Airway geometry models of children's lungs for use in dosimetry modeling.

Single-path whole-lung and lobar models of the lungs of 11 children between 3 mo and 21 yr of age were developed based on a combination of cast data and published information on distal airway dimensions. The cast data used to generate these models were taken from one of the largest databases of actual measurements in children. The methods used to develop the children's models were based on techniques that have been used to develop adult single-path airway geometry models. Model dimensions for the conducting airways, as well as the estimated dead space, for all children fell within the range of the limited published information. Thus, the method for estimating airway dimensions in adults may be successfully applied to develop estimates of airway dimensions in children. The predicted total lung capacity (TLC) for the older children (aged 8 to 21 yr) fell within or near the range arising from published scaling equations. The assumptions used to generate the gas exchange region for children 8 yr and older produced results that were reasonably consistent with available physiological data. However, these assumptions do not result in a physiologically consistent gas exchange region for children 3 yr of age and younger; also, to maintain physiologically reasonable relationships between dead space and alveolar volume, the models for children 3 yr of age and younger resulted in predicted TLCs well below those predicted using published scaling equations. These discrepancies may be reflective of dysanaptic growth, in which the alveolar region is growing more rapidly than the airways. The results for children 3 yr of age and under suggest the need for a greater understanding of lung development during this critical period. This is particularly important considering the increasing evidence that exposure to pollutants and other toxicants and allergens during the first 2 yr of life may have long-term consequences on respiratory disease outcomes. Our results suggest that the geometry model airway dimensions for all ages are appropriate for use with dosimetry models, but dosimetry modelers need to assess carefully the reasonableness of TLC and functional residual capacity volumes to which airway dimensions are scaled for children 3 yr of age and under.

Modeling age-related particle deposition in humans.

Inhalation of airborne material poses a potential health risk to various subpopulations one of which is children. Little is known about the fate of particles in the respiratory tracts of children. Modeling efforts have been limited due largely to the lack of adequate information on lung geometry during growth. Lung morphometry measurements in children and adults between 3 months and 21 years of age were used to create 5-lobe lung geometries. Each lobe had a dichotomous, symmetric branching structure and was structurally different from the other lobes. The lung geometries were used in a multiple-path particle deposition model to calculate particle deposition fractions in different regions, lobes and airway generations of the lungs. Simulated breathing patterns were representative of resting breathing. Age-dependent, semi-empirical expressions of particles losses in the nasal airways, which were based on fits to the available experimental measurements, showed larger nasal deposition in adults than in children. Predicted tracheobronchial deposition patterns were similar among different ages for a given particle size. In the alveolar region, the predicted deposition fraction varied with age such that a clear trend could not be identified. Deposition fraction in a lobe was proportional to the volume of air going to that lobe. Deposition fractions in the lower left and right lobes were similar but higher than those in the other lobes for a given particle diameter. Lobar deposition fraction adjusted for lobar lung volume or lung deposition fraction adjusted for lung volume was found to be a unique property for an individual and presented a means for age-dependent deposition comparisons. The adjusted tracheobronchial and pulmonary deposition fractions were greatest for infants and decreased with age. A similar trend was also observed for deposition fraction per unit area as a function of airway generation. The distribution of particle deposition fraction per unit surface area varied with particle size for an individual, with ultrafine particles being more uniformly distributed throughout the lungs and coarse particles depositing primarily in the first few tracheobronchial airways. The trend of particle deposition with age indicates that children, particularly infants, may be at a greater health risk from exposure to airborne particulate matter and noxious materials all other conditions being equal. The age-dependent predicted deposition fraction pattern per unit area of different size particles has implications in the calculation of inhaled reference concentrations as well as site-specific delivery of drugs and other therapeutic compounds to the lungs of patients.

Effects of subchronic inhalation exposure of rats to emissions from a diesel engine burning soybean oil-derived biodiesel fuel.

There is increasing interest in diesel fuels derived from plant oils or animal fats ("biodiesel"), but little information on the toxicity of biodiesel emissions other than bacterial mutagenicity. F344 rats were exposed by inhalation 6 h/day, 5 days/wk for 13 wk to 1 of 3 dilutions of emissions from a diesel engine burning 100% soybean oil-derived fuel, or to clean air as controls. Whole emissions were diluted to nominal NO(x) concentrations of 5, 25, or 50 ppm, corresponding to approximately 0.04, 0.2, and 0.5 mg particles/m(3), respectively. Biologically significant, exposure-related effects were limited to the lung, were greater in females than in males, and were observed primarily at the highest exposure level. There was a dose-related increase in the numbers of alveolar macrophages and the numbers of particles in the macrophages, as expected from repeated exposure, but no neutrophil response even at the highest exposure level. The macrophage response was reduced 28 days after cessation of the exposure. Among the high-level females, the group mean lung weight/body weight ratio was increased, and minimal, multifocal bronchiolar metaplasia of alveolar ducts was observed in 4 of 30 rats. Lung weights were not significantly increased, and metaplasia of the alveolar ducts was not observed in males. An increase in particle-laden macrophages was the only exposure-related finding in lungs at the intermediate and low levels, with fewer macrophages and fewer particles per macrophage at the low level. Alveolar histiocytosis was observed in a few rats in both exposed and control groups. There were statistically significant, but minor and not consistently exposure-related, differences in body weight, nonpulmonary organ weights, serum chemistry, and glial fibrillary acidic protein in the brain. There were no significant exposure-related effects on survival, clinical signs, feed consumption, ocular toxicity, hematology, neurohistology, micronuclei in bone marrow, sister chromatid exchanges in peripheral blood lymphocytes, fertility, reproductive toxicity, or teratology. This study demonstrated modest adverse effects at the highest exposure level, and none other than the expected physiological macrophage response to repeated particle exposure at the intermediate level.

Effect of heat stress on LPS-induced febrile response in D-galactosamine-sensitized rats.

We have previously reported that heat conditioning augments lipopolysaccharide (LPS)-induced fever in rats, which is accompanied by an accumulation of heat shock protein (HSP) in the liver and the reduction of the plasma level of tumor necrosis factor (TNF-alpha) (Kluger MJ, Rudolph K, Soszynski D, Conn CA, Leon LR, Kozak W, Wallen ES, and Moseley PL. Am J Physiol Regulatory Integrative Comp Physiol 273: R858-R863, 1997). In the present study we have tested whether inhibition of protein synthesis in the liver can reduce the effect of this heat conditioning on the LPS-induced febrile response in the rat. D-galactosamine (D-gal) was used to selectively inhibit liver protein synthesis. D-gal (500 mg/kg) or PBS as control was administered intraperitoneally 1 h before heat stress. LPS (50 microg/kg ip) was injected 24 h post-heat exposure. Treatment with D-gal blunted the febrile response to LPS. Moreover, heat-conditioned rats treated first with D-gal and subsequently with LPS demonstrated a profound fall in core temperature 10--18 h post-LPS. A significant increase of serum TNF-alpha accompanied this effect of D-gal on fever. Heat-conditioned animals receiving D-gal showed an inhibition in inducible HSP-70 in the liver. These data support the role of hepatic function in modulating the febrile response to LPS.

Response of F344 rats to inhalation of subclinical levels of sarin: exploring potential causes of Gulf War illness.

Subclinical, repeated exposures of F344 rats to sarin resulted in brain alterations in densities of chlonergic receptor subtypes that may be associated with memory loss and cognitive dysfunction. The exposures also depressed the immune system. The rat appears to be a good model for studying the effects of subclinical exposure to a nerve gas.

Distribution of particulate matter and tissue remodeling in the human lung.

We examined the relationship between intrapulmonary particle distribution of carbonaceous and mineral dusts and remodeling of the airways along anatomically distinct airway paths in the lungs of Hispanic males from the central valley of California. Lung autopsy specimens from the Fresno County Coroner's Office were prepared by intratracheal instillation of 2% glutaraldehyde at 30 cm H(2)O pressure. Two distinct airway paths into the apico-posterior and apico-anterior portions of the left upper lung lobe were followed. Tissue samples for histologic analysis were generally taken from the intrapulmonary second, fourth, sixth, and ninth airway generations. Parenchymal tissues beyond the 12th airway generation of each airway path were also analyzed. There was little evidence of visible particle accumulation in the larger conducting airways (generations 2-6), except in bronchial-associated lymphoid tissues and within peribronchial connective tissue. In contrast, terminal and respiratory bronchioles arising from each pathway revealed varying degrees of wall thickening and remodeling. Walls with marked thickening contained moderate to heavy amounts of carbonaceous and mineral dusts. Wall thickening was associated with increases in collagen and interstitial inflammatory cells, including dust-laden macrophages. These changes were significantly greater in first-generation respiratory bronchioles compared to second- and third-generation respiratory bronchioles. These findings suggest that accumulation of carbonaceous and mineral dust in the lungs is significantly affected by lung anatomy with the greatest retention in centers of lung acini. Furthermore, there is significant remodeling of this transitional zone in humans exposed to ambient particulate matter.

Dose-response relationships for induction of CYP1A1 and CYP1A2 enzyme activity in liver, lung, and skin in female mice following subchronic exposure to polychlorinated biphenyls.

The Toxic Equivalency Factor (TEF) method is used to estimate potential health risks associated with exposure to dioxin-like chemicals. The TEF method is a relative potency (REP) scheme that assumes dose additivity, that the chemicals produce the same response through the same mechanism, and that the REP of a chemical is equivalent for all responses. The present study estimates the REP for five PCBs with dioxin-like activity. Mice were exposed to either 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), 2,3,3',4, 4'-pentachlorobiphenyl (105), 2,3',4,4',5-pentachlorobiphenyl (118), 3,3',4,4',5-pentachlorobiphenyl (126), or 2,3,3',4,4'-, 5-hexachlorobiphenyl (156), five days/week for 13 weeks by oral gavage in a corn oil vehicle. Three days after the last dose, animals were euthanized and the ethoxyresorufin-O-deethylase activity was determined in liver, lung, and skin. Acetanilide-4-hydroxylase activity was determined in liver. In addition, liver and skin disposition of the chemicals were determined. REPs were estimated using a statistical method previously described (DeVito et al., Toxicol. Appl. Pharmacol.147, 267-280, 1997). For any given compound, the REP generally varied by less than a factor of four across endpoints when calculated based on an administered dose. However, typically there was one response for every chemical in which the REP was different by an order of magnitude or more from the other responses. There was some evidence that the REPs may be dose-dependent. While, in general, these data support the use of a single point estimate of the REP, the issue of dose-dependency requires targeted investigation.

1,3-butadiene: cancer, mutations, and adducts. Part I: Carcinogenicity of 1,2,3,4-diepoxybutane.

Reports in the literature suggest that one reason for the greater sensitivity of mice to the carcinogenicity of 1,3-butadiene (BD) is that exposed mice metabolize much more of the BD to 1,2,3,4-diepoxybutane (BDO2) than do exposed rats. The purpose of this study was to determine the tumorigenicity of BDO2 in rats and in mice exposed to the same concentration of the agent. Female B6C3F1 mice and Sprague-Dawley rats, 10 to 11 weeks old, 56 per group, were exposed by inhalation to 0, 2.5, or 5.0 ppm BDO2, 6 hours/day, 5 days/week for 6 weeks. Preliminary dosimetry studies in rodents exposed for 6 hours to 12 ppm BDO2 indicated that blood levels would be expected to be approximately 100 and 200 pmol/g at the two exposure concentrations in the rat and twice those levels in the mouse. During the 6-week exposure, the mice at the high exposure level showed signs of labored breathing during the last week, and four mice died. In the others, however, the respiratory symptoms disappeared after exposure ended. Rats showed no clinical signs of toxicity during exposure but developed labored breathing after the end of the exposure leading to the death of 13 rats within 3 months. At the end of the exposure, some animals (8 per group) were evaluated for the acute toxicity resulting from the BDO2 exposure. The remaining exposed rats and mice were held for 18 months for observation of tumor development. At the end of the exposure, rats had no biologically significant alteration in standard hematological parameters, but mice had a dose-dependent increase in neutrophils and decrease in lymphocytes. In both species the significant histopathologic lesions were in the nose, concentrated around the main airflow pathway. Necrosis, inflammation, and squamous metaplasia of the nasal mucosa, as well as atrophy of the turbinates, were all present at the end of exposure to 5.0 ppm. Within 6 months, necrosis and inflammation subsided, but squamous metaplasia remained in the mice. In rats that died after exposure, squamous metaplasia was seen in areas of earlier inflammation and, in other rats, extended beyond those areas with time. The metaplasia was severe enough to restrict and occlude the nasopharyngeal duct. Later, keratinizing squamous cell carcinomas developed from the metaplastic foci in rats but not mice. At the end of 18 months, the only significant increase in neoplasia in the exposed rats was a dose-dependent increase in neoplasms of the nasal mucosa (0/47, 12/48, and 21/48 for the control, 2.5 ppm, and 5.0 ppm exposures, respectively). Neoplasia of the nasal mucosa did not increase significantly in the mice; neoplastic lesions in the mice were observed in reproductive organs, lymph nodes, bone, liver, Harderian gland, pancreas, and lung. The only significant increase in neoplasms in a single organ in the mice was in the Harderian gland (0/40, 2/42, and 5/36 for the control, 2.5 ppm, and 5.0 ppm exposures, respectively). This tumor accounts for the apparent trend toward an increase in total neoplastic lesions in mice as a function of dose (10/40, 7/42, and 16/36 for control, 2.5 ppm, and 5.0 ppm exposures, respectively). These findings indicate that the metabolite of BD, BDO2, is carcinogenic in the respiratory tract of rats. An increase in respiratory tract tumors was not observed in similarly exposed mice despite the fact that preliminary studies indicated mice should have received twice the dose to tissue compared with the rats. High cytosolic activity of detoxication enzymes in the mouse may account, in part, for the differences in response.

Modeling energy deposition and cellular radiation effects in human bronchial epithelium by radon progeny alpha particles.

Energy deposition and cellular radiation effects arising from the interaction of single 218Po and 214Po alpha particles with basal and secretory cell nuclei were simulated for different target cell depths in the bronchial epithelium of human airway generations 2, 4, 6, and 10. To relate the random chord lengths of alpha particle tracks through spherical cell nuclei to the resulting biological endpoints, probabilities per unit track length for different cellular radiation effects as functions of LET were derived from in vitro experiments. The radiobiological data employed in the present study were inactivation and mutation (mutant frequency at the HPRT gene) in V79 Chinese hamster cells and inactivation and transformation in C3H 10T1/2 cells. Based on computed LET spectra and relative frequencies of target cells, probabilities for transformation, mutation, and cell killing in basal and secretory cells were computed for a lifetime exposure of 20 WLM. While predicted transformation probabilities were about two orders of magnitude higher than mutation probabilities, they were still about two orders of magnitude lower than inactivation probabilities. Furthermore transformation probabilities for basal cells are generally higher than those for secretory cells, and 214Po alpha particles are primarily responsible for transformations in bronchial target cells.

Enhanced pulmonary epithelial replication and axial airway mucosubstance changes in F344 rats exposed short-term to mainstream cigarette smoke.

Cigarette smoking is associated with respiratory diseases that may be caused by injury to specific pulmonary cells. The injury may manifest itself as site-specific enhanced cellular replication. In this study, rats were exposed either to mainstream cigarette smoke (CS; 250 mg total particulate matter/m(3)) or to filtered air (FA) for 6 h/day, 5 days/week, for 2 weeks. In one group, cells in S-phase were labeled over 7 days by bromodeoxyuridine (BrdU) released from implanted osmotic pumps (pump labeled), while another group received BrdU by injection 2 h prior to necropsy (pulse labeled). Morphometry showed that the type II epithelial BrdU labeling index (LI) was significantly elevated in the CS-exposed animals of both labeling groups. The axial airway and terminal bronchiolar LIs were enhanced by CS only in the pump-labeled group. In a third group (pulse labeled), 2 weeks of recovery following exposure to CS allowed a normalization in the type II LI. In the pump-labeled rats, the CS-induced elevation of the type II LI was greater than the LI elevation in conducting airways, suggesting that the parenchyma may have been injured more than the conducting airways. The terminal bronchiolar LI in the pump-labeled group, regardless of exposure, was significantly greater than the axial airway LI. Pump labeling, in contrast to pulse labeling, could therefore discern differences among replication rates of conducting airway epithelium in different regions of the lung. Mucosubstance (MS) within the axial airway epithelium was quantified by morphometry. The CS exposure did not increase the total number of MS-containing cells or the total number of axial airway epithelial cells, but there was a phenotype change in the MS cells. Neutral MS cells (periodic acid-Schiff-positive) were significantly decreased, while acid MS cells (alcian blue-positive) were slightly increased by CS exposure. Either cell replication and differentiation or differentiation alone may have changed the phenotype in the MS cell population.

Carcinogenicity of inhaled butadiene diepoxide in female B6C3F1 mice and Sprague-Dawley rats.

Previous studies suggest that the greater sensitivity of mice, compared to rats, to the carcinogenicity of 1,3-butadiene (BD) is linked to higher rates of BD metabolism to butadiene diepoxide (BDO2) by mice than rats. The purpose of this study was to determine the tumorigenicity of BDO2 in mice and rats exposed by inhalation to the same concentrations of the agent. Female B6C3F1 mice and Sprague-Dawley rats, 10-11 weeks old, 56/group, were exposed to 0, 2.5, or 5.0 ppm BDO2, 6 h/day, 5 days/week for 6 weeks. At the end of the BDO2 exposure, 8 animals/group were evaluated for toxicity. The remainder of the exposed rats and mice were held for up to 18 months for observation of tumor development. At the end of the exposure, rats had no biologically significant alteration in standard hematological parameters, but mice had a dose-dependent increase in neutrophils and decrease in lymphocytes. Most of the significant lesions in both species were in the nose, concentrated around the main airflow pathway. Necrosis, inflammation, and squamous metaplasia of the nasal mucosa, as well as atrophy of the turbinates, were all present in animals exposed to 5.0 ppm. In mice, necrosis and inflammation subsided within 6 months, but squamous metaplasia remained. In rats that died after exposure, squamous metaplasia was seen in areas of earlier inflammation and extended beyond those areas with time. The metaplasia was severe enough to restrict and occlude the nasopharyngeal duct. Later, keratinizing squamous-cell carcinomas developed from metaplastic foci in rats, but these were not seen in mice. At the end of 18 months, the only significant increase in neoplasia in the exposed rats was a dose-dependent increase in neoplasms of the nasal mucosa (0/47, 12/48, and 21/48 for the control, 2.5 ppm, and 5.0 ppm exposures, respectively). Neoplasia of the nasal mucosa did not increase significantly in the mice. Neoplastic lesions in the mice were observed in reproductive organs, lymph nodes, bone, liver, Harderian gland, pancreas, and lung, but the only significant increase in neoplasms in a single organ in the mice was in the Harderian gland (0/40, 2/42, and 5/36 for the control, 2.5 ppm, and 5.0 ppm exposures, respectively). This tumor accounts for the apparent trend toward an increase in total neoplastic lesions in mice as a function of dose (10/40, 7/42, and 16/36 for control, 2.5 ppm, and 5.0 ppm, respectively). These findings indicate that the metabolite of BD, BDO2, is carcinogenic in the upper respiratory tract of rats. An increase in upper respiratory tract tumors was not observed in similarly exposed mice, despite the fact that preliminary studies indicated mice should have received twice the dose to tissue than did the rats. Higher cytosolic activity of detoxication enzymes has been reported in the liver and lung cells of the mouse compared to the rat, and this may account, in part, for the differences in response. The transport of externally administered BDO2, into the cell and through the cytoplasm, might allow detoxication of the molecule before it reaches critical sites on the DNA. The results indicate that the site of formation of the BDO2 is important for tumor induction.

Comparative stochastic effects of inhaled alpha- and beta-particle-emitting radionuclides in beagle dogs.

The stochastic effects of inhaled, insoluble particles of alpha- or beta-particle-emitting radionuclides were compared in dogs. Male and female beagle dogs were exposed briefly by nasal inhalation to relatively insoluble aerosols of (239)PuO(2) or (144)Ce in fused aluminosilicate particles (FAP) and observed for cancer for their lifetimes. The initial lung burden and retention of each radionuclide was determined by whole-body counting of the emissions from (144)Ce-(144)Pr- or (169)Yb-labeled (239)PuO(2). Lung doses were calculated for each dog from these data. The lung doses ranged from 0.21 to 1200 Gy for (144)Ce FAP and 1.6 to 58 Gy for (239)PuO(2). Dogs with doses to the lung of about 60 Gy or greater from (144)Ce or about 2 Gy or greater from (239)PuO(2) had an increased incidence of lung carcinomas. In dogs exposed to (144)Ce FAP, three organs were targets for neoplasia: lung, tracheobronchial lymph nodes, and heart. The insoluble FAP carried to the lymph nodes draining the lung delivered high radiation doses to the nodes and adjacent heart, resulting in hemangiosarcomas of these organs. In the lung, high radiation doses induced hemangiosarcomas and carcinosarcomas. At lower doses, carcinomas of various histological patterns were induced in the lung. In dogs exposed to (239)PuO(2), the lung was the sole target organ for neoplasia. Nearly all of these neoplasms were carcinomas of various histological patterns. These results indicated that relatively low doses of alpha-particle radiation can induce pulmonary cancers, but relatively large doses of beta-particle radiation are required. In addition, inhaled beta-particle emitters can also induce cancers in lung-associated lymph nodes and heart at these larger absorbed radiation doses.

Comparative deterministic effects of inhaled, insoluble alpha- and beta-particle-emitting radionuclides in dogs.

This report compares the deterministic effects from an alpha-particle-emitting radionuclide, (239)PuO(2), and a beta-particle emitter, (144)Ce in fused aluminosilicate particles (FAP). The studies were conducted in beagle dogs of both genders exposed by inhalation to aerosols of the radionuclides. The initial lung burdens of (239)Pu and (144)Ce were determined by whole-body counting of the (169)Yb added to the plutonium aerosol during its preparation or the (144)Ce and its progeny (144)Pr. In addition, organ retention data were obtained from parallel serial sacrifice studies with the same aerosols. After exposure, the dogs were observed for health effects over their lifetime. The deterministic effects observed for both of these relatively insoluble aerosols were lymphopenia, fibrosis, atrophy of the lung-associated lymph nodes, and radiation pneumonitis. Due to the longer half-life of plutonium, the lymphopenia was more prolonged and the clinical course of the radiation pneumonitis more chronic than that resulting from cerium. The greater tissue penetration of the beta-particle emissions from the cerium resulted in more uniform dose distribution over the lung and the atria of the heart than from the alpha-particle emissions from plutonium.

Cigarette smoke exposure produces more evidence of emphysema in B6C3F1 mice than in F344 rats.

Cigarette smoke (CS) causes pulmonary emphysema in humans, but results of previous studies on CS-exposed laboratory animals have been equivocal and have not clearly demonstrated progression of the disease. In this study, morphometry and histopathology were used to assess emphysema in the lungs of B6C3F1 mice and Fischer-344 rats. The animals were exposed, whole-body, to CS at a concentration of 250 mg total particulate matter/m3 for 6 h/day, 5 days/week, for either 7 or 13 months. Morphometry included measurements of parenchymal air space enlargement (alveolar septa mean linear intercept [Lm], volume density of alveolar air space [VVair]), and tissue loss (volume density of alveolar septa [VVspt]). In addition, centriacinar intra-alveolar inflammatory cells were counted to assess species differences in the type of inflammatory response associated with CS exposure. In mice, many of the morphometric parameters indicating emphysema differed significantly between CS-exposed and control animals. In CS-exposed rats, only some of the parameters differed significantly from control values. The Lm in both CS-exposed mice and rats was increased at 7 and 13 months, indicating an enlargement of parenchymal air spaces, but the VVair was increased significantly only in CS-exposed mice. The VVspt was decreased at both time points in mice, but not in rats, indicating damage to the structural integrity of parenchyma. Morphologic evidence of tissue destruction in the mice included alveoli that were irregular in size and shape and alveoli with multiple foci of septal discontinuities and isolated septal fragments. Morphometric differences in the mice at 13 months were greater than at 7 months, suggesting a progression of the disease. Inflammatory lesions within the lungs of mice contained significantly more neutrophils than those lesions in rats. These results suggest that B6C3F1 mice are more susceptible than F344-rats to the induction of emphysema by this CS exposure regimen and that in mice the emphysema may be progressive. Furthermore, the type of inflammatory response may be a determining factor for species differences in susceptibility to emphysema induction by CS exposure.

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.

Upper respiratory tract surface areas and volumes of laboratory animals and humans: considerations for dosimetry models.

To facilitate the development of regional respiratory tract dosimetry comparisons between laboratory animal species and humans, published surface area (SA) and volume (VOL) data for the upper respiratory tract (URT) were reviewed. The review of the literature revealed that (1) different studies used different techniques to prepare specimens and make measurements, (2) different areas of the URT were measured, and (3) URT surface areas and volumes have been reported for a limited number of individual subjects within a species but for a relatively wide range of species. The published data are summarized in tables in this article. New measurements made in an F344 rat and in a female human subject are also presented. Despite the differences in experimental protocols, it was possible to fit allometric scaling equations to the data: In(SA, cm2) = -0.34 + 0.52 In(body weight, g) and In(VOL, cm3) = 1.70 + 0.78 In(body weight, g). Separate scaling equations were also fitted for rats alone. To illustrate the use of these scaling equations in quantitative human health risk assessment, two dose metrics (fractional absorption/cm2 URT SA and fractional absorption/g body weight) for predicted URT uptake in laboratory animals and humans were calculated for acrolein and epichlorohydrin. Expressed as an animal-to-human ratio, the 95% confidence interval for URT SA could change the predicted dose ratio by up to a factor of 2. Additional studies are needed to describe the entire URT (from the nares through the larynx) quantitatively and to decrease variability in scaling equation predictions as well as to develop additional species-specific scaling equations. Three-dimensional imaging techniques provide a noninvasive method to obtain URT surface areas and volumes in humans and the larger laboratory animals. Comparisons of magnetic resonance image (MRI) and computed tomography (CT) scans made as part of this study suggest that the greater clarity of the mucosal-air interface in the CT image provides better resolution for the study of anatomic features. Because there is no radiation exposure associated with MRI imaging, however, it is more safely used than CT scans in making repeated measurements in a subject to elucidate changes in URT geometry associated with normal nasal cycling or other physiological changes.

Dose-response relationships for polyhalogenated dioxins and dibenzofurans following subchronic treatment in mice. I. CYP1A1 and CYP1A2 enzyme activity in liver, lung, and skin.

The dose-response relationships for induction of liver, lung, and skin ethoxyresorufin-O-deethylase (EROD) activity and liver acetanilide-4-hydroxylase (ACOH) activity following subchronic exposure to either 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), 1,2,3,7,8-pentachlorodibenzo-p-dioxin, 2,3,7,8-tetrabromodibenzo-p-dioxin, 2,3,7,8-tetrachlorodibenzofuran (TCDF), 1,2,3,7,8-pentachlorodibenzofuran (1-PeCDF), 2,3,4,7,8-pentachlorodibenzofuran (4-PeCDF), or octachlorodibenzofuran (OCDF) were determined in female B6C3F1 mice in order to estimate the relative enzyme inducing potency of these chemicals in three different tissues. The relative potencies were calculated based on tissue concentrations as well as administered dose. A dose-dependent induction of EROD activity in liver, lung, and skin and of ACOH activity in liver was found for all seven chemicals. When based on administered dose, the relative potencies for specific congeners did not vary substantially among tissues. The relative potencies for TCDF and 1-PeCDF, congeners which have much shorter half-lives than TCDD, increased for all enzymes when estimated from tissue concentrations. The relative potency of OCDF, which is poorly absorbed, was greater when estimated from tissue concentrations than when estimated from administered dose. 4-PeCDF is highly sequestered in hepatic tissue and when the relative potency was estimated based on tissue concentration, its potency for skin enzyme induction increased. These data indicate that the relative potency of these chemicals is influenced not only by the relative binding affinity to the Ah receptor, but also by differences in pharmacokinetic properties of these chemicals. In addition, it may be useful to derive two sets of toxic equivalency factor values, one used for estimating intake equivalents and the other for estimating tissue equivalents.

Ozone uptake in healthy adult males during quiet breathing.

Experimental measurements of ozone (O3) uptake are needed for validation of dosimetry model parameters and in predictions as well as for determining factors affecting uptake and for making comparisons between subpopulations or across species. In this study, 10 healthy adult male subjects were exposed to 0.3 ppm O3 while seated and breathing naturally through the nose or mouth. Total respiratory tract O3 uptake, spontaneous breathing parameters, and respiratory gas exchange were measured for 10 min under steady-state conditions. The exposure protocol was replicated in each subject approximately 2 weeks after the first visit. On each visit, health exams were performed and spirometric lung measurements were obtained. The experimental design provided comparisons of total O3 uptake during nasal and oral breathing, differences in uptake in an individual at two time points, and an examination of between-subject variability in O3 uptake. Exposure to O3 had no effect on the breathing parameters or gas exchange. Oral and nasal breathing frequency averaged 16.2 +/- 1.1 (SE) and 16.0 +/- 1.2 breaths per minute with tidal volumes averaging 651 +/- 46 and 669 +/- 67 ml, respectively. A significant correlation (p < 0.01) was found for the minute volume during resting breathing with the percentage of uptake. The percentage of O3 uptake was consistently higher (p = 0.02) during oral breathing (76.5% +/- 3.3) than during nasal breathing (73.1% +/- 3.0) although this difference may not be biologically significant. The variability in percentage of uptake between subjects was substantial with calculated uptakes ranging from 51 to 96%, a difference of about 45%. Variability in percentage of uptake for an individual was less with the maximal difference between the first and second visits being about 20%; the average difference, however, was only about 3%. We conclude that total percentage of O3 uptake is approximately 75% in adult males during resting breathing. It is slightly greater during oral than during nasal breathing, will vary considerably among subjects, and is moderately reproducible within a subject.

Bronchiolarized metaplasia and interstitial fibrosis in rat lungs chronically exposed to high ambient levels of ozone.

The cellular and tissue changes in the lungs of rats were studied using electron microscopy following 20 months exposure to a range of ozone levels from 0.12 to 1.0 ppm. Male and female Fischer 344 rats were exposed and morphometric methods were used to determine the volume, surface area, and cellular changes observed in bronchiole-alveolar duct regions following chronic ozone exposure. No major gender-related effects were observed in response to chronic inhalation of ozone nor were significant effects of ozone exposure found in either terminal bronchioles or the proximal alveolar regions in animals chronically exposed to 0.12 ppm ozone. The proximal alveolar regions of animals exposed for 20 months to 0.5 and 1.0 ppm ozone were significantly altered with exposure. The high-dose, long-term exposure to ozone resulted in a pronounced increase in volume of both the interstitium and epithelium in the proximal alveolar regions. The thickening of the epithelium was due to a change in tissue type from the normal squamous epithelium to a cuboidal epithelium similar, but not identical, to that found in terminal bronchioles. This bronchiolar epithelial metaplasia of proximal alveolar ducts, which was dose related, was composed of differentiated ciliated and Clara cells similar to those found in terminal bronchioles. In addition, unique cells which contained morphologic features of many different cell types were observed. These cells, which may represent stem cells or differentiated but transformed cells, were found associated with the bronchiolar metaplasia of alveolar ducts. In conjunction with the epithelial changes, cellular and matrix components in the interstitium were increased with chronic exposure to 0.5 and 1.0 ppm ozone. All matrix components were increased including collagen, elastin, and basement membrane, as well as other acellular spaces which did not contain identifiable structures. The total volume of interstitial fibroblasts was also increased in the high-dose exposure group. Alveolar macrophages were increased only in the 1.0 ppm exposed animals. The cell and tissue changes in the terminal bronchioles were less pronounced indicating a relative resistance of this tissue to ozone and mainly consisted of a change in cell type from ciliated to Clara cells in the 1.0 ppm exposed animals. The relative resistance of bronchiolar tissue to high concentration ozone exposure and the extensive bronchiolar epithelial metaplasia may be an adaptive mechanism following chronic ozone exposure.(ABSTRACT TRUNCATED AT 400 WORDS)

Particle inhalability curves for humans and small laboratory animals.

Several inhalability curves for nose breathing in humans have been developed. No studies have been designed specifically to develop inhalability functions for animals, although it has been shown that pulmonary deposition of large particles (> 4-5 microns) via inhalation is minimal in laboratory animals [Raabe et al., Inhaled Particles VI, pp. 53-63. Pergamon Press, Oxford (1988)]. The logistic function was fitted to these animal deposition data of Raabe et al. (1988) to estimate an inhalability curve for laboratory animals. The logistic function was also fitted to the human data of Breysse and Swift [Aerosol Sci. Technol. 13, 459-464 (1990)] for comparison. The results suggest that ambient concentration is a good predictor (inhalability > 95%) of inhaled concentration for humans for particles < 11 microns dae. In small laboratory animals, however, the inhalable portion of the ambient concentration is predicted to be 95% for 0.7 microns dae particles but declines to 45% for 10 microns dae particles. It is, therefore, important to consider the effects of inhalability when estimating dose delivered to the target tissue in animals. In comparing delivered doses between animals and humans, adjusting for inhalability may change not only the magnitude of the difference but also which species is predicted to receive a greater delivered dose.