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Radionuclides concentrations in the Loire river system resulting from routine discharges of five nuclear power plants: assessment of dose to man*

Published online by Cambridge University Press:  17 June 2005

F. Siclet
Affiliation:
EDF, R&D, Laboratoire national d'hydraulique et environnement, 6 quai Watier, 78401 Chatou, France
M. Luck
Affiliation:
EDF, R&D, Laboratoire national d'hydraulique et environnement, 6 quai Watier, 78401 Chatou, France
J. G. Le Dortz
Affiliation:
EDF, R&D, Laboratoire national d'hydraulique et environnement, 6 quai Watier, 78401 Chatou, France
C. Damois
Affiliation:
EDF, R&D, Laboratoire national d'hydraulique et environnement, 6 quai Watier, 78401 Chatou, France
P. Ciffroy
Affiliation:
EDF, R&D, Laboratoire national d'hydraulique et environnement, 6 quai Watier, 78401 Chatou, France
F. Hendrickx
Affiliation:
EDF, R&D, Laboratoire national d'hydraulique et environnement, 6 quai Watier, 78401 Chatou, France
J. R. Courivaud
Affiliation:
EDF, R&D, Laboratoire national d'hydraulique et environnement, 6 quai Watier, 78401 Chatou, France
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Abstract

Low level radioactive liquid discharges have been carried out in the Loire river since 1963. Since then, the number of power plants located on the Loire river and its tributaries has been steadily increasing to reach, in the year 2000, 14 reactors operating on 5 different sites. The question arose to evaluate to what extent the addition of several nuclear power plants on the same river system could increase the concentrations in radionuclides in the environment and affect the dose to the public. To address this issue, EDF initiated in 1998 the “Loire river and estuary radioecology” program with the focus on assessing possible accumulation of radionuclide in river bottom sediments or on river shores. The following radionuclides were considered because of their importance in power plant liquid discharges: tritium, 14C, 58Co, 60Co, $^{110{\rm m}}$Ag, 134Cs, 137Cs, 54Mn, 124Sb, and 131I. Radionuclide concentrations in the dissolved, particulate and sedimentary forms were evaluated using the CRESCENDO model. The development and validation of this model required a multi-step process. The first step was to design a 350-km long 1D hydraulic and water transport based on currently available tools and data. Next, daily tritium concentrations measured in Angers, at the downstream limit of the river, were compared with computed values. The following step was to calibrate the sediment transport model. Areas where fine particles settled (dams and river shores) were monitored to improve our understanding of sediment dynamics. Then equations representing radionuclide exchange between water and particles were derived from laboratory experiments and included in the model. After each step the computed values were compared to measure data sets to ensure the model adequately described the processes involved. In the final step, the CALVADOS model was used to calculate dose to the public at different locations along the Loire river.

Type
Research Article
Copyright
© EDP Sciences, 2002

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References

* Cet article accompagnait le poster présenté au congrès “ The Radioecology-Ecotoxicology of Continental and Estuarine Environments, ECORAD 2001 ” édité par F. Bréchignac. Suite à une erreur, cet article n'a pas été intégré dans les actes du colloque (Radioprotection-colloques, volume 37, C1). Nous le reproduisons donc ici dans son intégralité, avec nos excuses aux auteurs.