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Table 1 (continued):<br />

Reference<br />

Emmelin et al.<br />

1993 Sweden<br />

Kaplan 1959<br />

USA<br />

Study Design,<br />

Population, and<br />

Exposures<br />

Case-control<br />

Exposure variable:<br />

Machine time<br />

high*<br />

Fuel consumption<br />

high*<br />

Exposed time<br />

high*<br />

Exposure &<br />

Smoking:<br />

Machine time<br />

medium<br />

high<br />

smoker<br />

Fuel consumption<br />

medium<br />

high<br />

smoker<br />

Exposed time<br />

medium<br />

high<br />

smoker<br />

Cohort<br />

Total<br />

Most likely<br />

exposed<br />

Epidemiological Studies of Exposure to Diesel Exhaust and Lung Cancer Studies<br />

Among Transport (i.e. bus) and Equipment Workers<br />

Cases<br />

or<br />

deaths<br />

14<br />

15<br />

19<br />

154<br />

49<br />

Effect<br />

Measure<br />

OR<br />

1.3<br />

1.7<br />

2.9<br />

1.8<br />

2.9<br />

5.7<br />

1.5<br />

2.9<br />

5.5<br />

2.7<br />

6.8<br />

6.2<br />

SMR<br />

0.80<br />

0.875<br />

Confidence<br />

Interval a or<br />

P-Value<br />

0.3-5.6**<br />

0.5-5.9**<br />

0.8-10.7**<br />

0.5-6.6**<br />

0.6-14.4**<br />

2.4-13.3**<br />

0.5-4.8**<br />

0.7-11.5**<br />

2.4-12.7**<br />

0.6-11.3**<br />

1.3-34.9**<br />

2.6-14.6**<br />

0.68-0.94<br />

N.S.<br />

Comments<br />

Study was a nested case-control of lung cancer<br />

among Swedish male dockworkers in the cohort<br />

studied by Gustafsson et al. (1986). 154 referents<br />

were matched to 50 cases on port and date of birth.<br />

Indices of exposure to diesel exposure were derived<br />

from employment records and records of annual fuel<br />

consumption by diesel vehicles. Three different<br />

exposure classifications were created: “machine<br />

time”, “fuel consumption” and “exposed time”.<br />

In<strong>format</strong>ion on smoking was obtained from<br />

questionnaires and interviews with foremen or<br />

workers who had worked with subjects. Response<br />

rate for mailed questionnaires was low (67%) but<br />

in<strong>format</strong>ion from the interviews was available for<br />

95% of the subjects. Some ex-smokers were<br />

classified as never smokers. No exposure level<br />

(“low”, “medium”, or “high”) was significant for<br />

any DE exposure scheme (only “high” strata<br />

reported here). Comparisons based on exposure and<br />

smoking tended to find more elevated risks.<br />

Investigators noted that the increase in the OR for<br />

both smoking and exhaust exposure indicate that<br />

smoking does not explain the results from the<br />

exposure-only models, and that there may be an<br />

interaction between smoking and exhaust exposure.<br />

No in<strong>format</strong>ion on asbestos exposure, which was<br />

said to have decreased by the 1970s. See also<br />

Gustafsson et al. (1986).<br />

* “Low” exposure category used for reference<br />

comparison.<br />

**Note: authors reported confidence intervals at<br />

90% level.<br />

Cohort consisted of 6,506 deaths among railroad<br />

workers from the Baltimore and Ohio Railroad Relief<br />

Department between 1953 and 1958.<br />

Subjects were categorized into 3 groups by exposed<br />

to diesel exhaust and compared with national lung<br />

cancer mortality rates. IARC noted that since<br />

the changeover to diesel engines began in 1935 and<br />

was 95% completed by 1959 (Garshick et al. 1988),<br />

few, if any, of the lung cancer deaths could have<br />

occurred in workers with more than 10 years of<br />

exposure to diesel exhaust. No data on smoking.<br />

a 95% Confidence intervals unless noted. N.S.= Not significant. No confidence intervals or p-values<br />

reported in original study. DE = Diesel Exhaust, OR = Odds Ratio, RR = Relative Risk, SIR =<br />

Standardized Incidence Ratio, SMR = Standardized Mortality Ratio<br />

445

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