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Transfer parameter values in temperate forest ecosystems: a review
Philippe Calmon1, Yves Thiry, Gregor Zibold
1Department of Radioecology, Institute of Radioprotection and Nuclear Safety, CE Cadarache, Saint Paul-lès-Durance Cedex, France. philippe.calmon@irsn.fr
Journal of Environmental Radioactivity
|December 23, 2008
Summary
Forest ecosystems exhibit complex radionuclide transfers, with soil acting as a long-term reservoir. This review quantizes radionuclide uptake in forest biota, highlighting higher transfers to mushrooms and berries compared to agricultural systems.
Area of Science:
- Environmental Science
- Ecology
- Radiochemistry
Background:
- Forests are complex ecosystems with diverse species, strata, and soil layers, leading to variable radionuclide transfer and redistribution patterns.
- Soil serves as the primary long-term reservoir for radionuclides, posing a continuous risk of plant and food contamination.
- Aggregated transfer factor (T(ag)) is used to quantify radionuclide contamination in forest products, integrating environmental and biological factors.
Purpose of the Study:
- To review quantitative information on radionuclide transfers to various forest biota, including trees, understorey vegetation, mushrooms, berries, and game animals.
- To compare radionuclide transfer dynamics in forest ecosystems with those in agricultural lands.
Main Methods:
- Literature review of quantitative data on radionuclide transfers.
- Analysis of aggregated transfer factor (T(ag)) values for different forest components and species.
- Comparison of contamination levels and transfer rates across various forest ecosystems (temperate, boreal) and biota.
Main Results:
- Mean T(ag) values for radiocaesium and radiostrontium in trees are around 10(-3) m(2)kg(-1) (dry weight), with foliage being more contaminated than wood.
- Radionuclide transfer to mushrooms and berries is significantly higher than in agricultural settings, with T(ag) for mushrooms varying widely (10(-3) to 10(1) m(2)kg(-1)) and berries around 0.01-0.1 m(2)kg(-1) (dry weight).
- Transfer to game animals and reindeer depends on soil and pasture conditions; muscle activity concentrations show variable decline rates, with wild boar exhibiting no decline due to feeding habits. In boreal forests, late-phase T(ag) for (137)Cs in moose and birds is ~0.01 m(2)kg(-1) (fresh weight).
Conclusions:
- Forest ecosystems demonstrate unique and often higher radionuclide transfer pathways compared to agricultural lands, particularly for specific biota like mushrooms and berries.
- The soil compartment's role as a long-term reservoir necessitates continued monitoring of radionuclide contamination in forest products.
- Variability in transfer factors is influenced by ecosystem characteristics, species-specific traits, and environmental conditions, requiring location-specific assessments.
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