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

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1 the latter, 16 were classified as benign keratinizing cystic tumors, and 4 were classified as<br />

2 carcinomas. No tumors were reported in 115 controls. The tumor incidence in this study was<br />

3 comparable to that reported previously <strong>for</strong> the diesel exhaust-exposed animals.<br />

4 The importance of DPM and of insoluble respirable particles in tumorigenic responses of<br />

·. 5 nits was investigated and reported by Heinrich et al. ( 1995). In this chronic inhalation exposure<br />

6 study, female Wistar rats were exposed to whole diesel exhaust (0.8, 2.5, or 7.0 mg/m 3 ), 18<br />

7 h/day, 5 days/week <strong>for</strong> up to 24 mo. Groups ofrats were also exposed to ultrafine Ti0 2 particles<br />

8 ( 10 mg/m 3 ) and car boD: black particles ( 11.6 mg/m 3 ) using the same exposure regimen, except<br />

9 that after 4 mo the exposure concentrations ofTi0 2 and carbon black were increased to obtain<br />

10 lung particle burdens similar to those observed in rats exposed to whole diesel exhaust. Controls<br />

11 were exposed to clean air. Following exposure to the test atmospheres, the rats were maintained<br />

12 in clean air atmospheres <strong>for</strong> an additional 6 mo.<br />

13 In analyzing the studies of Heinrich et al. (1986a,b ), Heinrich (1990), Mohr et al. (1986),<br />

14 and StOber (1986), it must be noted that the incidence of lung tumors occurring following<br />

15 exposure to whole diesel exhaust, coal oven flue gas, or carbon black ( 15 .8%, 18.1 %, and 8% to<br />

16 17%, respectively) was very similar. This occurred despite the fact that the PAH content of the<br />

17 P AH -enriched pyrolyzed pitch was more than three orders of magnitude greater than that of<br />

18 diesel exhaust; carbon black, on the other hand, had only traces of P AHs. Based on these<br />

19 findings, the organic fraction is not the sole cause. of tumor induction by diesel exhaust. This<br />

20 issue is discussed further in Chapter 10.<br />

21 · In the Heinrich et al. ( 1995) report, the cumulative exposures <strong>for</strong> the rats in the various<br />

22 treatments groups were 61.7, 21.8, and 7.4 g/m 3 x h <strong>for</strong> the high, medium, and low whole-<br />

23 exhaust exposures and 102.2 and 88.1 g/m 3 x h <strong>for</strong> the carbon black and Ti0 2 groups,<br />

24 respectively. For tumor incidence comparison (number of rats with tumors) among the diesel<br />

25 exhaust exposure groups, significant increases were observed in the high (22/100;p

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