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PubMed2000

Radon awareness, testing, and remediation survey among New York State residents.

Between November 1995 and January 1997, a radon awareness, testing, and remediation survey was conducted to measure general awareness and factual knowledge about radon and prevalence of radon testing and remediation among New York State residents. The survey found that 82% of 1,209 respondents had heard of radon, but only 21% were knowledgeably aware of radon. With regard to radon testing, only 15% of respondents who were aware of radon had their homes tested. The percentage of respondents who were aware or knowledgeably aware of radon increased with increasing education level. The findings from the study suggest that the New York State public awareness programs that targeted high radon areas did show some effect both by increasing public awareness and promoting residential testing. The relatively low percentage of respondents who were knowledgeably aware of radon and the low percentage who had tested their homes strongly suggest that renewed efforts by the public health community are needed to increase knowledge about radon and its health effects and to encourage radon testing and remediation.

Adolescent↗
PubMed1990

[Survey of indoor radon concentrations in Fukuoka and Kagoshima prefectures].

It is now well established that radon and its daughter products account for nearly half of the average population exposure to ionizing radiations and that radon is the greatest single source of natural radiation to the population. Radon and its daughters are alpha-emitters, which are more biologically damaging than beta- and gamma-radiations. A nationwide survey of radon concentration was conducted by the National Institute of Radiological Sciences in order to estimate the contribution of radon and its daughters to the population dose in Japan. Authors surveyed indoor radon concentrations in Fukuoka and Kagoshima prefectures as part of this project. A passive type radon dosimeter, in which a sheet of polycarbonate film as the alpha-ray detector was mounted, was used to measure indoor radon concentrations. The resulting distribution of the average annual indoor radon concentrations in both prefectures can be characterized by an arithmetic mean of 24.4 Bq/m3 and a standard deviation of 13.1 Bq/m3, by a geometric mean of 22.2 Bq/m3, and by a median of 20.7 Bq/m3. The geometric means of the distributions for Fukuoka and Kagoshima were 25.4, and 18.4 Bq/m3, respectively. Radon concentrations were also generally high in winter and low in summer. Regarding the analysis of correlations between the concentrations and construction materials, radon concentrations were generally high in Japanese houses with earthen walls and in concrete structures. These results showed that seasons, the type of building materials, and regional differences were significant factors in the variation of indoor radon concentration.

Background Radiation↗
PubMedDate not supplied

[Indoor radon pollution in houses in the Apulian Region of Italy and evaluation of the probability of lung cancer in the population].

BACKGROUND: Radon-222 is a gaseous radioactive chemical which can be transformed into other radioactive chemicals, defined as "products of decay" or "radon's daughter". The modality of radon penetration into the buildings depends on the convection motion created in the ground, which suck it back, so causing the penetration. The principal effect on human health is the increase risk of lung cancer, in proportion to the concentration and the time people spend indoors with exposure to radon. OBJECTIVES: The study proposed to estimate the expected cases of radon-induced lung cancer in the population of Apulia due to contamination by indoor radon. METHODS: The study used the data obtained in a national survey made by ANPA (National Environmental Protection Agency) and ISS (High Health Institute), with the collaboration of the Regional Reference Centres for the Control of Environmental Radioactivity (CRR). In the Apulia Region 310 families (5000 nationwide) were involved, which were selected so as to constitute a representative sample both of the region and the country. Appropriate instruments for the measurement of mean concentrations of indoor radon (passive nuclear trace monitors were installed in the homes of the sample families in two different periods of year). We evaluated the variations of indoor radon concentration in the houses during spring-summer and autumn-winter periods, observing a predictable increase in the latter period. We assessed concentrations in relation to: 1. architectural features and location, 2. construction year, 3. building material, 4. presence of windows. RESULTS: We found higher contamination in the oldest non-cement buildings and on the lower floors. In Lecce and Castrì di Lecce we found a mean radon concentration higher than the national and the regional mean, which is equivalent to annual exposure of 0.54 and 0.46 WLM respectively. For these levels we estimated that the expected cases of radon-induced lung cancer will be 1.5 in Lecce and 1.3 in Castrì per 10,000 inhabitants. CONCLUSION: The results of our investigations confirm that indoor radon pollution is a significant problem as it is one of the main causes of lung cancer. Hence, precautionary measures to reduce as much as possible exposure to indoor radon are highly recommended.

Air Pollutants, Radioactive↗
PubMed2004

A physiologically based assessment of human exposure to radon released from groundwater.

Most of the indoor radon comes directly from the soil beneath the foundation of a basement. Recently, radon from groundwater was found to make some contribution to the total inhalation risk associated with radon in indoor air. This study presents a realistic exposure assessment of a human to indoor radon released from groundwater. First, the prediction of indoor radon concentration released from groundwater was based on a three-compartment model that was developed to describe the transfer and distribution of the radon released from groundwater in a house through showers, washing clothes, and flushing toilets. Second, a physiologically based pharmacokinetic (PBPK) model for inhaled radon was developed and used to estimate tissue group concentrations in a human body. The PBPK model provides reasonable predictions of uptake, excretion, and distribution of retained radon among tissue groups in the body. Hence, the approach using the PBPK model combined with realistic indoor exposure scenarios predicts the radon concentrations in tissue groups in the body associated with the indoor radon pollution. The results obtained from the study will help increase the quantitative understanding of the risk assessment issues associated with the indoor radon released from the groundwater.

Air Pollutants, Radioactive↗
PubMed2006

Radon concentration in houses over a closed Hungarian uranium mine.

High radon concentration (average 410 kBq m-3) has been measured in a tunnel of a uranium mine, located 15-55 m below the village of Kovágószolos, Hungary. The mine was closed in 1997; the artificial ventilation of the tunnel was then terminated and recultivation works begun. In this paper, a study has been made as to whether the tunnel has an influence on the radon concentration of surface dwellings over the mining tunnel. At different distances from the surface projection of the mining tunnel, radon concentration, the gamma dose, radon exhalation and radon concentration of soil gas were measured. The average radon concentration in the dwellings was 483 Bq m-3. Significantly higher radon concentrations (average 667 Bq m-3) were measured in houses within +/-150 m from the surface projection of the mining tunnel +50 m, compared with the houses further than the 300-m belt (average 291 Bq m-3). The average radon concentration of the soil gas was 88.8 kBq m-3, the average radon exhalation was 71.4 Bq m-2 s-1 and higher values were measured over the passage as well. Frequent fissures crossing the passage and running up to the surface and the high radon concentration generated in the passage (average 410 kBq m-3) may influence the radon concentration of the houses over the mining tunnel.

Environmental Monitoring↗
PubMed1999

Alkaline single cell gel electrophoresis and human biomonitoring for genotoxicity: a study on subjects with residential exposure to radon.

Based on theoretical estimates and various correlation studies, it has been suggested that ingestion of radon in drinking water represents an increased risk for cancer. Such a risk has never been conclusively shown in epidemiological or experimental animal studies, however, and it has been questioned whether the radon level in the drinking water is of any significance in terms of overall radon exposure. Using primary DNA damage as a biological marker for an ongoing exposure to ionising radiation, the present study was undertaken to investigate whether people with different types of residential radon exposures differed with regard to their levels of DNA damage in circulating lymphocytes. DNA damage was measured in coded blood samples from 125 residents living in 45 households with different levels of radon-222 in the drinking water (10-2410 Bq/l) and indoor air (35-1025 Bq/m3) using alkaline single cell gel electrophoresis (the 'Comet' assay). Increased levels of radon in indoor air (>200 Bq/m3) were found to be associated with an increased level of DNA damage in peripheral lymphocytes (P</=0.05). No such correlation was seen for the radon concentrations in the drinking water, and there was no obvious relationship between the radon levels in drinking water and in indoor air. The results of the present study suggest that measures taken to reduce residential radon exposures should be focused on reducing radon levels in indoor air rather than minimising radon levels in drinking water.

Adolescent↗
PubMedDate not supplied

Contamination of individuals by radon daughters: a preliminary study.

Body radon daughter contamination reflects relative individual respiratory exposures to radon daughters; counts can be related both to household radon levels and to lung cancer risk factors such as sex and tobacco smoking. Radon daughters were counted by gamma spectroscopy from 180 adult residents of eastern Pennsylvania. A seven-position, 35-min scan was conducted in a mobile body counter, generally during afternoon or evening hours. Track-etch detectors for household radon were distributed, and were recovered from 80% of the subjects. Over 75% of the population had environmentally enhanced radon daughter contamination. House radon levels were strongly related, as anticipated, to radon daughter contamination in the 112 subjects for whom both sets of measurements were available (p less than .001); basement measurements were as strongly related to personal contamination as were living area measurements; bedroom measurements were slightly more strongly correlated. Both sex (p less than .02) and cigarette smoking (p less than .01) significantly modified the relationships, after nonlinear adjustment for travel times. Using a logarithmic model, a given house living-area radon level was associated in females with body contamination by radon daughters 2-3 times that in males. Nonsmokers had 2-4 times higher levels of contamination than smokers. Results are for the total of internal and external contamination, these being highly correlated in preliminary experiments. Time usage and activity patterns of the subjects are believed to be important in explaining these findings, and may become important variables in radon risk assessment.

Adult↗
PubMed1999

Study of indoor radon levels in high-rise air-conditioned office buildings.

A series of measurements were conducted to study the indoor radon pollution in air-conditioned high-rise office buildings. Continuous monitoring of indoor radon levels in nine air-conditioned premises located in six office buildings in Hong Kong was conducted from August 1996 to February 1998. Each of the tests lasted for at least 48 hours. The measurement covered both day time monitoring while the air-conditioning was on and night time monitoring while the air-conditioning was off. The indoor radon level followed inversely the operation pattern of the mechanical ventilation systems in the buildings. During office hours when the mechanical ventilation was on, the indoor radon level decayed and after the mechanical ventilation was off during non-office hours, the radon level increased. The average indoor radon level during office hours on the nine premises varied from 87 Bq/m3 to 296 Bq/m3, and the indoor averaged radon levels over both day time and night time periods without mechanical ventilation were about 25 percent higher. The air infiltration rate and the radon emission characteristics from the building materials were estimated from the radon build-up curves which were observed after the mechanical ventilation was off. The radon decay curve observed after the mechanical ventilation system was turned on was used to calculate the total fresh air intake rate. Average radon emanation rates of the building materials in the six buildings varied from 0.0019 to 0.0033 Bq/m2s. It has been found that building infiltration rate accounted for about 10-30 percent of the total building ventilation rate in the buildings depending on building tightness.

Air Conditioning↗
PubMed1996

Predicting radon testing among university employees.

To determine covariates of radon testing behavior, we surveyed by mail a random sample of all Boston University employees (N = 915) six to nine months after they had been informed of the availability of radon testing services through the University's medical center. The response rate was 58%. Analysis suggests blue collar workers were underrepresented within the response rate. Slightly more than half of the respondents (51%) were men. The majority (69%) were under the age of 45. Twenty-seven percent of the respondents (N = 143) had tested their homes for radon. Bivariate analysis revealed important differences between radon testers and nontesters. Testers were 12 times more likely to be home owners than renters (p = 0.00), and were more knowledgeable about radon's characteristics and testing procedures (p = 0.00). Testers were more likely to view radon as a serious problem (p = 0.00), to consider radon testing efficacious (p = 0.00), and to consider themselves susceptible to exposure (p = 0.00). Testers were also less likely to perceive barriers to radon testing. We used logistic regression to compare the usefulness of the Health Belief Model and the Diffusion of Innovations Model in predicting radon testing. We concluded that the knowledge deficits and barriers to radon testing identified in this study should be targeted in radon educational interventions.

Behavior↗
PubMed2006

Radon in Irish schools: the results of a national survey.

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.

Adolescent↗
PubMed1990

Indoor radon and lung cancer in China.

Radon has long been known to contribute to risk of lung cancer, especially in undergound miners who are exposed to large amounts of the carcinogen. Recently, however, lower amounts of radon present in living areas have been suggested as an important cause of lung cancer. In an effort to clarify the relationship of low amounts of radon with lung cancer risk, we placed alpha-track radon detectors in the homes of 308 women with newly diagnosed lung cancer and 356 randomly selected female control subjects of similar age. Measurements were taken after 1 year. All study participants were part of the general population of Shenyang, People's Republic of China, an industrial city in the northeast part of the country that has one of the world's highest rates of lung cancer in women. The median time of residence in the homes was 24 years. The median household radon level was 2.3 pCi/L of air; 20% of the levels were greater than 4 pCi/L. Radon levels tended to be higher in single-story houses or on the first floor of multiple-story dwellings, and they were also higher in houses with increased levels of indoor air pollution from coal-burning stoves. However, the levels were not higher in homes of women who developed lung cancer than in homes of controls, nor did lung cancer risk increase with increasing radon level. No association between radon and lung cancer was observed regardless of cigarette-smoking status, except for a nonsignificant trend among heavy smokers. No positive associations of lung cancer cell type with radon were observed, except for a nonsignificant excess risk of small cell cancers among the more heavily exposed residents. Our data suggest that projections from surveys of miners exposed to high radon levels may have overestimated the overall risks of lung cancer associated with levels typically seen in homes in this Chinese city. However, further studies in other population groups are needed to clarify the carcinogenic potential of indoor radon.

Adult↗
PubMed1996

Indoor radon exposure and risk of lung cancer: a nested case-control study in Finland.

BACKGROUND: Inhaled radon has been shown to cause lung cancer among underground miners exposed to very high radon concentrations, but the results regarding the effects of residential radon have been conflicting. PURPOSE: Our aim was to assess the effect of indoor radon exposure on the risk of lung cancer. METHODS: To investigate this effect, a nested case-control study was conducted in Finland. The subjects of the study were the 1973 lung cancer case patients (excluding patients with cancers of the pleura) diagnosed from January 1, 1986, until March 31, 1992, within a cohort of Finns residing in the same one-family house from January 1, 1967, or earlier, until the end of 1985 and 2885 control subjects identified from the same cohort and matched by age and sex. In September 1992, a letter was sent to all study subjects or proxy respondents explaining the purpose and methods of the study. After giving informed consent, the study participants were asked to fill out a questionnaire on smoking habits, occupational exposures, and other determinants of lung cancer risk and radon exposure. The odds ratio (OR) of lung cancer was estimated from matched and unmatched logistic regression analyses relative to indoor radon concentration assessed by use of a 12-month measurement with a passive alpha track detector. RESULTS. Five hundred seventeen case-control pairs were used in the matched analysis, and 1055 case subjects and 1544 control subjects were used in the unmatched analysis. The OR of lung cancer for indoor radon exposure obtained from matched analysis was 1.01 (95% confidence interval [CI] = 0.94-1.08) per 2.7 pCi/L (100 Bq m-3) after adjustment for the cigarette smoking status, intensity, duration, and age at commencement of smoking by subjects. For indoor radon concentrations 1.4-2.6, 2.7-5.3, 5.4-10.7, and 10.8-34.5 pCi/L (50-99, 100-199, 200-399, and 400-1277 Bq m-3, respectively), the matched ORs were 1.03 (95% CI = 0.84-1.26), 1.00 (95% CI = 0.78-1.29), 0.91 (95% CI = 0.61-1.35), and 1.15 (95% CI = 0.69-1.93), respectively, relative to the concentration below 1.4 pCi/L (0-49 Bq m-3). The unmatched analysis yielded similar results with somewhat smaller CIs. In the analyses stratified by age, sex, smoking status, or histologic type of lung cancer, no statistically significant indications of increased risk of lung cancer related to indoor radon concentration were observed for any of the subgroups. CONCLUSIONS: Our results do not indicate increased risk of lung cancer from indoor radon exposure. IMPLICATION: Indoor radon exposure does not appear to be an important cause of lung cancer.

Adolescent↗
PubMed2004

Radon in homes and risk of lung cancer: collaborative analysis of individual data from 13 European case-control studies.

OBJECTIVE: To determine the risk of lung cancer associated with exposure at home to the radioactive disintegration products of naturally occurring radon gas. DESIGN: Collaborative analysis of individual data from 13 case-control studies of residential radon and lung cancer. SETTING: Nine European countries. SUBJECTS: 7148 cases of lung cancer and 14,208 controls. MAIN OUTCOME MEASURES: Relative risks of lung cancer and radon gas concentrations in homes inhabited during the previous 5-34 years measured in becquerels (radon disintegrations per second) per cubic metre (Bq/m3) of household air. RESULTS: The mean measured radon concentration in homes of people in the control group was 97 Bq/m3, with 11% measuring > 200 and 4% measuring > 400 Bq/m3. For cases of lung cancer the mean concentration was 104 Bq/m3. The risk of lung cancer increased by 8.4% (95% confidence interval 3.0% to 15.8%) per 100 Bq/m3 increase in measured radon (P = 0.0007). This corresponds to an increase of 16% (5% to 31%) per 100 Bq/m3 increase in usual radon--that is, after correction for the dilution caused by random uncertainties in measuring radon concentrations. The dose-response relation seemed to be linear with no threshold and remained significant (P = 0.04) in analyses limited to individuals from homes with measured radon < 200 Bq/m3. The proportionate excess risk did not differ significantly with study, age, sex, or smoking. In the absence of other causes of death, the absolute risks of lung cancer by age 75 years at usual radon concentrations of 0, 100, and 400 Bq/m3 would be about 0.4%, 0.5%, and 0.7%, respectively, for lifelong non-smokers, and about 25 times greater (10%, 12%, and 16%) for cigarette smokers. CONCLUSIONS: Collectively, though not separately, these studies show appreciable hazards from residential radon, particularly for smokers and recent ex-smokers, and indicate that it is responsible for about 2% of all deaths from cancer in Europe.

Air Pollutants, Radioactive↗
PubMed1991

The relationship between radon knowledge, concern and behavior, and health values, health locus of control and preventive health behaviors.

Understanding similarities between health-related and radon-related knowledge, attitudes, and behaviors may suggest application of effective strategies of radon-related education in targeted populations. A mail survey was returned by 300 randomly selected homeowners in a community at risk for high home radon concentrations (50% response). While 64% were concerned, only 7% tested their homes. The expected association between radon knowledge, radon concern, and information-seeking was identified. In addition, those who tested their homes had greater knowledge and did more information seeking. Health values and radon concern were only weakly related. Environmental concern explained the greatest variance in radon concern (10%). Internal health locus of controls were more likely to have high radon concern. Of the preventive health behaviors, not smoking and seat belt use were the best predictors of variance in radon concern (5%). Segmenting the population is suggested for best educational outcome. Relating information to environmental issues may be helpful. Health-conscious people may need awareness of risks. Issues of self-control and radon testing and reduction may be helpful for some. Synergy between smoke and radon, compounded by smokers lack of concern suggests targeting smokers for education efforts.

Environmental Exposure↗
PubMed1990

Quantitative evaluation of the radon and lung cancer association in a case control study of Chinese tin miners.

Studies of underground miners have consistently shown an increased risk of lung cancer with cumulative exposure to radon-222 and its decay products. Although the deleterious effects of high radon exposure are clear, questions regarding the shape of the exposure-response relationship, and the effects of time factors such as attained age, time since exposure and early age at first exposure, the effect of exposure rate, and the joint association of radon exposure and tobacco use have not yet been fully clarified. This report considers these questions by fitting various models for the relative odds of disease to 74 male lung cancer cases who were diagnosed between 1981 and 1984 and were alive in 1985 and an equal number of controls. All subjects are current or past employees of the Yunnan Tin Corporation, Gejiu City, China, who reside in the local area. Workers were interviewed to obtain information on work history, from which radon exposure in cumulative working level months and arsenic exposure were estimated, and on tobacco use. Results indicate that excess relative risk increases by 1.7% per cumulative working level month [95% confidence interval (0.5, 5.4)]. The linear exposure response relationship significantly declines with year since last radon exposure (P = 0.02). The risk trend also declines with increasing exposure rate (P = 0.001), indicating that long duration of exposure at a low rate may be more deleterious than short duration of exposure at a high rate. A unique aspect of this study population is the very early ages at first radon exposure for many of the workers, about 37% of the radon-exposed workers were first exposed under the age of 13 years. The analysis shows no modification of the radon lung cancer relationship with age at first exposure. These patterns of risk with radon exposure are generally consistent with those reported in the recent National Academy of Sciences' Biological Effects of Ionizing Radiations IV report. The primary method of tobacco consumption in this area of China is by waterpipe. Lung cancer risk increases with pipe-years of use. The joint analysis of tobacco use and radon exposure supports the Biological Effects of Ionizing Radiations IV conclusion that the most likely model is between additive and multiplicative. The variations of the radon lung cancer relationship by years since last exposure and exposure rate are not affected by adjustment for arsenic exposure.

Adolescent↗
PubMed1993

[Information and involvement in health risks exemplified by a radon survey program].

As part of a large-scale radon testing program in homes for the region of the Southern Districts of the former German Democratic Republic (GDR) planned by the then West German Federal Ministry of the Environment, Natural Conservation and Reactor Safety and carried out by the Institute of Water, Soil and Air Hygiene (WaBoLu) of the West German Federal Health Office (BGA) in cooperation with the West German Federal Office for Environmental Protection (BfS) and the East German State Office for Atomic Safety (SAAS), the author (then employed at WaBoLu) was responsible for conducting the radon testing in the town of Schlema near the Czechoslovakian border in Southern Saxony. During preparatory work in this town in the fall of 1990, the author noted that the local population was very concerned about their potential radon problem. In the months previously, reports in newspapers and television had frequently pointed out the dangers to health of living in this region, often citing examples of particularly high radon levels from the area. Before the "opening" of the GDR to a free press in the fall of 1989, the local population had heard virtually nothing from the authorities about radon--neither of the possible health risk in general, nor of their own personal radon levels at home. This, together with the lack of experience of East Germans generally to evaluate critically and objectively information from the free press, had led to particularly high levels of anxiety and worry among the local population, even before radon concentrations in homes were known. In the light of these circumstances, the author decided to carry out the radon program with the help of the local school children. These children, aged 13 to 17, were entrusted with the task of carrying out the radon testing using a simple method developed by WaBoLu in all homes of the town. In class, they were informed not only about this testing method, but also about radon generally. It was hoped that, while testing in homes, the school children would pass on this knowledge to the homeowners and thus act as informal "multipliers" of correct information about radon. The approach taken is an example of how environmental hygiene and prevention-oriented environmental medicine could better handle environmental health risks that can be influenced by the individual. It is necessary to become more aware of the fact that all information intended to motivate individuals to protect themselves against environmental health risks may cause at the same time high levels of anxiety.(ABSTRACT TRUNCATED AT 400 WORDS)

Adolescent↗
PubMed1993

Public perceptions of radon risk.

Since 1984, a significant amount of media attention has focused on health threats from radon gas exposure. Using a probability telephone survey of adults (n = 685), we studied public perceptions of risk from radon exposure versus other environmental health risks. The results indicated that 92% of those individuals who had heard of radon believe radon to be a health risk, although only 4% believe they are currently exposed to high levels of radon gas. Perception of risk from radon was positively related to other perceptions of environmental risks. Younger and less educated individuals were more likely to perceive radon as a health risk. Women were three-and-one-half times as likely as men to perceive risk from radon. However, there was no significant relationship between perceived risk from radon and cigarette smoking. Media attention has apparently led to public awareness of radon hazards, but further attention is needed to improve smokers' awareness of their special risks from radon.

Adolescent↗
PubMed2001

Approaches to the assessment of long term exposure to radon and its progeny.

In recent years, a number of case-control epidemiological studies have taken place and others are in progress to evaluate the lung cancer risk to the general population from exposure to radon and its short-lived progeny in the indoor residential environment. While it is actually long term exposure over past decades to radon progeny by inhalation that dominates lung doses, for a number of practical reasons it is radon gas that is measured in these studies. Because the risk from radon and its progeny results from cumulative exposure over past decades rather than from contemporary exposure, it is necessary to reconstruct the historical exposures of subjects. A number of factors limit the accuracy of this approach of which the following are perhaps the most important: the mobility and residential history of the subjects; radon exposures elsewhere; and changes that may have occurred in the radon levels in current and previous residences. Measurement techniques to assist in making more direct retrospective assessments of radon exposure have appeared in the recent past and are the subject of this paper. These are based on the measurement of the long-lived radon progeny 210Po trapped in household artefacts such as glass or porous and spongy materials. In vivo measurements of skeletal 210Pb in exposed persons is also a method that is currently being investigated as a means to assess historical exposures to radon. The advantages and disadvantages of these methods are described here as well as their potential in future radon epidemiological studies.

Air Pollutants, Radioactive↗