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. 2017 Sep 8;12(9):e0184298. doi: 10.1371/journal.pone.0184298

Table 1. Summary information of the radon exposures in the 11 miner cohort studies.

Cohort Metal type Mean first year exposed Mean duration (y) Mean radon exposure (WLM)a, c Mean concentration (WL)a, c βradon, i (%)
China Tin 1955.6 12.9 286.0 1.7 0.16
Czechoslovakia Uranium 1951.0 6.7 196.8 2.8 0.34
Coloradob Uranium 1953.0 3.9 578.6 11.7 0.42
Ontario Uranium 1963.8 3.0 31.0 0.9 0.89
Newfoundland Fluorspar 1954.1 4.8 388.4 4.9 0.76
Sweden Iron 1934.1 18.2 80.60 0.4 0.95
New Mexico Uranium 1965.6 5.6 110.9 1.6 1.72
Beaverlodge (Canada) Uranium 1962.6 1.7 21.2 1.3 2.21
Port Radium (Canada) Uranium 1952.3 1.2 243.0 14.9 0.19
Radium Hill (Australia) Uranium 1956.0 1.1 7.6 0.7 5.06
France Uranium 1956.8 7.2 59.4 0.8 0.36
Total 1954.0 5.7 164.4 2.9

aWeighted by person-years; includes 5-year lag interval.

bExposures limited to < 3,200 WLM.

cOne working level (WL) is defined as any combination of short-lived radon progeny per liter of air that releases 1.3×105 million electron volts of alpha energy in decay. The ventilation was often poor in old uranium mines, and the radon progeny was approximately equilibrium with the radon itself. Under these conditions, each WL of radon progeny would correspond to 100 pCi/L of radon in air. Exposure to 1 working level (WL) for 170 h is defined as 1 working level months (WLM).