Single value risks tiers
Overview
Name | EC 2018 Acute Tier I | EC 2018 Chronic - Tier I | EC 2018 Acute Tier II | EC 2018 Chronic Tier II | EFSA 2022 Acute Tier I | EFSA 2022 Chronic Tier I | EFSA 2022 Acute Tier II | EFSA 2022 Chronic Tier II | EFSA 2023 Acute Prospective Tier II | EFSA 2023 Chronic Prospective Tier II |
---|---|---|---|---|---|---|---|---|---|---|
Single value risk calculation method |
FromIndividualRisks |
FromIndividualRisks |
FromIndividualRisks |
FromIndividualRisks |
FromIndividualRisks |
FromIndividualRisks |
FromIndividualRisks |
FromIndividualRisks |
FromIndividualRisks |
FromIndividualRisks |
Percentage for percentile |
0.1 |
0.1 |
0.1 |
0.1 |
0.1 |
0.1 |
0.1 |
0.1 |
0.1 |
0.1 |
Ignore sampling weights |
true |
true |
true |
true |
true |
true |
true |
true |
true |
true |
Exclude individuals with less than N days |
false |
true |
false |
true |
false |
true |
false |
true |
false |
true |
Total diet study concentration data |
false |
false |
false |
false |
false |
false |
false |
false |
false |
false |
Filter samples exceeding the concentration limits |
false |
false |
false |
false |
false |
false |
false |
false |
true |
true |
Use substance conversion rules |
true |
true |
true |
true |
true |
true |
true |
true |
true |
true |
Substance conversion method |
UseMostToxic |
UseMostToxic |
DrawRandom |
DrawRandom |
UseMostToxic |
UseMostToxic |
DrawRandom |
DrawRandom |
DrawRandom |
DrawRandom |
Retain all allocated substances after active substance allocation |
true |
true |
true |
true |
true |
true |
true |
true |
true |
true |
Account for substance authorisations in substance conversions |
false |
false |
true |
true |
false |
false |
true |
true |
true |
true |
Fix duplicate substance allocation inconsistencies |
false |
false |
false |
false |
false |
false |
false |
false |
false |
false |
Use extrapolation rules |
true |
true |
true |
true |
false |
false |
false |
false |
false |
false |
Threshold for extrapolation |
10 |
10 |
10 |
10 |
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Restrict extrapolations to equal MRLs |
true |
true |
true |
true |
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Restrict extrapolations to authorised uses |
true |
true |
true |
true |
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Impute water concentrations |
true |
true |
true |
true |
true |
true |
true |
true |
true |
true |
Water concentration value (µg/kg) |
0.1 |
0.1 |
0.05 |
0.05 |
0.1 |
0.1 |
0.05 |
0.05 |
0.05 |
0.05 |
Restrict water imputation to the five most toxic substances |
true |
true |
true |
true |
true |
true |
true |
true |
true |
true |
Restrict water imputation to authorised uses |
false |
false |
false |
false |
false |
false |
false |
false |
false |
false |
Restrict water imputation to approved substances |
false |
false |
false |
false |
true |
true |
true |
true |
true |
true |
Apply processing factors |
true |
true |
true |
true |
true |
true |
true |
true |
true |
true |
Use distribution |
false |
false |
false |
false |
false |
false |
false |
false |
false |
false |
Ignore processing factors less than 1 |
false |
false |
false |
false |
false |
false |
false |
false |
false |
false |
Unit variability model |
BetaDistribution |
BetaDistribution |
BetaDistribution |
BetaDistribution |
BetaDistribution |
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Estimates nature |
Realistic |
Realistic |
Realistic |
Realistic |
Realistic |
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Unit variability parameter |
VariabilityFactor |
VariabilityFactor |
VariabilityFactor |
VariabilityFactor |
VariabilityFactor |
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Apply occurrence pattern percentages |
false |
false |
true |
true |
false |
false |
true |
true |
true |
true |
Target level |
External |
External |
External |
External |
External |
External |
External |
External |
External |
External |
Compute cumulative risks |
true |
true |
true |
true |
true |
true |
true |
true |
true |
true |
Health effect type |
Risk |
Risk |
Risk |
Risk |
Risk |
Risk |
Risk |
Risk |
Risk |
Risk |
Risk characterisation ratio |
HazardExposureRatio |
HazardExposureRatio |
HazardExposureRatio |
HazardExposureRatio |
HazardExposureRatio |
HazardExposureRatio |
HazardExposureRatio |
HazardExposureRatio |
HazardExposureRatio |
HazardExposureRatio |
Risk threshold |
100 |
100 |
100 |
100 |
100 |
100 |
100 |
100 |
100 |
100 |
Use inverse distribution to calculate percentile |
true |
true |
true |
true |
true |
true |
true |
true |
true |
true |
Exposure calculation method |
ModelledConcentration |
ModelledConcentration |
ModelledConcentration |
ModelledConcentration |
ModelledConcentration |
ModelledConcentration |
ModelledConcentration |
ModelledConcentration |
ModelledConcentration |
ModelledConcentration |
Inclusion percentage variability interval |
99.8 |
99.8 |
99.8 |
99.8 |
99.8 |
99.8 |
99.8 |
99.8 |
99.8 |
99.8 |
Consumptions on the same day come from the same sample |
false |
false |
false |
false |
false |
false |
false |
false |
false |
false |
Use unit variability |
true |
true |
true |
true |
true |
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Model-then-add |
false |
false |
false |
false |
false |
false |
false |
false |
false |
false |
Covariate modelling |
false |
false |
false |
false |
false |
false |
false |
false |
false |
false |
Iterate survey |
false |
false |
false |
false |
false |
false |
false |
false |
false |
false |
Report consumptions and exposures per individual instead of per kg body weight |
false |
false |
false |
false |
false |
false |
false |
false |
false |
false |
Default concentration model |
Empirical |
Empirical |
Empirical |
Empirical |
Empirical |
Empirical |
Empirical |
Empirical |
Empirical |
Empirical |
Include MRL fallback model |
false |
false |
false |
false |
false |
false |
false |
false |
false |
false |
Restrict LOR imputation to authorised uses |
false |
false |
false |
false |
false |
false |
false |
false |
false |
false |
Censored values replacement |
ReplaceByLOR |
ReplaceByLOR |
ReplaceByLOR |
ReplaceByLOR |
ReplaceByLOR |
ReplaceByLOR |
ReplaceByLOR |
ReplaceByLOR |
ReplaceByLOR |
ReplaceByLOR |
Factor f (f x LOR or f x LOD or LOD + f x (LOQ - LOD) |
0.5 |
0.5 |
0.5 |
0.5 |
0.5 |
0.5 |
0.5 |
0.5 |
0.5 |
0.5 |
Sample based |
true |
true |
true |
true |
true |
true |
true |
true |
true |
true |
Impute missing values from available values (if unchecked, missing values are imputed with 0) |
true |
true |
true |
true |
true |
true |
true |
true |
true |
true |
Correlate imputed values with sample potency |
true |
true |
false |
false |
true |
true |
false |
false |
false |
false |
Use occurrence frequencies for imputation |
true |
true |
true |
true |
true |
true |
true |
true |
true |
true |
Parametric uncertainty |
false |
false |
false |
false |
false |
false |
false |
false |
false |
false |
N (number of days in survey) |
2 |
2 |
2 |
2 |
2 |
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Model type |
OIM |
OIM |
OIM |
OIM |
OIM |
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Scale up use frequency to 100% |
true |
true |
true |
true |
true |
true |
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Restrict use percentage up-scaling to authorised uses |
true |
true |
true |
true |
true |
true |
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Concentration limit filter exceedance factor |
2 |
2 |
||||||||
Include focal commodity concentrations |
true |
true |
||||||||
Focal commodity substance occurrence percentage |
20 |
20 |
||||||||
Adjustment factor for the focal food/substance concentration |
1 |
1 |
||||||||
Use deterministic substance conversions for focal commodity |
true |
true |
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Cumulation setting |
RPFWeighted |
RPFWeighted |