Quantitation and localization of pulmonary manganese superoxide dismutase and tumor necrosis factor alpha following exposure to ozone and nitrogen dioxide.

Tumor necrosis factor a (TNFalpha) and manganese superoxide dismutase (MnSOD) are thought to play critical roles in the process of lung injury, repair, and disease. The induction of TNFalpha and MnSOD were examined in a model of progressive pulmonary fibrosis along the length of the alveolar duct in rats exposed for 1, 5, and 8 weeks to a combination of 0.8 ppm ozone and 14.4 ppm nitrogen dioxide. This oxidant injury model results in a triphasic response with an initial inflammatory stage during weeks 1-3, followed by a partial resolution at weeks 4-5, and a final stage of rapidly progressive fibrosis during weeks 6-8. Changes in TNFalpha and MnSOD labeling for the proximal and distal alveolar ducts of the lungs were quantified using immunohistochemistry and morphometric techniques at 1, 5, and 8 weeks of exposure. A significant elevation in MnSOD was noted in alveolar macrophages and interstitial cells of the proximal and distal portions of the alveolar duct following 8 weeks of exposure. Labeling for TNFalpha only in the proximal region of the alveolar duct, was significantly increased in alveolar macrophages after 1 and 8 weeks of exposure, while a significant increase in TNFalpha labeling of interstitial cells in proximal regions was noted at all time points. We conclude that MnSOD is elevated in areas of focal injury as well as the more distal protected areas of the lungs, while TNFalpha correlates strongly with both the temporal and spatial aspects of greatest cellular injury in the lungs.

Consequences of prolonged inhalation of ozone on F344/N rats: collaborative studies. Part XIII. A comparison of changes in the tracheobronchial epithelium and pulmonary acinus in male rats at 3 and 20 months.

A limitation of the NTP/HEI Collaborative Ozone Project conducted with F344/N rats at the Battelle Pacific North-west Laboratories in Richland, WA (1991-1993) was that the study used only one time point (20 months) to examine the chronic effects of exposure to ozone. Issues the design of that study could not address were (1) the status of cellular differentiation at earlier time points during the course of ozone exposure; (2) whether changes that appeared to be compensatory after 20 months of exposure were due to ozone, or were aspects of the natural aging process in rats; (3) the inability to define adequately which effects were related specifically to the prolonged duration of exposure; and (4) how and what changes brought about by the natural aging process may have overridden or confounded a clear definition of the effects of exposure to ozone at ambient concentrations (e.g., 0.12 parts per million [ppm]), which are of most concern with long-term exposure to this pollutant. The present study examined the effects of a 3-month exposure to ozone under conditions identical to those of the 20-month NTP/HEI Collaborative Ozone Project. In our facilities at the University of California, Davis, we exposed 42 male F344/N rats to either filtered air or 0.12 or 1.0 ppm ozone. After 3 months of exposure to 1.0 ppm ozone, changes in the distribution of superoxide dismutase (SOD) in the copper-zinc (Cu-Zn) form were shown by a pattern of reduced staining in terminal bronchioles and the centriacinar region; and the manganese (Mn) form of SOD was elevated within the centriacinar region. Further analysis by transmission electron microscopy and immunogold labeling confirmed that Mn SOD was elevated within epithelial type II cells immediately distal to the bronchiole-alveolar duct, junction (BADJ). The trachea, three major bronchi, and a short-length and long-length airway path relative to the trachea were examined by morphometric techniques. The pulmonary acini arising from each of these two paths were also examined morphometrically as a function of distance into the alveolar duct. Cellular changes occurring in each of these anatomical regions after 3 months of exposure were analyzed and compared to the changes noted after the 20-month ozone exposures. We found significant increases in the volume density of nonciliated epithelial cells lining the trachea and caudal bronchi as well as in the proximal and terminal bronchioles of the cranial region at a concentration of 1.0 ppm ozone after both 3 and 20 months of exposure. Remodeling of the centriacinar region, particularly within the cranial region of the lungs after exposure to 1.0 ppm ozone, was statistically significant at both 3 and 20 months. No statistically significant effects were noted following exposure to 0.12 ppm ozone for either 3 or 20 months. An important finding was that age did not influence the effect of ozone on the lungs of rats. We conclude that long-term exposure to ozone, rather than the effects of aging, lead to significant alterations of epithelial cell populations lining the airways and centriacinar region of the lung. Marked cellular changes were noted after exposure to 1.0 ppm ozone, but not to 0.12 ppm.

Site- and cell-specific alteration of lung copper/zinc and manganese superoxide dismutases by chronic ozone exposure.

The antioxidant enzymes copper/zinc (Cu-Zn) and manganese (Mn) superoxide dismutase (SOD) have been implicated in protection of the lungs from oxidant damage. Mn SOD in particular may be related to acquired tolerance in cells following chronic ozone exposure. In order to study these protective and adaptive phenomena in oxidant injury, the cellular location and relative abundance of Mn SOD and Cu-Zn SOD were examined in the lungs of Fischer 344 rats following exposure to 0.0 and 1.0 ppm ozone for up to 3 mo using immunolabeling and morphometric techniques. Cu-Zn SOD labeling was found to be markedly reduced following ozone exposure in epithelial cells within airways and parenchyma. In contrast, a significant increase was noted in Mn SOD labeling in the centriacinar regions of exposed lungs for both alveolar macrophages and epithelial type II cells. Mn SOD labeling per epithelial type II cell was significantly increased in alveoli 0-400 microm beyond the bronchiole-alveolar duct junction (BADJ), while type II cell Mn SOD labeling was similar to control values with greater distance down the alveolar duct. No induction of Mn SOD was noted in type I epithelial cells, fibroblasts, or Clara cells. Thus, alterations in Cu-Zn and Mn SOD are both site and cell specific in the lungs. The differential increase in Mn SOD in type II cells of the proximal alveolar duct may reflect the ability of these cells to acquire tolerance and to resist further injury to repeated ozone exposure.