DANGER IN EXTRAPOLATING INDOOR RADON RISK FROM UNDERGROUND MINER DATA

2004 ◽  
Vol 87 (6) ◽  
pp. 670-671
Author(s):  
Philippe Duport
2014 ◽  
Vol 29 (2) ◽  
pp. 142-148 ◽  
Author(s):  
Tatyana Pavlenko ◽  
Olga German ◽  
Miroslava Frizyuk ◽  
Nikolay Aksenov ◽  
Anatoliy Operchyuk

In 2010 one area of Ukraine (Kirovograd area) was selected for a pilot project to reduce radon risks. The project consists of several stages: radon risk training for the public health professionals, measurements of radon concentration in schools and nurseries (more than 1000 buildings were examined), justifications of radon countermeasures and their implementation. The lognormal frequency distribution for equivalent equilibrium concentration was authentically established. The geometric mean of the indoor radon equivalent equilibrium concentration was established to 63 Bq/m3, and standard deviation is equal to 82 Bq/m3. The indoor radon equivalent equilibrium concentration ranged from 22 Bq/m3 to 809 Bq/m3. It was found that the national regulatory limit for this type of buildings was exceeded in more than 50% of the cases. The second phase of the project has a goal to remediate radon levels and reduce radon risks. Calculated exposure doses and radon risk were used to justify the remediation and assess the economic loss for the region caused by radon irradiation of the population.


2020 ◽  
Vol 55 ◽  
pp. S227-S233 ◽  
Author(s):  
C. Turcanu ◽  
C. Schieber ◽  
T. Schneider ◽  
C. Fallon ◽  
R. Geysmans ◽  
...  

Radon in buildings poses a significant health risk, being one of the most important causes of lung cancer deaths worldwide. Acknowledging that successful radon risk management requires engagement of stakeholders, this paper investigated prescriptions and practices for stakeholder participation. First, it points out the need to integrate radon risk management in a holistic approach to indoor air pollution, together with urban planning and energy saving policies. It then argues for establishing more systematic approaches to the involvement of stakeholders in the design, implementation and evaluation of radon actions. Finally, it suggests the development of context specific approaches for the engagement of stakeholders at local and regional level.


2003 ◽  
Vol 70 (3) ◽  
pp. 161-176 ◽  
Author(s):  
Lene H.S Veiga ◽  
Sérgio Koifman ◽  
Vicente P Melo ◽  
Ivanor Sachet ◽  
Eliana C.S Amaral

1998 ◽  
Vol 4 (4) ◽  
pp. 316-321
Author(s):  
Kęstutis Gasiūnas ◽  
Albinas Mastauskas ◽  
Gendrutis Morkūnas

Uranium and its daughters including Ra-226 are naturally present in the Earth's crust and other environmental bodies. During decay of Ra-226 radioactive noble gas radon is produced. This gas emanates to the atmosphere from solid matrixes containing Ra-226. It causes a special problem connected with the fact that radon accumulates in the closed spaces of buildings. Increased concentrations of radon indoors in many cases are the significant source of human exposure to ionizing radiation. Radon daughters having been deposited in the airways of human lungs are the source of alpha particles which irradiates the inner surface of airways. Since radiation quality of alpha radiation is high and small volumes of tissues are being irradiated, the influence of indoor radon as a source of ionizing radiation is significant. In order to forecast indoor radon concentrations and to take necessary remedial (in existing buildings) or prevention (in new buildings) measures, the main sources of indoor radon should be known in each country or geographical region. It may be soil, building materials, water and natural gas. It has been determined that the main source of indoor radon in Lithuania is soil. Permanent investigations of radionuclide content of building materials used or manufactured in Lithuania have not revealed any building materials with concentrations of naturally occurring radionuclides exceeding maximum permitted levels determined by the Lithuanian Hygienic Standards HN 40-1994. These investigations are performed by means of gamma spectrometry using the Ge spectrometer by Oxford after sample grinding and drying. A short review of radon risk mapping techniques used in Sweden, USA, Germany and Czech Republic is presented in paper. These techniques may be used for creation of similar technique in Lithuania with corrections connected with local geology. When determining radon risk mainly two parameters should be taken into account: radium content in soil (or radon content in soil air) which is associated with the type of soil and permeability of soil. The Lithuanian system of radon risk determination is not created yet because more detailed data on radon concentrations in soil air should be collected. Data from field measurements of radon concentrations in soil air and concentrations of naturally occurring radionuclides are presented. These measurements were carried out in some potentially important from the point of view of radon risk regions of Lithuania. Concentrations of Ra-226, Th-228 and K-40 in soil have been measured by gamma spectrometer GR-256 by Exploranium on the surface layer (up to 30 cm) of soil. Concentrations of radon in soil have been measured by MARKUS 10 in the depth of 70 cm. The measurements have been performed directly without sampling and sample preparation by digging the detector of Exploranium and pumping rod of MARKUS 10 in the investigated soil. The results indicate that there are some regions in Lithuania with radon concentrations in soil air exceeding 100 kBq/m3. Though radon risk depends on soil permeability these results show that these areas may be identified as areas of medium or even high radon risk. The system for classification of building sites in terms of indoor radon risk should be created in Lithuania in order to follow requirements of Lithuanian radiation protection standards and to keep below determined action levels of indoor radon- 400 Bq/m3 in existing buildings and 200 Bq/m3 in constructed ones. Results of indoor radon measurements are presented as well. The measurements have been performed in 400 randomly selected detached houses during heating season in two lowest permanently used rooms. Duration of one measurement exceeds 3 weeks. E-PERM electrets have been used for this type of measurements. The results show that the average concentration of indoor radon in Lithuania is 55 Bq/m3. In some cases these concentrations exceed the above-mentioned action levels and approach 2000 Bq/m. It shows that indoor radon problems exist in Lithuania as in many other countries. The average concentration of indoor radon in karst region is 125 Bq/m3. It shows that special attention should be paid to such regions because conditions for increased intake of radon to buildings may exist. Indoor radon is one of the main sources of exposure in Lithuania. In some cases it may be the essential source causing tens of milisieverts of annual effective dose. It shows that the problem of indoor radon is important in Lithuania.


Author(s):  
Javier Elío ◽  
Quentin Crowley ◽  
Ray Scanlon ◽  
Jim Hodgson ◽  
Stephanie Long ◽  
...  

Background: Indoor radon represents an important health issue to the general population. Therefore, accurate radon risk maps help public authorities to prioritise areas where mitigation actions should be implemented. As the main source of indoor radon is the soil where the building is constructed, maps derived from geogenic factors ([e.g. geogenic radon potential [GRP]) are viewed as valuable tools for radon mapping. Objectives: A novel indirect method for estimating the GRP at national/regional level is presented and evaluated in this article. Design: We calculate the radon risk solely based on the radon concentration in the soil and on the subsoil permeability. The soil gas radon concentration was estimated using airborne gamma-ray spectrometry (i.e. equivalent uranium [eU]), assuming a secular equilibrium between eU and radium (226Ra). The subsoil permeability was estimated based on groundwater subsoil permeability and superficial geology (i.e. quaternary geology) by assigning a permeability category to each soil type (i.e. low, moderate or high). Soil gas predictions were compared with in situ radon measurements for representative areas, and the resulting GRP map was validated with independent indoor radon data. Results: There was good agreement between soil gas radon predictions and in situ measurements, and the resultant GRP map identifies potential radon risk areas. Our model shows that the probability of having an indoor radon concentration higher than the Irish reference level (200 Bq m-3) increases from c. 6% (5.2% – 7.1%) for an area classified as Low risk, to c. 9.7% (9.1% – 10.5%) for Moderate-Low risk areas, c. 14% (13.4% – 15.3%) for Moderate-High risk areas and c. 26% (24.5% – 28.6%) for High risk areas. Conclusions: The method proposed here is a potential alternative approach for radon mapping when airborne radiometric data (i.e. eU) are available.


1988 ◽  
Vol 24 (1-4) ◽  
pp. 367-370 ◽  
Author(s):  
E. Stranden ◽  
T. Strand

Abstract Alum shale is known to contain enhanced levels of radium, and may thus be a source of enhanced radon concentrations. The Hedemarken area in the south-eastern part of Norway has, due to its high geological occurrence of alum shale, been the subject of an extensive study on indoor radon. Measurements of the activity concentration of soil and shale, radon exhalation from the ground and from geological samples, are reported, together with measurements of indoor radon concentrations in about 200 houses. In about 70 houses, the radon concentration exceeded 400 Bq.m-3, and the highest concentration (mean value for a house) was 5300 Bq.m-3. Radon exhalation measurements from the ground suggest that the alum shale areas generally should be classified as high radon risk areas.


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