在新的 Icrp 生物动力学模型计算基础上比较铀化合物的辐射毒性和化学毒性

A.A. Molokanov, N. Potsyapun, E.Yu. Maksimova, Yu. E. Kvacheva
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The calculations were carried out using new ICRP biokinetic models, which give more physiologically realistic representations of uptake and retention in organs and tissues, and excretion. Results: The dynamics of uranium activity in the kidneys was calculated for constant chronic inhalation intake over a 50-year period and for acute intake. It was shown that in case of chronic intake, the rate of accumulation of uranium in the kidneys, expressed in relative units, does not depend on the AMAD in the range from 0.3 to 20 μm and slightly depends on the types of compounds F, F/M, M and M/S, which include almost all chemical compounds of uranium. In case of acute intake, there is a rapid, within 1–3 days, an increase of uranium in the kidneys to a maximum value and then a gradual decrease to a value of 20 % of the maximum value in 20–60 days, depending on the type of compound F, M, F/M, M/S and AMAD in a wide range of values from 0.3 to 20 µm. To compare the radiation and chemical toxicity of uranium, the values of the committed effective dose were calculated, which is formed after intake of uranium aerosols of the types F, M, F/M and M/S and AMADs from 0.3 to 20 µm in an amount that creates the maximum concentration of uranium in the kidneys 0.3 µg/g for chronic intake and 3 µg/g for acute intake. The values of uranium intake per year in milligrams, which form the maximum concentration of uranium in the kidneys of 0.3 µg/g, in case of constant chronic intake of uranium aerosols, as well as the values of uranium intake in milligrams, which form the maximum concentration of uranium in the kidneys of 3 μg/g after a single intake of uranium aerosols in both case of the types F, M, F/M and M/S and AMAD in the range from 0.3 to 20 µm were calculated, which are evidently independent of the considered isotopic composition of the uranium. Conclusion: It is shown that chemical toxicity prevails over radiation toxicity for the types of uranium compounds F and F/M for all considered uranium isotopic composition, except for HEU; for the type of compound M it is the same for mixtures of NU and DU, and for the type M/S radiation toxicity prevails for all considered uranium isotopic composition. In case of chronic intake at committed effective dose exposure rate of several mSv per year, workers can suffer from the chemical toxicity of uranium when working with F and F/M compounds and isotope compositions of natural (NU), depleted (DU) and low enriched (LEU) uranium already after 1–2 years of work. 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引用次数: 0

摘要

目的:考虑到新的国际要求和建议的应用,协调和改进管理工人内部辐射照射的制度和确保辐射安全的基本要求。材料和方法:本文根据天然铀(NU)、贫铀(DU)、低浓铀(LEU)和高浓铀(HEU)的典型同位素组成在0.3 ~ 20 μm的AMAD范围内化合物F、M、F/M和M/S的类型,计算吸入摄入量和承诺有效剂量的水平,比较了铀化合物的辐射和化学毒性。这些化合物导致肾脏中铀的最大允许浓度。计算是使用新的ICRP生物动力学模型进行的,该模型提供了器官和组织中摄取和保留以及排泄的更现实的生理表征。结果:计算了50年期间持续慢性吸入和急性吸入的肾脏铀活性动态。结果表明,在慢性摄入的情况下,肾脏中铀的积累速率(以相对单位表示)不依赖于0.3 ~ 20 μm范围内的AMAD,而与化合物F、F/M、M和M/S的类型有轻微的关系,其中包括铀的几乎所有化合物。在急性摄入的情况下,肾脏中的铀在1-3天内迅速增加到最大值,然后在20 - 60天内逐渐减少到最大值的20%,这取决于化合物F, M, F/M, M/S和AMAD的类型,范围从0.3到20µM不等。为了比较铀的辐射和化学毒性,计算了承诺有效剂量值,该剂量是在摄入F、M、F/M和M/S型铀气溶胶和AMADs 0.3 ~ 20 μ M时形成的,其量在肾脏中产生的最大铀浓度为0.3 μ g/g,慢性摄入为0.3 μ g/g,急性摄入为3 μ g/g。铀在毫克,摄入每年的值构成的最大浓度铀0.3µg / g,肾脏的慢性摄入的常数的铀气溶胶,以及铀在毫克,摄入的值构成的最大浓度铀的肾脏后3μg / g单摄入铀气溶胶在两种类型的F, M, F / M和M / S和哈桑的范围从0.3到20µM计算,这显然与铀的同位素组成无关。结论:除高浓铀外,所有铀同位素组成中铀化合物F和F/M类型的化学毒性均大于辐射毒性;对于化合物M类型,NU和DU的混合物的辐射毒性是相同的,对于M/S类型的辐射毒性普遍存在于所有考虑的铀同位素组成中。在以每年数毫西弗的承诺有效剂量暴露率长期摄入铀的情况下,工人在工作1-2年后就可能在接触F和F/M化合物以及天然(NU)、贫(DU)和低浓(LEU)铀的同位素组成时遭受铀的化学毒性。在急性摄入的情况下,应以铀的化学毒性作为化合物F和F/M的限制暴露标准,也应以部分M (NU、DU和LEU的铀同位素组成)作为限制暴露的标准,这可以显着降低铀摄入的允许限度,几十倍甚至上百倍。
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Comparison of Radiation and Chemical Toxicity of Uranium Compounds on The Basis of Calculation by New Icrp Biokinetic Models
Purpose: Harmonization and improvement of the system for regulating the internal radiation exposure of workers and the basic requirements for ensuring radiation safety, taking into account the application of new international requirements and recommendations. Material and methods: The article presents a comparison of the radiation and chemical toxicity of uranium compounds, obtained on the basis of calculating the levels of inhalation intake and committed effective dose depending on the types of compounds F, M, F/M and M/S in the AMAD range from 0.3 to 20 μm for typical isotopic compositions of natural (NU), depleted (DU), low enriched (LEU) and highly enriched (HEU) uranium, which lead to the maximum permissible concentration of uranium in the kidneys. The calculations were carried out using new ICRP biokinetic models, which give more physiologically realistic representations of uptake and retention in organs and tissues, and excretion. Results: The dynamics of uranium activity in the kidneys was calculated for constant chronic inhalation intake over a 50-year period and for acute intake. It was shown that in case of chronic intake, the rate of accumulation of uranium in the kidneys, expressed in relative units, does not depend on the AMAD in the range from 0.3 to 20 μm and slightly depends on the types of compounds F, F/M, M and M/S, which include almost all chemical compounds of uranium. In case of acute intake, there is a rapid, within 1–3 days, an increase of uranium in the kidneys to a maximum value and then a gradual decrease to a value of 20 % of the maximum value in 20–60 days, depending on the type of compound F, M, F/M, M/S and AMAD in a wide range of values from 0.3 to 20 µm. To compare the radiation and chemical toxicity of uranium, the values of the committed effective dose were calculated, which is formed after intake of uranium aerosols of the types F, M, F/M and M/S and AMADs from 0.3 to 20 µm in an amount that creates the maximum concentration of uranium in the kidneys 0.3 µg/g for chronic intake and 3 µg/g for acute intake. The values of uranium intake per year in milligrams, which form the maximum concentration of uranium in the kidneys of 0.3 µg/g, in case of constant chronic intake of uranium aerosols, as well as the values of uranium intake in milligrams, which form the maximum concentration of uranium in the kidneys of 3 μg/g after a single intake of uranium aerosols in both case of the types F, M, F/M and M/S and AMAD in the range from 0.3 to 20 µm were calculated, which are evidently independent of the considered isotopic composition of the uranium. Conclusion: It is shown that chemical toxicity prevails over radiation toxicity for the types of uranium compounds F and F/M for all considered uranium isotopic composition, except for HEU; for the type of compound M it is the same for mixtures of NU and DU, and for the type M/S radiation toxicity prevails for all considered uranium isotopic composition. In case of chronic intake at committed effective dose exposure rate of several mSv per year, workers can suffer from the chemical toxicity of uranium when working with F and F/M compounds and isotope compositions of natural (NU), depleted (DU) and low enriched (LEU) uranium already after 1–2 years of work. In case of acute intake, the chemical toxicity of uranium should be taken as a criterion for limiting exposure for compounds F and F/M, and also partially M (for uranium isotope compositions of NU, DU and LEU), which can significantly, by tens and hundreds of times, reduce the permissible limit of uranium intake.
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来源期刊
Medical Radiology and Radiation Safety
Medical Radiology and Radiation Safety Medicine-Radiology, Nuclear Medicine and Imaging
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