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Biomedical subjects

D L Lundgren

Publications and source records attributed to D L Lundgren.

At least 19 recordsLinked to original sources

Chronic cigarette smoke exposure increases the pulmonary retention and radiation dose of 239Pu inhaled as 239PuO2 by F344 rats.

As a portion of a study to examine how chronic cigarette smoke exposure might alter the risk of lung tumors from inhaled 239puO2 in rats, the effects of smoke exposure on alpha-particle lung dosimetry over the life-span of exposed rats were determined. Male and female rats were exposed to inhaled 239PuO2 alone or in combination with cigarette smoke. Animals exposed to filtered air alone served as controls for the smoke exposure. Whole-body exposure to mainstream smoke diluted to concentrations of either 100 or 250 mg total particulate matter m(-3)(LCS or HCS, respectively) began at 6 wk of age and continued for 6 h d(-1), 5d wk(-1), for 30 mo. A single, pernasal, acute exposure to 239PuO2 was given to all rats (control, LCS and HCS) at 12 wk of age. Exposure to cigarette smoke caused decreased body weight gains in a concentration dependent manner. Lung-to-body weight ratios were increased in smoke-exposed rats. Rats exposed to cigarette smoke before the 239PuO2 exposure deposited less 239Pu in the lung than did controls. Except for male rats exposed to LCS, exposure to smoke retarded the clearance of 239Pu from the lung compared to control rats through study termination at 870 d after 239PuO2 exposure. Radiation doses to lungs were calculated by sex and by exposure group for rats on study for at least 360 d using modeled body weight changes, lung-to-body weight ratios, and standard dosimetric calculations. For both sexes, estimated lifetime radiation doses from the time of 239PuO2 exposure to death were 3.8 Gy, 4.4 Gy, or 6.7 Gy for the control, LCS, or HCS exposure groups, respectively. Assuming an approximately linear dose-response relationship between radiation dose and lung neoplasm incidence, approximate increases of 20% or 80% in tumor incidence over controls would be expected in rats exposed to 239PuO2 and LCS or 239PuO2 and HCS, respectively.

Administration, Inhalation↗

A biokinetic model for 137Cs.

An improved biokinetic model for 137Cs in humans was developed based on an analysis of data obtained from individuals internally contaminated during an accident in Goiania, Brazil, and other data. Seventeen children (ten girls and seven boys 1-10 y old), ten adolescents (four females and six males), and thirty adults, (fifteen females and fifteen males contaminated in the accident in Goiânia contributed to this study. 137Cs retention was determined through periodic measurements in a whole-body counter. In addition to the data on 137Cs retention from these individuals, data from a study on the metabolism of 137Cs in immature, adult, and aged Beagle dogs and data from the literature were used in the formulation of the 137Cs biokinetic model presented. Mathematically, the retention of cesium is described by three exponential terms, and the retention model is based on a step function of body weight. When the ICRP Publication 56 model for cesium was compared to the model suggested in this paper, it was determined that the ICRP model predicts lower effective doses in 5-y-old children and higher effective doses in infants, adolescents, and adults.

Adolescent↗

Dose responses from inhaled monodisperse aerosols of 244Cm2O3 in the lung, liver and skeleton of F344 rats and comparison with 239PuO2.

The purpose of this study was to obtain information on the alpha-particle dose-response relationship of 244Cm in rats. Rats were exposed briefly by inhalation to graded levels of monodisperse aerosols of 244Cm2O3 heat-treated at 1150 degrees C. The initial lung burden (ILB) of each animal was determined by the use of the gamma-ray-emitting radionuclide 243Cm in the aerosols. Seven groups of 84-day-old F344/Crl rats (a total of 637 males and 645 females) were exposed once to 244Cm2O3 or sham-exposed to filtered ambient air. Mean ILBs of all rats per group ranged from 0.51 +/- 0.17 (+/-SD) to 240 +/- 82 kBq kg-1 body weight. Mean lifetime alpha-particle doses to the lungs per group ranged from 0.20 +/- 0.069 (+/-SD) to 36 +/- 6.5 Gy. After death, each rat was radiographed and necropsied. Dose-related increases occurred in incidences of benign and malignant lung neoplasms, except for the groups of rats with higher mean ILBs that were examined histologically (98 +/- 18 and 240 +/- 77 kBq kg-1 body weight) in which survival was markedly decreased. Also, average alpha-particle doses of 0.0014 +/- 0.00058 (+/-SD) to 0.17 +/- 0.091 Gy and 0.18 +/- 0.007 to 1.6 +/- 1.1 Gy were also absorbed by the liver and skeleton, respectively, in the rats in the different exposure groups. Primary liver neoplasms occurred in several rats. However, the incidence of these lesions was not related to dose. Increased incidences of bone neoplasms occurred only in rats receiving higher doses to the skeleton. Excess numbers of rats with lung neoplasms per 10(4) Gy to the lung per group ranged from 760 +/- 430 (+/- SE) at a mean dose of 0.48 Gy to 84 +/- 16 at a mean dose of 37 Gy. Risk factors for the lowest and highest ILB kg-1 body weight groups were not considered reliable because of large errors associated with these calculations and the life-span shortening in the highest ILB kg-1 group. Inhaled 244Cm2O3 appeared to be about 50% less effective as a lung carcinogen in rats compared to 239PuO2 at similar doses.

Aerosols↗

Prussian Blue decorporation of 137Cs in beagles of different ages.

A 6-wk study was conducted using immature (4.7 mo), young adult (2.4 y), and aged (13.5 y) male beagles to determine the modifying effect of age on the effectiveness of Prussian Blue decorporation therapy for the removal of injected 137Cs. Whole-body clearance rates for injected 137Cs decreased with increasing age in the dogs. Treatment with Prussian Blue changed the ratio of fecal to urinary 137Cs excretion from 0.8 in untreated dogs to 2.2 in treated animals. The 137Cs concentrations in tissues of untreated and Prussian Blue-treated dogs at the end of the 6-wk study were similar, with the greatest concentrations in the skeletal muscle tissue, spleen, and kidneys. There was a lower concentration of 137Cs in the livers of the treated dogs. The reductions in the average total whole-body doses resulting from Prussian Blue treatment during the course of this study were 51% in the immature, 31% in the young adult, and 38% in the aged dogs. Because of the differences in the intake of Prussian Blue by the dogs in the different groups relative to their body weight, it is unclear as to the relative effectiveness of Prussian Blue in dogs of different ages.

Age Factors↗

Pulmonary carcinogenicity of relatively low doses of beta-particle radiation from inhaled 144CeO2 in rats.

This study was conducted to examine the carcinogenic effects of inhaled beta-particle-emitting radionuclides, particularly in lower dose regions in which there were substantial uncertainties associated with available information. A total of 2751 F344/N rats (1358 males and 1393 females) approximately 12 weeks of age at exposure were used. Of these, 1059 rats were exposed to aerosols of 144CeO2 to achieve mean desired initial lung burdens (ILBs) of 18 kBq (low level), 247 rats to achieve mean ILBs of 60 kBq (medium level) and 381 rats to achieve mean ILBs of 180 kBq (high level). Control rats (total of 1064) were exposed to aerosols of stable CeO2. Based on the 95% confidence intervals of the median survival times and the cumulative survival curves, there were no significant differences in the survival of groups of female and male exposed rats relative to controls. The mean lifetime beta-particle doses to the lungs of the rats in the four groups were: low level, 3.6 +/- 1.3 (+/-SD) Gy; medium level, 12 +/- 4.5 Gy; and high level, 37 +/- 5.9 Gy. The crude incidence of lung neoplasms increased linearly with increasing doses to the lungs (controls, 0.57%; low level, 2.0%; medium level, 6.1%; and high level, 19%). The estimated linear risk coefficients for lung neoplasms per unit of dose to the lung were not significantly different for the three dose levels studied. The risk coefficient at the lower level was 39 +/- 14 (+/-SE) excess lung neoplasms per 10(4) rat Gy; at the medium level the risk was 47 +/- 12; and at the higher level the risk was 50 +/- 9.0. The relationship of beta-particle dose to the lung and the crude incidence of lung neoplasms was described adequately by a linear function. We concluded that the risk of lung neoplasms in rats per unit of radiation dose did not increase with decreasing mean beta-particle dose to the lung over the range of 3.6 to 37 Gy. The weighted average of these three values was 47 +/- 6.4 (+/-SE) excess lung neoplasms per 10(4) rat Gy. To extend the risk coefficients for lung neoplasms to lower doses by experimentation will require much larger numbers of rats than used in this study.

Administration, Inhalation↗

Pulmonary carcinogenesis in the F344 and Wistar rat after inhalation of plutonium dioxide.

Pulmonary carcinogenesis was compared in female F344 and Wistar rats after inhalation of high-fired 239PuO2. Plutonium particle aggregation, as determined by quantitative light and scanning electron microscopic autoradiography, was greater for the F344 strain than for the Wistar strain. The median survival times were similar in control and low-dose (0.8-1.0 Gy) groups of both strains, but were significantly decreased in the high-dose (34-37 Gy) groups of both strains. Squamous metaplasia was not found in control or low-dose groups of either strain, but was found in 62-65% of high-dose groups of both strains. Adenomatous metaplasia was considerably higher in control and low-dose groups of F344 rats than in Wistar rats. A total of 87 lung tumors were found in 140 exposed F344 rats and 46 lung tumors in 176 exposed Wistar rats. The incidence of lung tumors in F344 rats was 1.7% in controls, 20% in the low-dose group and 82% in the high-dose group. The incidence of lung tumors in Wistar rats was 0.1% in controls, nil in the low-dose group and 68% in the high-dose group. About half of all lung tumors in both strains were considered to be the primary cause of death. The median survival times of rats of both strains in the high-dose groups that died with lung tumors were greater compared with rats in these groups that died without lung tumors. In contrast, these differences did not occur among rats in the low-dose groups. The absolute risk was 1900 lung tumors per 10(4) Rat-Gy for F344 rats receiving low doses and nil for Wistar rats receiving low doses, but about 210 lung tumors per 10(4) Rat-Gy for high-dose groups of both strains. The adenomatous tumor phenotype predominated in the F344 strain, while the squamous tumor phenotype predominated in the Wistar strain. Risk of squamous tumors was similar for both strains. Overall, the F344 strain appears to be more "sensitive" than the Wistar strain to formation of lung tumors at low to moderate doses from inhaled 239PuO2 due mostly to an increased incidence of adenomatous phenotype tumors.

Aerosols↗

Pulmonary carcinogenicity of repeated inhalation exposure of rats to aerosols of 239PuO2.

To study the long-term biological effects of repeated inhalation exposure to 239PuO2, 84-day-old rats were exposed to aerosols of 239PuO2 to re-establish desired 239Pu lung burdens of 26, 80 or 250 Bq every other month for 1 year (seven exposures). Other rats were exposed once at 84 or 450 days of age to achieve desired initial lung burdens of 30, 90, 280 or 850 Bq. The incidences of lung tumors were not significantly different (Fisher's exact test; P > 0.05) in groups of rats with similar lifetime mean alpha-particle doses to the lungs of 0.90 +/- 0.39 to 4.4 +/- 1.8 (+/- SD) Gy, whether exposed once or repeatedly. Among rats with mean alpha-particle doses of 12 +/- 2.4 to 10 +/- 2.1 Gy to the lungs after single or repeated exposures, respectively, the crude incidence of lung tumors was significantly less (Fisher's exact test; P < 0.05) in the rats exposed repeatedly. Times to death of rats with lung tumors were compared among groups with similar alpha-particle doses to the lungs after single or repeated exposure to 239PuO2. Those that died with lung tumors after repeated exposures died at times similar to (Mantel-Cox statistic; P > 0.05) or later than (Mantel-Cox statistic; P < 0.05) those for 84-day-old rats exposed once. The risk of lung tumors in rats per unit dose to the lungs was less in the rats exposed repeatedly than in those exposed once. It was concluded that alpha-particle doses to the lung of rats exposed repeatedly to aerosols of 239PuO2 were not more carcinogenic and possibly were less carcinogenic than the dose after a single inhalation exposure when rats with similar lifetime alpha-particle doses to the lungs were compared. The relative biological effectiveness in rats of the alpha-particle dose to the lungs from inhaled 239PuO2 relative to beta-particle doses to the lungs from inhaled 144CeO2 was 21 +/- 3.

Administration, Inhalation↗

Sequential analysis of the pathogenesis of plutonium-induced pulmonary neoplasms in the rat: morphology, morphometry, and cytokinetics.

Light microscopy, morphometry, and cytokinetic techniques were used to examine the dynamics of plutonium-induced pulmonary proliferative lesions and neoplasms in rats at several intervals to 450 days after inhalation exposure to aerosols of 239PuO2. Maximal increases in alveolar and bronchiolar epithelial cell labeling were seen at 30 days; decreasing subsequently, the levels remained elevated above control indices. Focal proliferative epithelial lesions developed in the lung by 180 days and before the onset of pulmonary neoplasms. Pulmonary neoplasms, predominantly adenocarcinomas and squamous cell carcinomas, were initially observed at 308 days. The proliferative lesions progressed through a succession of morphological changes leading to the development of neoplasms. The volume density (fraction) and epithelial surface area of foci of alveolar epithelial hyperplasia increased progressively between 180 and 450 days after exposure, in contrast to the other proliferative lesions. We conclude that plutonium-induced pulmonary neoplasms develop through a succession of focal proliferative lesions that represent developmental preneoplastic lesions. Progressive increases in volume and epithelial surface area of the alveolar epithelial hyperplasias suggest that they may be more at risk for neoplastic transformation than the other histological types of proliferative foci.

Adenocarcinoma↗

Pulmonary neoplasms in rats that inhaled cerium-144 dioxide.

The lung neoplasms induced in rats by inhaled, internally deposited 144CeO2 were described and classified using histologic criteria. F344 rats were exposed once or repeatedly by inhalation to 144CeO2 and observed for their life span. There was significant life shortening only in those rats with the highest radiation doses. In these rats, there was a high percentage of squamous cell carcinomas of the lung, as well as much lower percentages of adenocarcinomas of the lung, hemangiosarcomas of the lung, and pleural mesotheliomas. At lower doses, adenocarcinomas were the most predominant tumor. These adenocarcinomas were subdivided based on their histologic pattern: alveolar, papillary, tubular, or undifferentiated. Neither the mode of exposure (single or repeated) nor the sex of the rat influenced the lung tumor incidence or tumor type. The lung neoplasms induced by this beta-emitting radionuclide are similar in nature to those induced by alpha-emitting radionuclides deposited in the lung in rats. However, the radiation-induced squamous cell carcinomas of the lung differ from those induced by heavy particle loads of nonradioactive compounds. The radiation-induced squamous cell carcinomas occur in higher incidence and have a more malignant behavior than those induced by heavy particle loads.

Adenocarcinoma↗

Repeated inhalation exposure of rats to aerosols of 144CeO2. I. Lung, liver, and skeletal dosimetry.

To develop a better understanding of the influence of cumulative radiation dose and dose rate to the lungs on the biological responses to inhaled radionuclides, several studies are in progress at this institute in which laboratory animals have been exposed once or repeatedly to aerosols of insoluble particles containing 144Ce or 239Pu. In the study reported here, F344 rats were exposed repeatedly to aerosols of 144CeO2 beginning at 94 days of age to reestablish desired lung burdens of 1.9, 9.2, 46, or 230 kBq of 144Ce every 60 days for 1 year (seven exposures). Other 94-day-old rats were exposed once to achieve similar desired initial lung burdens of 144Ce. Older rats were exposed once to achieve desired initial lung burdens of 46 or 230 kBq when 500 days of age, the age of the repeatedly exposed rats when exposed for the last time. Control rats were either unexposed, sham-exposed once or repeatedly, or exposed once or repeatedly to stable CeO2. Approximately equal numbers of male and female rats were used. The cumulative beta-radiation doses to the lungs, liver, and skeleton of rats exposed repeatedly were similar to those of rats with similar total lung burdens of 144Ce from a single inhalation exposure. The average beta-radiation dose rate to the lungs of the rats exposed repeatedly was about one-fifth of that in rats with similar total lung burdens after a single exposure.

Aerosols↗

Repeated inhalation exposure of rats to aerosols of 144CeO2. II. Effects on survival and lung, liver, and skeletal neoplasms.

Groups of 94-day-old F344/Crl rats were exposed repeatedly to aerosols of 144CeO2 to reestablish desired lung burdens of 1.9, 9.2, 46, or 230 kBq of 144Ce every 60 days for 1 year (seven exposures). Other 94-day-old rats were exposed once to achieve similar desired initial lung burdens of 144Ce. Older rats were exposed once to achieve desired initial lung burdens of 46 or 230 kBq when 500 days of age, the same age at which rats had the last of the repeated exposures. Control rats were either unexposed, sham-exposed once or repeatedly, or exposed once or repeatedly to stable CeO2. Approximately equal numbers of male and female rats were used. The median survival time and cumulative percentage survival curves were significantly decreased only in male and female rats exposed repeatedly to reestablish a 230-kBq lung burden and among the 94-day-old male rats exposed once to achieve a 230-kBq lung burden of 144Ce. The crude incidences of primary lung cancers (well described by a single Weibull distribution function), time to death with lung tumors, and risk of lung cancer per unit of beta-radiation dose to the lungs were correlated with the cumulative beta-radiation dose rather than the rate at which the dose was accumulated. A linear function, 70 (+/- 7.3) + -0.15 (+/- 0.056) x dose (+/- SD), adequately described the excess numbers of rats with lung cancers over a beta-radiation dose range to the lungs of 6.8 to 250 Gy for two groups of rats with the highest doses to the lungs after a single exposure and for two groups with the highest doses after repeated exposure.

Aerosols↗

Modifying effects of preexisting pulmonary fibrosis on biological responses of rats to inhaled 239PuO2.

We investigated the modifying effects of preexisting, bleomycin-induced pulmonary fibrosis on the deposition, retention, and biological effects of inhaled 239PuO2 in the rat. Among rats exposed to similar airborne concentrations of 239PuO2, initial lung burdens of 239Pu per kilogram body mass were similar whether or not pulmonary fibrosis was present. However, clearance of 239Pu from the lungs was significantly decreased in the rats with preexisting pulmonary fibrosis. The incidence of lung lesions (epithelial hyperplasia, diffuse macrophage increases and aggregation, and loose and dense connective tissue) was significantly greater among rats with preexisting pulmonary fibrosis than among the exposed controls. Rats with preexisting fibrosis had shorter life spans than 239PuO2-exposed control rats. When groups of rats with similar alpha doses to the lungs were compared, the incidences of neoplastic lesions in the lung, the times to death of rats with lung neoplasms, and the risk of lung tumors per unit of alpha dose to the lungs in rats with or without pulmonary fibrosis were similar. The results of this study suggest that humans with uncomplicated pulmonary fibrosis may not be more sensitive to the carcinogenic effects of inhaled 239PuO2 than are individuals with normal lungs, assuming that the total alpha doses to the lungs are similar.

Administration, Inhalation↗

Biological effects of inhaled 239PuO2 in rats with pre-existing pulmonary emphysema.

The modifying effects of pre-existing pulmonary emphysema on the deposition, distribution, retention and effects of inhaled 239PuO2 in the rat were investigated. The presence of emphysema in the rats was documented by morphometric and respiratory function measurements. For rats exposed to similar airborne concentrations of 239PuO2, initial lung burdens of 239Pu per kg body mass were lower in rats with emphysema than in those without emphysema; however, the retention of 239Pu over time was similar in both groups. The distribution of 239Pu particles in the lungs of rats with emphysema tended to be more random than in the lungs of control rats. The life span, and incidences of non-neoplastic and neoplastic lesions in the lung, and risk of lung tumours per unit of alpha dose to the lungs in the rats with emphysema were similar to or less than in the control rats, when groups with similar initial lung burdens of 239Pu were compared. The results of this study suggest that humans with uncomplicated pulmonary emphysema are not necessarily more sensitive to the carcinogenic effects of inhaled 239PuO2 than individuals with normal lungs.

Administration, Inhalation↗

Deposition of cigarette smoke particles in the rat.

The fractional deposition of cigarette smoke particles in the respiratory tracts of rats was studied. Male and female rats were conditioned in nose-only exposure tubes 25 min/day for 2 days, exposed to cigarette smoke at mass concentrations of 95 or 341 mg/m3, 25 min/day for 3 days, and then exposed to smoke at mass concentrations of 212 and 657 mg/m3, 25 min/day for 5 days. Mainstream cigarette smoke was generated by a modified Walton smoking machine from two 1R3 research cigarettes burned sequentially for each exposure. Deposition studies were conducted by placing the rats in plethysmograph tubes to allow respiratory minute volume measurements during exposure, then exposing them to [14C]dotriacontane-labeled cigarette smoke at mass concentrations of 202 or 624 mg/m3 for 25 min, using the same smoking machine. Size distribution, real-time concentration, and 14C activity of the smoke particles were determined using a multijet Mercer impactor, a real-time aerosol monitor, and filter samples, respectively. Immediately after the exposure, the rats were terminated to determine the distribution of the 14C. Individual lung lobes, trachea and lobar bronchi, head, larynx, kidneys, liver, gastrointestinal (GI) tract, blood, and depleted carcass of each rat were analyzed for 14C content. Results showed that the GI tract contained 16-31% of the total activity, indicating significant clearance from the large airways and nose to the GI tract during the exposure and during the 10-15 min between the cessation of the exposure and the removal of the organs. Total deposition of the inhaled 14C activity was 20.1 +/- 1.6% for both exposure concentrations. The intrapulmonary deposition fractions (lung lobes plus airways below the lobar bronchi) were 12.4 +/- 0.9 and 15.9 +/- 1.4% for concentrations of 202 and 624 mg/m3, respectively, suggesting a slight enhancement in upper airway deposition for animals exposed to the higher smoke concentration.

Alkanes↗

Deposition and clearance of particles inhaled by beagle dogs previously exposed to SO2.

The effect of preexisting pulmonary disease on the deposition and retention of inhaled relatively insoluble radiolabeled particles was studied. Two dogs were exposed to 500 ppm sulfur dioxide 2 h/day, 5 days/week for 16 weeks and two dogs were sham-exposed to filtered air for the same period. Dogs exposed to sulfur dioxide developed chronic bronchitis during this exposure period. After the bronchitis had been established for 10 weeks, all 4 dogs were exposed by inhalation to 1.7 micron aerodynamic diameter 134Cs-labeled fused aluminosilicate particles (FAP) and the exposures to SO2 were discontinued. The bronchitis resolved within 4 weeks after SO2 was discontinued. Dogs were periodically whole-body counted and excreta were periodically collected and counted over a 385-day period following the 134Cs exposure. Deposition of the [134Cs]FAP in the pulmonary region averaged 42% for control dogs and 16% for dogs exposed to SO2; deposition in extrapulmonary regions of the respiratory tract averaged 58% for control dogs and 84% for dogs exposed to SO2. Although deposition patterns were different, early and long-term clearance pathways and rates were the same for all dogs, as indicated by analysis of whole body, excreta, and tissues for their burdens of 134Cs.

Aerosols↗

Effects of protraction of the alpha dose to the lungs of mice by repeated inhalation exposure to aerosols of 239PuO2.

To determine the long-term biological effects of protracted alpha irradiation of the lung, 84-day-old C57BL/6J mice were repeatedly exposed by inhalation to aerosols of 239PuO2 every other month for up to six exposures in 10 months to reestablish lung burdens of 20, 90, or 460 Bq. Other mice were exposed only once when either 84 or 460 days of age to achieve desired initial lung burdens of 20, 90, 460, or 2300 Bq. Suitable control groups were maintained. Groups of mice with similar cumulative alpha doses to the lung had 3.4 to 4.4 times greater incidence of pulmonary tumors (adenomas and adenocarcinomas) when the dose to the lung was protracted by the repeated inhalation exposures compared to mice that received a single inhalation exposure. Excess pulmonary tumors per unit dose to the lung were also greater in groups of repeatedly exposed mice compared to those exposed only once. Repeatedly exposed mice also died earlier with pulmonary tumors than did those exposed once. It appears that protraction of an alpha dose to lungs increases the carcinogenic risk of inhaled 239PuO2 in mice.

Administration, Inhalation↗

Sulfur dioxide-induced chronic bronchitis in beagle dogs.

This study was done to produce a model of chronic bronchitis. Twelve beagle dogs were exposed to 500 ppm sulfur dioxide (SO2) for 2 h/d, 5 d/wk for 21 wk and 4 dogs were sham-exposed to filtered ambient air for the same period. Exposure effects were evaluated by periodically examining the dogs using chest radiographs, pulmonary function, tracheal mucous clearance; and the cellular and soluble components of bronchopulmonary lavage fluids. Dogs were serially sacrificed after 13 and 21 wk of exposure and after 6 and 14 wk of recovery. Clinical signs produced in the SO2-exposed dogs included mucoid nasal discharge, productive cough, moist rales on auscultation, tonsilitis, and conjunctivitis. Chest radiographs revealed mild peribronchiolar thickening. Histopathology, tracheal mucous clearance measurements, and lavage cytology were consistent with a diagnosis of chronic bronchitis. It is concluded that repeated exposure to 500 ppm SO2 for 21 wk produced chronic bronchitis in the beagle dog. Complete recovery occurred within 5 wk following cessation of SO2 exposure.

Animals↗