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Architecture and management of a geological repository - Andra

Architecture and management of a geological repository - Andra

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11 – Operational SafetyTable 11.1.1 Equivalent dose rate in contact with primary packages [3]Type <strong>of</strong> packageNature <strong>of</strong> contentsMaximum EDR 152 incontact with the primarypackage (Sv.h -1 )B1, B7.2 Compacted activation products 25B2 Bituminised waste 2B3, B7.1,B7.3, B8Compacted or cemented technological waste 0.5B B4 Cemented cladding waste 0.5B5Compacted cladding waste with or withouttechnological waste15B6Cladding waste <strong>and</strong> technological waste indrums2C0C0 Vitrified waste 150Other C Vitrified waste 250CU1 (UOx) Spent fuel assembly 25SF CU2 (MOx) Spent fuel assembly 15CU3 Spent fuel 150• Internal exposureExposure through inhalation is associated, on the one h<strong>and</strong>, with radioactive gases <strong>and</strong> aerosolsemitted by some B waste packages between their reception at surface installations <strong>and</strong> subsequentemplacement in the disposal cell, <strong>and</strong> on the other, with radon gas emitted naturally by the <strong>geological</strong>environment into the drifts <strong>of</strong> the underground installations.Radioactive gases emitted by the packagesSome packages contain traces <strong>of</strong> radioactive gases. Measures to reduce the release <strong>of</strong> these gases werepresented in Chapter 4. However, these measures do not apply to packages that also generate hydrogendue to radiolysis (B2 <strong>and</strong> B5.1 waste packages). For B5.1 reference packages, the most pessimisticcase, the adopted release rates (in becquerels per hour <strong>and</strong> by primary package) are roughly 400 fortritium, 14 for carbon <strong>and</strong> 7,000 for krypton 85.Radon gas emitted by the rock in the underground installationsThe radon exhalation rate from the rock varies according to various factors such as : ventilation <strong>and</strong>nature <strong>of</strong> drift lining. At this stage, the value used corresponds to the average value observed inFrance.11.1.2.2 Dosimetric evaluationThe dosimetric evaluation [107] is carried out for each type <strong>of</strong> work station identified on the disposalsite <strong>and</strong> for the public around the periphery <strong>of</strong> the site.• Dosimetric evaluation for personnel operating in nuclear installationsThe results are presented by distinguishing between the different work stations in the surface <strong>and</strong>underground installations (cf. Table 11.1.2).152 In the case <strong>of</strong> slightly or highly exothermic packages, the values given here correspond to a packages with an age <strong>of</strong> 5 years in the case<strong>of</strong> B1 packages, 10 years for B5 <strong>and</strong> SF3 packages, 20 years for C0, 60 to 70 years for SF1 (UOx) <strong>and</strong> 90 years for SF2 (MOx).DOSSIER 2005 ARGILE -ARCHITECTURE AND MANAGEMENT OF A GEOLOGICAL DISPOSAL SYSTEM439/495

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