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用于级联冲击器采样数据的有效剂量缩放因子在tenorm吸入暴露中的应用。

Effective dose scaling factors for use with cascade impactor sampling data in tenorm inhalation exposures.

作者信息

Kim Kwang Pyo, Wu Chang-Yu, Birky Brian K, Bolch Wesley E

机构信息

Department of Nuclear and Radiological Engineering, University of Florida, Gainesville, 32611-8300, USA.

出版信息

Health Phys. 2005 Oct;89(4):359-74. doi: 10.1097/01.hp.0000167149.04026.0d.

Abstract

When assessing the effective dose to workers following radio-aerosol inhalation exposures, significant reductions in dose uncertainty can be achieved through direct measurement of the particle-size distribution. The University of Washington Mark III cascade impactor is one such air sampling device that permits the user to determine aerosol mass and radioactivity concentrations as a function of particle size within eight different size intervals (each corresponding to a different impactor stage or end filter). Traditionally, dose assessments made using the LUDEP code or other internal dosimetry software utilize this air sampling information by assigning the radioactivity measured at each stage as concentrated at a single representative size central to the size interval. In this study, we explore more realistic assumptions that the measured radioactivity distributes uniformly, linearly increases, or linearly decreases across the particle size interval for each impactor stage. The concept of an effective dose scaling factor, SF(E), is thus introduced whereby (1) the former approach can be used (which requires less computational effort using the LUDEP code), and (2) the resulting values of effective dose per stage can then be rescaled to values appropriate to a linear radioactivity distribution per stage. For a majority of (238)U-series radionuclides, particle size ranges, and absorption classes, differences in these two approaches are less than 10%, and thus no corrections in effective dose per particle stage are needed. Significant corrections, however, were noted in select cases. For uniform or linearly decreasing radioactivity distributions, end-filter particles (0.03 to 0.35 microm) of type F, M, or S radionuclides were assigned values of SF(E) ranging from 1.15 to 1.44, while 3(rd) stage particles (4.5 to 12 microm) of type M and S radionuclides were assigned values of SF(E) ranging from 1.11 to 1.53. When the cascade impactor measurements indicate a linear increase of activity across a given impactor-stage size range, values of SF(E) range from a high of 1.11 (6(th) stage particles of type F radionuclides) to lows of 0.85 to 0.91 (4(th) stage and end-filter particles of type M and S radionuclides). In these cases, the inhalation dose coefficient varies non-linearly across the particle size range, and the assumption of a mono-size distribution per impactor stage either underestimates (SF(E) > 1) or overestimates (SF(E) < 1) that stage's contribution to the worker effective dose.

摘要

在评估放射性气溶胶吸入暴露后工人的有效剂量时,通过直接测量粒径分布可显著降低剂量不确定性。华盛顿大学Mark III级联撞击器就是这样一种空气采样装置,它能让使用者确定气溶胶质量和放射性浓度随八个不同粒径区间(每个区间对应一个不同的撞击器阶段或终端过滤器)内粒径的变化情况。传统上,使用LUDEP代码或其他内部剂量测定软件进行剂量评估时,会将每个阶段测量的放射性视为集中在该粒径区间中心的单一代表性粒径上,从而利用这些空气采样信息。在本研究中,我们探讨了更现实的假设,即对于每个撞击器阶段,测量的放射性在粒径区间内均匀分布、线性增加或线性减少。因此引入了有效剂量缩放因子SF(E)的概念,据此:(1) 可以采用前一种方法(使用LUDEP代码时计算量较小),(2) 然后将每个阶段的有效剂量结果重新缩放到适合每个阶段线性放射性分布的值。对于大多数(238)U系放射性核素、粒径范围和吸收类别,这两种方法的差异小于10%,因此每个粒径阶段的有效剂量无需校正。然而,在某些特定情况下发现了显著的校正。对于均匀或线性减少的放射性分布,F、M或S型放射性核素的终端过滤器颗粒(0.03至0.35微米)的SF(E)值范围为1.15至1.44,而M和S型放射性核素的第三阶段颗粒(4.5至12微米)的SF(E)值范围为1.11至1.53。当级联撞击器测量表明在给定撞击器阶段粒径范围内活性呈线性增加时,SF(E)值范围从最高的1.11(F型放射性核素的第六阶段颗粒)到最低的0.85至0.91(M和S型放射性核素的第四阶段颗粒和终端过滤器颗粒)。在这些情况下,吸入剂量系数在粒径范围内呈非线性变化,并且每个撞击器阶段单一粒径分布的假设要么低估了(SF(E) > 1)要么高估了(SF(E) < 1)该阶段对工人有效剂量的贡献。

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