A determination of the risk of lung cancer at low levels of radon exposure is important for occupational radiation protection.
The risk of death from lung cancer at low radon exposure rates was investigated in the subcohort of 26 766 German uranium miners hired in 1960 or later.
A clear association between lung cancer mortality (n=334 deaths) and cumulative exposure to radon in working level months (WLM) was found. The excess relative risk per WLM was 0.013 (95% confidence intervals: 0.007; 0.021).
The present findings provide strong evidence for an increased lung cancer risk after long-term exposure to low radon exposure rates among Wismut miners. The results are compatible to those from residential radon studies and miner studies restricted to low levels.
There is strong scientific evidence from miner and residential radon studies that radon and its progeny cause lung cancer (UNSCEAR, 2009). Many of the cohorts on occupationally exposed miners include large numbers of individuals who worked in the 1940s and 1950s, when radon concentrations were extremely high. Such conditions do not reflect current occupational exposure scenarios of around two working level months (WLM) per year. Only a few miner studies provide risk estimates for long-term exposure to very low levels of radon (NRC, 1999; Tomasek et al, 2008a; Hunter et al, 2013; Zablotska et al, 2013; Kreuzer et al, 2014; Rage et al, 2014). Such risks, however, are highly relevant for current occupational radiation protection and calculation of lifetime risks for conversions from WLM into effective dose (Tomasek et al, 2008b). Extrapolation of risk from indoor radon studies to miners is difficult due to differences in duration of exposure, exposure to other occupational carcinogens and breathing rates.
The German miner cohort study offers a unique opportunity to investigate the lung cancer risk following occupational radon exposure at low exposure rates in miners. For this purpose, the subcohort of miners hired in 1960 or later (1960+ subcohort) was used, which is characterised by uniform very low exposure rates (average 0.2 working level) over a long time, high quality of exposure assessment and availability of individual data on important potential confounders.
Materials and Methods
The German ‘Wismut’ uranium miner study has been described in detail elsewhere (Walsh et al, 2015). The full cohort includes 58 982 men employed for at least 6 months between 1946 and 1989 in the uranium mining company Wismut in East Germany. The present analyses are based on the third mortality follow-up from 1 January 1960 to 31 December 2008 and include only workers hired in 1960 or later. Vital status was provided by local registration offices. Causes of deaths were obtained from death certificates and autopsy files from the Wismut pathology archive.
Exposure to radon and its progeny, long-lived radionuclides from uranium ore dust and external gamma radiation were determined from a comprehensive job-exposure matrix (JEM). Cumulative exposures are given in WLM for radon progeny, in mSv for the effective dose from external gamma radiation and in kBqh m−3 for long-lived radionuclides from uranium ore dust. Annual cumulative WLM from the JEM relate to ambient measurements of radon gas and estimated equilibrium factors from 1960 to 1964 and of radon progeny after 1964.
Information on smoking habits was obtained from the Wismut Health Archives, mainly from the documented post-1969 regular medical check-ups. Three smoking categories were defined: ‘non-smoker’ (in all years ‘non-smoker’), ‘moderate/heavy smoker’ (if in any year the classification ‘more than 5 years of smoking or more than 10 cigarettes smoked per day’ was indicated) and ‘light smoker’ (for all other specifications such as ‘occasional smoker’, ‘less than 5 years or less than 10 cigarettes smoked per day’, ‘cigar/pipe smoked’). Only the current smoking habits in a given year were documented in predefined categories, so for the ‘non-smoker’ category a distinction between lifelong non-smokers and ex-smokers is not possible.
Internal Poisson regression was applied to model lung cancer mortality rates depending on radon, similar to previous publications (Walsh et al, 2010). A grouped data set was created with the following cross-classifications: age and calendar year in 5-year intervals, duration of employment (0–4, 5–14 and 15+ years), cumulative 5-year lagged radon exposure w (0, >0–9, 10–49, 50–99, 100–199 and 200+ WLM), smoking in four categories and for 5-year lagged cumulative exposures to potential confounders. A linear model was fitted, ERR(w)=β w, where β quantifies the excess relative risk (ERR) per unit of cumulative radon exposure; 95% profile likelihood-based confidence intervals (CIs) were derived. In order to evaluate potential confounders, risk estimates were separately adjusted for external gamma radiation, long-lived radionuclides, silica dust and smoking. Effect modification by time since or age at exposure and exposure rate was tested as in previous publications (Walsh et al, 2010).
The 1960+ subcohort is relatively young; at end of follow-up 83.5% are alive (Table 1). The mean duration of employment was 10 years (range: 0.5–30 years), and the mean age at first employment was 21 years (range: 13–68 years). Information on smoking status was available for 56% of the subcohort members. Among those with known smoking status, 23% were non-smokers, 19% light smokers and 58% were moderate/heavy smokers. The corresponding numbers for individuals with lung cancer and known smoking status (n=172) are 5%, 8% and 87%, respectively.
A statistically significant linear association between lung cancer mortality and cumulative radon exposure (ERR/WLM=0.013; 95% CI: 0.007; 0.021) was found (Figure 1; Supplementary Table 1). Other models (such as linear quadratic or log linear) did not improve significantly the model fit (Supplementary Table 2). Separate adjustment for smoking status, external gamma radiation, long-lived radionuclides or silica dust led only to minor changes in the radon-related risk coefficient. A cutoff of radon exposures to <100 or 50 WLM resulted in a significant ERR/WLM of 0.016 or 0.013, respectively. There was no indication that the ERR/WLM differs by time since or age at median exposure or exposure rate (Supplementary Table 2). The ERR/WLM for non-/light smokers was slightly higher than that for moderate/heavy smokers, however, CIs broadly overlap. Exclusion of short-term employees (<5 years) led to an increased risk estimate (ERR/WLM=0.019; 95% CI: 0.011; 0.032).
The present study shows a clear statistically significant association between lung cancer mortality and low cumulative radon exposure (ERR/WLM=0.013; 95% CI: 0.007; 0.021) in Wismut uranium miners. Strengths of the Wismut 1960+ subcohort are the large number of long-term workers in this exposure range, a long follow-up period, a large number of lung cancer deaths and person-years at risk, leading to a high statistical power. Potential confounders such as external gamma radiation, long-lived radionuclides, silica dust and smoking could be controlled for and it was found that major confounding of the radon-related risk by these factors is unlikely. Even though all radon values were based on ambient measurements (instead of expert rating), some potential bias from uncertainty in exposure assessment and residual confounding by smoking cannot be entirely ruled out.
Findings from other miner studies
Previously, several approaches were used to determine the lung cancer risk associated with low cumulative radon exposures or exposure rates in miner cohorts. One approach was to apply the BEIR VI categorical exposure-age-concentration model and to calculate the risk related to the exposure rate category <0.5 WL (NRC, 1999). However, a formal test of statistical significance of the ERR/WLM in this category cannot be directly derived. Another approach that seems more appropriate is setting a cutoff at low exposures (e.g., 100 or 50 WLM) or including only a subgroup of workers with low exposure rates (e.g., those with a later begin of employment or millers; Supplementary Table 3). The majority of these studies show a statistically significant relationship between lung cancer risk and cumulative exposure to radon and no effect modification by time since or age at exposure. The observed risk coefficients are broadly consistent and range from 0.004 to 0.042 (see Figure 2).
Findings from residential radon studies
In a European pooled analysis of residential radon studies, an ERR per 100 Bq m−3 of 0.16 (95% CI: 0.05; 0.31) overall and of 0.25 (95% CI: 0.09; 0.49) for men was found after correction for measurement error (Darby et al, 2005). By using the conversion factor from Hunter et al (2013), a residential cumulative radon exposure of 100 Bq m−3 over 30 years assuming 7000 h per year spent in homes corresponds to 13.2 WLM. Thus, for men and women, the overall ERR/WLM is 0.16/13.2=0.012 (95% CI: 0.004; 0.023) and 0.019 (95% CI: 0.007; 0.037) for men only. This risk coefficient is compatible to the risk observed in the present study.
The present study demonstrates a clearly increased excess risk of lung cancer at low radon exposure rates among German uranium miners. The risk coefficients are of high precision and well controlled for potential confounders. Results are broadly consistent to other miner studies at low exposures or exposure rates and to indoor radon studies.
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Supplementary Information accompanies this paper on British Journal of Cancer website (http://www.nature.com/bjc)
Environmental Health and Preventive Medicine (2017)