Abstract
Radium-226, an alpha emitter with half-life 1600 years, is ubiquitous in natural environments. Present in rocks and soils, it is also absorbed by vegetation. The efficiency of Ra-226 uptake by plants from the soil is important to assess for the study of heavy metals uptake by plants, monitoring of radioactive pollution, and the biogeochemical cycle of radium in the Critical Zone. Using a thoroughly validated measurement method of effective Ra-226 concentration (ECRa) in the laboratory, we compare ECRa values of the plant to that of the closest soil, and we infer the Ra-226 soil-to-plant transfer ratio, R-SP, for a total of 108 plant samples collected in various locations in France. ECR, values of plants range over five orders of magnitude with mean (min-max) of 1.66 +/- 0.03 (0.020-113) Bq kg(-1). Inferred R-SP, values range over four orders of magnitude with mean (min-max) of 0.0188 +/- 0.0004 (0.00069-0.37). The mean R-SP value of plants in granitic and metamorphic context (0.073 +/- 0.002; n = 50) is significantly higher (12 +/- 1 times) than that of plants in calcareous and sedimentary context (0.0058 +/- 0.0002; n = 58). This difference, which cannot be attributed to a systematic difference in emanation coefficient, is likely due to the competition between calcium and radium. In a given substratum context, the compartments of a given plant species show coherent and decreasing R-SP values in the following order (acropetal gradient): roots > bark > branches and stems approximate to leaves. Oak trees (Quercus genus) concentrate( 226)Ra more than other trees and plants in this set. While this study dearly demonstrates the influence of substratum on the Ra-226 uptake by plants in non-contaminated areas, our measurement method appears as a promising practical tool to use for (phyto)remediation and its monitoring in uranium- and radium-contaminated areas.