Koranda J J, Robison W L
Environ Health Perspect. 1978 Dec;27:165-79. doi: 10.1289/ehp.7827165.
The accumulation of radionuclides by plants acting as a monitoring system in the environment may occur by two modes; foliar absorption by the leaves and shoot of the plant, or by root uptake from the soil. Data on plant accumulation of radionuclides may be obtained from studies of fission product radionuclides deposited as worldwide fallout, and from tracer studies of plant physiology. The epidermal features of plant foliage may exert an effect upon particle retention by leaves, and subsequent uptake of radionuclides from the surface. The transport of radionuclides across the cuticle and epidermis of plant leaves is determined in part by the anatomy of the leaf, and by physiological factors. The foliar uptake of fallout radionuclides, 99Sr, 131I, and 137Cs, is described with examples from the scientific literature. The environmental half-life of 131I, for example, is considerably shorter than its physical half-life because of physical and biological factors which may produce a half-life as short as 0.23/day. 99Sr and 137Cs are readily taken up by the leaf, but 137Cs undergoes more translocation into fruit and seeds than 99Sr which tends to remain in the plant part in which it was initially absorbed. Soil-root uptake is conditioned primarily by soil chemical and physical factors which may selectively retain a radionuclide, such as 137Cs. The presence of organic matter, inorganic colloids (clay), and competing elements will strongly affect the uptake of 99Sr and 137Cs by plants from the soil. The role of plants as monitors of radionuclides is twofold: as monitors of recent atmospheric releases of radionuclides; and as indicators of the long-term behavior of aged deposits of radionuclides in the soil.
植物的叶片和茎进行叶面吸收,或者通过根系从土壤中吸收。关于植物对放射性核素积累的数据可从对作为全球沉降物沉积的裂变产物放射性核素的研究以及植物生理学的示踪研究中获得。植物叶片的表皮特征可能会影响叶片对颗粒的滞留以及随后从表面吸收放射性核素。放射性核素穿过植物叶片角质层和表皮的运输部分取决于叶片的解剖结构和生理因素。本文以科学文献中的实例描述了沉降放射性核素99Sr、131I和137Cs的叶面吸收情况。例如,由于物理和生物因素,131I的环境半衰期远短于其物理半衰期,其环境半衰期可能短至0.23/天。99Sr和137Cs很容易被叶片吸收,但137Cs比99Sr更容易向果实和种子中转移,99Sr往往留在其最初吸收的植物部位。土壤-根系吸收主要受土壤化学和物理因素的制约,这些因素可能会选择性地保留放射性核素,如137Cs。土壤中有机物、无机胶体(粘土)和竞争元素的存在会强烈影响植物对土壤中99Sr和137Cs的吸收。植物作为放射性核素监测器的作用有两方面:作为近期大气中放射性核素释放的监测器;以及作为土壤中放射性核素陈旧沉积物长期行为的指示物。