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. 2006 May 30;114(9):1361–1366. doi: 10.1289/ehp.9070

Table 1.

Estimates of lung cancer deaths attributable to indoor radon exposure in France in 1999 according to different exposure–response relations.

No. of lung cancer deaths attributable to indoor radon
Percentiles
Attributable percentage
Dose–response relationships Mean ± SD UI (90%)a Mode 10th 50th 90th Dispersion Mean UI (90%)a
Studies of miners
 EADb 2,066 ± 82 1,934–2,203 2,001 1,962 2,064 2,171 1.14 8 8.0–9.0
 EACc 2,913 ± 92 2,763–3,067 2,834 2,795 2,912 3,032 1.11 12 11.0–12.0
 FCZd 3,108 ± 68 2,996–3,221 3,028 3,020 3,107 3,195 1.08 12 12.0–13.0
Indoor studies
 Lubin1e 543 ± 314 75–1,097 485 139 519 970 14.60 2 0.3–4.4
 Lubin25f 2,642 ± 1,396 518–5,121 2,982 920 2,856 4,671 9.90 11 2.1–20.0
 Darby 1,234 ± 492 593–2,156 995 688 1,151 1,884 3.64 5 2.4– 9.0
a

UIs from the uncertainty analysis.

b

EAD model (BEIR 1999).

c

EAC model (BEIR 1999).

d

Risk model from the European research project concerning the French and Czech cohort of uranium miners (Tirmarche et al. 2003).

e

Risk model from the joint analysis of the seven North American case-control studies restricted to subjects with some radon measurments within the ETW of 25 years (Lubin 2003).

f

Risk model from the joint analysis of the seven North American case-control studies restricted to individuals for whom measurements covered the whole ETW (Lubin 2003).