State Institution «O.M. Marzieiev Institute for Public Health of the National Academy of Medical Sciences of Ukraine», 50 Popudrenka St., Kyiv, 02094, Ukraine.
State institution «Public health center of the Ministry of health of Ukraine», 41 Yaroslavska St., Kyiv, 04071, Ukraine.
Probl Radiac Med Radiobiol. 2020 Dec;25:220-229. doi: 10.33145/2304-8336-2020-25-220-229.
To analyze and evaluate the available information to indoor radon concentration in the context of theimplementation of the radon action plan.
indoor radon-222 in dwellings by area and corresponding radiation risks of the population. Measurements were performed using passive track radonometry. The exposure time of the radonometers is atleast 30 days during heating season. Radiation risk calculations were performed according to the dose coefficientsand mathematical models of the ICRP.
It was found that for the whole country, reference level 300 Bq/m3 (radon gas) is exceeded in 16 % ofcases. It was found that geometric mean of radon gas levels was 120 Bq/m3 and varies from 35 to 265 Bq/m3 bydifferent area, namely the difference between radon levels in different territories of the country can be up to 7.5times. Variability of radon levels at the district level is also significant. It was found, radon activity concentrationdiffering by almost 10 times by districts with lognormal distribution and a geometric mean of 75 Bq/m3. The analy-sis of radiation risks of the population has established that estimated annual number of lung cancer deaths due toradon in Ukraine is almost 8,900 cases; and а direct economic loss for the country are estimated at more than $450 million a year.
Surveys of radon levels demonstrated significant variation in radon concentrations between different regions. For the whole country, reference level (300 Bq/m3) is exceeded on above 16 % of the dwellings, butpercentage of exceeding varies from 0.1 to 43.0 % by different area. Information on indoor radon concentrationsin almost a third of the country is non-available. For an effective implementation of the Action plan, it makes sense to introduce radon risk mapping.
分析和评估可获得的信息,以了解氡行动计划实施背景下的室内氡浓度情况。
通过地区划分的住宅内氡-222 及其对应的人口辐射风险。采用被动径迹氡测量法进行测量。氡测量计的暴露时间在供暖季节至少为 30 天。辐射风险计算根据 ICRP 的剂量系数和数学模型进行。
研究发现,全国范围内有 16%的住宅超过了参考水平 300 Bq/m³(氡气)。研究发现,氡气水平的几何平均值为 120 Bq/m³,因地区而异,范围在 35 到 265 Bq/m³之间,即该国不同地区的氡水平差异可达 7.5 倍。地区层面的氡水平变化也很显著。研究发现,氡气活度浓度在区一级的分布呈对数正态分布,几何平均值为 75 Bq/m³,变化幅度近 10 倍。对人口的辐射风险分析表明,乌克兰因氡导致的肺癌年死亡人数估计近 8900 例;该国每年的直接经济损失估计超过 4.5 亿美元。
氡水平调查表明,不同地区的氡浓度存在显著差异。全国范围内,有超过 16%的住宅超过了参考水平(300 Bq/m³),但不同地区的超标比例从 0.1%到 43.0%不等。全国近三分之一地区的室内氡浓度信息无法获得。为了有效实施行动计划,有必要引入氡风险图。