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SEVERE RADIATION ACCIDENTS AND THE ENVIRONMENT

机译:严重的辐射事故和环境

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In severe radiation accidents with releases of radionuclides into the environ-ment, high enough radiation doses are formed to potentially cause direct radiation injury of natural ecosystems. The dose fields characterizing the irradiation of plants, animals and humans in radioactive contamination of the environment are highly heterogeneous, and irradiation of natural objects per se has features such as non-equidosal effects. In other words, humans and various objects in the natural environment can receive different absorbed doses for an equal density of radioactive fallout. In this case, maximal doses in different representatives of nature (e.g. coniferous trees and some groups of animal populations such as those inhabiting forest litter or bottom sediments) can be 10-100 times higher than those in humans. Natural and artificial ecosystems and their main components are characterized by great differences in radiosensitivity. The total effect of these two factors - namely, heterogeneity of the dose field and non-equidosal pattern of irradiation, on the one hand, and differences in radiosensitivity, on the other - predetermines considerable differences in the degree of radiation injuries in ecosystems of various kinds. In the radiation accidents in the southern Urals (1957) and at Chernobyl (1986), coniferous forests proved to be in fact the only natural ecosystems where radiation injury manifestations were notable at the ecosystem level in large areas. Evident symptoms of radiation injury, up to lethality, were found in small areas of deciduous forests, as well as in mammals. Mesofauna of forest litters and benthic organisms inhabiting the water ecosystems proved to be radioecologically hot sites. The minimal injurious dose of chronic irradiation at the levels of ecosystems and populations of living organisms is 5 Sv/a. In representatives of animal populations in the zone of the Chernobyl accident, radiation injury of the thyroid caused by accumulation of iodine radionuclides proved to be of considerable pathological significance. For the processes of radiation effects in accidental radioactive contamination of lands, two (or three) periods are characteristic - the phase of acute radiation injury with possible manifestations of radiation injury is followed by the phase of post-radiation recovery [1].
机译:在放射性核素释放到环境中的严重辐射事故中,会形成足够高的辐射剂量,从而有可能对自然生态系统造成直接辐射伤害。表征环境放射性污染中的植物,动物和人的辐射的剂量场是高度异质的,自然物体本身的辐射具有诸如非等位效应的特征。换句话说,在相同密度的放射性尘埃下,人类和自然环境中的各种物体可以接受不同的吸收剂量。在这种情况下,不同自然界代表(例如针叶树和某些动物种群(例如居住在森林凋落物或底部沉积物中的那些种群))的最大剂量可能比人类的剂量高10-100倍。天然和人工生态系统及其主要组成部分的特征是放射敏感性差异很大。这两个因素的总效应,即一方面是剂量场的异质性和辐射的非等分模式,另一方面是放射敏感性的差异,预先确定了各种生态系统中的放射损伤程度存在很大差异。种。在乌拉尔南部(1957年)和切尔诺贝利(1986年)发生的辐射事故中,针叶林实际上是唯一在大范围的生态系统水平上表现出辐射伤害表现的自然生态系统。在小面积的落叶林以及哺乳动物中都发现了明显的辐射伤害症状,甚至达到致死性。栖息在水生态系统中的森林凋落物和底栖生物的中生动物被证明是放射生态学热点。在生态系统和活生物体种群的水平上,长期照射的最小伤害剂量为5 Sv / a。在切尔诺贝利事故地区的动物种群中,碘放射性核素积聚引起的甲状腺辐射损伤被证明具有相当大的病理意义。对于土地意外放射性污染中的辐射效应过程,特征是两个(或三个)时期-急性辐射伤害阶段(可能表现为辐射伤害)之后是辐射后恢复阶段[1]。

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