This paper presents the results of a survey of radon concentrations in Irish primary and post-primary schools. The objective of this survey was to assess the distribution of radon in Irish schools and to identify those requiring remedial work to reduce radon exposure to children and staff. All primary and post-primary schools were invited to participate in the survey. Indoor radon concentrations were measured during the academic year using integrating passive alpha track-etch detectors with a measurement period from three to nine months. The survey was carried out on a phased basis from 1998 to 2004 and is one of the most comprehensive of its kind undertaken in Europe. Measurements were completed in 38 531 ground floor classrooms and offices in 3826 schools, representing over 95% of the approximate 4000 primary and post-primary schools in Ireland. Of these, 984 schools had radon concentrations greater than 200 Bq m(-3) in 3028 rooms and 329 schools had radon concentrations in excess of 400 Bq m(-3) in 800 rooms. The average radon concentration in schools was 93 Bq m(-3). This results in an annual average effective dose to an Irish child from exposure to radon of 0.3 mSv per year, assuming that the long-term radon concentration is equal to the radon concentration present during the working hours and that the annual average occupancy is 1000 h per year. A programme of remediation of schools with radon concentrations above 200 Bq m(-3) has been put in place.
Published information on the distribution of radon levels in Spanish single family dwellings is used to evaluate the cost-effectiveness of three different intervention scenarios: remediation of existing dwellings, radon proofing of all future dwellings and the targetting of areas with higher than average indoor radon concentrations. Analysis is carried out on the basis of a Reference Level of for the existing housing stock and for new dwellings. Certain assumptions are made about the effectiveness and durability of the measures applied and annualised costs are used to calculate the costs per lung cancer death averted. The results reveal that targetting future housing is a more cost-effective option than remediation of existing dwellings with radon concentrations above the Reference Level - the costs per lung cancer death averted are typically $145 000. In high-risk areas, these costs can be considerably less, depending on the percentage of dwellings expected to exceed the Reference Level and the average savings in exposure as a result of the intervention. The costs of intervention to reduce lung cancer deaths following exposure to radon compare favourably with those of other health programmes in other countries.
Radon concentrations in homes have been shown to vary considerably with season. It is important to account for this by applying a correction factor to any home radon measurement of less than one year. To date, Irish radon measurement services have used correction factors based on data derived for the UK in the 1980s. In the absence of similar data for Ireland at the time, these were considered suitable for use due to the similarities between the climates, house types and lifestyles in the two countries. In order to better estimate the long-term radon concentration, measurements from 5640 Irish homes were used to derive a set of correction factors specifically for Ireland. These were generated by means of Fourier decomposition analysis and the new correction factors compared, using 95% confidence intervals, to those derived for the UK using the same analysis and to those currently in use for Ireland. In both cases, a significant difference was found between 10 of the 12 monthly seasonal correction factors. This paper presents the methods used in detail and the results of the analysis.
The results of a national radon survey of 1555 Spanish single family dwellings have been used as the basis for considering the need for and optimisation of intervention to reduce exposure. Certain assumptions have been made about the distribution of radon levels in apartments in order to define the total number of dwellings in need of remediation for reference levels within the range 200-600 Bq m-3. The costs of remediation have been based on the use of radon sumps and published data on installation and maintenance costs have been applied. The monetary value of radiation detriment has been calculated on the basis of the gross national product for Spain and a multiplication factor to account for psycho-social factors has been derived and applied. When compared with everyday risks over which the individual has some control, a reference level somewhere within the range 100-300 Bq m-3 is suggested. The results of cost-benefit analysis are inconclusive: the net benefit of intervention varies by less than 10% for the range of reference levels considered, The sensitivity of the results to changes in either the number of dwellings to be remediated or the monetary value of radiation detriment is also reported. In terms of lung cancer death averted, the costs are within the range $140000-$260000, the higher values being associated with the most restrictive reference level. It is concluded that a high degree of weight can be assigned to the social and political factors in any final decision on choice of reference levels and the responsible national agencies need to consider the costs per life saved by other health initiatives in order to derive maximum benefit from national expenditure.
An advisory reference level of 200 Bq m(-3) and a statutory reference level of 400 Bq m(-3) apply to radon exposure in Irish schools. Following the results of a national survey of radon in Irish schools, several hundred classrooms were identified in which the reference levels were exceeded and a remediation program was put in place. This paper provides an initial analysis of the effectiveness of that remediation program. All remediation techniques proved successful in reducing radon concentrations. Active systems such as radon sumps and fan assisted under-floor ventilation were generally applied in rooms with radon concentrations above 400 Bq m(-3). These proved most effective with average radon reduction factors of 9 to 34 being achieved for radon sumps and 13 to 57 for fan assisted under-floor ventilation. Both of these techniques achieved maximum radon reduction factors in excess of 100. The highest average reduction factors were associated with the highest initial radon concentrations. Passive remediation systems such as wall and window vents were used to increase background ventilation in rooms with radon concentrations below 400 Bq m(-3) and achieved average radon reductions of approximately 55%. Following the installation of active remediation systems, the radon concentration in adjacent rooms, i.e., rooms in which the radon concentration was already below 200 Bq m(-3) and therefore did not require remediation, was further reduced by an average of 25%. The long-term effectiveness of a number of radon sump systems with at least three years operation showed no evidence of fan failures. This study showed an apparent increase in sump effectiveness with time as indicated by an increase in radon reduction factors during this period.
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