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Annual Report for 2010/11 and Forward Programme - Sellafield Ltd

Annual Report for 2010/11 and Forward Programme - Sellafield Ltd

Annual Report for 2010/11 and Forward Programme - Sellafield Ltd

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SSEM/20<strong>11</strong>/4730 June 20<strong>11</strong>The data used <strong>for</strong> this initial assessment were limited to <strong>Sellafield</strong> beach areas because findrates at other beaches were too low <strong>for</strong> meaningful analysis, but supports the hypothesis thatrepopulation is significant <strong>for</strong> the <strong>Sellafield</strong> area <strong>for</strong> alpha-rich finds. Linking this conclusion tothe low interchange rate between the beach <strong>and</strong> sub-sea proposed earlier would suggestthat finds are predominately moved around from other areas of the beach by tidal action.Further work is planned on automating the GIS overlap assessment tool to help refine thisconclusion.Two reports have been received on statistical techniques that can be employed <strong>for</strong> theanalysis of beach monitoring data. The first report (Scott <strong>and</strong> Tyler, 20<strong>11</strong>a) givestechniques that can be employed to characterise beach finds <strong>and</strong> the second (Scott <strong>and</strong>Tyler, 20<strong>11</strong>b) gives guidance on the best 'statistical' monitoring system <strong>for</strong> future beachmonitoring programmes. The reports' recommendations <strong>and</strong> the initial SL response aregiven in the Table 3.17 <strong>and</strong> Table 3.18 below.Table 3.17. Statistical techniques report recommendations.Recommendations1 Systematic sampling areas required. The spatialheterogeneity of particle distribution may begoverned by sedimentological processes ofbeach accretion/erosion <strong>and</strong> particle selectivitythrough systematic processes of sorting (or lackof) of grain size. Non systematic sampling ofbeaches may lead to bias in the estimatedparticle density. In reporting the sampling ef<strong>for</strong>t,<strong>and</strong> to provide a basis <strong>for</strong> assessing thesystematic coverage of monitoring, it is importantthat the monitoring ef<strong>for</strong>t be reported as afootprint <strong>and</strong> as a proportion of the total availablearea on the beach. Comparison of successivefootprints will provide a basis <strong>for</strong> assessingsystematic coverage, i.e. contiguous areas arecovered <strong>and</strong> the frequency with which areas ofthe beach are sampled.2 Systematic temporal sampling of beachesrequired. The temporal heterogeneity of theparticle population may change with time,specifically the seasonality of tidal <strong>and</strong> waveenergy. Estimating particle density without atemporal perspective may result in an under oroverestimate in particle abundance.SL initial responseThe current reporting system is based on analpha-rich find footprint (i.e. it is judged thatthe 5cm to 10 cm turnover of s<strong>and</strong> over asingle tide will provide fresh area with respectto monitoring <strong>for</strong> 241 Am; which has a limit ofdetection of 1E+05 Bq at 5 cm depth). Thisrecommendation will be reviewed with respectto reporting radionuclide specific footprintsover radionuclide specific monitoring periods.There is little evidence of a seasonal affect inthe current data. The 20<strong>11</strong>/12 monitoringprogramme includes repeat areas <strong>for</strong><strong>Sellafield</strong>, St Bees, Braystones <strong>and</strong> Seascalebeaches. <strong>Sellafield</strong> beach, which isprogrammed <strong>for</strong> the most frequent monitoring<strong>and</strong> has the highest find rates, will providedata that should enhance the seasonalassessment capability. The repeat monitoringat St Bees (x5), Braystones (x3) <strong>and</strong> Seascale(x3) will provide additional supporting data.Future monitoring programmes will takeaccount of any seasonal affects found.© Nuclear Decommissioning Authority 20<strong>11</strong>. 59

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