Annual average and seasonal variations of residential radon concentration for all the Italian Regions

2005 ◽  
Vol 40 (2-6) ◽  
pp. 686-694 ◽  
Author(s):  
F. Bochicchio ◽  
G. Campos-Venuti ◽  
S. Piermattei ◽  
C. Nuccetelli ◽  
S. Risica ◽  
...  
2012 ◽  
Vol 112 ◽  
pp. 83-89 ◽  
Author(s):  
Dimitri D. Hauri ◽  
Anke Huss ◽  
Frank Zimmermann ◽  
Claudia E. Kuehni ◽  
Martin Röösli

2007 ◽  
Vol 103 (2) ◽  
pp. 185-190 ◽  
Author(s):  
J.M. Barros-Dios ◽  
A. Ruano-Ravina ◽  
J. Gastelu-Iturri ◽  
A. Figueiras

2015 ◽  
Vol 139 ◽  
pp. 149-153 ◽  
Author(s):  
Koseki Hayashi ◽  
Yumi Yasuoka ◽  
Hiroyuki Nagahama ◽  
Jun Muto ◽  
Tetsuo Ishikawa ◽  
...  

2021 ◽  
Vol 15 (Supplement_1) ◽  
pp. S587-S587
Author(s):  
M V Mauriz Barreiro ◽  
A Ruano-Raviña ◽  
I Baston-Rey ◽  
R Ferreiro-Iglesias ◽  
C Calviño-Suarez ◽  
...  

Abstract Background Inflammatory Bowel Disease (IBD) is a multifactorial pathology with an increasing incidence. There are environmental factors, many unknown, that participate in its development. There is no study having assessed a possible relationship with residential radon exposure, which is very high in the study area. The aim of this study was to analyze if residential radon concentration measured at a municipal level is associated with a higher incidence of IBD and its characteristics (clinical or demographic). Methods We performed an ecological study where we included all incident cases of IBD in the area of Santiago de Compostela between January and December 2017 in order to estimate municipal incidence rates. Radon levels at a municipal level were obtained from the Galician Radon Map and correlated with demographic factors and type of IBD. We used the Spearman’s correlation coefficient to test the existence of any association. Results 96 patients were included, 63 (65.6%) with Ulcerative Colitis, 29 (30.25) with Crohn’s Disease and 4 (4.2%) with indeterminate colitis. Median age was 41 (IQR: 33.5 to 56 years), and 50.0% were women. The incidence rate per 100.000 inhabitants-year in the study area was 21.6 cases. The median radon concentration was 104.9Bq/m3 (IQR: 91.0 to 154.6), without statistically significant differences in function of the location of the house (rural vs. urban) nor the type of edification (flat vs house), p >0.05. There were no statistically significant differences on the type of IBD developed (ulcerative colitis, Crohn’s disease or indeterminate colitis) regarding radon levels either (p>0.05). There were no statistically significant differences (p>0.05) between radon and sex of IBD cases. No correlation between radon levels and age of the individuals was observed (Spearman’s rho = -0.13, p-value 0.2), nor radon levels variation by age groups (p>0.05). There was no correlation between radon concentration and cumulative incidence of IBD at municipal level (Spearman’s rho = 0.13, p-value 0.5), as it is shown in figure 1. Conclusion In the area of Santiago de Compostela there is a higher incidence of IBD in comparison with previous studies taking western countries as reference. It is possible that some environmental risk factors, could be responsible of this difference. In this study we have not found any correlation with municipal average radon concentration and incidence of IBD or any of its types.


2020 ◽  
Vol 191 (2) ◽  
pp. 138-143
Author(s):  
G Venoso ◽  
M Ampollini ◽  
S Antignani ◽  
M Caprio ◽  
C Carpentieri ◽  
...  

Abstract Many international and national regulations on radon in workplaces, including the 2013/59/Euratom Council Directive, are based on the annual average of indoor radon concentration, assuming it is representative of the long-term average. However, a single annual radon concentration measurement does not reflect annual variations (i.e. year-to-year variations) of radon concentration in the same location. These variations, if not negligible, should be considered for an optimized implementation of regulations. Unfortunately, studies on annual variations in workplaces can be difficult and time-consuming and no data have been published on scientific journals on this issue. Therefore, we carried out a study to obtain a first evaluation of short-term annual variations in workplaces of a research institute in Rome (Italy). The radon concentration was measured in 120 rooms (mainly offices and laboratories) located in 23 buildings. In each room, two 1-year long measurements were performed, with an interval between the two measurements of up to 3 years. The results show variability between the two 1-year long measurements higher than the variability observed in a sample of dwellings in the same area. Further studies are required to confirm the results and to extend the study to other types of workplaces.


2010 ◽  
Vol 287 (2) ◽  
pp. 427-433 ◽  
Author(s):  
J. Somlai ◽  
J. Hakl ◽  
N. Kávási ◽  
G. Szeiler ◽  
P. Szabó ◽  
...  

1988 ◽  
Vol 24 (1-4) ◽  
pp. 231-235 ◽  
Author(s):  
H. Arvela ◽  
A. Voutilainen ◽  
I. Mäkeläinen ◽  
O. Castrén ◽  
K. Winqvist

Abstract Prediction of the variations of indoor radon concentration were calculated using a model relating indoor radon concentration to radon entry rate, air infiltration and meteorological factors. These calculated variations have been compared with seasonal variations of 33 houses during 1-4 years, with winter-summer concentration ratios of 300 houses and the measured dirunal variation. In houses with a slab in ground contact the measured seasonal variations are quite often in agreement with variations predicted for nearly pure pressure difference driven flow. The contribution of a diffusion source is significant in houses with large porous concrete walls against the ground. Air flow due to seasonally variable thermal convection within eskers strongly affects the seasonal variations within houses located thereon. Measured and predicted winter-summer concentration ratios demonstrate that, on average, the ratio is a function of radon concentration. The ratio increases with increasing winter concentration. According to the model the diurnal maximum caused by a pressure difference driven flow occurs in the morning, a finding which is in agreement with the measurements. The model presented can be used for differentiating between factors affecting radon entry into houses.


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