Published in: Proceedings of the 31st International Conference of Phenomena in Ionized Gases(ICPIG2013), July 14-19, 2013, Granada, Spain

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Gas phase hydrogen peroxide production in atmospheric pressure glow discharges operating in He - H2O Vasko, C.A.; van Veldhuizen, E.M.; Bruggeman, P.J. Published in: Proceedings of the 31st International Conference of Phenomena in Ionized Gases(ICPIG2013), July 14-19, 2013, Granada, Spain Published: 01/01/2013 Document Version Publisher s PDF, also known as Version of Record (includes final page, issue and volume numbers) Please check the document version of this publication: A submitted manuscript is the author's version of the article upon submission and before peer-review. There can be important differences between the submitted version and the official published version of record. People interested in the research are advised to contact the author for the final version of the publication, or visit the DOI to the publisher's website. The final author version and the galley proof are versions of the publication after peer review. The final published version features the final layout of the paper including the volume, issue and page numbers. Link to publication Citation for published version (APA): Vasko, C. A., Veldhuizen, van, E. M., & Bruggeman, P. J. (2013). Gas phase hydrogen peroxide production in atmospheric pressure glow discharges operating in He - H2O. In Proceedings of the 31st International Conference of Phenomena in Ionized Gases(ICPIG2013), July 14-19, 2013, Granada, Spain (pp. 10-14) General rights Copyright and moral rights for the publications made accessible in the public portal are retained by the authors and/or other copyright owners and it is a condition of accessing publications that users recognise and abide by the legal requirements associated with these rights. Users may download and print one copy of any publication from the public portal for the purpose of private study or research. You may not further distribute the material or use it for any profit-making activity or commercial gain You may freely distribute the URL identifying the publication in the public portal? Take down policy If you believe that this document breaches copyright please contact us providing details, and we will remove access to the work immediately and investigate your claim. Download date: 08. Oct. 2018

10 Gas phase hydrogen peroxide production in atmospheric pressure glow discharges operating in He-H 2 O C.A. VaskoP, E.M.van Veldhuizen, and P.J. BruggemanP Eindhoven University of Technology, Den Dolech 2, 5600 MB Eindhoven, The Netherlands The gas phase production of hydrogen peroxide (H 2 O 2 ) in a RF atmospheric pressure glow discharge with helium and water vapour has been investigated as a function of the gas flow. It is shown that the production of H 2 O 2 is through the recombination of two OH radicals in a three body collision and the main destruction is through radical reactions involving OH or surface losses at the electrodes. Balancing these production and losses of H 2 O 2 allows estimating OH densities which correspond with reported densities in literature for this type of discharge. 1. Introduction Non-equilibrium atmospheric pressure plasmas can produce a great amount of reactive species, including O, OH and H 2 O 2 [1]. A clear understanding of the mechanisms underlying the production of these reactive species may be of benefit to many different areas, such as biomedical, chemical and environmental applications. Among these reactive species, hydrogen peroxide (H 2 O 2 ) has recently become a focus of interest. It is an important oxidant, only second to molecular oxygen [2], and as the byproduct of oxidizing reactions involving H 2 O 2 in controlled environments is only water, can be considered as a green alternative for many applications [1,3,4]. Industrial/communal waste water treatment [3-5], detergents [5], as oxidant in catalytic reactions, disinfection, bleaching and wound healing [6] are further examples where H 2 O 2 is being applied. A recent review on H 2 O 2 production [7] revealed that a number of very different gas discharges have been investigated in the past and have reported a range of energy efficiencies η covering more than two orders of magnitude (0.1 80 g/kwh). As the dependencies of H 2 O 2 production and destruction in plasmas are not well understood, directly comparing fundamentally different discharges becomes a challenging task. In this work we present results on H 2 O 2 production in a He + H 2 O (1%) RF driven diffuse atmospheric pressure glow discharge (APGD) reactor for various gas flow rates. APGDs offer certain advantages for this investigation, such as low gas temperatures, a well defined residence time and a homogenous discharge. Results of modelling such an APGD [8] report efficiencies for H 2 O 2 production in the order of tens of g/kwh. The experimental setup and applied methods are presented first, followed presenting the H 2 O 2 production as a function of the gas flow rate and the discussion of the main production and destruction reactions of H 2 O 2 in the plasma. 2. Experimental Methods The plasma is a capacitively coupled RF driven APGD operating at ambient pressure and temperature as investigated in [9-11]. The reactor consists of two parallel stainless steel electrodes with approximately 1 mm gap and is operated with helium containing 1 % water vapour. To power the plasma, a RF signal is amplified using a power amplifier and coupled into the reactor using a matching network. A bidirectional coupler with thermal probes monitoring forward/reflected powers is placed between amplifier and the matching network, which consists of a coil and a resistor to ground. A current- and a voltage probe are used to monitor current and voltage signals. The APGD is operated around 9.5 MHz, with power operated at approximately 5 W, measured similar to the work in [12]. 3. Hydrogen peroxide detection The detection of H 2 O 2 produced in the APGD is based on Optical Absorption Spectroscopy (OAS). The effluent gas from the reactor is exposed to a solution of ammonium metavanadate (NH 4 VO 3 ), the resulting oxidation of V VII to V V by H 2 O 2 induces a colour change from which the concentration of H 2 O 2 can be obtained. This method is highly selective on and sensitive to H 2 O 2 in presence of other reactive species as described in detail in [13]. From the absorption signal, the concentration (c) of H 2 O 2 can be determined using the Beer-Lambert Law

I = I 0 e εcd with I/I 0 being the ratio of measured to reference intensity, d the optical absorption path length and ε the molar extinction coefficient of NH 4 VO 3 [13]. For every measurement run, the first obtained spectrum is used as a reference signal. Solving the equation for c, the H 2 O 2 concentration in mol.l -1 per sample can be obtained. Performing a measurement every minute results in a graph like in figure 1, where the slope of these points represent the H 2 O 2 yield in mol.l -1.min -1 in the detection volume. The density of H 2 O 2 in the plasma volume, n H2O2, can be estimated from the total gas flow and the obtained concentrations. All measurements in this work have been performed using this method. A LED with a maximum light intensity around 450 nm was chosen as light source. This is close to the highest reported sensitivity of the peroxovanadium solution to H 2 O 2. The LED has a high stability in time and a good signal to noise ratio. This allows for short integration times and a high reproducibility. Gas mixing in the detection vessel was also considered, as gas enters the vessel through a fairly large gas sieve forming bubbles in the volume above, where they interact with the liquid. The efficiency of this exchange depends on surface to volume ratio of the gas bubbles and the time these spend rising through the liquid column. In order to establish if any H 2 O 2 is lost due to insufficient mixing, two recipients were connected in series and c H2O2 was measured in simultaneously both vessels with the same method. No absorption signal was detected in the second vessel, even after a measurement time 4-5 times longer than the usual measurement times. The reproducibility of the measurements is within 10 % and clearly Figure 1: H 2 O 2 concentration as a function of time obtained using a colorimetric method in the detection vessel. Figure 2: H 2 O 2 gas phase density and energy efficiencies for He + 1% H 2 O at P plasma = 5W as a function of varying the total flow. of key importance. Systematic errors cannot be fully excluded at this point. However, the errors in this work are mostly determined by the discharge conditions and not by the detection method. Combining the power dissipated in the plasma with the concentration of H 2 O 2 in the liquid volume, the energy efficiency η of the reactor can be calculated. Gas phase densities of H 2 O 2 n H2O2 can be calculated knowing the total flow through the reactor. 4. Hydrogen Peroxide production as a function of flow In figure 2, trends for H 2 O 2 efficiency and densities are shown as a function gas flow at a constant plasma power of 5 W and 1% water content. Both n H2O2 and η increase with flow, but while η steadily increases, n H2O2 seems to reach a maximum at 2 slm. An important consideration of the calculation of the density should be made here: the calculation of n H2O2 in the plasma implicitly includes the assumption that no molecules are lost between production in the plasma and detection in the liquid phase. However, the dissociation of H 2 O 2 on surfaces is a known issue in surface chemistry and has been studied on various surfaces [14,15]. Losses for initial densities of 40000 ppm H 2 O 2 on Pyrex of 488 K have been reported to be below 0.1 % in [15]. Rescaled to the densities (order of 10 ppm) here, considering the surface area of parts exposed to the effluent gas before detection and their low temperature, this loss is negligible compared to other losses and the production rate of H 2 O 2 (discussed in the following). The calculated values of n H2O2 can thus be considered to accurately reflect the H 2 O 2 density in the reactor.

To explain this result, the balance of production and destruction processes of H 2 O 2 in the plasma at different flows has to be considered. This balance in the stationary state can be written as (n OH ) 2 n M k 1 = n i n H2O2 k i + Φ + Γ s, where the production equals bulk chemical losses with reactions induced by OH, H, O and electrons, losses due to gas flow Φ and surface reactions yielding a flux Γ s. The individual contributions will be discussed in the following. The main source for forming H 2 O 2 in nonequilibrium cold (300 400 K) atmospheric pressure plasmas containing water is via the three body recombination of the hydroxyl radical to form hydrogen peroxide [7,8] OH + OH + M H 2 O 2 + M. As the OH density is larger than the O and H density and the rates are smaller [8] their contribution in H 2 O 2 destruction can be neglected compared to the OH Recent results for a RF plasma jet investigating atomic oxygen formation [16] reported an electron density n e = 10 11 cm 3, for a power density comparable to our case. As a similar value can be expected for the He - H 2 O case, this can be applied to find an approximation for the electron induced losses. Using the rate for both electron attachment and dissociative attachment (calculated based on [17] with T e = 3 ev) and n e = 10 11 cm 3, these losses are less important compared to OH induced losses. Using the reaction rates available in literature [8,18] with assuming n e = 10 11 cm 3 and fitting n OH for the two cases of 2 and 4 slm results in a good balance with n OH = 1.5 10 14 cm 3 (figure 2). Reducing n e does not yield a good balance with a realistic n OH. The obtained n OH seems to be in line with densities reported in [19], where the reported value is only 35% lower when the same power density is considered. As the discharge gap is half of that in reference [19], surface losses will be more important in the present case which could explain the slightly lower n OH obtained in the fit. The observed discrepancy at lower flows in figure 3 could be attributed to higher impurities at low gas flow rates. These lead to higher OH losses and thus to higher H 2 O 2 losses, which are not accounted for in the model. From figure 3 it shows that the dominant loss mechanisms for H 2 O 2 are OH induced losses in the bulk and losses of H 2 O 2 to the surfaces of the reactor. 5. Conclusions In this work a colorimetric method is used to determine the H 2 O 2 density in an APGD. Its maximum value is 7 ppm and depends on the gas flow. Balancing the main production and loss mechanisms for H 2 O 2 allow estimating the OH density. This yields a density of 1.5 10 14 cm -3 similar to measured densities previously reported in literature. The main loss mechanism of H 2 O 2 is the recombination with OH radicals in the bulk of the plasma. 6. Acknowledgments This work is supported by the Dutch Technology Foundation (STW). Figure 3: Balancing production and losses of H 2 O 2 for a fitted OH density. Molecules in the discharge can also be lost at the metal surfaces of the electrodes. An estimate of the net flux Γ s of H 2 O 2 molecules to a surface can be made based on considerations in [15]. 5. References [1] P. Bruggeman, C. Leys, J. Phys. D 42, 5 (2009) 053001. [2] G. Goor, Catalytic Oxidations with Hydrogen Peroxide as Oxidant G. Strukul, Ed., Dordrecht (1992). [3] C.W. Jones, Application of Hydrogen Peroxide and Derivatives London. Royal Society of Chemistry, London (1990). [4] W. Eul, A. Moeller, N. Steiner, Hydrogen Peroxide. John Wiley & Sons, LTD (2000). [5] W. Hess, 4th ed., Kirk-Othmer Encyclopedia of Chemical Technology, J. Kroschwitz and M. Howe-Grant, Eds. Wiley (1995).

[6] R. Burlica, R. Grim, K.-Y. Shih, D. Balkwill, B. R. Locke, 7, 8 (2010) 640 649. [7] B. R. Locke and K.-Y. Shih, PSST 20, 3 (2011) 034006. [8] D. X. Liu, P. Bruggeman, F. Iza, M. Z. Rong, M. G. Kong, PSST 19, 2 (2010) 025018. [9] P. Bruggeman, D. C. Schram, M. G. Kong, C. Leys, Plasma Process. Polym. 6, 11(2009) 751 762. [10] N. Knake, S. Reuter, K. Niemi, V. Schulzvon der Gathen, J. Winter, J. Phys. D 41, 19 (2008) 194006. [11] F. Iza, J. Lee, M. Kong, PRL 99, 7 (2007) 075004. [12] S. Hofmann, A. F. H. V. Gessel, T. Verreycken, P. Bruggeman, PSST 20, 6 (2011). [13] R. F. P. Nogueira, M. C. Oliveira, W. C. Paterlini, Talanta 66, 1 (2005) 86 91. [14] R. Baldwin and D. Brattan, Chem. Kin. 8, 1, (1966) 110 119. [15] C. N. Satterfield, T. W. Stein, Ind. Eng. Chem. Res. 49 (1957) 1173 1180. [16] J. Waskoenig, K. Niemi, N. Knake, L. M. Graham, S. Reuter, V. S.-v. D. Gathen, T. Gans, PSST 19, 4 (2010) 045018. [17] D. Nandi, E. Krishnakumar, A. Rosa, W.-F. Schmidt, E. Illenberger, Chemical Physics Letters 373, 5-6 (2003) 454 459. [18] NIST Chemical Kinetics Database, http://kinetics.nist.gov. [19] P. J. Bruggeman, G. Cunge, N. Sadeghi, PSST 21, 3 (2012).