Alapi, Tünde

Farkas, Luca

Scheres Firak, Daniele

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26th International Symposium on Analytical and Environmental Problems 74  Xe*-EXCIMER LAMP VERSUS LOW PRESSURE MERCURY VAPOR LAMP – THE COMPARISON OF THE EFFICIENCY OF 185 nm WITH 172 nm RADIATION, BASED ON H2O2 FORMATION AND COUMARIN OXIDATION  Tünde Alapi, Luca Farkas, Daniele Scheres Firak  Department of Inorganic and Analytical Chemistry, University of Szeged, H-6720 Szeged, Dóm tér 7, Hungary Email: alapi@chem.u-szeged.hu  Abstract VUV photolysis is a widely used method for producing high purity water by efficiently removing organic substances present in low concentrations. This process is based on the direct photolysis of water, which results in the formation of HO and H radicals. In the case of photo-initiated Advanced Oxidation Processes (AOPs), such as VUV photolysis, the lamp type determines the effectiveness. There are two types of light sources commonly used in VUV photolysis: the low-pressure mercury vapor (LPMV) lamps and the Xe* excimer lamp. In this work, the efficiency of the low-pressure mercury vapor (LPM) lamp, which emits at 254 and 185 nm (UV/VUV185 nm lamp), and the Xe* excimer lamp, which emits at 172 nm (VUV172 nm) photons, were compared. The comparison of the efficiency of the VUV light sources was based on the formation of H2O2 in the case of the pure water as well as on the transformation of coumarin (COU) and formation of its hydroxylated product, umbelliferone (7-HO-COU).   Introduction The VUV photolysis is mainly used and investigated for the elimination and mineralization of various organic pollutants in aqueous solutions [1,2]. Organic and inorganic molecules or ions have high absorption coefficients in the VUV region. However, in aqueous solutions, the VUV radiation is absorbed almost exclusively by water because its concentration (55.5 mol dm–3) highly exceeds those of the dissolved compounds. Absorption of the VUV radiation results in the homolysis and, with lower quantum yield, the photochemical ionization of water molecules:  H2O + hν (<190 nm) → H• + HO•  H2O + hν (<200 nm) → [e−,H2O+] + H2O → [e−,H2O+] + (H2O) → eaq− + HO• + H3O+  There are some characteristic differences between the 185 and 172 nm VUV light irradiated solutions, which are the consequence of the extremely high absorption coefficient and low penetration depth of the 172 nm VUV light.    Table 1. The molar absorption coefficient and the penetration depth of 185 and 172 nm VUV light in water and the quantum yields of the formation of reactive species [3-5]   absorption coefficient (cm-1) penetration depth in water (mm) quantum yield Φ(•OH)/ Φ(H•) Φ(eaq-) 172 nm 550 0.036 0.42 0.05 185 nm 1.53 11 0.33 0.05  The extremely low penetration depth of 172 nm photons results in a very thin (0.04 mm) photoreaction zone containing high concentrations of primary radicals. The carbon-centered 26th International Symposium on Analytical and Environmental Problems 75  radicals, formed by the reaction of organic substances with H• and HO•, react immediately with dissolved O2 and form organic peroxyl radicals. As a result, an O2-depleted layer is formed next to the lamp wall. The VUV photon flux of the Xe-excimer lamp  generally highly exceeds that of the low- pressure mercury vapor lamps that emits both 254 nm and 185 nm photons. Although several authors published results about the efficiency of the low-pressure mercury-vapor lamp for the elimination of organic substances from waters [6-9], the studies about the Xe-excimer lamp [10], especially the comparison of these two light sources [5] , are quite rare.  Experimental For the VUV172 nm radiation, a Xe2* excimer lamp (Radium XeradexTM, 130 mm long, 46 mm diameter, 20 W) was used, which was centred in a high purity silica quartz envelope (53 mm diameter), able to transmit the 172 nm light. The aqueous solution was circulated continuously (375 mL min−1) between the reactor and the reservoir. A double walled, water-cooled reactor was used, and the temperature was set to 25 ± 0.5 °C. Samples were taken from the reservoir. The volume of the treated solution was 500 mL, the thickness of the irradiated water layer was 5 mm. The low-pressure mercury vapour (LPMV) lamp (UV/VUV185 nm lamp GCL307T5VH/CELL, 227 mm arc length, produced by LightTech) was used for the UV/VUV (254 nm/185 nm) photolysis. The UV/VUV185 nm lamp’s envelope was made of synthetic quartz to be able to transmit the VUV185 nm photons. The volume of the treated solution was 500 mL, the thickness of the irradiated water layer was 20 mm. In the case of VUV172 nm and UV/VUV185 nm photolysis, O2 or N2 gas was bubbled continuously through the solution. Coumarine (Sigma-Aldrich, ≥98,5%) solutions were made in ultrapure Milli-Q water (MILLIPORE Milli-Q Direct 8/16). The transformation of coumarin (COU) was followed by a spectrophotometer (Agilent 8453). The concentration was determined from the absorbance of the solution at 277 nm. Fluorescence spectroscopy (Hitachi F4500) was applied to determine the concentration of umbelliferone (7-HO-COU). The wavelength of excitation was 387 nm. The determination of its concentration was based on the intensity of the emitted fluorescence light at 455 nm. The concentration of H2O2 was measured with a cuvette test by Merck, with a 0.015 - 6.00 mg dm-3 measuring range.  Results and discussion In the case of the VUV photolysis, the 172 nm and 185 nm VUV light is absorbed by water to form reactive species, such as hydrogen radicals (H), hydroxyl radicals (HO), and, with a lower yield, hydrated electrons (eaq-) 2. The VUV flux of light sources determines their efficiency in terms of radical formation and consequently the removal of organic matter from water. The VUV photon flux was determined with methanol actinometry [11], and was found to be 32 times higher for the excimer lamp (1.04×10-5 molphoton s-1) than for the LPM lamp (3.23×10–7 molphoton s-1). The UV photon flux was 3.70×10-6 molphoton s-1.  The recombination of primer radicals results in the formation H2O, H2 and H2O2 [12]:  2 HO•  H2O2     k = 4.0×109 – 2.0×1010 dm3 mol-1 s-1 2 H•  H2      k= 1.0×1010 dm3 mol-1 s-1  HO• + H•  H2O     k  = 2.4×109 dm3 mol-1 s-1  26th International Symposium on Analytical and Environmental Problems 76  In the presence of dissolved O2, the reaction of O2 with H• hinders the recombination of primary radicals [12]:  H• + O2  HO2•     k = 2.1×1010 dm3 mol-1 s-1  O2 + eaq-  O2•−     k = 2.0×1010 dm3 mol-1 s-1   The further reactions of HO2• and O2•− also produce H2O2 [13]:  HO2• + H2O ⇋ H3O+ + O2−   pKa = 4.8  O2−+ HO2• + H2O  O2 + H2O2 + HO-     k = 9.7×107 dm3 mol-1 s-1   At first, the H2O2 concentration and its formation rate were determined and compared in the case of both lamps, in O2 saturated and O2-free Milli-Q waters. In O2 saturated waters, the rate of H2O2 formation was about twice as high, while the equilibrium concentration was almost 50-fold higher in the 172 nm irradiated solution than in the 254/185 nm irradiated Milli-Q water. This result reflects well the nearly 30-fold higher VUV photon flux of the Xe*-excimer lamp. In the case of 172 nm VUV photolysis, the formation rate and equilibrium concentration of H2O2 in O2-free solution was about 20% of the values determined in O2-saturated water. There was no H2O2 formation in O2-free water for irradiation at 254/185 nm.  Table 2. The initial transformation rates and equilibrium concentration of H2O2  determined in Milli-Q water   O2 saturated Milli-Q water O2-free Milli-Q water Xe-excimer lamp, 172 nm r0 (×10-8 mol dm-3 s-1) 10.53 2.85 ceq (×10-6 mol dm-3) 102 19 LPMV lamp 254/185 nm r0 (×10-8 mol dm-3 s-1) 4.83 - ceq (×10-6 mol dm-3) 2.1 -  The transformation of COU is negligible in 254 nm irradiated solutions, its transformation is due to the reaction with HO• (k = 6.9×109 mol1 dm3 s1) and H• (k = 2.5×109 mol1 dm3 s1) [14], in both UV/VUV185nm and VUV172nm irradiated solutions. Although the reaction of dissolved O2 with H• inhibits the transformation of COU via H• initiated reaction, it has no negative effect in the 172 irradiated solution, and increased the transformation rate by 20% in the UV/VUV185nm irradiated solution. Dissolved O2 generally has a positive effect on the radical based transformation of organic substances due to the formation of organic peroxyl radical (R-COO•) from carbon-centered radicals (R-C•). The formation of R-COO• opens up a new pathway for the transformation of organic substances and hinders the backward reactions. In terms of COU transformation rate, it is likely that the negative and positive effects of O2 are compensated for each other.  The formation of 7-HO-COU starts with the addition of HO• to the aromatic part of COU. From the carbon-centered radical, there are two possibilities of the 7-HO-COU formation: without dissolved O2 the reaction of two carbon-centered radical results in the formation of hydroxylated product and COU (Fig. 1). However, in the presence of O2, 7-HO-COU is formed exclusively through organic peroxyl radicals (Fig. 2). Consequently, the dissolved O2 highly enhances the formation of hydroxylated products, such as 7-HO-COU.    26th International Symposium on Analytical and Environmental Problems 77  Taking into account the different photon fluxes, we compared the efficiency of photolysis at 172 nm and 185 nm in the transformation of COU and formation of 7-HO-COU. Despite the photon flux more than 30 times higher, the conversion rate of COU was only 5-6 times higher, while the formation rate of 7-HO-COU was only 2-3 times higher in the case of the excimer lamp compared to the LPMV lamp. It has to be mention that, in 172 nm irradiated aqueous solutions of organic substances, due to the extremely high HO• concentration close to the wall of the lamp, an O2-depletion layer forms. Thus, the positive effect of O2 via peroxyl radical formation is less pronounced.       Fig. 1 The HO initiated formation of 7-HO-COU from COU in the presence (light blue frame) and absence (dark green frame) of O2  Table 3. The initial transformation rate of COU and the formation rate of 7-HO-COU in UV/VUV185nm and VUV172nm radiated solutions (c0COU = 1.0×10-4 M) The effect of dissolved O2  UV/VUV185nm VUV172 nm VUV photon flux φ (molphoton s-1) 3.23×10–7  1.04×10-5   O2 N2 O2 N2 r0COU (×10-8 mol dm-3 s-1) 3.77 3.12 20.2 19.5 Φ (r0COU/ φ) 0.23 0.38 0.039 0.038 r07-HO-COU (×10-9 mol dm-3 s-1) 1.03 0.29 2.53 9.60 r0COU O2/ r0COU N2 1.21 1.04 r07-HO-COU O2/ r07-HO-COU N2 3.58 2.63 Comparison of the VUV172nm/VUV185 nm photolysis  O2 N2 r0COU172nm/r0COU 185nm 5.36 6.25 r0COU 172nm/r0COU 185nm 2.46 3.33  The quantum yield of the COU transformation was one magnitude lower for VUV185 nm photolysis than VUV172 nm photolysis (Table 3.). The reason is probably the extreme inhomogeneity of the 172 nm irradiated aqueous solutions of organic substances.               O O O OHHOHO OOHO OO OH OHHOOHO OOHHO + + H2O  + O2 +   HO2  COU 7-HO-COU            COU 7-HO-COU 26th International Symposium on Analytical and Environmental Problems 78  Conclusion In this work, we compared the efficiencies of two VUV light sources, the low-pressure mercury vapor lamp (UV/VUV185nm) and the Xe-excimer lamp (VUV172nm). The H2O2 concentration formed in the 185 and 172 nm Milli-Q irradiated waters well reflects the almost 30-fold higher VUV photon flux of the Xe * -excimer lamp. The high photon flux and the low penetration depth of VUV light at 172 nm causes extreme inhomogeneity in VUV photolysis of an aqueous solution of organic matter. This inhomogeneity is the reason why the apparent quantum yield of the COU transformation is one order of magnitude lower in the 172 nm irradiated solution than with 185 nm irradiation.  Acknowledgements This publication was supported by the János Bolyai Research Scholarship of the Hungarian Academy of Sciences, and new national excellence program of the Ministry for Innovation and Technology (ÚNKP-20-5-SZTE-639 and ÚNKP-20-3-SZTE-459). The authors thanks the financial support from the project Hungarian Scientific Research Fund (NKFI contract number FK132742)   References  [1] Alapi, T. Schrantz., K.; Arany, E., Kozmér Zs., Chapter 3: Vacuum UV radiation-driven processes, in Advanced Oxidation Processes for Water Treatment, Editor: Stefan, M.I., 2017. IWA Publishing [2] Oppenländer, T., Photochemical Purification of Water and Air. 2003. Wiley-VCH, Weinheim [3] Weeks, J. L., Meaburn, G. M. A. C., Gordon, S., Radiation Research, 1963. 19(3), 559–567. [4] Heit, G.,  Braun, A. M., Water Sci. Technol., 1997. 35(4), 25–30. [5] Al-Gharabli, S., Engeßer, P., Gera, D., Klein, S., Oppenländer, T., Chemosphere, 2016. 144, 811–815. 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Xe-excimer lamp versus mercury vapor lamp - the comparison of the efficiency of 185 nm with 172 nm radiation, based on H2O2 formation and coumarin oxidation

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Xe-excimer lamp versus mercury vapor lamp - the comparison of the efficiency of 185 nm with 172 nm radiation, based on H2O2 formation and coumarin oxidation

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