Sekine  T.

Tagami  K.

Uchida  S.

English

紀要類 (bulletin)departmental bulletin pape

Tagami, K.

Uchida, S.

Sekine, T.

Tohoku University Repository (TOUR) / 東北大学機関リポジトリ

Transfer Factors of Technetium-99 for VariousPlants in Forests著者 Tagami  K., Uchida  S., Sekine  T.journal orpublication titleCYRIC annual reportvolume 2005page range 93-97year 2005URL http://hdl.handle.net/10097/50324CYRIC Annual Report 2005    V. 6.  Transfer Factors of Technetium-99 for Various Plants in Forests    Tagami K.1, Uchida S.1, and Sekine T2.  1Environmental and Toxicological Sciences Research Group, National Institute of Radiological Sciences 2Center for the Advancement of High Education, Tohoku University    Introduction Technetium belongs to the Mn group and it has no stable isotopes.  Among its radioactive isotopes, 99Tc is of potential long-term importance in the environment, because 99Tc is a pure beta emitter (Emax=0.29 keV) and its half-life is 2.11 x 105 y.  It is produced in the fissions of 235U and 239Pu at relatively high ratios of ca. 6%, which is similar to the values for 137Cs and 90Sr.  Technetium-99 is widely distributed in the environment as a result of fallout from nuclear weapons testing and discharges from nuclear facilities.  The quantity of 99Tc produced by atmospheric nuclear weapon explosions was estimated to be 140 TBq using an equal fission yield to that of 137Cs and actual 137Cs deposition data1).  The release of 99Tc by nuclear industries through 1986, as estimated by Luykx2), was of the order of 1000 TBq.  This was mainly from nuclear fuel reprocessing and most of the 99Tc was discharged into the sea and 99Tc concentration in the terrestrial environment is very low3).  The amount introduced via nuclear medical use of 99mTc (half-life: 6.01 h) is negligible.  For example, the amounts from 99Mo-99mTc generators and 99mTc used during 2004 in Japan were 173 TBq and 325 TBq, respectively4), which corresponds to ca. 1.6 MBq of 99Tc generation in total.  Due to very low concentration and analytical difficulties for determination of 99Tc in environmental samples, there is a general lack of data on the levels in the literature. Therefore, the behavior of 99Tc in the terrestrial environment is not well understood. However, it is necessary to obtain transfer parameters under natural conditions for a realistic long-term radiological assessment such as soil-to-plant transfer factors (TFs, concentration in plant/concentration in soil).  Thus, we focused on the Chernobyl site where 99Tc concentration levels have already been shown to be higher than those from global fallout Tc5).  The concentrations of 99Tc in plant leaves collected in three forests  93near the Chernobyl site were determined.  The samples were leaves of raspberry, strawberry and pink plants, black alder, birch, cowberry and oak trees, and ferns.  Since TFs are usually high in leafy vegetables and grass as reported in Reference 6, leaves of raspberry, strawberry and pink plants are of the most interest in this study for comparison purposes.  Experimental A Tc-selective chromatographic resin (Eichrom Industries Inc., TEVA resin) was used for Tc purification.  Deionized water (>17.6 MΩ) was used throughout the work. Technetium-95m, which was obtained from an Nb foil using the reaction 93Nb (a, 2n) 95mTc, was applied to determine the recovery of 99Tc in the samples during the chemical separation procedure.  The 95mTc was made at Cycrotron and Radioisotope Center, Tohoku University6).  A standard 99Tc solution available from Amersham (Solution TCZ.44) was used for calibrating the ICP-MS. Leaves of 27 plant samples were collected at the Chernobyl site in 1994 and 1995 by the Federal Office for Radiation Protection, Germany, assisted by Moscow State University, Russia, and the Research and Industrial Association 'Pripyat', Ukraine.  The sampling was carried out in three forests, D1, D3 and K2, around the Chernobyl Nuclear Power Plant.  Forests D1 and D3 were 28.5 km and 26 km to the south of the reactor, respectively, while forest K2 was 6 km to the southeast. Soil samples were also collected at the same sampling sites and the details were reported previously5).  A simple wet digestion method in combination with an TEVA resin separation method was applied for 99Tc.  After incineration of the soil samples at 450˚C, a certain amount of 95mTc was added and they were mixed uniformly.  Then, Tc was extracted with 4M HNO3 while heating the samples at 100˚C in a glass beaker covered with a watch glass. The residue was removed by filtration and the solution was diluted to obtain the acidity of ca. 0.1M HNO3 and passed through a TEVA resin column to purify and concentrate Tc isotopes.  Technetium adsorbed on the resin was eluted with 5 mL of 8 M HNO3 solution. The volume of the 99Tc fraction from the TEVA column solution was reduced to near dryness (<70˚C) and then dissolved in 5mL of 2% HNO3 solution. Radiochemical recoveries of Tc plant samples were monitored with 95mTc activities.  Then the solution was introduced into an ICP-MS (Yokogawa, PMS-2000).   94Results and Discussion Total chemical recoveries throughout the method with 95mTc ranged from 0.48 to 0.92 with an average of 0.76.  No relation was found between sample amount and recovery.  Three replicates of samples K2-94F-1 and D3-94G-1 were used in amounts of 1 - 2.6 g and 1.8 - 10.2 g, respectively, and there were no differences between their recoveries.  However, the recoveries of two sub-samples of K2-94G-2 and D1-94G-1 differed by about 0.1 and 0.2, respectively; when sample amounts increased, the recoveries decreased. Possibly, plant matrices, such as K, Ca and Cl, would affect the 99Tc recovery, especially at the TEVA resin separation steps. Technetium-99 concentrations in all samples are listed in Table 1 and they ranged from <0.006 to 6.0 mBq g-1. For 11 samples, especially in the tree group, it was hard to determine 99Tc, because of its low concentration. TF is defined as the ratio of activity concentration in plant (in Bq g-1 dry weight (DW)) to activity concentration in soil (in Bq g-1 DW).  It has been noted that forest under story plants are expected to take up radionuclides mainly from organic layers and therefore, concentration of 99Tc in organic soil would be important for estimation of its uptake.  Thus, TFs were calculated in terms of activity concentration in a plant relative to activity concentration in organic soil.  Table 1 also shows the TFs of Tc for all the samples.  They ranged from <0.016 to 0.28 for Fern, 0.009 to 0.47 for Herb and <0.006 to 0.05 for Tree groups based on the 99Tc contents of the organic layers.  The highest TF was found in the leaves of raspberry.  The observed-TFs were lower than the IAEA-compiled values of 8.1 - 2600 for leafy vegetables, fodder and grass7); other reported values are as listed in Table 2. Comparing the TF for Tc reported for various plants grown in soil, the present results were almost the same as the data observed in reclaimed land10), although the data from pot experiments11) were much higher. From these results, we concluded Tc bioavailability in the natural environment would be lower than the bioavailabilities obtained from laboratory studies that used TcO4- to obtain Tc TFs.  It is known that the most plant-available form of Tc is TcO4-, and other forms have less availability to plants.  Thus, TcO4- was not the only Tc chemical from in these forests.  Possibly most Tc was in less soluble form, such as organically bound forms, sesquioxide bound and lower oxidation forms12).  Concerning the Herb group, the TFs were 0.17-0.47 at K2, 0.20-0.32 at D1 and 0.009-0.086 at D3.  The TFs for the samples collected at D3 were lower than those at D1 and K2.  This might be due to the fact that D3 was a so-called wet forest and reducing  95conditions might possibly exist.  The bioavailable Tc was presumably influenced by the soil redox conditions: Tc would be transformed from to a lower oxidation and less available form under a relatively low redox condition.  Due to the relatively low redox conditions of the D3 site, the TFs were lower than those in K2 and D1 sites. Thus, the low TFs we observed in this study implied that 8-9 years after 99Tc release from the Chernobyl Nuclear Power Plant, Tc should have been transformed to insoluble or less plant-available forms.  Technetium would not be in readily available form to plants in the natural environment.   References  1) Aarkrog A., Dahlgaard H., Hallstadius L., Holm E., Mattson S., Rioseco J., Technetium in the Environment (Desmet G. and Myttenaere C. eds.), Elsevier Appl. Sci. Pub., London (1986) 69. 2) Luykx F., Technetium in the Environment (Desmet G. and Myttenaere C. eds.), Elsevier Appl. Sci. Pub., London (1986) 21. 3) Tagami K., Uchida S., J. Nucl. Radiochem. Sci. 3 (2002) 1. 4) Japan Isotope Association, Statistics on the Use of Radiation in Japan (2005) 38. 5) Uchida S., Tagami K., Wirth E., Rühm W., Chemosphere 39 (1999) 2757. 6) Sekine T., Konishi M., Kudo H., Tagami K., Uchida S., J. Radioanal. Nucl. Chem. 239 (1999) 483. 7) IAEA, Handbook of Parameter Values for the Prediction of Radionuclide Transfer in Temperate Environments, Technical Reports Series No. 364. IAEA, Vienna, (1994) 14. 8) Vandecasteele C.M., Dehut J.P., Van Laer S., Deprins D., Myttenaere C., Health Phys. 57 (1989) 247. 9) Hoffman F.O., Garten C.T., Jr., Lucas D.M., Huckabee J.W., Environ. Sci. Technol. 16 (1982) 214. 10) Green N., Wilkins B.T., Davidson M.F., Hammond D.J., J. Environ. Radioactiv. 27 (1995) 35. 11) Echevarria G., Morel J.L., Florentin L., Leclerc-Cessac, E. J. Environ. Radioact. 70 (2003) 85. 12) Tagami K., Uchida S., Toxicol. Environ. Chem. 56 (1996) 235.    96Table 1.  Chemical recovery of 95mTc, concentration of 99Tc and transfer factor in plant samples  collected in forests within the 30-km zone around the Chernobyl Nuclear Power Plant.   Plant type Place  Tc-95m RecoveryTc-99 mBq g-1 dry  Transfer factor Fern K2 94Fern-1a 0.847 2.42 ± 0.18     94Fern-1b 0.895 2.37 ± 0.29     94Fern-1c 0.884 2.31 ± 0.26 0.276 ±0.019   95Fern-1 0.829 0.603 ± 0.045 0.045 ±0.003   95Fern-2 0.749 3.79 ± 0.35 0.283 ±0.026  D3 94Fern-1 0.661 < 0.040  < 0.016    95Fern-2 0.483 < 0.031  < 0.018    95Fern-3 0.844 < 0.069  < 0.040  Glass K2 94Glass-1 0.599 4.04 ± 0.42 0.470 ±0.051   94Glass-2a 0.747 1.30 ± 0.17     94Glass-2b 0.852 1.57 ± 0.16 0.168 ±0.015   95Glass-1 0.739 6.02 ± 0.52 0.450 ±0.039   95Glass-2 0.762 3.61 ± 0.33 0.269 ±0.025  D1 94Glass-1a 0.596 0.254 ± 0.022     94Glass-1b 0.824 0.451 ± 0.090 0.318 ±0.042   94Glass-2 0.563 0.222 ± 0.017 0.200 ±0.015   95Glass-1 0.901 0.257 ± 0.021 0.231 ±0.019  D3 94Glass-1 0.868 0.215 ± 0.016 0.092 ±0.006   94Glass-2 0.706 0.094 ± 0.008 0.039 ±0.003   94Glass-3 0.553 0.128 ± 0.011 0.053 ±0.004   95Glass-1 0.915 0.016 ± 0.003 0.009 ±0.002 Tree D1 94Tree-1 0.898 < 0.006  < 0.006    95Tree-1 0.883 0.013 ± 0.001 0.012 ±0.001  D3 94Tree-1 0.878 < 0.035  < 0.014    94Tree-2 0.652 < 0.040  < 0.016    94Tree-3 0.850 < 0.056  < 0.023    94Tree-4 0.633 < 0.028  < 0.011    95Tree-1 0.685 < 0.028  < 0.016    95Tree-2 0.543 < 0.023  < 0.013    95Tree-3 0.856 < 0.028  < 0.016    95Tree-4 0.843 0.094 ± 0.011 0.055 ±0.007   Table 2.  Transfer factors for Tc reported for various plants grown in soil. Crop TF Conditions Reference Grass pasture mixture 6 Lysimeter 8 Herbaceous vegetation 6.7-22 Silt loam, Field 9 Grass 0.91-3.02 Reclaimed land, Field 10 Rye grass 44-371 Cambisol, Pot 11 Herbaceous vegetation 0.009-0.47 Podzol, Peat-gley, Field This study   97

Transfer Factors of Technetium-99 for Various Plants in Forests

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Transfer Factors of Technetium-99 for Various Plants in Forests

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