使用 IBA CYCLONE 18/9 HC 回旋加速器生产以 18F 为基础的放射性药物时 β 放射性核素的积累分析

С. Д. Бринкевич, Д. И. Бринкевич, А. И. Киевицкая, А. Н. Кийко, И. А. Ковалёв, Sviatoslav D . Brinkevich, D. Brinkevich, H. I. Kiyavitskaya, Aliaksandr N . Ki y ko, Igor A. Kovalev
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引用次数: 0

摘要

为了明确放射性废物管理方案,研究人员利用 IBA CYCLONE 18/9 HC 回旋加速器研究了以 18F 为基础的放射性药物生产过程中不良β发射放射性核素(PH)的积累情况。结果表明,最主要的杂质 PH 是氚,当水受到 [18O]H2O 质子辐照时,由 18O(p, t) 16O 反应生成。3H 的主要部分(约 95%)留在再生水中。1.6% 的累积氚活度随气体和水蒸气离开合成区。含氚废物(小瓶中的再生水)在处理过程中可被视为活性极低的废物。随着靶的工作时间超过 2500 µA - h,靶材料的腐蚀/侵蚀过程会增加,从而导致再生水、吸附净化筒和成品剂型中的不良放射性核素浓度急剧增加。氚的浓度不会显著增加。在再生水[18O]H2O 和成品放射性药物[18F]NaF 的 β 光谱中,除了氚引起的最大值外,光谱的低能和高能部分都出现了一些最大值。由于活化靶壁的沥滤作用,其他不需要的 β-发射体也会在水中积累。测量水中的氚活度[18O]H2O 作为其再富集指标的可能性已经得到证实。说明了控制中间产品、生产废料和最终放射性药物中杂质 β-发射 PH 含量的必要性。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Analysis of the accumulation of β-emitting radionuclides in the production of radiopharmaceuticals based on 18F using the IBA CYCLONE 18/9 HC cyclotron
In order to clarify the scheme of radioactive waste management, the accumulation of undesirable beta-emitting radionuclides (PH) in the production of radiopharmaceuticals based on 18F using the IBA CYCLONE 18/9 HC cyclotron was investigated. It is shown that the dominant impurity PH is tritium, which is formed by the reaction of 18O(p, t) 16O when water is irradiated with [18O]H2O protons. The main proportion of 3H (about 95%) remains in the regenerated water. 1.6 % of the accumulated tritium activity is carried away from the synthesis zone with gases and water vapor. Tritium-containing waste (regenerated water in vials) can be considered as waste of a very low level of activity during disposal. With an increase in the operating time of the target over 2500 µA · h, the processes of corrosion /erosion of target materials increase, which leads to a sharp increase in the concentration of undesirable radionuclides in regenerated water, sorption purification cartridges and the finished dosage form. The concentration of tritium does not increase significantly. In the β-spectra of regenerated water [18O]H2O and the finished radiopharmaceutical [18F]NaF, in addition to the maximum due to tritium, a number of maxima appear in both the low- and high-energy parts of the spectrum. Other undesirable β-emitters accumulate in water as a result of leaching of the activated target wall. The possibility of using measurements of tritium activity in water [18O]H2O as an indicator of its re-enrichment has been demonstrated. The necessity of controlling the content of impurity beta-emitting PH in intermediate products, production waste and final radiopharmaceutical is shown.
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