Agent | Main* | Montreal level 1-2-3† | Montreal level 1-3-9‡ | Montreal level 1-10-100§ | FINJEM occupation¶ | Montreal medium or high** | Montreal unweighted level†† | Prevalence×level‡‡ | Montreal median§§ |
Asbestos | 8 | 0.60 | 0.30¶¶ | 0.53 | 0.60 | 0.80 | – | 0.77 | 0.16 |
Iron compounds | 23 | 0.52 | 0.63 | 0.57 | 0.43 | 0.65 | – | 0.47 | 0.82 |
Lead compounds | 12 | 0.47 | 0.44 | 0.50 | 0.39 | 0.05 | – | 0.31 | 0.62 |
Chromium compounds | 9 | 0.87 | 0.82 | 0.87 | 0.68 | 0.57 | – | 0.40 | 0.74 |
Welding fume | 17 | 0.65 | 0.62 | 0.61 | 0.64 | 0.90 | 0.87 | 0.53 | 0.74 |
Aromatic hydrocarbon solvents | 5 | 0.45 | 0.22 | 0.45 | 0.45 | 0.21 | – | 0.67 | 0.22 |
Toluene | 6 | −0.24 | −0.38 | −0.24 | −0.35 | −0.21 | – | −0.31 | −0.15 |
Formaldehyde | 9 | 0.60 | 0.60 | 0.60 | 0.60 | 0.76 | – | 0.88 | – |
Carbon monoxide | 23 | −0.01 | −0.04 | 0.01 | −0.08 | −0.23 | – | 0.00 | 0.01 |
Polycyclic aromatic hydrocarbons | 20 | 0.03 | 0.16 | 0.09 | −0.04 | −0.44 | 0.68 | 0.02 | 0.21 |
Benzo(a)pyrene | 5 | −0.35 | −0.35 | −0.35 | −0.35 | −0.18 | – | −0.54 | −0.35 |
Diesel engine exhaust | 15 | 0.65 | 0.40 | 0.60 | 0.70 | 0.24 | 0.64 | 0.07 | 0.10 |
Gasoline engine exhaust | 21 | 0.31 | 0.24 | 0.34 | 0.27 | 0.72 | 0.53 | 0.26 | 0.31 |
Flour dust | 5 | 0.89 | 0.89 | 0.89 | 0.89 | – | – | 0.92 | 0.89 |
↵* 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.