Tsuda Shuichi, Saito Kimiaki
Research Group for Radiation Transport Analysis, Nuclear Science and Engineering Center, Japan Atomic Energy Agency, Tokai-mura 319-1195, Japan.
Fukushima Environmental Safety Center, Sector of Fukushima Research and Development, Japan Atomic Energy Agency, Tokyo 100-8577, Japan.
J Environ Radioact. 2017 Jan;166(Pt 3):419-426. doi: 10.1016/j.jenvrad.2016.02.008. Epub 2016 Mar 5.
Spectrum-dose conversion operators, the G(E) functions, for common NaI(Tl) scintillation survey meters and CsI(Tl) detectors are obtained for measurements in a semi-infinite plane of contaminated ground field by photon-emitting radionuclides (ground source). The calculated doses at a height of 100 cm from the ground in Cs-contaminated environments by the Monte Carlo simulation technique are compared with those obtained using the G(E) functions by assuming idealized irradiation geometries such as anterior-posterior or isotropic. The simulation reveals that one could overestimate air dose rates in the environment by a maximum of 20-30% for NaI(Tl) detectors and 40-50% for CsI(Tl) detectors depending on photon energy when using the G(E) functions assuming idealized irradiation geometries for ground source measurements. Measurements obtained after the nuclear accident in Fukushima reveal that the doses calculated using a G(E) function for a unidirectional irradiation geometry are 1.17 times higher than those calculated using a G(E) function for the ground source in the case of a CsI(Tl) scintillation detector, which has a rectangular parallelepiped crystal (13 × 13 × 20 mm). However, if a G(E) function is used assuming irradiation to a surface of the detector, the doses agree with those of the ground source within 2%. These results indicate that in contaminated environments, the commonly used scintillation-based detectors overestimate doses within the acceptable limit. In addition, the degree of overestimation depends on the irradiation direction of each detector assumed for developing the G(E) function. With regard to directional dependence of the detectors, reliable air dose rates in the environment can be obtained using the G(E) function determined in unidirectional irradiation geometry, provided that the irradiation surface of the crystal is determined properly.
针对常见的碘化钠(铊)闪烁式测量仪和碘化铯(铊)探测器,通过光子发射放射性核素(地面源)在受污染地面场的半无限平面中进行测量,获得了能谱剂量转换算子,即G(E)函数。通过蒙特卡罗模拟技术计算了在铯污染环境中距地面100厘米高度处的剂量,并与通过假设理想化照射几何形状(如前后照射或各向同性照射)使用G(E)函数获得的剂量进行了比较。模拟结果表明,在使用G(E)函数假设地面源测量的理想化照射几何形状时,根据光子能量,对于碘化钠(铊)探测器,环境中的空气剂量率可能会高估最多20% - 30%,对于碘化铯(铊)探测器可能会高估40% - 50%。福岛核事故后的测量结果表明,对于具有长方体晶体(13×13×20毫米)的碘化铯(铊)闪烁探测器,在单向照射几何形状下使用G(E)函数计算的剂量比在地面源情况下使用G(E)函数计算的剂量高1.17倍。然而,如果假设探测器表面受到照射而使用G(E)函数,剂量在2%以内与地面源的剂量一致。这些结果表明,在受污染环境中,常用的基于闪烁的探测器在可接受的限度内高估了剂量。此外,高估程度取决于为开发G(E)函数所假设的每个探测器的照射方向。关于探测器的方向依赖性,只要正确确定晶体的照射表面,使用在单向照射几何形状中确定的G(E)函数就可以获得环境中可靠的空气剂量率。