Table 1.
Exposure group | n | N | % > LOD | µ Y | σ 2Y | µ X | 95 % CI | σ 2bY (%) | σ 2wY (%) |
---|---|---|---|---|---|---|---|---|---|
Benzene | |||||||||
Refinery workersa | 24 | 43 | 91 | 4.6 | 3.7 | 610 | 230–1600 | 0 | 100 |
Refinery employees | 15 | 27 | 93 | 4.5 | 3.1 | 430 | 140–1300 | 8 | 92 |
Contractorsa | 9 | 16 | 88 | 4.7 | 4.9 | 1200 | 150–9500 | 0 | 100 |
1,3-Butadiene | |||||||||
Refinery workers | 24 | 43 | 91 | 1.9 | 1.5 | 14 | 8.4–24 | 22 | 78 |
Refinery employees | 15 | 27 | 96 | 1.9 | 1.4 | 13 | 7.1–24 | 11 | 89 |
Contractors | 9 | 16 | 81 | 1.9 | 2.2 | 20 | 4.7–80 | 79 | 21 |
n number of workers, N number of measurements, % > LOD percentage of samples above limit of detection (LOD). LODs were 5 µg/m3 for benzene and 1 µg/m3 for 1,3-butadiene, µ Y = mean (log scale) exposure, σ 2Y = the total variance (log scale), µ X = arithmetic mean exposure (µ X = exp(µ Y + σ 2Y/2)), CI confidence intervals for the arithmetic mean exposure, σ 2bY = between-individual variance component (log scale), σ 2wY = within-individual variance component (log scale)
aOne measurement of 2500 µg/m3 included