1 / 29

Screening tier comparisons

Screening tier comparisons. ERICA, RESRAD-BIOTA & EA R&D128 Follow-up actions from Vienna workshop. Vienna scenario. Comparison of the three openly available models – RESRAD-BIOTA, ERICA-Tool & EA R&D128 River receiving mixed radionuclide discharges from multiple sources. Results.

elvinar
Download Presentation

Screening tier comparisons

An Image/Link below is provided (as is) to download presentation Download Policy: Content on the Website is provided to you AS IS for your information and personal use and may not be sold / licensed / shared on other websites without getting consent from its author. Content is provided to you AS IS for your information and personal use only. Download presentation by click this link. While downloading, if for some reason you are not able to download a presentation, the publisher may have deleted the file from their server. During download, if you can't get a presentation, the file might be deleted by the publisher.

E N D

Presentation Transcript


  1. Screening tier comparisons ERICA, RESRAD-BIOTA & EA R&D128 Follow-up actions from Vienna workshop

  2. Vienna scenario • Comparison of the three openly available models – RESRAD-BIOTA, ERICA-Tool & EA R&D128 • River receiving mixed radionuclide discharges from multiple sources

  3. Results • ERICA – highest dose rate (circa E3 µGy/h) predicted for insect larvae dominated by 234Th • R&D128 – highest dose rate (circa E3 µGy/h) predicted for amphibian dominated by 239Pu • RESRAD-BIOTA – 137Cs was the only nuclide to result in a risk quotient (RQ) in excess of 1 (for riparian animal)

  4. Decision to further compare the screening tiers of the three models – 1 Bq per unit media model runs • Associated ‘request’: can PROTECT establish the degree of conservatism ?

  5. Screening tiers – similarities/differences(where we think the conservatism is) • Comparison of outputs

  6. ERICA-Tool - Tier 1 • Recommends enter maximum media activity concentration • 95th percentile environmental media concentration limits (EMCLs) predicted using default transfer parameters pdfs (conservative habitat assumption) • 10 µGy h-1 • 40 µGy h-1 terrestrial animals / 400 µGy h-1 plants and all aquatic organisms • Risk quotients reported for most limiting organism (and media) for each radionuclide and for ecosystem

  7. ERICA-Tool Tier 1 result

  8. EMCL for water – takes into account external exposure from sediment (kd) or water and internal exposure estimated from water conc. using CR EMCL for sediment - takes into account external exposure from sediment or water (kd) and internal exposure estimated from water conc. (kd) using CR ERICA EMCLs Freshwater EMCLs Cd-109 Sediment = 2.61E4 Bq/kg Water = 51 Bq/l Cs-137 Sediment = 8000 Bq/kg Water = 5.1E-2 Bq/l

  9. ERICA EMCLs

  10. ERICA Tier 2 • Organism specific dose rates and RQs (from total predicted dose rate) reported: • Best estimate • Conservative estimate • Conservative dose estimated by applying uncertainty factor (UF) to the best estimate, where: • UF 3 ≈ 95th percentile prediction • UF 5 ≈ 99th percentile prediction

  11. ERICA Tier 2

  12. ERICA Tier 2 • In theory conservative estimate with UF=3 should approximate to Tier 1 result [with same input] and Tier 3 95th percentile prediction • Generally works: some case where it does not for aquatic ecosystems if input to sediment

  13. A thought on UF =3 Cs-137 BWG Chernobyl

  14. RESAD-BIOTA (USDOE) Tier 1 • Recommend enter maximum media activity concentration • Media activity concentrations compared to biota concentration guidelines (BCG): • Infinitely large/small geometries assumed • 100 % in soil; sediment-water interface • Conservative CR (BiV) values (not kd) • 1 mGy/d (40 µGy h-1) terrestrial & riparian animals / 10 mGy/d (400 µGy h-1 ) terrestrial plants & aquatic animals • More limited range of organisms considered than ERICA (which includes e.g. planktons, lichen which tend to have ‘high exposure’ estimates)

  15. RESRAD-BIOTA Tier 1 CRs • Aquatic animals – maximum • Predominantly taken from Till & Meyer 1983 maximum of the 84th %ile from collated data for fish, mollusc or crustacean • Terrestrial plants – maximums • Predominantly taken from Till & Meyer 1983 considers food crops, forage & grass • Terrestrial/Riparian animals – most derived using kinetic-allometric approach – 95th %ile

  16. BGCs • Terrestrial - Soil & water • Aquatic & Riparian - Sediment & water

  17. BGCs • Aquatic animals • Sediment - External exposure from sediment • Water – Internal & external exposure from water • Riparian animals • Sediment – Internal & external exposure from sediment • Water – Internal & external exposure from water • Terrestrial animals • Soil - Internal & external exposure from soil • Water - Internal & external exposure from water • Terrestrial plants • Soil - Internal & external exposure from soil • Water - External exposure from water

  18. EA R&D128 - screening • As applied – maximum inputs • Compares results to 5 µGy h-1 for screening (40 µGy h-1 action level) • Default transfer parameters used • Some transfer values are highly conservative

  19. Screening tier predictions • Assuming 1 Bq soil/water/sediment • Against 40/400 µGy h-1 • Terrestrial – freshwater only [RESRAD-BIOTA does not consider marine] • Radionuclides common to RESRAD-BIOTA & ERICA-Tool • Not H-3 & C-14 for terrestrial: RESRAD-BCGs for soil; ERICA EMCL for air • Compared as RQs

  20. Terrestrial RESRAD-BIOTA & ERICA-Tool + EA R&D128

  21. Terrestrial – EA 5 µGy h-1

  22. RQ Min/Max > 10

  23. Freshwater – input to water

  24. ERICA kd’s often comparatively high RQ Min/Max > 10

  25. Freshwater – input to sediment

  26. RQ Min/Max > 10

  27. Comment • Used in basic screening assessments (their envisaged main use) the readily available models can give widely differing results • (yet again) predominantly explained by transfer elements

More Related