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

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1 control]). Heinrich et al. (1986a,b; see also StOber, 1986) found a significant increase in wet and<br />

2 dry weights of the lungs of rats and mice exposed at 4.24 mg/m 3 particulate matter <strong>for</strong> 1 year in<br />

3 comparison with controls. After 2 years, the difference was a factor of2 (mice) or 3 (rats). After<br />

4 the same exposure periods, the hamsters showed increases of 50 to 75%, respectively. Exposure<br />

5 to equivalent filtered diesel exhaust caused no significant effects in any of the species. Vinegar<br />

6 et al. (1980, 1981a,b) exposed hamsters to two levels of diesel exhaust with resultant<br />

7 concentrations of about 6 and 12 mg/m 3 .particulate matter <strong>for</strong> 8 h/day, 7 days/week <strong>for</strong> 6 mo.<br />

8 Both exposttres significantly increased lung weight and lung weight to. body weight ratios. The<br />

9 difference between lung weights of exposed and control hamsters exposed to 12 mg/m 3<br />

1 0 particulate matter was approximately twice that of those exposed to 6 mg/m 3 •<br />

11 · Heinrich et al. (1995) reported that rats exposed to 2.5 and 7 mg/m 3 <strong>for</strong> 18 h/day, 5<br />

12 · days/week <strong>for</strong> 24 mo showed significantly lower body weights than control starting at day 200 in<br />

13 the high-concentration group and at day 440 in the low-concentration group. Body weight in the<br />

14 low-concentration group was unaffected, as was mortality in any group. Lung weight was<br />

15 increased in the 7 mg/m 3 group starting at 3 mo and persisting throughout the study while the 2.5<br />

16 mg/m 3 group showed increased lung weight only at 22 and 24 mo of exposure. Mice (NMRI ·<br />

17 strain) exposed to 7 mg/m 3 in this study <strong>for</strong> 13.5 mo had no increase in mortality and minimal,<br />

18 insignificant decreases in body weight. Lung weights were dramatically affected, with increases<br />

19 progressing throughout the study from 1.5-fold at 3 mo to 3-fold at 12 mo. Mice (NMRI and<br />

20 C57BL/6N strains) were also exposed to 4.5 mg/m 3 <strong>for</strong> 23 mo. In NMRI mice, the body weights<br />

21 were reported to be significantly lower than controls, but the magnitude of the change is not<br />

22 reported so biological significance cannot be assessed. Mortality was slightly increased, but<br />

23 statistical significance is not reported. The C57BL/6N mice showed minimal effects on body<br />

24 weight and mortality, which were not reported to be statistically significant. Lung weights were<br />

25 dramatically affected in both strains.<br />

26 Nikula· et al. ( 1995) exposed male and female F344 rats to diesel particle concentrations ·.<br />

27 of2.4 and 6.3 mg/m 3 <strong>for</strong> 16 h/day, 5 days/week, <strong>for</strong> 23 mo in a study designed to compare the<br />

28 effects of diesel with those of carbon black. Significantly reduced survival was observed in<br />

29 males exposed to 6.3 mg/m 3 but not in females or at the lower concentration. Body weights were<br />

30 decreased by exposure to 6.3 mg/m 3 diesel exhaust in both male and female rats throughout the<br />

31 exposure period. Significant increases in lung weight were first seen at 6 mo in the high-<br />

32 exposure group and at 12 to 18 mo in the low-exposure group.<br />

33 No evidence was found in the published literature that chronic exposure to diesel exhaust<br />

34 affected the weight of body organs other than the lung and heart (e.g., liver, kidney, spleen, or<br />

35 testes) (Table 5-4). Morphometric analysis of hearts from rats and guinea pigs exposed to 0.25,<br />

2/1/98 5-29 DRAFT --DO NOT CITE OR QUOTE

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