Université de Paris, Institut de Physique du Globe de Paris, CNRS, F-75005 Paris, France.
Université de Paris, Institut de Physique du Globe de Paris, CNRS, F-75005 Paris, France.
Sci Total Environ. 2021 Apr 20;766:142655. doi: 10.1016/j.scitotenv.2020.142655. Epub 2020 Oct 8.
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 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 concentration (EC) in the laboratory, we compare EC values of the plant to that of the closest soil, and we infer the Ra soil-to-plant transfer ratio, R, for a total of 108 plant samples collected in various locations in France. EC values of plants range over five orders of magnitude with mean (min-max) of 1.66 ± 0.03 (0.020-113) Bq kg. Inferred R values range over four orders of magnitude with mean (min-max) of 0.0188 ± 0.0004 (0.00069-0.37). The mean R 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 values in the following order (acropetal gradient): roots > bark > branches and stems ≈ leaves. Oak trees (Quercus genus) concentrate Ra more than other trees and plants in this set. While this study clearly demonstrates the influence of substratum on the Ra 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.
镭-226 是一种半衰期为 1600 年的 α 发射器,在自然环境中普遍存在。它存在于岩石和土壤中,也被植被吸收。评估植物从土壤中吸收镭的效率对于研究植物对重金属的吸收、放射性污染监测以及关键带镭的生物地球化学循环都很重要。本研究使用经过彻底验证的实验室有效镭浓度 (EC) 测量方法,将植物的 EC 值与最接近的土壤进行比较,并推断出总共 108 个植物样本的镭土壤-植物转移比 (R),这些样本是在法国各地不同地点采集的。植物的 EC 值跨越了五个数量级,平均值 (最小值-最大值) 为 1.66 ± 0.03 (0.020-113) Bq kg。推断的 R 值跨越了四个数量级,平均值 (最小值-最大值) 为 0.0188 ± 0.0004 (0.00069-0.37)。在片麻岩和变质岩背景下的植物的平均 R 值 (0.073 ± 0.002; n = 50) 明显高于在碳酸盐岩和沉积岩背景下的植物的平均 R 值 (0.0058 ± 0.0002; n = 58) (0.073 ± 0.002; n = 50) 显著更高 (12 ± 1 倍)。这种差异不能归因于发射系数的系统差异,可能是由于钙和镭之间的竞争。在给定的基质背景下,同一植物物种的各个器官的 R 值呈以下顺序(向顶梯度)逐渐降低:根 > 树皮 > 树枝和茎≈叶。在本研究中选择的树木和植物中,栎属 (栎属) 树种比其他树种更能富集镭。虽然这项研究清楚地表明了基质对非污染地区植物吸收镭的影响,但我们的测量方法似乎是一种很有前途的实用工具,可用于铀和镭污染地区的(植物)修复及其监测。