Table 4

Influence of different assumptions on the observed Spearman correlation coefficient between FINJEM and Montreal exposure estimates

AgentMain*Montreal level 1-2-3Montreal level 1-3-9Montreal level 1-10-100§FINJEM occupationMontreal medium or high**Montreal unweighted level††Prevalence×level‡‡Montreal median§§
Asbestos80.600.30¶¶0.530.600.800.770.16
Iron compounds230.520.630.570.430.650.470.82
Lead compounds120.470.440.500.390.050.310.62
Chromium compounds90.870.820.870.680.570.400.74
Welding fume170.650.620.610.640.900.870.530.74
Aromatic hydrocarbon solvents50.450.220.450.450.210.670.22
Toluene6−0.24−0.38−0.24−0.35−0.21−0.31−0.15
Formaldehyde90.600.600.600.600.760.88
Carbon monoxide23−0.01−0.040.01−0.08−0.230.000.01
Polycyclic aromatic hydrocarbons200.030.160.09−0.04−0.440.680.020.21
Benzo(a)pyrene5−0.35−0.35−0.35−0.35−0.18−0.54−0.35
Diesel engine exhaust150.650.400.600.700.240.640.070.10
Gasoline engine exhaust210.310.240.340.270.720.530.260.31
Flour dust50.890.890.890.890.920.89
  • * Spearman correlation coefficient between Montreal and FINJEM estimates using a combination of ISCO'68 code and period as the unit of comparison, the 1-5-25 scaling scheme to average the low-medium-high exposure levels in Montreal data, only Montreal data corresponding to likelihood rating ‘probable’ or ‘definite’, only Montreal data corresponding to exposed for at least low exposure during 2 h per week and calculating a weekly average index from concentration and frequency of exposure for the Montreal estimate.

  • The Montreal quantitative index was constructed using a linear (1-2-3) scaling scheme for the low, medium, high categories.

  • The Montreal quantitative index was constructed using an exponential (1-3-9) scaling scheme for the low, medium, high categories.

  • § The Montreal quantitative index was constructed using an exponential (1-10-100) scaling scheme for the low, medium, high categories.

  • The comparison cell was based on the FINJEM job codes instead of on the ISCO'68 codes.

  • ** Only Montreal jobs corresponding to exposed for at least 2 h per week at medium or higher were included in the comparison.

  • †† Montreal exposure level not weighted by frequency of exposure.

  • ‡‡ Comparison of FINJEM P×L to the product of prevalence and exposure level for Montreal instead of FINJEM L to Montreal exposure level.

  • §§ Each cell-specific estimate is calculated using the median of individual jobs level instead of the arithmetic mean.

  • ¶¶ Values in bold indicate important differences with the agreement seen in the main comparison effort.