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WG8 Biota modelling: Further development of transfer and exposure - - PowerPoint PPT Presentation
WG8 Biota modelling: Further development of transfer and exposure - - PowerPoint PPT Presentation
MODARIA WG8 Biota modelling: Further development of transfer and exposure models and application to scenarios Objectives ........ to improve Member States assessment capabilities for protection of the environment by comparing, improving
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Why?
- Revised BSS –assessment of radiological
environmental impact
- Revised ICRP Recommendations & RAP
Framework developments
- Available models are relatively new and
being developed
- Various national initiatives
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What did EMRAS I & II WG’s achieve?
- Demonstrated that the dosimetric components
(DCC) of commonly used models give generally comparable estimates of dose when assume homogenous distribution in organism and media.
- But not the transfer components – predictions of
- rganisms equilibrium activity concentrations
vary by orders of magnitude
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Scenario applications
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Perch Lake (Chalk River Canada)
- Models validated using
laboratory data performed relatively poorly
- Models using water
chemistry in transfer prediction performed relatively well
- Predictions for
mammals/heptofaua poor
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Perch Lake (Chalk River Canada)
- Models validated using
laboratory data performed relatively poorly
- Models using water
chemistry in transfer prediction performed relatively well
- Predictions for
mammals/heptofaua poor
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Chernobyl Exclusion Zone
- Orders of magnitude
variation in predicted
- rganism concentrations
- External dose predictions
reasonable (TLDs on small mammals)
- Importance of correct
parametersation of diet in foodchain models
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Chernobyl Exclusion Zone
- Orders of magnitude
variation in predicted
- rganism concentrations
- External dose predictions
reasonable (TLDs on small mammals)
- Importance of correct
parametersation of diet in foodchain models
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Little Forest Burial Ground
- How to address ‘unusual’
exposure scenarios (tree growing on waste trenches)
- Progeny assumptions
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Beaverlodge Lake
- Progeny assumptions
- Data gaps
- Recommendations on
monitoring programmes (organisms and radionuclides)
- Heterogeneous media
distribution
- Uncertainty of Kd
- ‘Consensus approach’
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‘Wetland’
- Perhaps surprisingly little
variation in organism activity concs (draft wildlife TRS available)
- Assumptions of diet source
(aquatic or terrestrial)
- External dose - correction (or
not) of soil moisture content
- First model-data comparison of
C-14 specific activity approaches for wildlife
1 10 100 1000 10000 100000
Trees Snakes Frogs Insects Peat moss Small plants Rodents
14C (Bq/kg f.w.)Erica (eriss/ARPANSA) Erica (ANSTO) Erica (CEH) Erica (SCK) RESRAD-Biota K-Biota Measured
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‘Benefits’
- Realisation of need to compile transfer
parameters (CR) for wildlife (EMRAS II WG)
– used for draft IAEA TRS on wildlife CR values and ICRP-114
- Various model improvements/identification
- f limitations
- Training
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MODARIA – potential activities
- Scenario applications
– those to date relatively simplistic – concentrated on model-data comparisons and not application to assessments – How integrate with human assessments
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MODARIA – potential activities
- Training
– best practice guidance (linked to scenarios)
- Non-equilibrium conditions (EMRAS II review)
– Identify scenarios (source terms/radionuclides) where dynamic models may be required – Scenarios testing using existing models/adapt human assessment models (compare to equilibrium assumptions) – How interpret results?
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MODARIA – potential activities
- ‘Dosimetry’
– Heterogeneous distribution in environment – Heterogeneous distribution in organism (other
- n-going activities?)
– Plant geometetries
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Interactions with other WG
- Integration human-wildlife assessment
- Effects group (interpretation of dynamic
models, heterogeneous distribution activities)
- Developments for ‘Radioecology data’ WG
(inc. application of outputs) feedback limitations/scenario applications
- Scenario sharing (marine, legacy, routine