Title: Regulations the Netherlands for regular discharges of radioactivity (aquatic environment)
1Regulations the Netherlands for regular
discharges of radioactivity (aquatic environment)
- R. Heling
- NRG-Arnhem
- The Netherlands
2Hydrological ModelsRelevance
- Application
- Nuclear accidents
- Regular discharges
- Relevance
- dosisbelasting niet verwaarloosbaar maar niet
cruciaal in reguliere situaties, in
ongevalssituaties perceptie van het risico een
probleem
3Type of modelling
- Runoff, Transport land-to-water
- Transport in rivers
- Transport in estuaries en coastal regions
- Transport in reservoirs en lakes
- Transport in groundwater
4Different kind of models (1)
- Hydrodynamics
- Transport of radionuclides
- Near- field to far field modelling
- Modelling of short, middle, and long-term
5Aquatic model and type (2)
- Runoff 2D (grens 1000 km2) algoritme
- Rivers 2D, 1D, box, multi-box
- Lakes 3D, 2D, box
- Estuaries 3D, 2D, box
- Coast Box, 2D, 3D
- Groundwater 1D, 2D, 3D
6Modelberekeningen
- Oplossen van de advectie/diffusie vergelijking
(numeriek) - Verzamelen inputgegevens
- bijv meteo, bathymetry, lozingen, water afvoer,
salinity, getijdengegevens - Klant krijgt eindresultaat toegesneden op de
vraagstelling
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9Tsjernobyl koelvijver Dnjepr
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113D model Estuarium (Dniepr Boeg) Sr-90
12Groundwater model (beneath the Chernobyl)
Sr-90
90Sr (Bq/L) in groundwater - 2045
13North Sea THREETOX
Cs-137 in Seawater
Cs-137 Bottom sediments
Hypothetical Discharge Borssele PP (NL)
14POSEIDON Coastal regions
Local compartments can be added by user
15Besluit Stralingsbescherming 2001 Article 35 (and
108)
16Necessary to model or not?
- Radiotoxicity-equivalence
- Activity leading to 1Sv effective dose by
ingestion - Modelling not needed if
- Surface waters A 0.1 RE
- On the sewer system A 10 RE
17Derived criteria
Wsn secondary level test assuming dilution
108, leading to 1 uSv/ yr, (unit f RE) so Wsn
100 RE, leading to this dose. Wmax
A/RE Criteria (max) - 100 uS / yr (max per
location, above no permit) Criteria (low) 1 uS
/ yr (SN secondary level) under this no
modelling needed External irradiation 10 us/yr
(SN), under this no modelling needed Wmax/Wsn lt1
dose lt 1 uSv, no modelling needed
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19Discharge per year, under which no permit needed,
otherwise acquiring permit obliged (dose less
than 10 uSv/yr).
20Model Concept DOVISDosisberekening voor de
Omgeving bij Vergunningverlening Ioniserende
Straling
- To model objects
- Rivers
- Lakes
- Coastal region
- Estuaries
- Waste Water Treatment Installations
- Important Note IF the system is connected to the
coastal region, the these should be included as
well
21Model conceptDOVIS
- Processes
- sedimentation
- resuspension
- Transport between compartments
- Daughter - nuclides
- Standard Kd- values
- Not obliged Sediment - water interaction
- These processes have to taken account in the
model, more processes are of course allowed in
more complex models
22Model concept DOVIS
- Exposure pathways
- Consumption fishery products
- Consumption drinking water
- Consumption agricultural products
- (irrigation)
- External irradiation
- Secondary pathways
- Usage of harbour sludge and sewer sludge in
agriculture - Irrigation
- Effect of flooding
- Residence at the coast (sea)
23Source to Dose
Sewage sludge
Meat/Dairy products
Floodplains
Water
Fish
Dose Calculations (input consumption Behaviour
Population)
Drinking water
Sediment
Irrigation
Agricultural Pr.
Sand
External Irridation (Inhalation)
24Choice Dispersion modelCriteria
- Grid resolution (homogeneous mixing)
- Dynamic or Steady-State
- Conservative or non-conservative behaviour
radionuclide
- Reference Group (gt5 of the population)
- Available input data (very restrictive)
- Drinking water inlet location (lakes, rivers)
- Fish migration
25Company Consultant
- Company
- Discharge data
- Discharge scenario
- Discharge rates
- Radionuclides in discharge
- Consultant
- Collects model input
- Calculation concentrations radionuclides
- Calculation doses
26Case Study (1) North Sea
- Discharges NORM on the continental shelf
(continuous) - Discharges of radioactivity in the Westerscheldt
estuary. (semi-continuous) - Question Does it matter which compartments are
chosen, and which model has been applied
27Case Study (2) Noordzee
- Scenario 1 Coast at Rotterdam (min)
- Scenario 2 Coast at Rotterdam (max)
- Scenario 3 Continental Shelf
- Scenario 4 Westerschelde estuary
- Comparison between NRG models for the coastal
waters with PC CREAM (commercial dose assessment
tool, HPA (formerly NRPB, UK)
28Case Study (3) North Sea Model configuration PC
CREAM - NRG models
Model configurations
29NRG model 10 compartiments
30Case Study (4) Noordzee Model input
- Exposure pathways
- inhalation (particles, sea spray)
- consumption (fish, mussels, shrimps)
- External irradiation (beach)
- Dose
- After a year (Scen. 4. Westerscheldt)
- Yearly Dose (other scenario's)
- Discharge
- scenario 4 real estimated release into the
environment - Other scenario's Unit Discharge
31Case Study (5) NoordzeeReferentiegroepen
32Case Study (6) NoordzeeTabel resultaat NRG-1
model
10 compartimenten Rotterdam-Den Helder 1GBq/yr
33Case Study (7) Noordzee Resultatenvergelijking
PC-CREAM en NRG modellen (-)
Dominant belastingspad
1 TBq /jaar Ra-226 (2.8 105 RE)
34Discharge Westerscheldt (1E5 MBq/y)
35Case Study (8) North SeaConclusies
- Choice of compartment size affects the results.
- Commercial software not straight-forwarded
applicable (be careful for wrong usage). - Inhalation negligible exposure pathway
- Dosis below the legal upper limit of 100 ?Sv
36Huidige Beschikbaarheid Modellen NRG
- Alle lozingssituaties zijn te modelleren m.b.v
RIVTOX, COASTOX, SUSTOX, WATOX, THREETOX,
LAKECO-B, en POSEIDON - Meestal voldoet 1D model of compartiment model
voor reguliere lozing - Aanpassing voor RWZIs en baggerslib noodzakelijk
37Tot slot Praktische punten
- Binnen NRG expertise aanwezig
- Projecten kunnen worden geformuleerd
- Voor toxische stoffen expertise binnen KEMA/NRG
- Alle modellen betrouwbaar uitgebreid getest en
gevalideerd in internationale projecten (EC,
IAEA) in de afgelopen 15 jaar