Health Assessment Document for Diesel Emissions - NSCEP | US ...
Health Assessment Document for Diesel Emissions - NSCEP | US ...
Health Assessment Document for Diesel Emissions - NSCEP | US ...
Create successful ePaper yourself
Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.
1 from surrogates (next of kin being either a spouse or an offspring) were found to be accurate by<br />
2 Lerchen and Samet (1986) and McLaughlin et al. (1987). Lerchen and Samet (1986) did not<br />
3 detect any consistent bias in the report of cigarette consumption. In contrast, overreporting of<br />
4 cigarette smoking by surrogates was observed by Rogot and Reid ( 197 5), K.olonel et al. ( 1977),<br />
5 and Humble et al. (1984). Kolonel et al. (1977) found that the age at which an individual started-<br />
6 smoking was reported within 4 years of actual age 84% ofthe time. The indication from these<br />
7 studies is that surrogates were able to provide fairly credible in<strong>for</strong>mation on the smoking habits<br />
8 of the study subjects. If the surrogates of the cases were more likely to. overreport cigarette<br />
9 smoking as compared to the controls, then it might be harder to find an effect of diesel exhaust<br />
1 0 because most of the increase in lung cancer would be attributed to smoking rather than to the<br />
11 effect of exposure to diesel exhaust.<br />
12<br />
13 8.5.5. Criteria of Causal Inference<br />
14 In most situations epidemiologic data are used to delineate the causality of certain health<br />
15 effects. Several cancers have been causally associated with exposure to agents <strong>for</strong> which there is<br />
16 no direct biological evidence. Insufficient knowledge about the biological basis <strong>for</strong> diseases in<br />
17 humans makes it difficult to identify exposure to an agent as causal, particularly <strong>for</strong> malignant<br />
18 diseases when the exposure was in the distant past. Consequently, epidemiologists and biologists<br />
19 have provided a set of criteria that define a causal relationship between exposure and the health<br />
·20 outcome. A causal interpretation is enhanced <strong>for</strong> studies that meet these criteria. None of these<br />
21 criteria actually proves causality; actual proof is rarely attainable when dealing with<br />
22 environmental carcinogens. None of these criteria should be considered either necessary (except<br />
23 temporality of exposure) or sufficient in itself. The absence of any one or even several of these<br />
24 criteria does not prevent a causal interpretation. However, if more criteria apply, it provides<br />
25 more credible evidence <strong>for</strong> causality.<br />
26 Thus, applying the criteria of causal inference to the seven cohort mortality and eight<br />
. .<br />
27 case-control stuqies in which risk of lung cancer was assessed resulted in the following:<br />
28<br />
29<br />
30"<br />
31<br />
32<br />
33<br />
34<br />
35<br />
36<br />
37<br />
2/1198<br />
• Temporality: There is a temporality of exposure to diesel exhaust prior to the<br />
occurrence of lung cancer.<br />
• Strength of association: The strength of association between exposure and the<br />
occurrence of lung cancer in the cohort studies showed a 30% to 57% higher risk<br />
among exposed persons as compared to nonexposed (Howe et al., 1983; Wong et al.,<br />
1985; Boffetta and Stellman, 1988; Garshick et al., 1988). In case-control studies, the<br />
risk varied from 20% to 89% higher among exposed as compared to nonexposed<br />
(Williams et al., 1977; Hall and Wynder, 1984; Damber and Larsson, 1987; Garshick<br />
8-66 DRAFT--DO NOT CITE OR QUOTE