dc.description.abstract |
An attempt has been made in the work to assess the radiological consequences due to
the deposition of lJ7es and Illr on ground, planl, milk and meat Emphasis on the
determination oflhe migration parameters oflhesc radionuclides has been given in the
present work. The migration parameters e.g., mainly the transfer factors (TFs) and
distribution coefficients (1<.0)of 1J1eshave been investigated using the soil of the
AERE campus. The IF values of ])'1 have been taken from the literatures. TFs of
1l1es have been measured both in pot and field experiments and compared with the
calculated results using Absalom model. In the pol experiment, TF values were
measured for the main foodstuffs in Bangladesh such as leafy vegetables (LaIshak,
Palangshak), Ladyfinger, Radish, Potato, Potato Plant, Paddy, Paddy plant, Grass,
Ginger, Ginger plant, Turmeric, and Tunneric plant by pot experiments grown in the
AERE soil. IF values of the leafy parts and products of the corresponding plants were
found to lie within the range of2.02 x 10-1 to 1.8 x 10'2, whieh compares well with
literature values. 11has been observed that the TF values in the leafy part of the plants
are higher than the products. II' values of 137CS measured by field experiment for the
leafy plants grown in the contaminated land within the AERE campus were found to
lie within the range of 2, 7 x 10.2 to 4.7 x 10-2,which are again in agreement with the
literature and also with the measured values by pot experiment. Soil characteristics
have also been investigated to assist the measured values of the corresponding
radionuelide with the prediction of Absalom model which considered pH, organic
maller content, exchangeable K" and clay content as input model parameter. The
calculated values compares well with the measured values for pot and field
experiments.
Ko defined as the ratio of concentration of a radionuclide absorbed in solid phase to
the concentration of that radionuclide left in liquid phase were found to be 2327, 591,
209, 78, and 84 mVgm at depths 0-5, 20-25, 45-60, 90-115, and 150-175 It
respectively using batch method.
vii
The source term and release rate for the above mentioned radionuc1ides as well as
Gaussian diffusion factor and diffusion ,coefficients as a function of downwind
distance have also been investigated. The maximum air concentratIOn has been
estimated to identify downwind distance that was found to be 100 m from the core of
the reactor. Then the ground concentration, concentration in vegetation, milk and
meat as well as probable doses to human population through ground deposition,
ingestion of vegetation, milk and meat for the above-mentioned radionuc1ides have'
also been estimated. The maximum dose due to 1l11,'J7Cs and both (1J1r+IJ)CS) for all
pathway summed were found to be 26.379, 0.0280 and 26.407 I-lSvfhr respectively.
The maximum dose due to IJ7CSwas within the background limit (0.30 flSvihr) but
the maximum dose due to tJlr was higher. However, the dose due to Ill! (t'l2 = 8.04
days) will be reduced to background level within ten half-lives (;=.80days).
Vegetation was found to be the dominant contributor both for "'I and IJ7Cs (- 90%)
compared to other pathways. Contribution of Ill1 in milk is higher (7%) than the
contribution of mCs (3%) while the contribution of l)7Cs in meat is higher (5%) than
that of "lr (2%). For both tJlr and 1l7CSthe contribution from ground deposition is
almost negligible (1%) compared to vegetation.
The measured site characterization data can be used as a reference database while
predicting the migration behavior of radionuc1ides through various media around
AERE campus. Radionuclidc concentration and probable dose assessment of the
human population living in the vicinity of the 3 MW reactor site could be utilized to
comply with the regulatory requirements. This study can ultimately be used to
determine the radiological protective measures, which might be required to ensure the
safety of the human population living in the vicinity ofthe reactor site . |
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