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1979, Nature
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Individuals receive a significant part of their radiation exposure indoors. We anticipate that this exposure is likely to increase in the near future, due to a growing use in the building industry of recycled materials and materials previously regarded as waste. Such materials often contain elevated levels of natural radionuclides. Directive 2013/59/Euratom ('Basic Safety Standards', BSS) pays comprehensive attention to indoor exposure from natural radionuclides, but proper implementation of all corresponding BSS regulations is not straightforward , especially when regarding the regulation of building materials containing so-called Annex XIII materials. In this paper, we discuss the most relevant deficiencies in the BSS and present a practical approach to cope with these. Our most important observation is that adequate methods for assessing the annual dose due to gamma radiation from building materials are not provided by the BSS. This is in particular difficult because compliance of single building materials has to be tested, but the corresponding BSS reference level refers to gamma radiation emitted by all building materials present in a room. Based on a simple model of three layers of building materials , we present a set of operational conditions for building materials, either used for construction purposes ('bulk layers') or for the finishing of walls, floors and ceilings ('superficial layers'). Any customary combination of building materials meeting these conditions will stay below the BSS reference level for gamma radiation. This statement holds for the middle of a reference room, but is not always the case close to the walls, especially when low density materials with a relatively high content of natural radionuclides are present at the inner side of the room. This can be avoided by applying more strict conditions for those kind of materials than presented in this paper. We further focus on the indoor exposure to thoron progeny. Building materials that pass the test for gamma radiation can still be a significant source for indoor air concentrations of thoron progeny. When the average annual thoron inhalation dose were to be restricted to 1 mSv a −1 − a level comparable to the BSS reference level for gamma radiation − the activity concentration of Ra-224 in (especially porous) building materials used for wall finishing purposes should be limited to a value of typically 50 Bq kg −1. Even if our suggested approach of the BSS regulations is fully implemented, it still allows for a significant increase in the average radiation exposure in dwellings due to external radiation and thoron progeny. However, the situation will be worse if a less strict interpretation of the BSS regulations will be applied.
SSRN Electronic Journal, 2020
Radon is a naturally occurring radioactive, colorless, tasteless and odorless gas which is chiefly present inside the earth. The earth is heterogeneous and not homogeneous .The concentration of radon inside the earth therefore varies with latitude, longitude and altitudes. The earth has two sources of heat –solar energy on the surface and radioactive decay of certain materials within itself. Radon is a gas which is released during the intermediate stage of radioactive decay inside the earth. Anthropological activities involve two major types of interventions into the earth –transfer of load and/or anchoring and for prospecting. Both these activities release radon onto the surface. The various ways in which this harmful radioactive gas is released into our confined indoor spaces is discussed and presented. The causes for the same are analyzed and the harmful effects of the same are enumerated. Simple, practical and out of the box solutions are proposed to alleviate this problem. It is also ensured that all the mitigation measures proposed are sustainable, eco-friendly and have the least impact on the environment. It is also reiterated that unless some positive and decisive steps are taken at the earliest the sixth extinction of our planet is a mere formality.
Background: Radon gas, which emanates from thorium and uranium ore-bearing rocks scattered throughout the surface soil and underground, can concentrate indoors and reach levels that represent a public health risk. According to the World Health Organization (WHO) and the US Environmental Protection Agency (EPA), radon is the second leading cause of the lung cancer worldwide. Due to the direct correlation between the lung cancer and radon exposure, it is important to directly, accurately, simply, and rapidly measure radon accumulation in Iranian dwellings built with various materials. Thus, the aim of this study was to measure the effects of these materials on ambient radon concentrations in Iran dwellings.
The health risks associated with exposure to radon are variously described across different jurisdictions but the exposure-risk scenario may change as buildings are better sealed to make them more energy efficient as a climate change mitigation strategy. Radon which is ubiquitous in the air and often concentrated inside buildings may become more concentrated with better sealed buildings. Some countries such as the UK and the US currently have radon mitigation design standards and building codes which they use for the design and construction of buildings, whereas some other countries such as Australia and New Zealand presently take little or no cognisance of the potential problem of radon exposure in buildings. The increasing awareness of constructing well sealed and insulated buildings that are more energy-efficient is likely to result in increased radon concentrations in buildings. Radon is a known carcinogen that is a significant cause of lung cancer, and greater concentrations of radon in buildings are likely to result in increased levels of lung cancer. Better sealed energy-efficient buildings are undoubtedly required as a climate change mitigation strategy but there needs to be a greater awareness of the potential problem of increased radon concentrations so that buildings are also designed and constructed to address this.
Nature, 2021
Radioactive radon gas inhalation is a major cause of lung cancer worldwide and is a consequence of the built environment. The average radon level of properties built in a given period (their 'innate radon risk') varies over time and by region, although the underlying reasons for these differences are unclear. To investigate this, we analyzed long term radon tests and buildings from 25,489 Canadian to 38,596 Swedish residential properties constructed after 1945. While Canadian and Swedish properties built from 1970 to 1980s are comparable (96-103 Bq/m 3), innate radon risks subsequently diverge, rising in Canada and falling in Sweden such that Canadian houses built in the 2010-2020s have 467% greater radon (131 Bq/m 3) versus Swedish equivalents (28 Bq/m 3). These trends are consistent across distinct building types, and regional subdivisions. The introduction of energy efficiency measures (such as heat recovery ventilation) within each nation's build codes are independent of radon fluctuations over time. Deep learning-based models forecast that (without intervention) the average Canadian residential radon level will increase to 176 Bq/m 3 by 2050. Provisions in the 2010 Canada Build Code have not significantly reduced innate radon risks, highlighting the urgency of novel code interventions to achieve systemic radon reduction and cancer prevention in Canada.
Radiation Protection Dosimetry, 2013
The average radon concentration in Israeli dwellings was assessed by combining the results of a 2006 radon survey in singlefamily houses with the results of a 2011 radon survey in apartments of multistorey buildings. Both surveys were based on long-term measurements using CR-39 detectors. The survey in multistorey buildings was intended to assess the influence of recent practices in the local building industry on the radon concentrations. These practices include the use of building materials with higher concentrations of the natural radionuclides in the last 20 y than before, as well as the improvement in sealing techniques over that period. Another practice in place since the early 1990 s is the building of a shielded area in every apartment that is known as an RSS (residential secure space). The RSS is a room built from massive concrete walls, floor and ceiling that can be hermetically sealed and is intended to protect its residents from a missile attack. The influence of the above-mentioned features on radon concentrations was estimated by dividing the participating apartments into two groups: apartments in buildings >20 y, built using building materials with low concentrations of the natural radionuclides, regular sealing and without an RSS and apartments in buildings newer than 10 y, built using building materials with higher concentrations of the natural radionuclides, improved sealing and including an RSS. It was found that the average radon concentration in apartments in new buildings was significantly higher than in old buildings and the average radon concentration in single-family houses was significantly higher than in apartments in multistorey buildings. Doses due to indoor radon were estimated on the basis of the updated information included in the 2009 International Commission on Radiological Protection statement on radon.
Journal of Environmental Radioactivity
Radon, a naturally occurring radioactive gas generated underground by radioactive decay of nuclides contained in certain types of rocks, can concentrate inside buildings, where it poses the second-largest risk factor for lung cancer, after smoking. The highest concentrations of domestic radon in the UK occur in the southwestern counties of Devon and Cornwall, but certain areas in Northamptonshire and surrounding counties in the English Midlands also have high levels. It has been shown that it is possible both to reduce the radon concentrations in existing houses and to build new homes with appropriate protection. Since 1999, the UK's Building Regulations have specified that all new homes should be built with a combined radon-proof/damp-proof membrane plus, in Radon Affected Areas, a sump under the building. However, the building regulations do not require that the radon level is measured once the house is built and so there is little information on the effectiveness of these measures. Builders generally do not mention radon, and when asked, just confirm that their houses are built to current standards. To better understand the efficacy or otherwise of the currently mandated radon-protection measures, a crosssectional investigation was carried out in 26 new housing developments in high-radon areas in Northamptonshire. In a targeted mail-shot, 1056 householders were invited to apply for a free radon test; 124 replied (11.7%). In total, 94 pairs of detectors were returned (70.1% of responders), of which two were spoiled, giving a total of 92 results. Following processing and seasonal correction, the arithmetic mean radon concentration in the target houses was 45% of the arithmetic mean radon concentration in existing houses in the postcode sectors where the houses were built and were approximately log-normally distributed. No results exceeded the UK Action Level of 200 Bq. m −3 but three were above the Target Level of 100 Bq. m −3. The results suggest that the radon-proof membranes in general ensure that radon concentrations in new homes constructed in accordance with the Building Regulations in Radon Affected Areas (RAAs) are satisfactorily low. However, there is a very small statistical probability that levels in a small number of homes will be close to or above the Action Level, particularly in areas of high radon potential. As a result, the Public Health England (PHE) recommendation for testing in the first year of occupation should be adopted as a legal requirement.
Commonly used building construction materials, radiation shielding bricks, hematite aggregate and other materials have been analyzed for the activity concentration of the natural radionuclides, namely 238 U, 232 Th and 40 K, besides the radon exhalation rates. The activity concentration for 238 U, 232 Th and 40 K varies from 2971 to 9874 Bq kg À1 , 2072 to 11272.8 Bq kg À1 , and 20078 to 1908715.6 Bq kg À1 , respectively, in various materials studied in the present work. Radon activity in the various samples varies from 190711 to 313714 Bq m À3 , the mass exhalation rate for radon varies from 1.0570.07 to 1.9270.09 mBq kg À1 h À1 and surface exhalation rate varies from 9.070.30 to 19.8722 mBq m À2 h À1 for materials under investigation. The activity concentrations of uranium, thorium and potassium and radon exhalation rates vary from material to material. Thorium and potassium activity in the granite materials is higher, followed by radiation shielding material compared to other common construction materials. Uranium activity concentration is higher in cement as compared to radiation shielding material and other common construction materials. The absorbed dose varies from 23 to 185 nGy h À1 and the indoor annual effective dose varies from 0.11 to 0.91 mSv. The outdoor annual effective dose varies from 0.03 to 0.23 mSv. The absorbed dose and the effective dose equivalent are found to be higher in the granite, followed by radiation shielding material and other common construction materials. In all the samples, the activity concentration of 238 U, 232 Th and 40 K is found below the permissible levels. A strong correlation coefficient has been observed between radon activity and surface exhalation rate (correlation coefficient ¼ 0.899).
International Congress …, 2002
Civil and Environmental Engineering, 2021
Radon is a naturally occurring radioactive gas, which tends to accumulate inside built structures. It is therefore necessary to include techniques to mitigate radon concentration during refurbishing work. The aim of this study is to assess the effectiveness of a number of mitigation techniques, under real conditions, to determine which is most suitable, in each case, for use in rebuilding solutions. The methodology consisted in performing four experimental tests on mitigation strategies recommended by the Código Técnico de la Edificación (Technical Building Code) (CTE-DB-HS6) and by the Government of the Autonomous Community of Galicia, (Xunta de Galicia, 2018). The concentration was measured with three different systems: radon in soil at 80 cm, passive detectors to confirm mean concentration, and continuous monitoring by devices calibrated at the LaRUC Laboratory of the University of Cantabria, in order to compare the results of the tests. The experiments were carried out in premis...
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