22nd International Symposium on Plasma Chemistry July 5-10, 2015; Antwerp, Belgium Production of reactive oxygen and nitrogen species during driven dc atmospheric pressure glow discharge generated in contact with liquid P. Jamróz, A. Dzimitrowicz, K. Greda and P. Pohl Wroclaw University of Technology, Faculty of Chemistry, Division of Analytical Chemistry and Chemical Metallurgy, Wybrzeze Stanislawa Wyspianskiego 27, PL-50370 Wroclaw, Poland Abstract: The stable atmospheric pressure glow discharges (APGDs) were generated in contact with a flowing liquid cathode. As an anode, a gaseous argon and helium microjets or a metallic electrode were applied. All discharges were operated in the ambient air atmosphere at a supplied power lower than 40 W. The different atomic and molecular species were excited in the core of these discharges. The emission spectra of the investigated APGDs were dominated by the bands of the OH, N 2 , NO, and NH molecules. In addition, the atomic O I and H and ionic O II emission lines were identified. The mechanisms of the processes occurred in the interfacial discharge-liquid zones as well as in the liquid phases and responsible for the production of the reactive species were discussed. The production of H 2 O 2 , NO 3 -, NO 2 - as well as the OH radicals in the liquid phase and the fall of the solution pH was confirmed. Keywords: atmospheric pressure glow discharge, plasma – liquid interaction, reactive oxygen species, reactive nitrogen species 1. Introduction The cold atmospheric plasmas, sometimes called as the non-thermal plasmas or the atmospheric pressure plasmas, generated in and in contact with liquids are frequently applied in the studies related to the environmental protection and the biomedical engineering [1,2]. Apparently from the literature, it is possible to apply such cold atmospheric plasmas in the water cleaning, the sterilization, the bacteria inactivation as well as in the environmental remediation processes and other biochemical processes [1-5]. These plasma sources were also applied as cheap and efficient excitation and atomic sources in the analytical atomic spectrometry for the elemental analysis [6]. So far, the different constructions of the cold atmospheric plasma sources, e.g., the atmospheric pressure glow discharge, the dielectric barrier discharge, the corona plasma, the pulsed plasma, the transient spark discharge and the plasma needles, have been successfully employed in the various processes related to the emerging field of the plasma medicine [1,2,5]. Among them, the atmospheric pressure glow discharges generated in and in contact with liquids were established to be the rich sources of the various oxygen (ROS) and nitrogen (RNS) chemically active species, e.g., hydrogen peroxide (H 2 O 2 ), singlet oxygen (1O 2 ), ozone (O 3 ), hydroxyl (OH), hydroperoxyl (O 2 H) and oxygen (O) radicals, superoxide (O 2 -) ions, hydrogen peroxonitrate (ONOOH), NO and NO 2 [3,4]. Being rich sources of the reactive oxygen species and the reactive nitrogen species, the atmospheric pressure glow discharges could also be applied for the bio-decontamination and the purification of the water samples in a continuous flow mode, which is P-I-3-9 rarely encountered in the literature. They could also be used for the fast and cheap synthesis of the biocompatible nanoparticles [4]. The main aim of the present work was to elucidate the discharge-liquid interactions as well as the production of the chemically reactive species in the discharge and in the liquid phase of different atmospheric pressure glow discharges generated in contact with flowing liquid cathodes. The emission spectra of the discharge were determined and compared in order to clarify what kind of the elementary processes exist in the atmospheric pressure glow discharge sources. The suitability of the described atmospheric pressure glow discharge sources in the biomedical engineering was also evaluated. 2. Experimental setup The atmospheric pressure glow discharges were generated in contact with liquid cathodes. A schematic representation of the discharge systems used in the present work is given in Fig. 1. The stable discharges were resulted from applying high voltages (1000-1300 V) to the electrodes. 1 OH N2 NH NO N2+ OH b) Fig. 1. The experimental set-up (not to scale). Atmospheric pressure glow discharges were obtained by the direct-current (dc) discharge with a miniature argon or helium gas flow passed through a steel nozzle (internal diameter 0.5 mm) or a molybdenum rod anode (outer diameter 2 mm). A high voltage (HV) positive bias direct current (dc) power supply with a maximum power output of 200 W, working in the discharge current range within 0-100 mA, was used. Additionally, a ballast resistor (R=10 kΩ) working in the anode circuit was applied to stabilize the discharge current. Atmospheric pressure glow discharges were operated in the ambient air atmosphere at a discharge current of 40 mA. A peristaltic pump (Lab Craft, France) was applied to deliver the water sample solutions into the discharge zone. The water sample solutions, treated by both atmospheric pressure glow discharges, were collected into 10-mL stoppered glass tubes and directly analysed by the chemical methods of the analysis (using the UV-Vis absorption spectrophotometry as well as the fluorescence method). Additionally, a production yield of the reactive species in the plasma gaseous phase was investigated using the optical emission spectroscopy. For this purpose, a JY Triax 320 monochromator (with holographic gratings: 1200 and 2400 grooves per mm and a R-928P photomultiplier) and a miniaturized CCD spectrometer (Blue Wave UV2) with optical fibers were applied. The emission of the atmospheric pressure glow discharges was measured in the discharge-liquid interfacial zone. 3. Results and discussion The typical emission spectra of the atmospheric pressure glow discharges (APGDs) are presented in Figs. 2a, 2b and 2c in the range of 200-900 nm. As can been see on the Fig. 2, the NO, N 2 and OH species were easily excited in all analysed discharges. a) 2 N2 Na H O II c) Ar H O O Fig. 2. The emission spectra of atmospheric pressure glow discharges generated in contact with flowing liquid cathodes in the range of a) 200-400nm b) 400-600 nm and c) 600-900 nm The most prominent was the (0-0) band of the OH radical at 306.4 nm belonging to the A2Σ-X2Π system and the (0-0) band at 337.1 nm of the N 2 molecule belonging to the second positive system (C3Π u -B3Π g ). In the 200270 nm spectral region, numerous bands of the NO molecule, belonging to the γ-system (A2Σ+-X2Π), were also observed. The atomic hydrogen (H) lines of the Balmer series (at 656.2, 486.1 and 434.1 nm) as well as the atomic oxygen (O I) at 777.2, 777.4 and 844.6 nm and the ionic oxygen (O II) at 441.5, 459.1, 459.6, 467.4, P-I-3-9 466.6 and 470.7 nm emission lines were noted for all the investigated discharges. The (0-0) and (1-1) bands of the NH molecule (the A3Π-X3Σ- system) with the band heads at 336.0 and 337.0 nm were also identified especially in the case of the atmospheric pressure glow discharge operated with the argon microjet. The relatively weak bands of the N 2 moleculte (the B3Π g -A3Σ+ u system) in the range of 650-750 nm were excited in the case of the atmospheric pressure glow discharge system with both the argon or helium microjets. Additionally, only for the discharge system with the argon microjet numerous atomic argon (Ar I) emission lines in the spectral range of 650-800 nm (with the excitation energies within 13-15 eV) as well as the weak (0-0) and (0-1) bands of the N 2 + molecule (the B2Σ+ u -X2Σ+ g system) at 391.4 and 427.8 nm, respectively, were noted. It should be noted that the intensities of the NO and N 2 molecular band heads observed for the atmospheric pressure glow discharge with the helium microjet were higher in comparison to those obtained with the atmospheric pressure glow discharge system with the argon microjet or the pin electrode. On the other hand, the most intense emission of the OH molecule was noted in the systems with the pin electrode and the argon microjet. Moreover, the studied atmospheric pressure glow discharge sources were established to produce an intensive UV radiation. The OH radicals with an oxidation potential of 2.80 V were probably generated in the interfacial zone as a result of the processes of water dissociation and/or their ions (e.g. H 2 O+) coming from the sputtering/ionization processes of the water molecules [3, 4] e.g.: (1) H 2 O + e = H + OH + e H 2 O+ + e = H + OH (2) H 2 O+ + H 2 O = H 3 O+ + OH (3) The formation of the OH radicals in the liquid phase was confirmed using the chemical dosimetry method with terephthalic acid. A LED diode (working at 310 nm) was applied as a light source to excite the product of the reaction of terephthalic acid with OH radicals, i.e., 2hydroxyterephthalic acid. The fluorescence signal of the latter compound was detected at 425 nm and confirmed the production of the OH radicals in the liquid phase. It was presumed that the NO/NO 2 molecules were produced in the discharge zone as a result of the reaction of nitrogen coming from the air atmosphere with oxygen [3], e.g.: N 2 + O = NO + N (4) N + O 2 = NO + O (5) NO + O + M = NO 2 + M (6) P-I-3-9 In the solutions treated by the discharges, the hydrogen peroxide molecules (H 2 O 2 ) and the nitrate (NO 3 -) and the nitrite (NO 2 -) ions were identified. The source of H 2 O 2 was probably the oxidative processes of water or other reactions [3,4,7], e.g.: + H2 2H 2 O* = H 2 O 2 (7) OH + OH = H 2 O 2 (8) The main sources of the nitrite and the nitrite ions were nitric oxide (NO) and/or nitric dioxide (NO 2 ) [3,8]. These species reacted with the OH radicals or water molecules, e.g.: (9) NO + OH = HNO 2 NO 2 + OH = HNO 3 (10) 2NO 2 + 3H 2 O = NO 3 - + NO 2 - + 2H 3 O+ (11) In each case, the growth of the concentration of the H 3 O+ ions and consequently a drop of the pH in the solutions treated by the discharges were also observed, probably due to the reactions of nitrogen oxide with water or the OH radicals (see reactions 9-11). The fall of the pH in the solutions is rather connected with the enhanced production of nitric acid (HNO 3 ). Under the acidic conditions, hydrogen peroxonitrate (ONOOH) with an oxidation potential of 2.44V could also be produced from the nitrate ions (NO 2 -) and the hydrogen peroxide molecules (H 2 O 2 ) [5, 9]: (12) NO 2 - + H 2 O 2 + H 3 O+ = ONOOH + 2H 2 O The identified reactive species could act as oxidants in the various biochemical and biotechnology reactions. In order to confirm the role of the reactive species in the selected biochemical systems, some additional experiments would be performed. 4. Conclusions The stable non-thermal direct current atmospheric pressure glow discharges were generated in contact with the flowing liquid cathodes using different kinds of the anode system, i.e., the solid pin and argon or helium gaseous microjets. The all atmospheric pressure sources were operated in the open to air atmosphere. The following species: N 2 , NH, NO, OH, H and O were excited in the examined discharges. Additionally, the atmospheric pressure glow discharge sources emitted the relative strongly radiation in the UV range. Hydrogen peroxide (H 2 O 2 ), the OH radicals in addition to the nitrate (NO 3 -) and the nitrite (NO 2 -) ions were identified in the water sample solutions treated by these discharges as a result of the chemical reactions occurred in the interfacial discharge-liquid zone. A growth of the concentration of the H 3 O+ ions in the liquid phase was noted for all the examined atmospheric pressure glow discharge systems. 3 5. References [1] A. Fridman and G. Friedman. Plasma Medicine, Willey (2013). [2] Y. Yang, Y. I. Cho and A. Friedman. Plasma discharge in liquid. Water treatment and applications, CRC Press Boca Raton (2012). [3] P. Jamróz, K. Gręda, P. Pohl, W. Żyrnicki. Plasma Chem Plasma Process., 34, 25(2014). [4] P. Jamróz, K. Gręda and P. Pohl. Plasma Process. Polym., 11, 755 (2014). [5] Z. Machala, B. Tarabova, K. Hensel, E. Spetlikova, L. Sikurova and P. Lukes. Plasma Process. Polym., 10, 649 (2013). [6] K. Greda, P. Jamroz and P. Pohl. J. Anal. At. Spectrom., 28, 1233 (2013). [7] B. R. Locke and K. Y. Shih. Plasma Sources Sci. Technol., 20, 034006 (2011). [8] X. Liu, H. Zhang, D. Qin, Y. Yang, Y. Kang, F. Zou and Z. Wu. Plasma Chem. Plasma Process., 35, 321 (2015). [9] T. Shimizu, Y. Iwafuchi, G. E. Morfill and T. Sato. New J. Phys., 13, 053025 (2011). 6. Acknowledgement The work was financed by a statutory activity subsidy from the Polish Ministry of Science and Higher Education for the Faculty of Chemistry of Wrocław University of Technology. The project supported by Wroclaw Centre of Biotechnology, the programme The Leading National Research Centre (KNOW) for years 2014-2018 was also acknowledged. 4 P-I-3-9
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