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. Author manuscript; available in PMC: 2006 Sep 1.
Published in final edited form as: Cancer Causes Control. 2006 Sep;17(7):911–919. doi: 10.1007/s10552-006-0027-5

Table 4.

RR of lung cancer mortality 1959–1996 and intensity and years of diesel exposure weighteda cumulative years of work in an engineer or conductor job group, stratified by year of hire (1939–1944 and 1945–1949). Models are adjusted for age, work in any shop category, years of employment and time since last worked as time dependent covariates, and include a 5-year exposure lag.

Quintiles of “intensity-years”
Hire Date Not Exposed Q1 Q2 Q3 Q4 Q5
1939–1949 (all) Cases 916 410 522 472 507 460
Person years 334,704 248,599 152,914 107,566 94,294 81,655
RR ref 1.37 1.37 1.47 1.35 1.35
95% CI 1.21–1.56 1.23–1.53 1.32–1.65 1.20–1.51 1.19–1.53
1939–1944 Cases 687 326 394 417 427 363
Person years 236,377 199,407 115,233 97,381 78,075 66,103
RR ref 1.26 1.33 1.33 1.28 1.24
95% CI 1.09–1.46 1.17–1.51 1.17–1.50 1.13–1.45 1.08–1.43
1945–1949 Cases 229 80 98 93 76 97
Person years 98,327 49,892 29,621 18,810 15,434 15,073
RR ref 1.63 1.54 2.02 1.50 1.81
95% CI 1.24–2.14 1.21–1.96 1.58–2.59 1.14–1.96 1.39–2.35
a

The intensity score, based on the overall distribution of the EAF, was divided into three groups: <20 μg/hr (group 1), 20-<25 μg/hr (group 2), and ≥25 μg/hr (group 3). For each cohort member, “intensity-years” was calculated by multiplying the year-specific intensity score (1, 2, or 3), and years of diesel exhaust exposure weighted by diesel fraction (DF).