Margaret G. Ménache

Epithelial injury and interstitial fibrosis in the proximal alveolar regions of rats chronically exposed to a simulated pattern of urban ambient ozone

n Abstractn n Electron microcopic morphometry was used to study the development of lung injury during and after chronic (78 weeks) exposure to a pattern of ozone (O3) designed to simulate high urban ambient concentrations that occur in some environments. The daily exposure regimen consisted of a 13-hr background of 0.06 ppm, an exposure peak that rose from 0.06 to 0.25 ppm, and returned to the background level over a 9-hr period, and 2-hr downtime for maintenance. Rats were exposed for 1, 3, 13, and 78 weeks. Additional groups of rats exposed for 13 or 78 weeks were allowed to recover in filtered clean air for 6 or 17 weeks, respectively. Rats exposed to filtered air for the same lengths of time were used as controls. Samples from proximal alveolar regions and terminal bronchioles were obtained by microdissection. Analysis of the proximal alveolar region revealed a biphasic response. Acute tissue reactions after 1 week of exposure included epithelial inflammation, interstitial edema, interstitial cell hypertrophy, and influx of macrophages. These responses subsided after 3 weeks of exposure. Progressive epithelial and interstitial tissue responses developed with prolonged exposure and included epithelial hyperplasia, fibroblast proliferation, and interstitial matrix accumulation. The epithelial responses involved both type I and type II epithelial cells. Alveolar type I cells increased in number, became thicker, and covered a smaller average surface area. These changes persisted throughout the entire exposure and did not change during the recovery pefiod, indicating the sensitivity of these cells to injury. The main response of type II epithelial cells was cell proliferation. The accumulation of interstitial matrix after chronic exposure consisted of deposition of both increased amounts of basement membrane and collagen fibers. Interstitial matrix accumulation underwent partial recovery during follow-up periods in air; however, the thickening of the basement membrane did not resolve. Analysis of terminal bronchioles showed that short-term exposure to O3 caused a loss of ciliated cells and differentiation of preciliated and Clara cells. The bronchiolar cell population stabilized on continued exposure; however, chronic exposure resulted in structural changes, suggesting injury to both ciliated and Clara cells. We conclude that chronic exposure to low levels of O3 causes epithelial inflammation and interstitial fibrosis in the proximal alveolar region and bronchiolar epithelial cell injury.n n

Radon progeny dosimetry in the rat lung.

Deposition, mucociliary clearance, and dosimetry for the inhalation of radon progeny in the rat lung have been simulated for a variety of inhalation conditions. Computations indicate that the exposure-dose conversion factor for the rat lung is approximately twice as high as the corresponding value for the human lung for the same exposure conditions. However, if typical aerosol characteristics are used for animal inhalation experiments and human indoor exposures, the resulting exposure-dose conversion factors are comparable, thereby suggesting similar lung cancer risks per unit exposure. The predicted relative effects of radon progeny disequilibrium and unattached fractions on bronchial doses agree with results from inhalation experiments with laboratory rats.

Relative sensitivities of 2,3,7,8-tetrachlorodibenzo-p-dioxin-induced Cyp1a-1 and Cyp1a-2 gene expression and immunotoxicity in female B6C3F1 mice.

Improvements in risk assessment require better linkage of exposure to response by the determination of target tissue dose. The relative sensitivity of several responses in female B6C3F1 mice was compared on the basis of administered and target tissue dose spanning 3 orders of magnitude. Twenty-four hours after administration, [3H]TCDD was detected in the heart, spleen, kidney, uterus, thymus, lung, and liver, and the highest concentrations were noted in the liver, uterus, and lung. At doses from 5 to 25 ng/kg, hepatic [3H]TCDD levels associated with the cytosolic and nuclear subcellular fractions increased from 12 to 62% of the total liver levels and then decreased at higher doses. At the two lowest doses used in the enzyme induction study, 5 and 10 ng/kg, the levels of specifically bound nuclear Ah receptor complex liganded with [3H]TCDD were 2.3 and 2.5 fmol/mg protein. Slightly higher levels of nuclear Ah receptor complex were observed at doses between 25 and 100 ng/kg (i.e., 3.6 to 4.2 fmol/mg protein) and a steep dose-dependent increase in nuclear Ah receptor levels was noted at doses of 500, 1000, and 5000 ng/kg (8.0, 39.3, and 92.8 fmol/mg protein, respectively). The dose-dependent effects of [3H]TCDD on hepatic Cyp1a-1 and Cyp1a-2 mRNA levels, ethoxyresorufin O-deethylase (EROD) activity, and the splenic antibody plaque-forming cell (PFC) response to sheep red blood cells were also determined; the latter response was determined 9 days after administration of TCDD. Statistically significant induction of hepatic Cyp1a-1 was observed at lower doses (25 ng/kg) than any other marker, followed by induction of EROD and PFCs expressed per spleen or per 10(6) cells which was observed at 100 ng TCDD/kg and at higher doses. Cyp1a-2 was elevated significantly relative to control at doses > or = 1000 ng/kg. The ED50 value for PFCs/10(6) cells was the lowest of the variables analyzed and was not statistically significantly different from control (91 +/- 92 ng/kg). A 50% increase in Cyp1a-2 and Cyp1a-1 mRNA levels was observed at doses of 736 +/- 132 and 1630 +/- 431 ng/kg, respectively. Due to variability in response in PFCs/spleen and the submaximal induction of EROD activity, ED50 values could not be calculated for these responses. The analyses indicate that the immunosuppressive response (when normalized for the number of spleen cells) may be depressed by administered doses as low as 90 ng TCDD/kg body weight. A 50% increase in Cyp1a-1 or Cyp1a-2 was observed at higher administered doses (1630 or 736 ng/kg, respectively.(ABSTRACT TRUNCATED AT 400 WORDS)

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.

Inhalation reference dose (RfDi): An application of interspecies dosimetry modeling for risk assessment of insoluble particles

Accurate extrapolation of animal toxicity data for human health risk assessment requires determination of the effective dose to the target tissue and the sensitivity of the target tissue to that dose. The methodology for deriving reference doses [the U.S. Environmental Protection Agencys (EPA) benchmark values for gauging systemic toxicity] for oral exposures has not included dosimetry modeling. Dosimetry data facilitate evaluation of concentration-response data with respect to the dose-response relationships used in quantitative risk assessment. Extension of this methodology to derivation of inhalation reference doses (RfDi) should account for the dynamics of the respiratory system as the portal of entry. Predictive physiologically based modeling of the inhalation of reactive gases has recently been demonstrated (Overton and Miller 1988). Models that describe the deposition of hygroscopic particles and account for chemical factors that affect clearance mechanisms and gas uptake are under development. This paper presents a method for calculating a dosimetric adjustment factor based on the values for the initial deposited dose of insoluble particles in an animal species and in humans. The ratio of these two values serves as a scaling factor that can be applied in the R f D methodology to account for the dosimetric differences in the inhaled deposited dose. This application for insoluble particles illustrates the feasibility of interspecies dosimetry calculations for extrapolating the toxicological results of inhaled agents to human exposure conditions for more accurate risk estimation.

An Empirical Dosimetry Model of Aerodynamic Particle Deposition in the Rat Respiratory Tract

AbstractModels of airborne particle behavior in both the rodent and the human lung are needed to evaluate health effects following inhalation exposures for human health risk assessment as well as for therapeutic applications. We describe an empirical dosimetry model that can be used to predict fractional deposition of particles in the aerodynamic size range (i.e., diameter >0.5 μm) in the extrathoracic (ET), tracheobronchial (TB), and alveolar (A) regions of the rat lung. Independent equations for deposition efficiency of monodisperse particles in each of the three regions were selected after evaluating three unique functions as well as different parameterizations of independent variables consistent with the mechanisms of particle deposition in each region. For all of the functions fit to the deposition efficiency data, the asymptotic R2 exceeded 0.95. Based on comparisons of the root mean square error (MSE) from the different deposition efficiency equations, as well as of other statistical tests, the log...

Models of the Tracheobronchial Airways of the Dog Lung

AbstractTwo models of the geometry of the tracheobronchial (TB) region of the dog have been developed based upon lung cast data of two beagle dogs (Raabe et al., 1976). These models consist of lengths, diameters, and branching angles of the TB airways. Because the data were incomplete, a method was developed to estimate these parameters for the missing airways based upon relationships between parent airway diameter and daughter airway diameters. Compared to the model of the complete TB region for one dog, the cast data account for only 8% of the total number of TB airways, 42% of the surface area, and 84% of the volume. Single-path models, in which one path represents the entire TB region, were then constructed based upon the two completed models and assumptions about air flow rates in their airways. The airway dimensions in the sequential segments of the single-path models were calculated using the subset of complete model airways that had the average time of flight from the trachea to the terminal bronc...