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Health Assessment Document for Diesel Emissions - NSCEP | US ...

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1 The corresponding odds ratios <strong>for</strong> petrol exhausts were 0.6 (95% Cl = 0.3, 1.3), 1.4 (95% CI =<br />

2 .0.5, 3.7), and 3.9 (95% CI = 0.4, 35.5). Restricting the analysis to only moderate or high annual<br />

3 doses of exposure adjusted <strong>for</strong> year of birth and smoking showed a sevenfold increased risk <strong>for</strong>·<br />

4 subjects exposed to both diesel and petrol exhausts (OR= 7.1, 95% CI = 0.9, 58.8). For<br />

· 5 exposure to diesel (OR= 1.1) and petrol (OR= 1.0) exhausts alone, no excess risk was detected<br />

6 in this analysis. Odds ratios were calculated <strong>for</strong> low, moderate, and high exposure to benzene,<br />

7 with rates of 1.7 (95% CI = 0.6, 5.1) <strong>for</strong> low annual doses, 1.1 (95% CI = 0.3, 4.5) <strong>for</strong> moderate<br />

8 annual doses, and 3.0 (95% CI = 1.0, 8.7) <strong>for</strong> high annual doses.<br />

9 The authors discuss misclassification and confounding as sources of bias in this study.<br />

10 To examine misclassification they compared hygienist-assessed exposure and self-reported<br />

11 exposure <strong>for</strong> printing ink and found a higher relative risk and fewer exposed subjects <strong>for</strong><br />

12 hygienist-assessed exposure, indicating that specificity was a problem <strong>for</strong> self-reported exposure.<br />

13 It is not known to what extent this may have affected the risk estimates <strong>for</strong> diesel exhausts since<br />

14 data on self-reported exposure to diesel are not presented. They also mention the possibility of<br />

15 exposure misclassification from using an average annual dose in which a person exposed to an<br />

16 agent at a high level <strong>for</strong> a few working days and a person exposed to a low level <strong>for</strong> many days<br />

17 are both rated as exposed to low annual doses. Although statistically nonsignificant elevated<br />

18 odds ratios of 1.3, 2.3, and 2.9 were derived <strong>for</strong> low, moderate, and high levels of diesel<br />

19 exposure, the authors state that some of their subjects may have later worked in jobs with<br />

20 benzene exposure, and because an elevated risk was detected <strong>for</strong> benzene exposure, this<br />

21 ·confounding effect may explain some of the excess risk. An almost statistically significant<br />

22 interaction was observed <strong>for</strong> exposure to combined diesel and petrol exhausts (OR =·7.1, 95% CI<br />

23 = 0.9, 58.8), which changed to 5.1 (95% CI = 0.6, 43.3) after adjustment <strong>for</strong> benzene exposure,<br />

24 again providing evidence <strong>for</strong> the confounding role of benzene exposure in explaining some of the<br />

25 observed results.<br />

26 Table 8-3 summarizes the bladder cancer case-control studies.<br />

27<br />

28 8.5. DISC<strong>US</strong>SION AND SUMMARY<br />

29 Certain extracts of diesel exhaust have been demonstrated to be both mutagenic and<br />

30 carcinogenic in animals and in humans. Animal data suggest that diesel exhaust is a pulmonary<br />

31 carcinogen among rodents exposed by inhalation to high doses over long periods of time.<br />

32 Because large working populations are currently exposed to diesel exhaust and because<br />

33 nonoccupational ambient exposures currently are of concern as well, the possibility that exposure<br />

34 to this complex mixture may be carcinogenic to humans has become an importantpublic health<br />

35 issue.<br />

2/1/98 8-54 DRAFT--DO NOT CITE OR QUOTE

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