Walsh L, Zhang W, Shore R E, Auvinen A, Laurier D, Wakeford R, Jacob P, Gent N, Anspaugh L R, Schüz J, Kesminiene A, van Deventer E, Tritscher A, del Rosarion Pérez M
a BfS - Federal Office for Radiation Protection, Radiation Protection and Health, Neuherberg, Germany.
Radiat Res. 2014 Nov;182(5):556-72. doi: 10.1667/RR13779.1. Epub 2014 Sep 24.
We present here a methodology for health risk assessment adopted by the World Health Organization that provides a framework for estimating risks from the Fukushima nuclear accident after the March 11, 2011 Japanese major earthquake and tsunami. Substantial attention has been given to the possible health risks associated with human exposure to radiation from damaged reactors at the Fukushima Daiichi nuclear power station. Cumulative doses were estimated and applied for each post-accident year of life, based on a reference level of exposure during the first year after the earthquake. A lifetime cumulative dose of twice the first year dose was estimated for the primary radionuclide contaminants ((134)Cs and (137)Cs) and are based on Chernobyl data, relative abundances of cesium isotopes, and cleanup efforts. Risks for particularly radiosensitive cancer sites (leukemia, thyroid and breast cancer), as well as the combined risk for all solid cancers were considered. The male and female cumulative risks of cancer incidence attributed to radiation doses from the accident, for those exposed at various ages, were estimated in terms of the lifetime attributable risk (LAR). Calculations of LAR were based on recent Japanese population statistics for cancer incidence and current radiation risk models from the Life Span Study of Japanese A-bomb survivors. Cancer risks over an initial period of 15 years after first exposure were also considered. LAR results were also given as a percentage of the lifetime baseline risk (i.e., the cancer risk in the absence of radiation exposure from the accident). The LAR results were based on either a reference first year dose (10 mGy) or a reference lifetime dose (20 mGy) so that risk assessment may be applied for relocated and non-relocated members of the public, as well as for adult male emergency workers. The results show that the major contribution to LAR from the reference lifetime dose comes from the first year dose. For a dose of 10 mGy in the first year and continuing exposure, the lifetime radiation-related cancer risks based on lifetime dose (which are highest for children under 5 years of age at initial exposure), are small, and much smaller than the lifetime baseline cancer risks. For example, after initial exposure at age 1 year, the lifetime excess radiation risk and baseline risk of all solid cancers in females were estimated to be 0.7 · 10(-2) and 29.0 · 10(-2), respectively. The 15 year risks based on the lifetime reference dose are very small. However, for initial exposure in childhood, the 15 year risks based on the lifetime reference dose are up to 33 and 88% as large as the 15 year baseline risks for leukemia and thyroid cancer, respectively. The results may be scaled to particular dose estimates after consideration of caveats. One caveat is related to the lack of epidemiological evidence defining risks at low doses, because the predicted risks come from cancer risk models fitted to a wide dose range (0-4 Gy), which assume that the solid cancer and leukemia lifetime risks for doses less than about 0.5 Gy and 0.2 Gy, respectively, are proportional to organ/tissue doses: this is unlikely to seriously underestimate risks, but may overestimate risks. This WHO-HRA framework may be used to update the risk estimates, when new population health statistics data, dosimetry information and radiation risk models become available.
我们在此介绍世界卫生组织采用的一种健康风险评估方法,该方法为估算2011年3月11日日本大地震及海啸后福岛核事故的风险提供了一个框架。人们高度关注了福岛第一核电站受损反应堆产生的辐射对人类健康可能造成的风险。根据地震后第一年的参考暴露水平,对事故后每年的累积剂量进行了估算并应用。对于主要放射性核素污染物((134)Cs和(137)Cs),估算了相当于第一年剂量两倍的终身累积剂量,其依据是切尔诺贝利数据、铯同位素的相对丰度以及清理工作情况。考虑了对特别放射敏感的癌症部位(白血病、甲状腺癌和乳腺癌)的风险,以及所有实体癌的综合风险。针对不同年龄暴露人群,根据终身归因风险(LAR)估算了事故辐射剂量导致的癌症发病的男性和女性累积风险。LAR的计算基于日本近期的癌症发病率人口统计数据以及日本原子弹幸存者寿命研究的当前辐射风险模型。还考虑了首次暴露后最初15年的癌症风险。LAR结果也以占终身基线风险(即无事故辐射暴露情况下的癌症风险)的百分比形式给出。LAR结果基于参考第一年剂量(10 mGy)或参考终身剂量(20 mGy),以便可将风险评估应用于重新安置和未重新安置的公众成员以及成年男性应急工作人员。结果表明,参考终身剂量对LAR的主要贡献来自第一年剂量。对于第一年剂量为10 mGy并持续暴露的情况,基于终身剂量的终身辐射相关癌症风险(最初暴露时5岁以下儿童风险最高)很小,且远低于终身基线癌症风险。例如,在1岁时首次暴露后,女性所有实体癌的终身额外辐射风险和基线风险估计分别为0.7·10(-2)和29.0·10(-2)。基于终身参考剂量的15年风险非常小。然而,对于儿童时期的首次暴露,基于终身参考剂量的15年风险分别高达白血病和甲状腺癌15年基线风险的33%和88%。在考虑一些注意事项后,结果可按特定剂量估计进行缩放。一个注意事项与缺乏确定低剂量风险的流行病学证据有关,因为预测风险来自拟合到宽剂量范围(0 - 4 Gy)的癌症风险模型,该模型假设剂量小于约0.5 Gy和0.2 Gy时实体癌和白血病的终身风险分别与器官/组织剂量成比例:这不太可能严重低估风险,但可能高估风险。当有新的人群健康统计数据、剂量测定信息和辐射风险模型可用时,这个世界卫生组织健康风险评估框架可用于更新风险估计。