Pulmonary inflammation and epithelial injury in response to acute ozone exposure in the rat.

To document the time course of the inflammatory response and epithelial injury in the lung following an acute ozone exposure, rats were exposed to 1.0 ppm ozone for periods between 4 and 24 hr. Some of the exposures were followed by postexposure periods in filtered air for up to 20 hr. Bronchoalveolar lavage fluid (BALF) analysis and electron microscopic morphometry on centriacinar regions of lungs fixed by intravascular perfusion were used to assess the degree of pulmonary inflammation and epithelial cell necrosis. Total protein and numbers of neutrophils and epithelial cells in BALF increased as the duration of ozone exposure increased, while BALF macrophages decreased. Quantitation of the neutrophil response in centriacinar lung regions (capillary, interstitial, and epithelial/luminal compartments of the terminal bronchiole and proximal alveolar duct) by morphometry generally correlated with the BALF analysis, and revealed a greater volume per surface area epithelial basal lamina (Vs) of neutrophils in the terminal bronchiole compartments compared to proximal alveoli. Necrosis of epithelial cells in terminal bronchioles, primarily ciliated cells, occurred as early as 4 hr after initiation of ozone exposure, before marked neutrophil migration, and continued during periods of maximal neutrophil influx. We concluded that the early epithelial necrosis in terminal bronchioles during the first few hours of ozone exposure was primarily due to direct ozone toxicity, but could not rule out the possibility of neutrophils contributing to the injury at later time points, especially between 8 and 12 hr of exposure (during periods of maximal neutrophil migration).     

INTERSPECIES DIFFERENCES IN TIME COURSE OF PULMONARY TOXICITY FOLLOWING REPEATED EXPOSURE TO OZONE

To compare the extent and time course of pulmonary injury and repair in 3 rodent species, rats, mice and guinea pigs were continuously exposed for 3, 7, 28, and 56 days to 400 and 800 mug O3/m3 (0.2 and 0.4 ppm). Recovery from 28 days of exposure was studied at 3, 7, and 28 days after exposure. Pulmonary injury and repair was studied at various time points by histology, electron microscopy, morphometry, and biochemistry. In all 3 species a concentration-related centriacinar inflammation occurred, with a maximum after 3 days of exposure. The number of alveolar macrophages and the pulmonary cell density in the centriacinar region increased progressively until 56 days of exposure, with the guinea pig the most sensitive species. Only the mouse displayed a concentration and exposure-time dependent hypertrophy of bronchiolar epithelium. After 56 days of exposure to 800 mug O3/m3 in the rat and the guinea pig, giant lamellar bodies in type II cells were present. Exposures for 3 and 7 days at near ambient ozone concentrations (400mug O3/m3) resulted in significantly elevated lung enzyme activities in the mouse, and in significant histological and morphometric changes in all 3 species. In rat and guinea pigs exposures for 56 days resulted in alveolar duct fibrosis. The highest biochemical response and the slowest recovery from ozone exposure were seen in the mouse. Histology, morphometry, and biochemistry revealed a total recovery from a 28-day exposure period in rats after 28 days, while in guinea pigs the ductular septa were still thickened and in mice all enzyme activities were still elevated in comparison with control values. In conclusion, the response of mice to ozone was evaluated as most severe, followed by those of guinea pigs and least in rats.     

Comparison of acute ozone-induced nasal and pulmonary inflammatory responses in rats

The centriacinar pulmonary lesion induced by ozone has been extensively characterized, but little is known about the effects of this oxidant gas in the upper airways. The present study was designed to compare the effects of acute ozone exposure in the nose and lungs of rats. We examined the cellular inflammatory responses in the nasal cavity and lower respiratory tract by means of nasal and bronchoalveolar lavage and morphometric quantitation of neutrophils within the nasal mucosa and pulmonary terminal bronchioloalveolar duct regions (i.e., centriacinar). Rats were exposed to 0.0, 0.12, 0.8, or 1.5 ppm ozone for 6 hr and were sacrificed immediately or 3, 18, 42, or 66 hr following exposure. Eighteen hours after exposure, increased numbers of neutrophils, as compared to controls, were recovered from nasal lavage fluid (NLF) of rats exposed to 0.12 ppm ozone. There was no change in the number of neutrophils recovered from bronchoalveolar lavage fluid (BALF) at any time after exposure. Rats exposed to 0.8 ppm ozone had more neutrophils in NLF than controls immediately after exposure, but no concomitant increase in BALF neutrophils at that time. However, as the number of neutrophils in BALF increased (maximum at 42 hr), the number of neutrophils recovered from NLF decreased (minimum at 42 hr). Rats exposed to 1.5 ppm ozone had no significant increases in nasal neutrophils in NLF at any time after exposure but had greatly increased numbers of neutrophils in BALF 3, 18, and 42 hr after exposure. The number of neutrophils recovered by nasal and bronchoalveolar lavage accurately reflected the tissue neutrophil response at sites within the nasal cavity and lung that were injured by acute ozone exposure. Our results suggest that at high ozone concentrations (0.8 and 1.5 ppm), the acute nasal inflammatory response is attenuated by a simultaneous, competing, inflammatory response within the centriacinar region of the lung. Analysis of nasal lavage fluid for changes in cellular composition may be a useful indicator of acute exposure to ambient levels of ozone, but at higher ozone levels, the nasal cellular inflammatory response may underestimate the effects of ozone on nasal and pulmonary epithelia.     

Age-related morphometric differences in responses of rat lungs to ozone

The influence of age on morphologic changes in lungs of rats exposed to ozone was studied in female Sprague-Dawley rats, aged 60 and 444 days. Rats of both age groups were exposed continuously for 72 hr to either 0.35 or 0.80 ppm ozone, or to filtered air. Tissues were evaluated using light microscopic morphometry and scanning electron microscopy. The lungs from ozone-exposed 60-day-old rats had larger volume fractions of centriacinar lesions than lungs from exposed 444-day-old rats. Within each age group there was an observed dose response, with rats exposed to 0.80 ppm ozone having larger volume fractions of lesions than those exposed to 0.35 ppm. Only the 444-day-old rats lost body weight during the exposure period. They also had smaller fixed lung volumes than same-aged controls. All 60-day-old rats gained weight during the exposure period, although rats exposed to 0.80 ppm ozone gained less than filtered air controls. Lesions observed in both age groups of female rats were qualitatively similar to those previously described in young adult male rats. We conclude that there are age-related differences in the morphometric responses of rats to ozone exposure. Younger rats had larger proportions of centriacinar lesions and macrophages while older rats had greater body weight and lung volume changes.     

Proliferative responses of rat nasal epithelia to ozone

The epithelium of the female Fischer 344/N rat anterior nasal cavity was examined and found to be composed of four types of epithelia: squamous, ciliated respiratory, nonciliated cuboidal/transitional, and olfactory. DNA replication in these tissues was monitored by bromodeoxyuridine (BrdUrd) incorporation. Labeled cells were identified using a monoclonal antibody recognizing BrdUrd. Ciliated respiratory, nonciliated cuboidal/transitional, and olfactory epithelia from control animals had a low level of DNA replication (1 labeled cell/mm basal lamina); in contrast, the squamous epithelium contained 40 labeled cells per millimeter basal lamina. Female Fischer 344/N rats were exposed to 0.0, 0.12, 0.27, or 0.8 ppm ozone, 6 hr/day for up to 7 days. Observations were made after 3 or 7 days of exposure and after 3 or 7 days of recovery from the 7-day exposure. Following exposure to 0.8 ppm ozone, a transient but marked increase in DNA replication was seen in the nonciliated cuboidal/transitional, while in ciliated respiratory and olfactory epithelia the transient increase in DNA replication was less marked. This increase was prominent after 3 days of exposure and absent by 7 days of exposure in all but the cuboidal/transitional epithelium. Exposure to 0.8 ppm ozone for either 3 or 7 days resulted in hyperplasia of the cuboidal epithelium. A depressed level of DNA replication was seen in the squamous epithelium following 7 days of recovery from 7 days of ozone exposure to 0.8 ppm ozone. This study shows that there are regional differences in DNA replication within the anterior nasal epithelium of the rat and that these levels are modulated by exposure to irritants. The cuboidal/transitional epithelium was the most responsive epithelial cell type to the effects of ozone exposure and may, therefore, provide a sensitive indicator of irritant damage to the respiratory tract.     

Species differences in impairment and recovery of alveolar macrophage functions following single and repeated ozone exposures.

Effects of single (0.4 ppm for 3, 6, or 12 hr) and repeated (0.4 ppm, 12 hr/day for 3 or 7 days) in vivo ozone exposures on rat and mouse alveolar macrophage functions and cell number were investigated. Single ozone exposure of rats resulted in a small (approximately 15%) decrease in Fc-receptor-mediated phagocytosis and phorbol ester-induced superoxide production by the alveolar macrophages and was followed by recovery above control levels within 12 hr of exposure. Repeated exposures of rats for up to 7 days did not alter alveolar macrophage functions, with the exception of the effects of 3 days of exposure on superoxide production (71 +/- 9% as compared with the controls). In mice, significant changes in alveolar macrophage functions were not observed until 12 hr of exposure (at that timepoint phagocytosis was 74 +/- 2%). Repeated ozone exposures of mice did not cause a further decrease in phagocytosis (at Day 7, 74 +/- 14%). Both after 3 and 7 days of repeated ozone exposure of mice, superoxide production by the alveolar macrophages was inhibited approximately 50%. In rats and mice, repeated ozone exposures led to an increase in the number of alveolar macrophages. In mice, this increase appeared at a later time point (at Day 7 vs Day 3) and was less pronounced (at Day 7, 139 +/- 9% vs 179 +/- 17%) as compared with rats. In summary, our data show that rat and mouse alveolar macrophages have different susceptibilities to both single and repeated in vivo ozone exposures.     

EFFECTS OF DIESEL EXHAUST ENRICHED CONCENTRATED PM2.5 IN OZONE PREEXPOSED OR MONOCROTALINE-TREATED RATS

Epidemiological studies have observed statistical associations between short-term exposure to increased ambient particulate air pollution and increased hospital admissions, medication use, pulmonary morbidity, and mortality. To examine the effects of particle air pollution in animals, rats with a preexisting pulmonary inflammation (induced by 1600 µg/m 3 ozone) or hypertension (induced by monocrotaline, MCT) were nose-only exposed to concentrated freshly generated diesel exhaust particles (DEP) mixed with ambient air (CDP). It was hypothesized that a single 6-h exposure to PM exacerbates respiratory inflammatory processes, which affects health parameters in the blood. Histopathology of lung and nose, bronchiolar lavage (BAL), and blood analyses were performed at 1, 2, and 4 days after of the CDP exposure. Morphometry of BrdU-labeled cells in lung and nose was performed at 4 days postexposure. One day after ozone exposure, a mild inflammatory reaction in the centriacinar area was present, consisting of an increase in cellularity of septa and in the number of alveolar macrophages, decreasing in time. Additional CDP exposure did not influence this pattern, except for alveolar macrophages that were loaded with CDP. The only effect seen in the nose after ozone exposure was a slight hypertrophy of the septal mucous cells. Additional exposure to CDP did not change this appearance. MCT-treated rats showed hypertrophy of the media of the pulmonary muscular arteries that was not effected by CDP. BrdU labeling of predominantly Clara cells in the terminal bronchioles was significantly increased after ozone exposure as well as after MCT treatment, whereas this labeling index was markedly enhanced after an additional exposure to CDP. However, no increases in Clara cell protein (CC16) levels were measured of Clara cell protein (CC16) in either BAL or blood. BrdU labeling in the nasal epithelium was not influenced by exposure to ozone or ozone + CDP. CDP exposures did not induce significant toxic effects in the lungs. CDP exposures clearly induced an oxidative stress that was indicated by increasing glutathione levels in BAL with time. In addition, blood fibrinogen levels were enhanced in pulmonary hypertensive rats exposed to CDP. The present study demonstrates that very high CDP concentrations are needed to result in pulmonary changes in animal models with a preexisting pulmonary inflammation or hypertension that continue for days after a single exposure. In addition, CDP has the potential to induce changes in blood. It has not yet been determined how the effects seen with CDP would compare to similar levels of ambient particles.     

Cell Proliferation in the Respiratory Tract of Hamsters Continuously Exposed During 4 Weeks to 0.8 PPM Ozone

Abstract

Male Syrian golden hamsters were exposed to 0.8 ppm ozone, 24 h/day for 4 wk. Cumulative labeling indices were measured during each week of exposure in the lung, the intrapulmonary airways, the trachea, and the nasal passages. In the alveolar zone, ozone did not affect labeling indices beyond the centriacinar region. In the terminal bronchioles and large intrapulmonary airways, labeling indices were significantly higher than in controls throughout exposure to ozone. The largest increase was seen during wk I. In the trachea and the nasal passages, a significant increase in cell labeling was only seen during wk I; thereafter the values returned to control levels. It was concluded that exposure to 0.8 ppm ozone produces signs of proliferative activity during a 4-wk continuous exposure in the epithelium of the intrapulmonary airways, but not in other sites.     

Effects of diesel exhaust enriched concentrated PM2.5 in ozone preexposed or monocrotaline-treated rats

Epidemiological studies have observed statistical associations between short-term exposure to increased ambient particulate air pollution and increased hospital admissions, medication use, pulmonary morbidity, and mortality. To examine the effects of particle air pollution in animals, rats with a preexisting pulmonary inflammation (induced by 1600 microg/m(3) ozone) or hypertension (induced by monocrotaline, MCT) were nose-only exposed to concentrated freshly generated diesel exhaust particles (DEP) mixed with ambient air (CDP). It was hypothesized that a single 6-h exposure to PM exacerbates respiratory inflammatory processes, which affects health parameters in the blood. Histopathology of lung and nose, bronchiolar lavage (BAL), and blood analyses were performed at 1, 2, and 4 days after of the CDP exposure. Morphometry of BrdU-labeled cells in lung and nose was performed at 4 days postexposure. One day after ozone exposure, a mild inflammatory reaction in the centriacinar area was present, consisting of an increase in cellularity of septa and in the number of alveolar macrophages, decreasing in time. Additional CDP exposure did not influence this pattern, except for alveolar macrophages that were loaded with CDP. The only effect seen in the nose after ozone exposure was a slight hypertrophy of the septal mucous cells. Additional exposure to CDP did not change this appearance. MCT-treated rats showed hypertrophy of the media of the pulmonary muscular arteries that was not effected by CDP. BrdU labeling of predominantly Clara cells in the terminal bronchioles was significantly increased after ozone exposure as well as after MCT treatment, whereas this labeling index was markedly enhanced after an additional exposure to CDP. However, no increases in Clara cell protein (CC16) levels were measured of Clara cell protein (CC16) in either BAL or blood. BrdU labeling in the nasal epithelium was not influenced by exposure to ozone or ozone + CDP. CDP exposures did not induce significant toxic effects in the lungs. CDP exposures clearly induced an oxidative stress that was indicated by increasing glutathione levels in BAL with time. In addition, blood fibrinogen levels were enhanced in pulmonary hypertensive rats exposed to CDP. The present study demonstrates that very high CDP concentrations are needed to result in pulmonary changes in animal models with a preexisting pulmonary inflammation or hypertension that continue for days after a single exposure. In addition, CDP has the potential to induce changes in blood. It has not yet been determined how the effects seen with CDP would compare to similar levels of ambient particles.     

Four-Day Repeated Inhalation and Recovery Study of Methyl lsocyanate in F344 Rats and B6C3F1 Mice

F344 rats and B6C3F1 mice of both sexes were exposed by inhalationto 0, l,and 3 ppm methyl isocyanate (MIC) for 4 consecutivedays (6 hr/day) followed by a recovery period of 91 days. Fivemice and rats/sex/group except the 3 ppm group (5 rats/ sexon Day 7 and 2 males on Day 28) were killed on Days 7, 28, 49,and 91 after the exposure and examined histopathologically.Forty-nine of 56 male rats, 51 of 56 female rats, and 1 of 56male mice in the 3 ppm group died by 28 days; early death animalswere also examined histologically. Exposure-related changesoccurred in rats and mice of both sexes in the 3 ppm group only.Lesions of the nasal cavity in rats and mice were characterizedby regeneration of the olfactory and respiratory epithelia secondaryto epithelial erosion. By Day 28 the olfactory and respiratoryepithelia in mice appeared normal, while in rats incompleteregeneration of the olfactory epithelium was still present.Regeneration of the respiratory epithelium in the trachea ofrats occurred in the 3 ppm group and the epithelium appearedto return to normal by Day 28. Lung lesions in rats consistedof mural and/or intraluminal fibrosis secondary to extensiveerosion of the respiratory epithelium in the major bronchi tothe terminal bronchioles. Acute inflammation of the small airways,occasional hyaline membranes of alveolar walls, and pulmonaryatelectasis were also seen. Alveolar fibrosis was observed inrats found dead from Day 14 on and in male rats killed on Day28. Atrophy of the thymus and spleen, atrial thrombosis of theheart, and hepatocellular necrosis were frequently seen in ratsdying following MIC exposure. The lung lesions in mice werequalitatively similar to those in rats, but were restrictedto the major bronchi. Minimal intraluminal or mural fibrosiswas still present in mice on Day 91. In a separate study, asingle 6-hr exposure of five male rats to 3 ppm MIC was followedby a recovery period of 7 days. The lesions of the respiratorysystem were essentially the same as those in the 3 ppm groupkilled on Day 7 after the 4-day repeated exposure of MIC, butthe alveolar lesions were more severe.     

Effects of nitrous acid exposure on pulmonary tissues in guinea pigs

Many epidemiological studies on the effects of nitrogen dioxide (NO₂) on respiratory function may have included nitrous acid (HONO) exposures in their measures, because conventional NO₂ assays detect HONO as NO₂. A few epidemiological studies and human HONO inhalation experiments have associated HONO with decrements in lung functions. However, there have been few HONO exposure experiments in animals. This study aims to develop a HONO generation system for the animal exposure experiments, and to assess the association of HONO exposure with histopathologic alterations in the respiratory tract of guinea pigs. We exposed the guinea pigs to 3.6?ppm HONO with secondary products of 0.3?ppm NO₂ and 1.6?ppm nitric oxide (NO) for 4 weeks (24?h/day). We conducted histopathologic analyses and measured specific airway resistance (sRaw) from 7?h 40?min to 8?h 30?min after the end of HONO exposure. We found pulmonary emphysema-like alterations in the alveolar duct centriacinar regions, distortion of the centriacinar regions of alveolar ducts with extension of the bronchial epithelial cells and smooth muscle cells, and expansion of bronchial epithelial cells, in the HONO exposure. These histopathologic results suggest that a high concentration of HONO with some NO₂ and NO may associate with decrements in lung functions and some respiratory symptoms. Although the increased tendency of the sRaw value was observed in the HONO exposure group, no statistically significant difference was found between the sRaw values from the HONO exposure group and the filtered air group (p?=?0.06, student’s t-test).     

Inhalation Studies in Rats Exposed to Dimethylacetahide (DMAc) from 3 to 12 Hours Per Day

ABSTRACT

Male rats were exposed by inhalation from 10 to 300 ppm Dimethylacetamide (DMAc) for either 3, 6, or 12 hrs/day for a total of 10 exposures (5 exposures, 2 rest days, 5 exposures). Rats were observed daily for signs of DMAc-related effects, growth was monitored by body weights, clinical laboratory tests and microscopic examination of the liver, testes epididymides, and nasal passages were conducted. One half of the rats in each group was allowed a 14-day post-exposure period to evaluate the reversibility of DMAc-induced changes. No clinical signs of toxicity or DMAc-related gross changes at necropsy were seen in any of the rats although 1 rat exposed to 300 ppm for 12 hours per day died following the seventh exposure. Slight (< 5%) decreases in body weight gain were seen in rats exposed to 300 ppm for 6 or 12 hrs/day. Serum cholesterol levels were elevated in rats exposed to either 100 or 300 ppm (all exposure durations) and in rats exposed to 30 ppm for 12 hours. Total serum protein concentrations were increased in rats exposed for 12 hours/day to either 30, 100, or 300 ppm. Hepatocellular hypertrophy together with margination of hepatocellular cytoplasmic contents and lipid-like cytoplasmic vacuolation in hepatocytes were seen microscopically only in rats exposed for 12 hours/day to 300 ppm. Recovery from these liver changes was not complete after 14-day post-exposure period. No evidence of either testicular damage or irritation to the upper respiratory tract was seen.     

Replicative dna synthesis in tissues of the rat exposed to aged and diluted sidestream smoke

Abstract

Male Sprague-Dawley rats were exposed to aged and diluted sidestream smoke (ADSS) from Kentucky 1R4F reference cigarettes for 6 h/day, 5 days/wk, for a 13-wk period. Exposure concentrations were 0, 0.1, 1, and 10 mg ADSS/m³. Exposures were conducted in whole-body inhalation chambers. Rats were held in nose-only exposure tubes for the 6-h exposures to minimize pelt deposition and subsequent ingestion of ADSS. Groups of 10 rats from each exposure group were killed after 5, 28, and 90 d of exposure to examine the rates of replicative DNA synthesis; 6 rats from each exposure group were kept for a 90-day recovery period after termination of exposures to examine replicative DNA synthesis rates. Three days prior to each scheduled necropsy, an osmotic pump containing 5-bromo-2′-deoxyuridine (BrdU) was implanted subcutaneously. After necropsy, tissues were processed for examination of BrdU-containing cells at several sites. Incorporation of BrdU was assessed either by counting the number of labeled cells along a length of an epithelial surface or by counting the number of labeled cells in an area of tissue. Tissues examined were from the nasal cavity, ventral larynx, and trachea, in addition to bronchial, bronchiolar, and alveolar regions of the lung. Endocardium, myocardium, epicardium, and aortic smooth muscle sites were also examined. Increased replicative DNA synthesis occurred in some sites of the respiratory tract at the 5-day timepoint at the mid or high exposure concentrations, although at 28 and 90 days, these effects had diminished in intensity or were not present, indicating adaptation to the ADSS exposure. The only tissues with elevated rates of replicative DNA synthesis at 90 days were the cuboidal and respiratory epithelium at the most rostra! portion of the nasal cavity at the highest exposure concentration. Increased rates of replicative DNA synthesis were not noted in heart tissues or lung alveolar epithelium at any concentration at any time point. Examination of rats killed after the end of the 90-day recovery period indicated that the increase in replicative DNA synthesis was not sustained after termination of exposures. The no observed effect level (NOEL) for increased replicative DNA synthesis after subchronic exposure to ADSS in the rat is greater than 1 mg ADSS/m³.     

ATTENUATION AND RECOVERY OF PULMONARY INJURY IN RATS FOLLOWING SHORT-TERM,REPEATED DAILY EXPOSURE TO OZONE

Controlled human and epidemiology studies have demonstrated that during repeated exposure to ozone (O 3) attenuation of lung function responses may occur. It is yet unknown whether inflammatory and biochemical effects in lower airways of humans, as observed upon single O 3 exposure, also show a diminutive response following repeated exposure to O 3. The aim of this study was to investigate inflammatory, permeability, and histopathological responses in lungs of rats following repeated daily O 3 exposure and to study the time course of attenuation and recovery of these effects using single O 3 challenges at various postexposure times. To aid in animal-to-human extrapolation, this study and a previously reported human study (Devlin et al., 1997) were designed with similar protocols. Wistar rats were exposed for 5 consecutive days to 0.4 ppm O 3 for 12 h/night. Subsequently, the time course of postexposure recovery was determined by a single challenge of 12 h to 0.4 ppm O 3 after a 5-, 10-, 15-, or 20-day recovery period. Broncho-alveolar lavage (BAL) examination and histopathology were performed 12 h after this O 3 challenge. To quantify the magnitude of the O 3 response, results were compared with a group exposed only once for 12 h to 0.4 ppm O 3 and sacrificed simultaneously. The results demonstrate that a single exposure of 0.4 ppm O 3 causes marked permeability and inflammatory responses in lower airways of rats, as evidenced by enhanced BAL fluid levels of proteins, fibronectin, interleukin (IL)-6, and inflammatory cells. However, 5 days of exposure to 0.4 ppm O 3 for 12 h/night resulted in a complete disappearance of these responses, resulting in BAL fluid values that were not different from those observed in unexposed controls. Postexposure analyses of pulmonary response to O 3 challenges demonstrated that these attenuated responses show a gradual recovery. The data indicate that with respect to BAL fluid levels of albumin, IL-6, and number of macrophages and neutrophils, the period for lung tissue to regain its full susceptibility and responsiveness to O 3 following a 5-day preexposure period is approximately 15-20 days. Remarkably, the total protein and fibronectin responses in BAL fluid still exhibited an attenuated response to an O 3 challenge at 20 days postexposure. Morphometry (number of BrdU-labeled cells in terminal bronchiolar epithelium, and number of alveolar macrophages) showed that after a recovery of 5-10 days following a 5-day preexposure the response to a challenge was identical to that after a single exposure. These results suggest that complete repair from lower airway inflammation caused by short-term, repeated exposure to O 3 may take longer than previously assumed.     

Inhalation toxicity of cyclododecatriene in rats.

Cyclododecatriene (CDDT, CAS No. 4904-61-4) was tested for its inhalation toxicity in rats following repeated exposures. Male rats were exposed nose-only to CDDT for 6 hr/day, 5 days/wk for a total of 9 exposures over 2 weeks. Particular attention was paid to neurotoxicologic endpoints. Concentrations of 0 (control), 5, 50, and 260 ppm were studied. The 260 ppm chamber contained both vapor and aerosol while the 5 and 50 ppm chambers were vapor only. Four groups of 10 rats each were used to measure standard clinical signs and growth, clinical pathology (including hematology, biochemistries, and urine analysis), and tissue pathology. Another 4 groups of similar size were used for neurotoxicity testing. In the standard toxicity groups, 1/2 of the rats were sacrificed 1 day following the 9th exposure; the other half underwent a 2-week recovery period prior to being sacrificed (recovery group). During the exposures rats inhaling 260 ppm had a diminished or absent response to an alerting stimulus. Irregular respiration and lethargy were observed in these rats immediately following exposure. These signs were rapidly reversible and were not seen prior to the subsequent exposure. Body weights in rats exposed to either 50 or 260 ppm were significantly lower than the corresponding controls. No compound-related clinical pathology changes were seen in any of the test groups and tissue pathology effects only occurred in the nasal tissue. In rats exposed to 260 ppm, minimal degeneration/necrosis of nasal olfactory epithelium was observed in rats examined immediately following the exposure period. This change was not seen in the recovery rats. Functional observational battery (FOB) assessments and motor activity (MA) evaluations conducted after the 4th and 9th exposures on rats from all test groups, and specific neuropathologic evaluation on perfused brain, spinal cord, and skeletal muscle from rats exposed to 260 ppm failed to demonstrate any specific neurotoxicity. Outward signs of sedation were seen at the top level tested. Under the conditions of this test, the no-observed-adverse-effect level (NOAEL) was determined to be 5 ppm based upon a reduced rate of body weight gain in the 50 ppm group. No specific neurotoxicity was detected and the histopathologic response was limited to reversible changes in the nasal epithelia in rats exposed to 260 ppm.     

Preneoplastic transformation of rat tracheal epithelial cells by ozone

The transforming potency of ozone for rat tracheal epithelial (RTE) cells exposed in vivo or in vitro was determined. RTE cells isolated from rats exposed to ozone (0, 0.14, 0.6, or 1.2 ppm, 6 hr/day, 5 days/week for 1, 2, or 4 weeks) showed no increase in the frequency of preneoplastic transformation compared to cells isolated from unexposed rats, although ozone-induced morphologic changes were observed in exposed tracheas. In contrast, preneoplastic variants of RTE cells were induced by multiple, but not single, exposures of RTE cells to ozone in culture. RTE cells exposed biweekly to ozone (approximately 0.7 ppm for 40 min, nine total exposures) had approximately twofold increases in the frequency of preneoplastic transformation compared to that of concurrent controls exposed to air. Single, 40-min exposures to ozone (approximately 1 or approximately 10 ppm) did not induce preneoplastic variants. However, single, 40-min exposures of RTE cells to approximately 10 ppm ozone did result in approximately 40% decreases in colony-forming efficiency. In addition, single, 40-min exposures of RTE cells to approximately 1 ppm ozone reduced the transforming potency of a subsequent exposure to the direct-acting chemical carcinogen N-methyl-N'-nitro-N-nitrosoguanidine (MNNG). When multiple ozone exposures followed exposure to MNNG (approximately 0.7 ppm ozone for 40 min, nine biweekly exposures), an additive (or possibly a multiplicative) effect of ozone on MNNG-induced preneoplastic transformation was seen. These results demonstrate that ozone can, under some conditions, induce preneoplastic variants of RTE cells. In addition, depending on the sequence or combinations of exposures, ozone can reduce or, possibly, increase, the transforming potency of the carcinogen MNNG for rat tracheal cells in culture.     

Attenuation and recovery of pulmonary injury in rats following short-term,repeated daily exposure to ozone

Controlled human and epidemiology studies have demonstrated that during repeated exposure to ozone (O(3)) attenuation of lung function responses may occur. It is yet unknown whether inflammatory and biochemical effects in lower airways of humans, as observed upon single O(3) exposure, also show a diminutive response following repeated exposure to O(3). The aim of this study was to investigate inflammatory, permeability, and histopathological responses in lungs of rats following repeated daily O(3) exposure and to study the time course of attenuation and recovery of these effects using single O(3) challenges at various postexposure times. To aid in animal-to-human extrapolation, this study and a previously reported human study (Devlin et al., 1997) were designed with similar protocols. Wistar rats were exposed for 5 consecutive days to 0.4 ppm O(3) for 12 h/night. Subsequently, the time course of postexposure recovery was determined by a single challenge of 12 h to 0.4 ppm O(3) after a 5-, 10-, 15-, or 20-day recovery period. Bronchoalveolar lavage (BAL) examination and histopathology were performed 12 h after this O(3) challenge. To quantify the magnitude of the O(3) response, results were compared with a group exposed only once for 12 h to 0.4 ppm O(3) and sacrificed simultaneously. The results demonstrate that a single exposure of 0.4 ppm O(3) causes marked permeability and inflammatory responses in lower airways of rats, as evidenced by enhanced BAL fluid levels of proteins, fibronectin, interleukin (IL)-6, and inflammatory cells. However, 5 days of exposure to 0.4 ppm O(3) for 12 h/night resulted in a complete disappearance of these responses, resulting in BAL fluid values that were not different from those observed in unexposed controls. Postexposure analyses of pulmonary response to O(3) challenges demonstrated that these attenuated responses show a gradual recovery. The data indicate that with respect to BAL fluid levels of albumin, IL-6, and number of macrophages and neutrophils, the period for lung tissue to regain its full susceptibility and responsiveness to O(3) following a 5-day preexposure period is approximately 15-20 days. Remarkably, the total protein and fibronectin responses in BAL fluid still exhibited an attenuated response to an O(3) challenge at 20 days postexposure. Morphometry (number of BrdU-labeled cells in terminal bronchiolar epithelium, and number of alveolar macrophages) showed that after a recovery of 5-10 days following a 5-day preexposure the response to a challenge was identical to that after a single exposure. These results suggest that complete repair from lower airway inflammation caused by short-term, repeated exposure to O(3) may take longer than previously assumed.     

Alveolar epithelial cell injuries by subchronic exposure to low concentrations of ozone correlate with cumulative exposure

Electron microscopy morphometry has been used to study the effects of cumulative exposure of low levels of inhaled O3 on lung proximal alveolar tissue. Six-week-old Fisher 344 rats were exposed to O3 in two different subchronic low-level exposure patterns. The first was a 12 hr/day exposure for 6 weeks and included two O3 concentrations, 0.12 and 0.25 ppm. The second consisted of an exposure profile having a background level of 0.06 ppm with an exposure peak 5 days each week that went from 0.12 to 0.25 ppm and back to 0.12 ppm over a 9-hr period. Rats given the second exposure pattern were exposed for either 3 or 13 weeks. Changes in the volumes of alveolar epithelium were found to be consistent and reproducible markers for cell injury and/or response. Results from the first study indicated that the relative volume of the type I epithelium increased 13 and 23% over the control value (p less than 0.05) following exposures for 6 weeks to 0.12 and 0.25 ppm, respectively. The magnitude of the increases were clearly concentration related. Similarly, when a fixed exposure concentration was employed the relative volume of type I epithelium was found to increase in proportion to the exposure time. In the second exposure, increases of 9 and 33% in relative volume of type I epithelium were found respectively after 3 and 13 weeks of exposure. If the total exposure determined by the product of O3 concentration (including background) and exposure time is plotted against the relative volume of type I epithelium from both the 0.12 ppm (60.5 ppm-hr) and 0.25 ppm (126 ppm-hr) exposures and the 3-week (45.3 ppm-hrs) and 13-week (196.2 ppm-hr) exposures, a linear relationship between increases in type I cell volume and the concentration X time product is observed. The coefficient of correlation (r2) for the linear regression of the animal means is 0.72. Changes in the volume of Type II epithelial cell also correlate with the concentration X time product (r2 = 0.66). This suggests that epithelial cell reactions to low-level subchronic exposure of O3 are directly related to the cumulative oxidant concentration. The pattern of exposure did not appear to affect the resulting degree of injury. Furthermore, a low level of background exposure may contribute to the epithelial cell injuries.     

Sensory irritation tolerance and cross-tolerance in F-344 rats exposed to chlorine or formaldehyde gas

Inhalation of chlorine (Cl2) or formaldehyde (HCHO) stimulates the trigeminal nerve endings in the nasal mucosa and results in respiratory rate depression in a concentration-dependent manner. To determine tolerance and cross-tolerance, the concentration-response curves of respiratory depression were compared between naive rats and rats pre-exposed to Cl2 or HCHO. Chlorine tolerance development was time and concentration dependent, being significant following a 1-day (6 hr/day), 10 ppm exposure, and reaching the maximum in 4 days. At 2.5 ppm of Cl2, tolerance was significant only after 10 days of exposure. Rats tolerant to Cl2 also showed cross-tolerance to HCHO. Tolerance to HCHO was observed in rats exposed to 28 ppm for 4 days, but not in groups exposed to 15 ppm for 1, 4, or 10 days. However, significant cross-tolerance to Cl2 was evident following a 1-day exposure to 15 ppm HCHO, with greatest effect seen in the group exposed for 10 days. Tolerance was reduced after a 7-day recovery following a 4-day exposure. Cross-tolerance was reduced also, but to a much lesser extent. These results suggest a common mechanism for tolerance and cross-tolerance development, but different reactive sites may exist for Cl2 and HCHO at the trigeminal nerve endings.     

Inhalation Toxicity of Cyclododecatriene in Rats

ABSTRACT

Cyclododecatriene (CDDT, CAS No. 4904-61-4) was tested for its inhalation toxicity in rats following repeated exposures. Male rats were exposed nose-only to CDDT for 6 hr/day, 5 days/wk for a total of 9 exposures over 2 weeks. Particular attention was paid to neurotoxicologic endpoints. Concentrations of 0 (control), 5, 50, and 260 ppm were studied. The 260 ppm chamber contained both vapor and aerosol while the 5 and 50 ppm chambers were vapor only. Four groups of 10 rats each were used to measure standard clinical signs and growth, clinical pathology (including hematology, biochemistries, and urine analysis), and tissue pathology. Another 4 groups of similar size were used for neurotoxicity testing. In the standard toxicity groups, 1/2 of the rats were sacrificed 1 day following the 9th exposure; the other half underwent a 2-week recovery period prior to being sacrificed (recovery group). During the exposures rats inhaling 260 ppm had a diminished or absent response to an alerting stimulus. Irregular respiration and lethargy were observed in these rats immediately following exposure. These signs were rapidly reversible and were not seen prior to the subsequent exposure. Body weights in rats exposed to either 50 or 260 ppm were significantly lower than the corresponding controls. No compound-related clinical pathology changes were seen in any of the test groups and tissue pathology effects only occurred in the nasal tissue. In rats exposed to 260 ppm, minimal degeneration/necrosis of nasal olfactory epithelium was observed in rats examined immediately following the exposure period. This change was not seen in the recovery rats. Functional observational battery (FOB) assessments and motor activity (MA) evaluations conducted after the 4th and 9th exposures on rats from all test groups, and specific neuropathologic evaluation on perfused brain, spinal cord, and skeletal muscle from rats exposed to 260 ppm failed to demonstrate any specific neurotoxicity. Outward signs of sedation were seen at the top level tested. Under the conditions of this test, the no-observed-adverse-effect level (NOAEL) was determined to be 5 ppm based upon a reduced rate of body weight gain in the 50 ppm group. No specific neurotoxicity was detected and the histopathologic response was limited to reversible changes in the nasal epithelia in rats exposed to 260 ppm.