mechanisms. The occurrence of such reports is

understandably limited as in most water treatment studies the gas phase contains air for practical reasons, and thus O2 at least as a partial constituent. Oxidation for example under Ar has

shown similar efficiency with air11, but papers describing oxidation under pure nitrogen plasma are scarce. More importantly, these reports tend to describe plasma discharge types that

substantially differ from our PCD configuration. It should be noted that here, the absence of O2 does not suggest that Eq. (1) would be invalid under these circumstances. Instead, it is

proposed in4 that the atomic hydrogen H (a product in Eq. (1)) recombines with the OH radical in the absence of O2, which is a strong H scavenger following Eq. (2)5.

$${\rm{H}}+{{\rm{O}}}_{2}+M\to {{\rm{HO}}}_{2}+M$$ (2) In other words, OH radicals are not able to react with the dissolved species if H is not scavenged. It is, however, interesting to

consider why OH radicals in this case are completely unreactive in the liquid phase without O2, while they can be effective even in anaerobic natural waters12. In the present study, we

address this problem by suggesting that OH radicals are formed only from water vapor and their transfer through the gas-liquid interface is the decisive process for successful oxidation of

dissolved components. We arrive at this conclusion by describing: (i) OH radical oxidation of gaseous nitrogen and acetone without ambient O2; (ii) zero oxidation of oxalic acid (OA) in the

liquid phase in the absence of O2; and (iii) demonstrating the temperature dependence of the possibility of the OH radical diffusing unreacted through the interface under air plasma. These

observations provide essential information for the conceptualization of new PCD-based OH radical processes by enabling mapping of the kind of redox reactions that are achievable. RESULTS AND

DISCUSSION Ambient plasma is known to result in oxidation of N2, producing dissolved NOx in water treatment applications. In this study, the experiments showed temperature and pulse

frequency as having no effect on the yield of NOx (per energy dose), measured as aqueous total nitrogen (TN). Since water vapor pressure increases with temperature, it would be reasonable to

assume that the density of gaseous OH radicals would correlate with it. The observed temperature independence of N2 oxidation is therefore very interesting, as it does not display any

correlation to water vapor pressure, which at 13…30 °C ranges from 1.51 to 4.25 kPa. In agreement with previous studies13,14, the indifference towards pulse frequency indicates that only

short-lived species present during and shortly after the pulses contributed to NOx formation (OH radical lifetime on water surface is ~2.7 µs15, 1–2 orders of magnitude longer above the

surface5). Under N2, however, the TN formation rate at 1.98 g kWh−1 was almost half that in air, 3.69 g kWh−1. It should be noted that the yield in air is over twice the TN 1.77 g kWh−1

calculated from NO3 − formation presented in14, which is probably due to the water being introduced in aerosol form, rather than the previously applied showering approach, substantially

increasing the gas-liquid contact area (see Experimental Methods). The dissolved TN evolution observed under N2, i.e. in the absence of O2, suggests OH radical induced oxidation taking place

in the gas phase because simultaneously there was zero oxidation in the liquid phase, as will be discussed below. The difference in formation rates under air and N2 indicates that nitrogen

oxidation is supported by oxygen, which acts as a strong atomic H scavenger and contributes to the formation of strong oxidants. The evolution of TN concentration under air and N2 is

presented in Fig. 1. Since variation in the process parameters (temperature and pulse frequency) had no effect on TN formation rate against delivered energy, the values presented are

averages of all experiments under a given atmosphere. In agreement with previous findings14, the dissolved TN in treatment under air was found to consist only of NO3 −. Without oxygen, also

NO2 − was identified, which may simply be explained by the absence of O3 since dissolved O3 readily oxidizes NO2 −, producing mainly NO3 − and O2(1Δg)16. The gas phase oxidation was

confirmed with concentrated acetone solutions (17%); acetone oxidation under N2 resulted in notable accumulation of dissolved oxidation products, acetic17 and formic acid18, during the

treatment. The IC detector response for acetate and formate showed an increase consistent with delivered energy dose. Some inaccuracy of the acetate and formate concentrations may occur due

to the partial overlapping of the chromatogram peaks (the chromatograms are presented in Supplementary Discussion 1). The evolution of the oxidation products, however, confirm the gas phase

formation of OH radicals, whereas with the dissolved probe compound (OA), there was no indication of liquid phase OH radical activity under N2 atmosphere (discussed further below). It should

be noted that under these conditions, the presence of lower oxidation state NOx may enhance the OH induced oxidation process via secondary reactions19, the extent of which may provide

excellent topics for further research. The ion chromatograms of the acetone oxidation products with NO2 − and NO3 − are presented in Fig. 2. Temperature and pulse frequency displayed

consistent correlation with OA oxidation energy efficiency in the experiments conducted under air, the reaction rates exhibiting kinetic profile change from zero to first order along the

decrease in both parameters from the highest to the lowest applied values, as can be seen in Fig. 3. The oxidation efficiency at 300 and 500 pps is at similar range while distinctly lower at

833 pps. The difference stems mainly from the role of O3 6. At equal energy doses, the amount of pulses and thus the amount of OH from Eq. (1) can be considered constant: the role of O3 can

then be considered from the difference in treatment times at different frequencies. The OA oxidation yield at 833 pps is almost halved from 13 to 30 °C, while its improvement when changing

to 500 pps, attributable to longer treatment time, varies very little at any temperature, which emphasizes the temperature dependence of OH radical in the oxidation of the dissolved species

(calculations in Supplementary Discussion 2). By taking the reaction rates from the 0…5 kWh m−3, wherein the degradation is practically linear in all cases (see Fig. 3), the frequency

dependent decelerations of the OA oxidation rates caused by temperature increase can be directly visualized (Fig. 4). Given the very low reactivity of O3 and OA at low pH, the magnitude of

the temperature effect seen in Fig. 4 - strong even at high pulse frequency - is largely attributed to OH radicals. For reference, at similar concentrations and pH, aqueous OA reduction by

O3 alone was reported in20,21 as a maximum of ~10% for 30…60 min treatment. The applied O3 concentration ranged from similar20 to an order of magnitude higher21 compared to our process7.

Since formation of OH radicals is induced by electrons with ~3 orders of magnitude higher temperature than that of ions and molecules22, the rate of it cannot practically be dependent on the

gas temperature range in the current experiments. It can be therefore concluded that high temperature increases OH radical activity instead, which, however, results in decreasing the

oxidation rates of dissolved components due to promotion of premature radical termination reactions. Several possibilities for these reactions are described in23,24. Under N2, TOC remained

unchanged i.e. zero oxidation for OA was observed at any combination of pulse frequency and applied temperature. The result is in agreement with earlier research, where even phenol remained

unoxidized in PCD treatment without molecular oxygen4. The liquid phase OH radical formation testing by using KMnO4 as an atomic H scavenger also yielded zero oxidation of OA, further

demonstrating that no OH radicals are formed in the liquid phase, and that the radicals must therefore come from the gas side of the interface. During the treatment, the permanganate was

gradually reduced to Mn(IV)O2, which is an inevitable development due to the NOx formation. This development is presented in Supplementary Discussion 3. These findings extend and are

supported by the report of Kanazawa _et al_.5, where gas-phase OH radical formation and its dissolution into liquid phase are discussed and OH lifetime on water surface found to be

substantially shorter than in humid air. In summary, via simple experiments with a PCD plasma water treatment system under air and N2, we have showed that although OH radicals are active

also in the liquid phase, in the present kind of plasma-water interaction they are formed in the gas phase only (i.e. from water vapor), and that the gas-liquid interface is a major barrier

for the efficient utilization of the radicals in oxidation of aqueous compounds. The absence of atomic H scavengers in the gas phase promotes OH recombination with H, which is too fast for

OH radicals to cross the gas-liquid interface boundary unreacted. Liquid-phase H scavenging does not enable OH induced oxidation, suggesting that no radicals are produced on the liquid side.

In the absence of gaseous H scavengers, oxidation by OH still occurs in the gas phase because the radicals do not need to cross an interfacial boundary. Temperature increases OH radical

reactivity, which hinders oxidation energy efficiency of dissolved compounds by promoting premature reactions, i.e. reactions occurring prior to successful transfer through the interface.

METHODS The PCD reactor used is a vertical wire-plate configuration with a pulse generator adjustable to deliver identical pulses (22 kV and 180 A peak amplitude) at 50 to 833 pulses per

second (pps) at corresponding nominal power of 6 to 100 W (0.12 J per pulse). Water was sprayed from above into direct contact with the plasma, using five axial-flow full cone atomizer

nozzles, at volumetric flow rate of 1.8 L min−1. Below the reactor is a tank holding the treated solution, a jacketed vessel coupled with a thermostat for adjusting the operating

temperature. For experiments under N2, oxygen absence was confirmed by measuring gas composition in the water tank headspace, using an oxygen analyzer (based on paramagnetic susceptibility

measurements). The practical concept is illustrated in Fig. 5. A more detailed technical description of the PCD system (excluding the atomizer setup) and a pulse oscillogram can be found in

our previous publication6. Oxalic acid (OA) concentrations were measured by analyzing the total organic carbon (TOC) concentrations (applying catalytic combustion at 680 °C) coupled with a

total nitrogen (TN) unit for simultaneous TN analysis. Since OA has no organic oxidation products, i.e. is directly oxidized to CO2, TOC corresponds directly to OA concentration. Similarly,

in the experiments under air, TN value can be used to determine NO3 concentrations since PCD yields no other dissolved NOx species under air, as mentioned above. Acetone oxidation products,

formate and acetate, were observed using an ion chromatograph (IC) with an anion column. In the experiments under N2 atmosphere, IC was also used to identify any presence of NO2 −. For the

OH reactions with dissolved components, OA at 60 mg L−1 (pH ~3.4) was used as the organic probe compound for favoring OH radical over O3 reactions, following the low reactivity of OA with

ozone (_k_ ≤ 4 ∙ 10−2 M−1 s−1  25 at pH 5–6; for the reaction with OH _k_ = 5.3 ∙ 106 M−1 s−1  26), emphasized under acidic conditions. The experiments were conducted in 10 L batches and

sampling was done at 2.5 kWh m−3 intervals of discharge energy per treated water volume until 10 kWh m−3. The experiments were carried out at three pulse frequencies, 300, 500 and 833 pps:

due to the identic pulses, increasing frequency at fixed energy doses results in reduced treatment time, lower frequency therefore giving the longer living species, like O3, more time to

react with the probe compound. The experiments were conducted at temperatures of 13, 20 and 30 °C. For the experiments under N2, the system was flushed with N2 until all oxygen was replaced.

For these experiments, the treated solution was also degassed before introduction into the tank and kept running through the system under N2 atmosphere for 40 minutes before starting the

experiment to ensure negligible dissolved oxygen. N2 inflow was kept at 7 L min−1 throughout the experiments to ensure zero oxygen intake from ambient air. To ascertain whether OH radical

formation in the liquid phase occurs, potassium permanganate KMn(VII)O4 (0.1 mM) was used in a separate experiment as an atomic H scavenger in the dissolved phase. For any reaction following

Eq. (1), the permanganate would not be oxidized by OH but instead serve as an oxidant for atomic H. Under N2, thus scavenged atomic H in the liquid phase would enable OH radical reactions

with OA. To exclude oxalate oxidation by permanganate, sodium oxalate was in this case used at neutral pH and at the lowest applied temperature of 13 °C, under which conditions permanganate

is not reactive with oxalate. Gas phase oxidation under N2 was studied with a 17% acetone solution, exploiting the high volatility of the substance. Run under N2 atmosphere, acetone was used

to demonstrate organic species oxidation in the gas phase by OH radicals from water vapor, in the absence of O2. The experimenting was conducted at 833 pps and 20 °C and acetone solution

volume was reduced to 7 L for convenience, and the process overall duration was extended to 18.03 kWh m−3 of delivered energy to highlight the observable effects. DATA AVAILABILITY The

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INFORMATION AUTHORS AND AFFILIATIONS * School of Engineering Science, Lappeenranta University of Technology, P.O. Box 20, 53851, Lappeenranta, Finland Petri Ajo * School of Advanced

Manufacturing Technologies, Tomsk Polytechnic University, 2A Lenina Ave., 634028, Tomsk, Russia Iakov Kornev & Sergei Preis Authors * Petri Ajo View author publications You can also

search for this author inPubMed Google Scholar * Iakov Kornev View author publications You can also search for this author inPubMed Google Scholar * Sergei Preis View author publications You

can also search for this author inPubMed Google Scholar CONTRIBUTIONS P.A. conducted the experimental part and wrote the body of the manuscript. I.K. and S.P. participated in the results

analysis and experimental design, and writing the final version of the paper. All authors reviewed the manuscript. CORRESPONDING AUTHOR Correspondence to Petri Ajo. ETHICS DECLARATIONS

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Hydroxyl Radical Transfer Through the Gas-Liquid Interface. _Sci Rep_ 7, 16152 (2017). https://doi.org/10.1038/s41598-017-16333-1 Download citation * Received: 01 September 2017 * Accepted:

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