Rationale/Objective: Excess lung cancer risks associated with exposure to inhaled radon decay products among uranium miners has well been established. Although ingestion is also a potentially important route of exposure, the relationship between ingested radon decay products and gastrointestinal cancer risks are not well examined. The objective of this study is to determine the relationship between exposure to radon decay products and the incidence and mortality of gastrointestinal (esophagus, stomach, and colorectal) cancer among men employed as uranium miners in Ontario. Secondly, to determine whether the duration of exposure (dose rate), years since last exposure and age at first exposure modify these associations. Methods: A cohort of miners who had ever worked in an Ontario uranium mine between 1954 and 1996 was created using the Mining Master File and the National Dose Registry. Cumulative radon exposures measured in Working Level Months (WLM) were previously estimated for each miner. Cancer diagnoses (1964-2004) and cancer deaths (1954-2004) occurring in Ontario were determined by probabilistic record linkage with the Ontario Cancer Registry. To calculate person-years at risk, non-cancer deaths were also ascertained from the Ontario mortality file for the period between 1954 and 2004. Poisson regression methods for grouped data were used to estimate the relative risks (RR) and 95% Confidence Intervals (CI) by exposure level. Results/Conclusions: The final cohort consisted of 28,273 Ontario uranium miners. By the end of 2004, 34 miners had been diagnosed with esophageal cancer, 86 with stomach cancer, and 359 with colorectal cancer. There were 40 deaths due to esophageal cancer, 69 from stomach cancer, and 176 from colorectal cancer. When comparing the highest cumulative exposure category (>40 WLM) to the referent group (0 WLM), significant increases in both stomach (RRIncidence= 2.30, 95% CI;1.02-5.17 and RRMortality=2.90, 95% CI;1.11-7.63) and colorectal cancers (RRIncidence =1.56, 95% CI;1.07-2.27 and RRMortality =1.74, 95% CI;1.01-2.99) after adjusting for age at risk and period effects. However, no relationships were observed for esophageal cancer. Suggestive evidence of modifying effects of these associations by duration of employment (dose rate) and years since last exposure for colorectal cancer was also observed.

Rationale/Objective: Excess lung cancer risks associated with exposure to inhaled radon decay products among uranium miners has well been established. Although ingestion is also a potentially important route of exposure, the relationship between ingested radon decay products and gastrointestinal cancer risks are not well examined. The objective of this study is to determine the relationship between exposure to radon decay products and the incidence and mortality of gastrointestinal (esophagus, stomach, and colorectal) cancer among men employed as uranium miners in Ontario. Secondly, to determine whether the duration of exposure (dose rate), years since last exposure and age at first exposure modify these associations. Methods: A cohort of miners who had ever worked in an Ontario uranium mine between 1954 and 1996 was created using the Mining Master File and the National Dose Registry. Cumulative radon exposures measured in Working Level Months (WLM) were previously estimated for each miner. Cancer diagnoses (1964-2004) and cancer deaths (1954-2004) occurring in Ontario were determined by probabilistic record linkage with the Ontario Cancer Registry. To calculate person-years at risk, non-cancer deaths were also ascertained from the Ontario mortality file for the period between 1954 and 2004. Poisson regression methods for grouped data were used to estimate the relative risks (RR) and 95% Confidence Intervals (CI) by exposure level. Results/Conclusions: The final cohort consisted of 28,273 Ontario uranium miners. By the end of 2004, 34 miners had been diagnosed with esophageal cancer, 86 with stomach cancer, and 359 with colorectal cancer. There were 40 deaths due to esophageal cancer, 69 from stomach cancer, and 176 from colorectal cancer. When comparing the highest cumulative exposure category (>40 WLM) to the referent group (0 WLM), significant increases in both stomach (RRIncidence= 2.30, 95% CI;1.02-5.17 and RRMortality=2.90, 95% CI;1.11-7.63) and colorectal cancers (RRIncidence =1.56, 95% CI;1.07-2.27 and RRMortality =1.74, 95% CI;1.01-2.99) after adjusting for age at risk and period effects. However, no relationships were observed for esophageal cancer. Suggestive evidence of modifying effects of these associations by duration of employment (dose rate) and years since last exposure for colorectal cancer was also observed.

Radon is a human carcinogen and is an important occupational and public health concern. Radiation protection programs, implemented since the 1950s and 1960s, have significantly reduced radon levels in uranium mines and improved the quality of exposure information. Precise quantification of the risk of lung cancer at low levels of radon exposure and the factors that confound and modify this risk are important for occupational radiation protection. This is a joint cohort study of 408 lung cancer deaths and 394,236 person-years of risk from the Czech, French and Canadian male uranium miners, employed in 1953 or later, with cumulative radon exposures < 100 working level months (WLM). Internal Poisson regression models, stratified by cohort, age at risk and calendar year period at risk were used to calculate the linear excess relative risk (ERR) per unit cumulative radon exposure (lagged five-years). The impact of effect modifiers: time since exposure, attained age, and exposure rate were assessed using an exposure-age-concentration model. Finally, sensitivity analyses assessed the confounding effect of unmeasured tobacco smoking on the radon-lung cancer mortality risk estimate. A statistically significant linear relationship between radon and lung cancer mortality was found, with ERR/WLM = 0.017 (95% confidence intervals (CI): 0.009–0.028) at < 100 WLM cumulative radon exposures. In trend analyses, statistically significant risk was observed at cumulative exposures as low as 10–19 WLM, with RR = 1.64 (95% CI: 1.03–2.65, N = 48 deaths). Radon exposures received in more recent periods (5–14 years previously) had the greatest risk of lung cancer mortality. These risks decreased with increasing time since exposure and attained age. No effect of exposure rate, separate from measures of cumulative exposure, was observed at low radon levels. The confounding effect of unmeasured tobacco smoking was small and did not substantially change the radon-lung cancer mortality risk estimates found. These findings provide strong evidence for an increased risk of lung cancer mortality after long-term low radon exposure among Czech, French and Canadian uranium miners. The results are compatible with other studies of miners restricted to low radon levels and residential radon studies. The results suggest radiation protection measures are of significant importance among modern uranium miners with low radon exposure levels.

Dans les études épidémiologiques, les erreurs de mesure de l’exposition étudiée peuvent biaiser l’estimation des risques liés à cette exposition. Un grand nombre de méthodes de correction de l’effet de ces erreurs a été développé mais en pratique elles ont été rarement appliquées, probablement à cause du fait que leur capacité de correction et leur mise en œuvre sont peu maîtrisées. Une autre raison non moins importante est que, en l’absence de données répétées ou de données de validation, ces méthodes de correction exigent la connaissance détaillée des caractéristiques (taille, nature, structure et distribution) des erreurs de mesure. L’objectif principal de cette thèse est d’étudier l’impact de la prise en compte des erreurs de mesure dans les analyses du risque de décès par cancer du poumon associé à l’exposition au radon à partir de la cohorte française des mineurs d’uranium (qui ne dispose ni de données répétées, ni de données de validation). Les objectifs spécifiques étaient (1) de caractériser les erreurs de mesure associées aux expositions radiologiques (radon et ses descendants, poussières d’uranium et rayonnements gamma), (2) d’étudier l’impact des erreurs de mesure de l’exposition au radon et à ses descendants sur l’estimation de l’excès de risque relatif (ERR) de décès par cancer du poumon et (3) d’étudier et comparer la performance des méthodes de correction de l’effet de ces erreurs. La cohorte française des mineurs d’uranium comprend plus de 5000 individus exposés de manière chronique au radon et à ses descendants qui ont été suivis en moyenne pendant 30 ans. Les erreurs de mesure ont été caractérisées en prenant en compte l’évolution des méthodes d’extraction et de la surveillance radiologique des mineurs au fil du temps. Une étude de simulation basée sur la cohorte française des mineurs d’uranium a été mise en place pour étudier l’impact de ces erreurs sur l’ERR ainsi que pour comparer la performance des méthodes de correction. Les résultats montrent que les erreurs de mesure de l’exposition au radon et à ses descendants ont diminué au fil des années. Pour les premières années, avant 1970, elles dépassaient 45 % et après 1980 elles étaient de l’ordre de 10 %. La nature de ces erreurs a aussi changé au cours du temps ; les erreurs essentiellement de nature Berkson ont fait place à des erreurs de nature classique après la mise en place des dosimètres individuels à partir de 1983. Les résultats de l’étude de simulation ont montré que les erreurs de mesure conduisent à une atténuation de l’ERR vers la valeur nulle, avec un biais important de l’ordre de 60 %. Les trois méthodes de correction d’erreurs considérées ont permis une réduction notable mais partielle du biais d’atténuation. Un avantage semble exister pour la méthode de simulation extrapolation (SIMEX) dans notre contexte, cependant, les performances des trois méthodes de correction sont fortement tributaires de la détermination précise des caractéristiques des erreurs de mesure.Ce travail illustre l’importance de l’effet des erreurs de mesure sur les estimations de la relation entre l’exposition au radon et le risque de décès par cancer du poumon. L’obtention d’estimation de risque pour laquelle l’effet des erreurs de mesure est corrigé devrait s’avérer d’un intérêt majeur en support des politiques de protection contre le radon en radioprotection et en santé publique. / In epidemiological studies, measurement errors in exposure can substantially bias the estimation of the risk associated to exposure. A broad variety of methods for measurement error correction has been developed, but they have been rarely applied in practice, probably because their ability to correct measurement error effects and their implementation are poorly understood. Another important reason is that many of the proposed correction methods require to know measurement errors characteristics (size, nature, structure and distribution).The aim of this thesis is to take into account measurement error in the analysis of risk of lung cancer death associated to radon exposure based on the French cohort of uranium miners. The mains stages were (1) to assess the characteristics (size, nature, structure and distribution) of measurement error in the French uranium miners cohort, (2) to investigate the impact of measurement error in radon exposure on the estimated excess relative risk (ERR) of lung cancer death associated to radon exposure, and (3) to compare the performance of methods for correction of these measurement error effects.The French cohort of uranium miners includes more than 5000 miners chronically exposed to radon with a follow-up duration of 30 years. Measurement errors have been characterized taking into account the evolution of uranium extraction methods and of radiation protection measures over time. A simulation study based on the French cohort of uranium miners has been carried out to investigate the effects of these measurement errors on the estimated ERR and to assess the performance of different methods for correcting these effects.Measurement error associated to radon exposure decreased over time, from more than 45% in the early 70’s to about 10% in the late 80’s. Its nature also changed over time from mostly Berkson to classical type from 1983. Simulation results showed that measurement error leads to an attenuation of the ERR towards the null, with substantial bias on ERR estimates in the order of 60%. All three error-correction methods allowed a noticeable but partial reduction of the attenuation bias. An advantage was observed for the simulation-extrapolation method (SIMEX) in our context, but the performance of the three correction methods highly depended on the accurate determination of the characteristics of measurement error.This work illustrates the importance of measurement error correction in order to obtain reliable estimates of the exposure-risk relationship between radon and lung cancer. Corrected risk estimates should prove of great interest in the elaboration of protection policies against radon in radioprotection and in public health.

La relation entre le risque de décès par cancer du poumon et l’exposition au radon est aujourd’hui établie, notamment à partir des études conduites chez les mineurs d’uranium. Mais de nombreuses interrogations persistent sur les risques de cancers extra-pulmonaires et de maladies non-cancéreuses, et sur l'impact sur la santé des autres expositions radiologiques professionnelles. L’objectif général de cette thèse est de contribuer à l’estimation des risques radio-induits aux faibles débits de dose au travers de l'analyse des risques de décès par cancer du rein et par Maladie de l'Appareil Circulatoire (MAC) chez les mineurs d’uranium.Les analyses du risque de décès par cancer du rein ont été réalisées au sein de la cohorte française des mineurs d'uranium (n=5 086 ; période de suivi : 1946-2007), la cohorte post-55 (n=3 377 ; période de suivi : 1957-2007) et la cohorte allemande de la Wismut (n=58 986; période de suivi : 1946-2003) au sein desquelles sont respectivement répertoriés 24, 11 et 174 décès par cancer du rein. L’exposition au radon et à ses descendants à vie courte (exprimée en Working Level Month WLM), aux poussières d’uranium (kBqh.m-3) et aux rayonnements gamma (mSv) a été estimée individuellement et la dose absorbée au rein a été calculée. La relation dose-réponse a été affinée par rapport à l'analyse classique en considérant deux types de réponse : le risque instantané de décès par cancer du rein (analyse classique, Cause-specific Hazard Ratio (CSHR) estimé avec le modèle de Cox) et sa probabilité d'occurrence au cours du suivi (Subdistribution Hazard Ratio (SHR) estimé avec le modèle de Fine & Gray). Un excès de mortalité par cancer du rein était observé dans la cohorte française (SMR = 1,62 IC95%[1,04; 2,41]), mais pas dans la cohorte post-55. Dans la cohorte de la Wismut, un déficit de mortalité par cancer du rein était observé (0,89 [0,78; 0,99]). Pour ces trois populations, aucune relation n'a pu être mise en évidence entre les expositions radiologiques (ou la dose au rein) et le risque de décès par cancer du rein (ex : CSHRWismut_radon/100WLM=1,023 [0,993; 1,053]), ni avec sa probabilité d'occurrence au cours du suivi (ex : SHRWismut_radon /100WLM=1,012 [0,983; 1,042]).L’étude du risque de décès par MAC dans la cohorte française a montré une augmentation significative du risque de décès par MAC (n=442, CSHR/100WLM=1,11 [1,01; 1,22]) et par Maladie CérébroVasculaire (MCeV, n=105, CSHR/100WLM=1,25 [1,09; 1,43]) avec l’exposition au radon. Une enquête cas-témoins nichée au sein de la cohorte a été mise en place pour recueillir dans les dossiers médicaux les facteurs de risque classiques de MAC (surpoids, hypertension, diabète...) pour 313 mineurs (76 décès par MAC (dont 26 par Cardiopathie Ischémique (CI) et 16 par MCeV) et 237 témoins). Pour les trois expositions radiologiques, la relation exposition-risque a été analysée au sein d'une pseudo-cohorte (obtenue en pondérant les observations par l'inverse de la probabilité de sélection, n=1 644 pseudo-individus) avec le modèle de Cox, en ajustant sur les différents facteurs de risque. L’association entre les expositions radiologiques et le risque de décès par MAC, CI ou MCeV n'était pas significative (ex : CSHRMAC_radon/100WLM=1,43 [0,71; 2,87]). La prise en compte des facteurs de risque ne modifiait pas sensiblement cette association.L'absence de relation dose-réponse significative suggère que l'excès de mortalité par cancer du rein chez les mineurs français serait induit par d'autres facteurs, non-disponibles pour cette analyse. La faible variation des coefficients avec l'ajustement sur les facteurs de risque de MAC dans l'enquête cas-témoins nichée soutient l'hypothèse de l'existence d'une augmentation du risque de MCeV dans la cohorte française associée à l’exposition au radon. La poursuite du suivi de la cohorte permettra d'affiner ces résultats. / The relation between lung cancer risk and radon exposure has been clearly established, especially from the studies on uranium miner cohorts. But the association between radon exposure and extrapulmonary cancers and non-cancer diseases remains not well known. Moreover, the health risks associated with the other mining-related ionizing radiation exposures are still under consideration. The aim of this thesis is to contribute to the estimation of the radio-induced health risks at low-doses through the analysis of the kidney cancer and Circulatory System Disease (CSD) mortality risks among uranium miners.Kidney cancer mortality risk analyses were performed from the French cohort of uranium miners (n=5086; follow-up period: 1946-2007), the post-55 cohort (n=3,377; follow-up period: 1957-2007) and the German cohort of the Wismut (n=58,986; follow-up period: 1946-2003) which included 24, 11 and 174 deaths from kidney cancer, respectively. The exposures to radon and its short-lived progeny (expressed in Working Level Month WLM), to uranium ore dust (kBqh.m-3) and to external gamma rays (mSv) were estimated for each miners and the equivalent kidney dose was calculated. The dose-response relation was refined considering two responses: the instantaneous risk of kidney cancer mortality (corresponding to the classical analysis, Cause-specific Hazard Ratio (CSHR) estimated with the Cox model) and its occurrence probability during the follow-up (Subdistribution Hazard Ratio (SHR) estimated with the Fine & Gray model). An excess of kidney cancer mortality was observed only in the French cohort (SMR = 1.62 CI95%[1.04; 2.41]). In the Wismut cohort, a decrease of the kidney cancer mortality was observed (0.89 [0.78; 0.99]). For these three cohorts, the occupational radiological exposures (or the equivalent kidney dose) were significantly associated neither with the risk of kidney cancer mortality (e.g. CSHRWismut_radon/100WLM=1.023 [0.993; 1.053]), nor with its occurrence probability during the follow-up (e.g. SHRWismut_radon /100WLM=1.012 [0.983; 1.042]).CSD mortality risk analyses in the French cohort showed a significant increase of the risks of mortality from CSD (n=442, CSHR/100WLM=1.11 [1.01; 1.22]) and from CerebroVascular Disease (MCeV, n=105, CSHR/100WLM=1.25 [1.09; 1.43]) with radon exposure. A case-control study nested in the French cohort was set up to collect the information related to CSD risk factors (overweight, hypertension, diabetes...) from the medical records of 313 miners (76 deaths from CSD (including 26 from Ischemic Heart Disease (IHD) and 16 from MCeV) and 237 controls). For the three radiological exposures, the exposure-risk relation was analyzed in a pseudo-cohort (n=1,644 pseudo-individuals, obtained from the weighting of the observations by their inverse selection probability) with the Cox model, adjusted for the CSD risk factors. The association between the radiological exposure and the risk of mortality from CSD, IHD or MCeV was not significant (e.g. CSHRCSD_radon/100WLM=1.43 [0.71; 2.87]). The adjustment for CSD risk factors did not substantially change the exposure-risk relation.The lack of a significant dose-response relation suggests that the excess of kidney cancer mortality among the French uranium miners may be induced by other risk factors, unavailable for this study. The small change of the coefficients observed after adjustment for CSD risk factors in the nested case-control study supports the assumption of the existence of the MCeV mortality risk increase associated with radon exposure in the French cohort of uranium miners. Future analyses based on further follow-up updates should allow to confirm or not these results.

Objective: To determine if paternal preconception exposure to ionizing radiation through uranium mining increases the risk of congenital anomaly (CA) in offspring. Methods: A population-based matched case-control study was conducted. Cases were infants with CAs recorded in the Canadian Congenital Anomalies Surveillance System and born alive in Ontario 1979-86 (ICD-9 codes 740-759); controls were liveborn infants without CAs identified from Ontario birth certificates and individually matched to cases (case-control file {CCF}). Exposed fathers were identified through the linkage of the CCF to the Mining Master File or the National Dose Registry file, which include those who worked in Ontario uranium mines 1952-1986. For men who linked with a case or control child, radon, gamma and total gonadal doses were estimated for three preconception periods: entire, 3-months and 6-months. Odds ratios were estimated using conditional logistic regression. Results: Linkage of 28,991 uranium miners and 40,482 case-control pairs of fathers and offspring in the CCF identified 431 discordant pairs. There was no evidence of increased risk of a child having a CA if the father was ever a uranium miner before conception of the child (OR=0.89, 95% CI=0.74–1.08). Since gamma radiation (especially during the 6-month preconception period) is more biologically relevant to gonads than radon, further analyses were performed on 117 discordant pairs where data on gamma exposures were available. When ever/never miner, exposed to gamma (yes/no), and gamma dose-response variables were all in the model, there was no ever/never miner effect (OR=1.20, 95% CI=0.85–1.69, p-value=0.30), an inverse association for exposure to gamma (OR=0.42, 95% CI=0.25–0.71, p-value=0.001), but most importantly, there was no statistically significant dose-response relationship between gamma dose during the 6-month preconception period and all CAs (OR=1.15 per loge {mSv+0.01}, 95% CI=0.83–1.59, p-value=0.40). Similarly, no dose-response relationship was observed for exposure to gamma radiation in the 3-month preconception period, or for radon or total gonadal radiation in the 3- or 6-month preconception periods. Conclusion: There was no increased risk of a CA among liveborn children of Ontario uranium miners who were exposed to radon, gamma or total radiation during the 3- or 6-month periods before conception.

Objective: To determine if paternal preconception exposure to ionizing radiation through uranium mining increases the risk of congenital anomaly (CA) in offspring. Methods: A population-based matched case-control study was conducted. Cases were infants with CAs recorded in the Canadian Congenital Anomalies Surveillance System and born alive in Ontario 1979-86 (ICD-9 codes 740-759); controls were liveborn infants without CAs identified from Ontario birth certificates and individually matched to cases (case-control file {CCF}). Exposed fathers were identified through the linkage of the CCF to the Mining Master File or the National Dose Registry file, which include those who worked in Ontario uranium mines 1952-1986. For men who linked with a case or control child, radon, gamma and total gonadal doses were estimated for three preconception periods: entire, 3-months and 6-months. Odds ratios were estimated using conditional logistic regression. Results: Linkage of 28,991 uranium miners and 40,482 case-control pairs of fathers and offspring in the CCF identified 431 discordant pairs. There was no evidence of increased risk of a child having a CA if the father was ever a uranium miner before conception of the child (OR=0.89, 95% CI=0.74–1.08). Since gamma radiation (especially during the 6-month preconception period) is more biologically relevant to gonads than radon, further analyses were performed on 117 discordant pairs where data on gamma exposures were available. When ever/never miner, exposed to gamma (yes/no), and gamma dose-response variables were all in the model, there was no ever/never miner effect (OR=1.20, 95% CI=0.85–1.69, p-value=0.30), an inverse association for exposure to gamma (OR=0.42, 95% CI=0.25–0.71, p-value=0.001), but most importantly, there was no statistically significant dose-response relationship between gamma dose during the 6-month preconception period and all CAs (OR=1.15 per loge {mSv+0.01}, 95% CI=0.83–1.59, p-value=0.40). Similarly, no dose-response relationship was observed for exposure to gamma radiation in the 3-month preconception period, or for radon or total gonadal radiation in the 3- or 6-month preconception periods. Conclusion: There was no increased risk of a CA among liveborn children of Ontario uranium miners who were exposed to radon, gamma or total radiation during the 3- or 6-month periods before conception.