8G. Lujanien_e et al. / <strong>Journal</strong> <strong>of</strong> <strong>Environmental</strong> <strong>Radioactivity</strong> xxx (2012) 1e10Fig. 8. An example <strong>of</strong> 72 h air mass backward trajectories ended at Vilnius sampling site at 19 UTC at 20, 500, 1000 m AGL on 29 January, 1997, on 06 June, 1999 and on 03 February,2001 for 4 analyzed sectors (modified after De Cort et al., 1998).239,240Pu,241Am, nBq/m350 239,240 Pu40302010241 Am137 Cs4321137Cs, µBq/m 3005 6 7 8 9 10 11 12 1 2 3 4 5 6 72005-2006Fig. 9. Activity concentrations <strong>of</strong> 239,240 Pu and 241 Am in monthly aerosol samples andmonthly average activity concentrations <strong>of</strong> 137 Cs in 2005e2006 in Vilnius.Fig. 10. Alfa-spectrum <strong>of</strong> Pu isotopes separated from aerosol samples collectedbetween 23 March and 15 April.Please cite this article in press as: Lujanien_e, G., et al., Radionuclides from the Fukushima accident in the air over Lithuania: measurement andmodelling approaches, <strong>Journal</strong> <strong>of</strong> <strong>Environmental</strong> <strong>Radioactivity</strong> (2012), doi:10.1016/j.jenvrad.2011.12.004
G. Lujanien_e et al. / <strong>Journal</strong> <strong>of</strong> <strong>Environmental</strong> <strong>Radioactivity</strong> xxx (2012) 1e10 9(Hirose and Sugimura, 1990). This is approximately the same levelas observed in the aerosol samples collected in Vilnius.The activity ratio <strong>of</strong> 238 Pu/ 239,240 Pu detected at the Fukushimasite was reported to be 2 (TEPCO, 2011). Assuming the backgroundratio equal to the global fallout determined on the basis <strong>of</strong> the longtermmeasurements at the Vilnius site (Lujanien_e et al., 2009) wecan estimate the contribution <strong>of</strong> the Fukushima plutonium bysimple calculations (Hirose and Sugimura, 1990) using thefollowing equation:Fð%Þ ¼100$ðR M R G Þ=ðR F R G Þwhere F is the Fukushima originated 239,240 Pu fraction, R M , R G and R Fare the measured, global fallout and Fukushima derived ratios <strong>of</strong>238 Pu/ 239,240 Pu, respectively. According to these estimations thecontribution <strong>of</strong> the Fukushima derived 239,240 Pu is 59% or 26.4nBq/m 3 .The mean activity concentration <strong>of</strong> 137 Cs found in Vilniusduring the studied period was 118 mBq/m 3 . The background 137 Csactivity concentration can be estimated from the sample collectedone week before the accident and it was 0.7 0.1 mBq/m 3 . Fromthese estimations the mean Fukushima originated 239,240 Pu/ 137 Csratio could be 2$10 4 . The activity ratio <strong>of</strong> 239,240 Pu/ 137 Cs in theChernobyl originated hot particles was 2$10 2 . A fractionationduring the long-distance transport may have resulted in thevariation <strong>of</strong> the ratio at different locations (Pöllänen et al., 1997;Hirose and Sugimura, 1990). Further analyses (ICPMS and AMS)are in progress, which will help to explain Pu origin in thissample.4. ConclusionsFrom the presented data on variations <strong>of</strong> activity concentrations<strong>of</strong> studied radionuclides, from the analyses <strong>of</strong> meteorologicalsituation, and on the basis <strong>of</strong> the modelling exercises we canconclude that the complicated air mass transport, different arrivaltime, arrival height and downward air mass transport resulted intwo maxima <strong>of</strong> 131 I and 137 Cs activity concentrations in the nearsurfaceatmosphere. An increase in the 131 I and 137 Cs activityconcentrations up to 3800 mBq/m 3 and up to 1070 mBq/m 3 wasobserved on 28 March e 1 April and up to 500 mBq/m 3 and up to1000 mBq/m 3 was found on 3e4 April, respectively. In addition to131 I and 137 Cs, traces <strong>of</strong> other radionuclides were detected, and 132 I,132 Te, 129 Te, 129m Te and 136 Cs among them. The comparison <strong>of</strong> theChernobyl and Fukushima accidents indicated the higher activityconcentration <strong>of</strong> radionuclides by 4 orders <strong>of</strong> magnitude anda broader spectrum <strong>of</strong> radionuclides in the Chernobyl plume ascompared to the Fukushima one. Large collected air volumesallowed us to determine for the first time in Europe the activityratio and concentration <strong>of</strong> Fukushima derived 238 Pu and 239,240 Puisotopes. Approximately twice higher Pu activity concentration asexpected, and 238 Pu/ 239,240 Pu ratio not typical either for globalfallout or the Chernobyl accident was found in the integratedaerosol sample.AcknowledgementsThis research was partially supported by the Structural Funds <strong>of</strong>EU - the Research and Development Operational Program fundedby the ERDF (project No. 26240220004). The authors thankstudents <strong>of</strong> the Chemical Department <strong>of</strong> the Vilnius University fortechnical assistance. The authors gratefully acknowledge theNOAA Air Resources Laboratory (ARL) for the provision <strong>of</strong> theREADY website (http://www.arl.noaa.gov/ready.php) used in thispublication.ReferencesAbe, T., Kosako, T., Komura, K., 2010. Relationship between variations <strong>of</strong> 7 Be, 210 Pband 212 Pb concentrations and sub-regional atmospheric transport: simultaneousobservation at distant locations. J. Environ. Radioact. 101, 113e121.Bolsunovsky, A., Dementyev, D., 2011. Evidence <strong>of</strong> the radioactive fallout in thecenter <strong>of</strong> Asia (Russia) following the Fukushima nuclear accident. J. Environ.Radioact. doi:10.1016/j.jenvrad.2011.06.007.Chino, M., Nakayama, H., Nagai, H., Terada, H., Katata, G., Yamazawa, H., 2011.Preliminary estimation <strong>of</strong> release amounts <strong>of</strong> 131 I and 137 Cs accidentally dischargedfrom the Fukushima Daiichi nuclear power plant into the atmosphere.J. Nucl. Sci. Technol. 48, 1129e1134.De Cort, M., Dubois, G., Fridman, Sh.D., Germenchuk, M.G., Izrael, Yu.A., Janssens, A.,Jones, A.R., Kelly, G.N., Kvasnikova, E.V., Matveenko, I.I., Nazarov, I.M.,Pokumeiko, Yu.M., Sitak, V.A., Stukin, E.D., Tabachny, L.Ya., Taturov, S.Yu.,Avdyushin, S.I., 1998. Atlas <strong>of</strong> Caesium Deposition on Europe after the ChernobylAccident European Commission report EUR16737, Luxembourg.Diaz Leon, J., Jaffe, D.A., Kaspar, J., Knecht, A., Miller, M.L., Robertson, R.G.H.,Schubert, A.G., 2011. Arrival time and magnitude <strong>of</strong> airborne fission productsfrom the Fukushima, Japan, reactor incident as measured in Seattle, WA, USA.J. Environ. Radioact. 102, 1032e1038.Draxler, R.R., Rolph, G.D., 2011. HYSPLIT (Hybrid Single-particle Lagrangian IntegratedTrajectoy). NOAA Air Resources Laboratory, Silver Spring, MD, USA.http://ready.arl.noaa.gov/HYSPLIT.php.Fushimi, K., Nakayama, S., Sakama, M., Sakaguchi, Y., 2011. Measurement <strong>of</strong> airborneradioactivity from the Fukushima reactor accident in Tokushima, Japan. J. Phys.Soc. Jpn. arXiv:1104.3611v2.Hirose, K., Sugimura, Y., 1990. Plutonium isotopes in the surface air in Japan: effect<strong>of</strong> chernobyl accident. J. Radioanal. Nucl. Chem. Articles 138, 127e138.Hu, Q.-H., Weng, J.-Q., Wang, J.-S., 2010. Sources <strong>of</strong> anthropogenic radionuclides inthe environment: a review. J. Envirom. Radioact. 101, 426e437.IAEA, 2006. <strong>Environmental</strong> Consequences <strong>of</strong> the Chernobyl Accident and TheirRemediation: Twenty Years <strong>of</strong> Experience. RARS, Vienna.IAEA, 2011. Briefing on Fukushima Nuclear Accident. www.iaea.org/newscenter/news/tsunamiupdate01.html/ 12 April 2011.Jordan, C.E., Dibb, J.E., Finkel, R.E., 2003. 10 Be/ 7 Be tracer <strong>of</strong> atmospheric transportand stratosphere-troposphere exchange. J. Geophys. Res. 108, 4234e4247.Koch, D.M., Jacob, D.J., Graustein, W.C., 1996. Vertical transport <strong>of</strong> troposphericaerosols as indicated by 7 Be and 210 Pb in a chemical tracer model. J. Geophys.Res. 101, 18,651e18,666.Kownacka, L., 2002. Vertical distributions <strong>of</strong> beryllium-7 and lead-210 in thetropospheric and lower stratospheric air. Nukleonika 47, 79e82.Land, C., Feichter, J., 2003. Stratosphereetroposphere exchange in a changingclimate simulated with the general circulation model MAECHAM4. J. Geophys.Res. 108, 8523e8532.Livingston, H.D., Povinec, P.P., 2002. Millennium perspective on the contribution <strong>of</strong>global fallout radionuclides to ocean science. Health Phys. 82, 656e668.Lozano, R.L., Hernández-Ceballos, M.A., Adame, J.A., Casas-Ruíz, M., Sorribas, M., SanMiguel, E.G., Bolívar, J.P., 2011. Radioactive impact <strong>of</strong> Fukushima accident on theIberian Peninsula: evolution and plume previous pathway. Environ. Int. 37,1259e1264.Lujanas, V., Lujanien_e, G., 2007. Application <strong>of</strong> cosmogenic radionuclides in ozonetracer studies. J. Radioanal. Nucl. Chem. 274, 287e291.Lujanas, V., Mastauskas, A., Lujaniene, G., Spirkauskaite, N., 1994. Development <strong>of</strong>radiation in Lithuania. J. Environ. Radioact. 23, 249e263.Lujanien_e, G., Aninkevicius, V., Lujanas, V., 2009. Artificial radionuclides in theatmosphere over Lithuania. J. Environ. Radioact. 100, 108e119.Lujanien_e, G., Sapolaite, J., Remeikis, V., Lujanas, V., Jermolajev, A., Aninkevicius, V.,2006. Cesium, americium and plutonium isotopes in ground level air <strong>of</strong> Vilnius.Czech. J. Physiol. 56 (Suppl. 4), D55eD61.Lujanien_e, G., Lujanas, V., Mastauskas, A., Ladygien_e, R., Ogorodnikov, B.L.,Stelingis, K., 1998. Influence <strong>of</strong> physico-chemical forms <strong>of</strong> radionuclides on theirmigration in the environment. Radiochim. Acta 82 (1), 305e310.Lujanien_e, G., 2000. Investigation <strong>of</strong> cosmogenic radionuclide carriers in theatmosphere. Czech. J. Phys. 50, 321e329.Lujanien_e, G., 2003. Study <strong>of</strong> removal processes <strong>of</strong> 7 Be and 137 Cs from the atmosphere.Czech. J. Phys. 53, A57eA65.Lujanien_e, G., Lujanas, V., Jankunait _e, D., Ogorodnikov, B.I., Mastauskas, A.,Ladygien_e, R., 1999. Speciation <strong>of</strong> radionuclides <strong>of</strong> the chernobyl origin inaerosol and soil samples. Czech. J. Phys. 49 (1), 107e112.Lujanien_e, G., Bycenkien_e, S., Sciglo, T., Povinec, P.P., Gera, M., Bartok, J., Gazák, M.,2011. Radionuclides from the Fukushima Accident in Europe e Modelling theAir Mass Transport. In: Proceedings FSKD 2011, vol. 4, 26-28 July, 2011,Shanghai, China, pp. 2775e2777.Lujanien_e, G., Ogorodnikov, B., Budyka, A., Skitovich, V., Lujanas, V., 1997.An investigation <strong>of</strong> changes in radionuclide carrier properties. Adv. Space. Res.35, 71e90.Manolopoulou, M., Vagena, E., Stoulos, S., Ioannidou, A., Papastefanou, C., 2011.Radioiodine and radiocesium in Thessaloniki, Northern Greece due to theFukushima nuclear accident. J. Environ. Radioact. 102, 796e797.Martin, J.M., Thomas, A.J., 1988. Anomalous concentrations <strong>of</strong> atmosphericplutonium-238 over Paris. J. Environ. Radioact. 7, 1e16.Masson, O., Baeza, A., Bieringer, J., Brudecki, K., Bucci, S., Cappai, M., Carvalho, F.P.,Connan, O., Cosma, C., Dalheimer, A., Didier, D., Depuydt, G., De Geer, L.E., DePlease cite this article in press as: Lujanien_e, G., et al., Radionuclides from the Fukushima accident in the air over Lithuania: measurement andmodelling approaches, <strong>Journal</strong> <strong>of</strong> <strong>Environmental</strong> <strong>Radioactivity</strong> (2012), doi:10.1016/j.jenvrad.2011.12.004