Dubeau J, Heinmiller B E, Corrigan M
DETEC, Gatineau, Quebec, CanadaJ8T 4J1.
Canadian Nuclear Laboratories, Chalk River, Ontario, CanadaK0J 1J0.
Radiat Prot Dosimetry. 2017 Apr 28;174(3):371-376. doi: 10.1093/rpd/ncw220.
There is the possibility for a worker at a nuclear installation, such as a nuclear power reactor, a fuel production facility or a medical facility, to come in contact with radioactive contaminants. When such an event occurs, the first order of business is to care for the worker by promptly initiating a decontamination process. Usually, the radiation protection personnel performs a G-M pancake probe measurement of the contamination in situ and collects part or all of the radioactive contamination for further laboratory analysis. The health physicist on duty must then perform, using the available information, a skin dose assessment that will go into the worker's permanent dose record. The contamination situations are often complex and the dose assessment can be laborious. This article compares five dose assessment methods that involve analysis, new technologies and new software. The five methods are applied to 13 actual contamination incidents consisting of direct skin contact, contamination on clothing and contamination on clothing in the presence of an air gap between the clothing and the skin. This work shows that, for the cases studied, the methods provided dose estimates that were usually within 12% (1σ) of each other, for those cases where absolute activity information for every radionuclide was available. One method, which relies simply on a G-M pancake probe measurement, appeared to be particularly useful in situations where a contamination sample could not be recovered for laboratory analysis.
在核设施(如核电站反应堆、燃料生产设施或医疗设施)工作的工人有可能接触到放射性污染物。当此类事件发生时,首要任务是通过迅速启动去污程序来照顾工人。通常,辐射防护人员会在现场用盖革-弥勒(G-M)薄窗探头对污染情况进行测量,并收集部分或全部放射性污染物用于进一步的实验室分析。然后,值班的健康物理学家必须利用现有信息进行皮肤剂量评估,该评估结果将被记入工人的永久性剂量记录中。污染情况往往很复杂,剂量评估可能会很繁琐。本文比较了五种涉及分析、新技术和新软件的剂量评估方法。这五种方法被应用于13起实际污染事件,包括直接皮肤接触、衣物污染以及衣物与皮肤之间存在气隙时的衣物污染。这项工作表明,对于所研究的案例,在每种放射性核素的绝对活度信息可用的情况下,这些方法提供的剂量估计值通常彼此相差在12%(1σ)以内。有一种方法仅依赖于G-M薄窗探头测量,在无法获取污染样本进行实验室分析的情况下似乎特别有用。