French Institute for Radiological Protection and Nuclear Safety (IRSN), PRP-ENV/SERIS/L2BT, CE Cadarache bt 186, BP 3, 13115 Saint-Paul-lez-Durance, France.
J Environ Radioact. 2013 Jul;121:43-54. doi: 10.1016/j.jenvrad.2012.04.013. Epub 2012 May 18.
Apart from radiocaesium and radiostrontium, there have been few studies on the foliar transfer of radionuclides in plants. Consequently, specific translocation factor (ftr) values for (129)I, (79)Se and (36)Cl are still missing from the IAEA reference databases. The translocation of short - lived isotopes, (125)I and (75)Se, and of (36)Cl to wheat grain were measured under field conditions following acute and chronic wet foliar contamination at various plant growth stages in the absence of leaching caused by rain. The translocation factors ranged from 0.02% to 1.1% for (125)I (a value similar to Sr), from 0.1% to 16.5% for (75)Se, and from 1% to 14.9% for (36)Cl. Both (36)Cl and (75)Se were as mobile as Cs. The phenomenological analysis showed that each element displayed a specific behavior. Iodide showed the lowest apparent mobility because of its preferential fixation in or on the leaves and a significant amount probably volatilized. Selenite internal transfer was significant and possibly utilized the sulphur metabolic pathway. However bio - methylation of selenite may have led to increased volatilization. Chloride was very mobile and quickly diffused throughout the plant. In addition, the analysis underlined the importance of plant growth responses to annual variations in weather conditions that can affect open field experiments because plant growth stage played a major role in ftr values dispersion. The chronic contamination results suggested that a series of acute contamination events had an additive effect on translocated elements. The highest translocation value obtained for an acute contamination event was shown to be a good conservative assessment of chronic contamination if data on chronic contamination translocation are lacking. The absence of rain leaching during the experiment meant that this investigation avoided potential radionuclide transfer by the roots, which also meant that radionuclide retention on or in the leaves was maximized. This study was therefore able to obtain accurate translocation factors, which are probably among the highest that could be recorded.
除放射性铯和放射性锶之外,有关植物中放射性核素叶部转移的研究还很少。因此,国际原子能机构的参考数据库中仍然缺乏放射性碘-129、硒-79 和氯-36 的具体迁移系数(ftr)值。在不存在因降雨引起淋溶的情况下,本研究在田间条件下,于不同的作物生长阶段,对急性和慢性湿叶污染后短寿命同位素 125I 和 75Se 以及 36Cl 向小麦籽粒中的迁移进行了测量。在没有雨水淋溶的情况下,对不同生长阶段的作物进行急性和慢性湿叶污染,结果表明,125I 的迁移系数范围为 0.02%1.1%(与 Sr 的迁移系数相似),75Se 的迁移系数范围为 0.1%16.5%,36Cl 的迁移系数范围为 1%~14.9%。氯-36 和硒-75 的迁移能力与铯相同。现象学分析表明,每种元素都表现出特定的行为。由于碘化物优先固定在叶片上或叶片内,且可能有大量碘化物挥发,因此显示出最低的表观迁移率。亚硒酸盐的内部转移非常显著,可能利用了硫代谢途径。然而,亚硒酸盐的生物甲基化可能导致其挥发增加。氯非常活跃,可迅速扩散到整个植株。此外,分析强调了植物生长对年际天气变化的响应的重要性,因为天气变化会影响田间实验,因为作物生长阶段在 ftr 值的分散中起着主要作用。慢性污染的结果表明,一系列急性污染事件对迁移元素具有累加效应。如果缺乏慢性污染的迁移数据,那么急性污染事件中获得的最高迁移值可很好地保守评估慢性污染。实验过程中没有雨水淋溶,这意味着本研究避免了根部可能的放射性核素转移,这也意味着叶片上或叶片内的放射性核素的保留达到最大化。因此,本研究能够获得准确的迁移系数,这可能是记录到的最高迁移系数之一。