Dietary advice
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Dietary advice
Objective Dose reduction by giving people dietary advice to
reduce their radionuclide intake.
Other Benefits Help people maintain their way of life.
Enables informed choice.
Countermeasure description Provision of advice to people on ways to restrict their
dietary radionuclide intake. For example, advice to
reduce consumption of specific foodstuffs (e.g. game,
mushrooms etc.), to not drink water from private
cisterns, or to prepare food in ways that reduce
contamination levels (e.g. washing and peeling
vegetables and fruit, brining fish, cooking meat etc.).
Advice may vary from suggestions as to which
foodstuffs can be eaten without restrictions, which
would be okay to eat occasionally, and which should
be avoided completely. The advice can be
communicated in the media (e.g. newspapers,
internet) and as specially produced leaflets.
Target Anyone who wants to reduce their dose, or who may
have a high dose due to dietary preferences
Targeted radionuclides Caesium, strontium, but may be effective for other
radionuclides
Scale of application Generally applicable to all population groups although
may be most appropriate to critical groups (e.g.
people with a high rate of wild food consumption).
Contamination pathway Plant-animal-people; plant-people, animal people
Exposure pathway Ingestion
Time of application Any time after deposition, or for as long as selected
foodstuffs have enhanced activity concentrations
Constraints
Legal constraints Possible liability from unforeseen health
consequences or economic side-effects for specialist
food producers.
Social constraints Countermeasure may be met with strong resistance
from local populations for whom collection of wild
(forest) food has a cultural and economic significance.
For socially isolated/independent rural Populations
e.g. the Saami, a key issue may be trust (or lack of)
in the institutions/experts advising dietary
restrictions.
Environmental constraints N/A
Communication constraints Availability of communication lines, language and
literacy of certain groups.
Dialogue and dissemination of information is required
with affected communities.
Effectiveness:
Countermeasure effectiveness Reductions of up to 85% have been reported for food
preparation methods. Common methods are boiling,
pickling and brining
Factors influencing effectiveness of Effectiveness depends on foodstuffs, radionuclide
procedure (Technical) concentrations and methods of preparation (see
above).
Factors influencing effectiveness of Willingness of affected population to accept this type
procedure (social) of intervention and their willingness to follow the
advice.
The extent to which advice is used.
Individual willingness to submit to restrictions.
Effectiveness of preparation procedures will often
only be effective if cooking fluids/bones etc. are
discarded.
Feasibility:
Required specific equipment Normal cooking implements
Required ancillary equipment None (unless this countermeasure is to be
supplemented by provision of counting equipment)
Required utilities and infrastructure Communication lines (internet, fax machines,
telephones etc.).
Required consumables Dependent on communication method
Required skills Communication skills
Required safety precautions N/A
Other limitations N/A
Waste:
Amount and type None, except household waste.
Possible transport, treatment and N/A
storage routes.
Factors influencing waste issues N/A
Doses:
Averted dose Individual averted doses
Factors influencing averted dose Willingness to follow advice, contamination level in
foodstuffs, time after deposition
Additional dose N/A
Intervention costs:
Equipment N/A
Consumables Price for printing leaflets to be collated for different
countries
Operator time The time used for giving advice will depend on the
communication method (personal contact, internet,
telephone, fax etc.)
Factors influencing costs
Communication costs Dialogue and dissemination of information about the
countermeasure (its rationale and possible
alternatives) within affected communities.
Compensation costs Compensation can be considered in special cases,
such as populations for whom “free-food” as a
cultural or economic significance. For example, in
Norway, reindeer herders are given compensation for
having an alternative diet amounting to 250 EUR/y
per family member if the contamination in their
reindeers was above 600 Bq/kg the previous year
(the CFIL for general foodstuffs). If the contamination
was over 3000 Bq/kg (CFIL for reindeer meat for
sale) the previous year, each person receives an
extra compensation of 125 EUR/y. The compensation
can be used for buying less contaminated reindeer
meat from other areas, buying other kinds of meat or
clean feeding reindeers consumed by the family to
obtain <600 Bq/kg.
Waste cost N/A
Assumptions
Cost effectiveness:
Side-effect evaluation:
Ethical considerations Self help
Improves personal control and ability to make
informed choices
Communicates authorities‟ trust in the public
Possible liability issues in the case of unforeseen
health effects
Possible negative effects on food producers if the
public avoids specialist foodstuffs from contaminated
areas.
Possible negative effects on the poor if the
countermeasure results in cheap “contaminated
foodstuffs”.
Environmental impact Possible ecological effect from increase in game
population if hunting/fishing declines, or cessation of
large-scale fungi/berry collection. Could be positive
(e.g. conservation of habitats and increased nutrient
availability resulting from increased decomposition)
or negative (e.g., change in ecological equilibrium,
lack of foodstuffs for due to increased competition).
Agricultural impact Knock-on lack of production from social side-effects
on food production in one area may result in
increased production on other areas.
Possible increased utilisation of agricultural
grasslands or crops by „uncontrolled‟ game species
Social impact Changed relationship to land/forests and potential
change of behaviour resulting from changes in
people‟s perceptions of land as a „natural‟ resource, to
being „unnatural‟ or in some way its resources
damaged/polluted.
Loss of traditional activities e.g. gathering free food
Negative social and psychological impact – loss of
sense of control over the situation as all local/home-
produced foods are „bad‟. Should perhaps be
combined with advice on how to manage diets (also
depends on trust in experts/responsible authorities).
Other side effects, pos. or neg. Replacement foods may be required
Stakeholder opinion
Practical experience Used in western Europe (especially Scandinavia) and
the FSU after the Chernobyl accident. Proven to be a
cheap and effective countermeasure, if people are
willing to follow the advice.
Key references Brynildsen, L.I. et al., 1996. Countermeasures for
radiocaesium in animal products in Norway after the
Chernobyl accident – techniques, effectiveness and
costs. Health Physics 70: 665-672.
Strand, P. et al. Chernobyl fallout: internal doses to
the Norwegian population and the effect of dietary
advice. Health Physics 63(4), 385-392, 1992.
Petäjä, E. et al. Reduction of radioactive caesium in
meat and fish by soaking. Journal of Env.
Radioactivity 16:273-285, 1992.
IAEA Technical Report Series No. 364: Handbook of
parameter values for the prediction of radionuclide
transfer in temperate environments, 1994.
Long et al., 1995
Tønnessen, A. et al. 1996. Personal use of
countermeasures seen in a coping perspective.
Radiation Protection Dosimetry, 68: 261-266.
Comments Self-help countermeasure.
Can be combined with provision of counting
equipment.
Examples of edible fungi species grouped on basis of
radiocaesium accumulating ability:
Suillus, Tricholoma, Xerocomus, Rozites (high
accumulators)
Cantharellus, Lactarius (medium accumulators)
Leccinum, Boletus (low accumulators)
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