Comparison of pulmonary and pleural responses of rats and hamsters to inhaled refractory ceramic fibers

The present study was designed to determine whether pleural fiber burdens or subchronic pleural fibroproliferative and inflammatory changes can help explain the marked interspecies differences in pleural fibrosis and mesothelioma that are observed following long-term inhalation of RCF-1 ceramic fibers by rats and hamsters. Fischer 344 rats and Syrian golden hamsters were exposed to RCF-1 for 4 h per day, 5 days per week, for 12 consecutive weeks. Lung and pleural fiber burdens were characterized during and after exposure. For all time points, approximately 67% of fibers associated with lung tissues from both rats and hamsters were longer than 5 microns in length. In comparison, fibers longer than 5 microns recovered from the pleural compartment, following a 12-week exposure and 12 weeks of recovery, accounted for 13% (hamsters) and 4% (rats) of the distribution. In the 12 weeks after the cessation of exposure, the number of fibers longer than 5 microns in length remained constant in the hamster at approximately 150 fibers per cm2 pleura. This was 2 to 3 times the corresponding fiber surface density in the rat. Significant pulmonary and pleural inflammation was detected at all time points and for both species. DNA synthesis by pleural mesothelial cells was quantified by bromodeoxyuridine uptake following 3 days of labeling. Labeling indices were higher in hamsters than in rats, both for RCF-1-exposed and filtered air-control animals and was highest for the parietal surface of the pleura. Significantly greater collagen deposition was measured in the visceral pleura of hamsters 12 weeks post-exposure but was not significantly elevated in rats. These findings demonstrate that subchronic inhalation exposure to RCF-1 induces pleural inflammation, mesothelial-cell turnover, pleural fibrosis, and an accumulation of fibers with a length greater than 5 microns in the hamster. The accumulation of long fibers in the pleural space may contribute to the pathology observed in the hamster following chronic inhalation of RCF- 1, whereas the presence of short, thin fibers may play a role in the acute-phase biological response seen in both species.      

Pulmonary responses of mice, rats, and hamsters to subchronic inhalation of ultrafine titanium dioxide particles.

A multispecies, subchronic, inhalation study comparing pulmonary responses to ultrafine titanium dioxide (uf-TiO(2)) was performed. Female rats, mice, and hamsters were exposed to aerosol concentrations of 0.5, 2.0, or 10 mg/m(3) uf-TiO(2) particles for 6 h/day, 5 days/week, for 13 weeks. Following the exposure period, animals were held for recovery periods of 4, 13, 26, or 52 weeks (49 weeks for the uf-TiO(2)-exposed hamsters) and, at each time point, uf-TiO(2) burdens in the lung and lymph nodes and selected lung responses were examined. The responses studied were chosen to assess a variety of pulmonary parameters, including inflammation, cytotoxicity, lung cell proliferation, and histopathological alterations. Retained lung burdens increased in a dose-dependent manner in all three species and were at a maximum at the end of exposures. Mice and rats had similar retained lung burdens at the end of the exposures when expressed as mg uf-TiO(2)/mg dry lung, whereas hamsters had retained lung burdens that were significantly lower. Lung burdens in all three species decreased with time after exposure, and, at the end of the recovery period, the percentage of the lung particle burden remaining in the 10 mg/m(3) group was 57, 45, and 3% for rat, mouse, and hamster, respectively. The retardation of particle clearance from the lungs in mice and rats of the 10 mg/m(3) group indicated that pulmonary particle overload had been achieved in these animals. Pulmonary inflammation in rats and mice exposed to 10 mg/m(3) was evidenced by increased numbers of macrophages and neutrophils and increased concentrations of soluble markers in bronchoalveolar lavage fluid (BALF). The initial neutrophil response in rats was greater than in mice, whereas the relative increase of macrophages was less than in mice. The neutrophilic response of rats, but not mice, declined in a time-dependent manner correlating with declining lung burdens; however, the fraction of recovered neutrophils at 52 weeks postexposure was equivalent in the two species. Consistent increases in soluble indicators of toxicity in the BALF (LDH and protein) occurred principally in rats and mice exposed to 10 mg/m(3) and diminished with time postexposure. There were no significant changes in cellular response or with markers indicating toxicity in hamsters, reflecting the capacity of these animals to rapidly clear particles from the lung. Progressive epithelial and fibroproliferative changes were observed in rats of the 10 mg/m(3) group. These lesions consisted of foci of alveolar epithelial proliferation of metaplastic epithelial cells (so-called alveolar bronchiolization) circumscribing aggregated foci of heavily particle-laden macrophages. The observed epithelial proliferative changes were also manifested in rats as an increase in alveolar epithelial cell labeling in cell proliferation studies. Associated with these foci of epithelial proliferation were interstitial particle accumulation and alveolar septal fibrosis. These lesions became more pronounced with increasing time postexposure. Epithelial, metaplastic, and fibroproliferative changes were not noted in either mice or hamsters. In summary, there were significant species differences in the pulmonary responses to inhaled uf-TiO(2) particles. Under conditions where the lung uf-TiO(2) burdens were equivalent, rats developed a more severe inflammatory response than mice and, subsequently, developed progressive epithelial and fibroproliferative changes. Clearance of particles from the lung was markedly impaired in mice and rats exposed to 10 mg/m(3) uf-TiO(2), whereas clearance in hamsters did not appear to be affected at any of the administered doses. These data are consistent with the results of a companion study using inhaled pigmentary (fine mode) TiO(2) (Bermudez et al., 2002) and demonstrate that the pulmonary responses of rats exposed to ultrafine particulate concentrations likely to induce pulmonary overload are different from similarly exposed mice and hamsters. These differences can be explained both by pulmonary respy response and by particle dosimetry differences among these rodent species.     

Long-term pulmonary responses of three laboratory rodent species to subchronic inhalation of pigmentary titanium dioxide particles.

Female mice, rats, and hamsters were exposed to 10, 50, or 250 mg/m(3) pigmentary titanium dioxide (p-TiO(2)) particles for 6 h per day and 5 days per week for 13 weeks with recovery groups held for an additional 4, 13, 26, or 52 weeks postexposure (46 weeks for the p-TiO(2)-exposed hamsters). At each time point p-TiO(2) burdens in the lung and lymph nodes and selected lung responses were examined. The responses studied were chosen to assess a variety of pulmonary parameters, including inflammation, cytotoxicity, lung cell proliferation, and histopathologic alterations. Burdens of p-TiO(2) in the lungs and in the lung-associated lymph nodes increased in a concentration-dependent manner. Retained lung burdens following exposure were greatest in mice. Rats and hamsters had similar lung burdens immediately postexposure when assessed as milligrams of p-TiO(2) per gram of dried lung. Particle retention data suggested that pulmonary overload was achieved in both rats and mice at the exposure levels of 50 and 250 mg/m(3). Under the conditions of the present study, hamsters were better able to clear p-TiO(2) particles than were similarly exposed mice and rats. Pulmonary histopathology revealed both species and concentration-dependent differences in p-TiO(2) particle retention patterns. Inflammation was noted in all three species at 50 and 250 mg/m(3), as evidenced by increases in macrophage and neutrophil numbers and in soluble indices of inflammation in bronchoalveolar lavage fluid (BALF; rats > mice, hamsters). In mice and rats, the BALF inflammatory responses remained elevated relative to controls throughout the entire postexposure recovery period in the most highly exposed animals. In comparison, inflammation in hamsters eventually disappeared, even at the highest exposure dose, due to the more rapid clearance of particles from the lung. Pulmonary lesions were most severe in rats, where progressive epithelial- and fibroproliferative changes were observed in the 250 mg/m(3) group. These epithelial proliferative changes were also manifested in rats as an increase in alveolar epithelial cell labeling in cell proliferation studies. Associated with these foci of epithelial proliferation were interstitial particle accumulation and alveolar septal fibrosis. In summary, there were significant species differences in pulmonary responses to inhaled p-TiO(2) particles. Under conditions in which the lung p-TiO(2) burdens were similar and likely to induce pulmonary overload, rats developed a more severe and persistent pulmonary inflammatory response than either mice or hamsters. Rats also were unique in the development of progressive fibroproliferative lesions and alveolar epithelial metaplasia in response to 90 days of exposure to a high concentration of p-TiO(2) particles.     

Mesothelial Cell Proliferation Induced by Intrapleural Instillation of Man-Made Fibers in Rats and Hamsters

Long-term inhalation exposure to a biopersistent man-made ceramicfiber (RCF 1) results in a high incidence of pleural mesotheliomasin Syrian golden hamsters but not in identically ex posed rats.To understand better the mechanisms involved in the intraspeciespathobiology of fiber-exposed mesothelium, the ability of thetwo different man-made fibers to induce cell prolif erationin hamster and rat pleural mesothelial cells was investigated.Three dose levels of either glass fibers (MMVF 10) or ceramicfibers (RCF 1) were instilled intrapleurally into male Fischer344 rats and male Syrian Golden hamsters. Rats and hamsterswere exposed to approximately equal numbers of long thin fibersper kilogram of body weight using a single intra- pleural instillation.Bromodeoxyuridine (BrdU) was administered via an implanted osmoticpump, and mesothelial cell proliferation was assessed at 7 and28 days postinstillation (P1) using immunocytochemical visualizationof labeled S-phase cells. Both rats and hamsters exhibited dose-dependentincreases in proliferation of pleural mesothelial cells followingexposure to both fiber types. Interspecies differences in mesothelialcell proliferation were noted for fiber type and pleural site.At 28 days PI, RCF-induced mesothelial cell proliferation wasfound to be more pronounced in hamsters than in rats in thecaudal visceral pleural. Comparing both fibers either by equalmass or by equal fiber numbers, mesothelial cell proliferationin RCF 1-treated animals was higher than in animals exposedto MMVF 10, especially in hamsters, and may be a factor in thedifference in mesothelioma induced by the two fibers. The highersustained (28 day) mesothelial cell proliferation in the visceralpleural of hamsters exposed to RCF may contribute to the species-specificdifferences in mesothelioma incidence found in long-term rodentinhalation studies.     

Effects of subchronically inhaled carbon black in three species. I. Retention kinetics, lung inflammation, and histopathology.

Exposure to high concentrations of carbon black (Cb) produces lung tumors in rats, but not mice or hamsters, presumably due to secondary genotoxic mechanisms involving persistent lung inflammation and injury. We hypothesized that the lung inflammation and injury induced by subchronic inhalation of Cb are more pronounced in rats than in mice and hamsters. Particle retention kinetics, inflammation, and histopathology were examined in female rats, mice, and hamsters exposed for 13 weeks to high surface area Cb (HSCb) at doses chosen to span a no observable adverse effects level (NOAEL) to particle overload (0, 1, 7, 50 mg/m(3), nominal concentrations). Rats were also exposed to low surface area Cb (50 mg/m(3), nominal; LSCb). Retention and effects measurements were performed immediately after exposure and 3 and 11 months post-exposure; retention was also evaluated after 5 weeks of exposure. Significant decreases in body weight during exposure occurred only in hamsters exposed to high-dose HSCb. Lung weights were increased in high-dose Cb-exposed animals, but this persisted only in rats and mice up to the end of the study period. Equivalent or similar mass burdens were achieved in rats exposed to high-dose HSCb and LSCb, whereas surface area burdens were equivalent for mid-dose HSCb and LSCb. Prolonged retention was found in rats exposed to mid- and high-dose HSCb and to LSCb, but LSCb was cleared faster than HSCb. Retention was also prolonged in mice exposed to mid- and high-dose HSCb, and in hamsters exposed to high-dose HSCb. Lung inflammation and histopathology were more severe and prolonged in rats than in mice and hamsters, and both were similar in rats exposed to mid-dose HSCb and LSCb. The results show that hamsters have the most efficient clearance mechanisms and least severe responses of the three species. The results from rats also show that particle surface area is an important determinant of target tissue dose and, therefore, effects. From these results, a subchronic NOAEL of 1 mg/m(3) respirable HSCb (Printex 90) can be assigned to female rats, mice, and hamsters.     

STUDIES ON THE INHALATION TOXICOLOGY OF TWO FIBERGLASSES AND AMOSITE ASBESTOS IN THE SYRIAN GOLDEN HAMSTER. PART II. RESULTS OF CHRONIC EXPOSURE

Fiberglass (FG) is the largest category of man-made mineral fibers (MMVFs). Many types of FG are manufactured for specific uses-building insulation, air handling, filtration, and sound absorption. In the United States, > 95% of FG produced is for building insulation. Several inhalation studies in rodents of FG building insulation have shown no indication of pulmonary fibrosis or carcinogenic activity. However, because of increasing use and potential for widespread human exposure, a chronic toxicity/carcinogenicity inhalation study of a typical building insulation FG (MMVF 10a) was conducted in hamsters, which were shown to be highly sensitive to the induction of mesotheliomas with another MMVF. A special-application FG (MMVF 33) and amosite asbestos were used for comparative purposes. Groups of 140 weanling male Syrian golden hamsters were exposed via nose-only inhalation for 6 h/day, 5 days/wk for 78 wk to either filtered air (chamber controls) or MMVF 10a, MMVF 33, or amosite asbestos at 250-300 WHO fibers/cm3 with two additional amosite asbestos groups at 25 and 125 WHO fibers/cm3. They were then held unexposed for 6 wk until 10-20% survival. After 13, 26, 52, and 78 wk, various pulmonary parameters and lung fiber burdens were evaluated. Groups hamsters were removed from exposure at 13 and 52 wk and were held until 78 wk (recovery groups). Initial lung deposition of long fibers (> 20 mum in length) after a single 6-h exposure was similar for all 3 fibers exposed to 250-300 fibers/cm3. MMVF 10a lungs showed inflammation (which regressed in recovery hamsters) but no pulmonary or pleural fibrosis or neoplasms. MMVF 33 induced more severe inflammation and mild interstitial and pleural fibrosis by 26 wk that progressed in severity until 52 wk, after which it plateaued. While the inflammatory lesions regressed in the recovery animals, pulmonary or pleural fibrosis did not. A single multicentric mesothelioma was observed at 32 wk. No neoplasms were found in the remainder of the study. Amosite asbestos produced dose-related inflammation and pulmonary and pleural fibrosis as early as 13 wk in all 3 exposure levels. The lesions progressed during the course of the study, and at 78 wk severe pulmonary fibrosis with large areas of consolidation was observed in the highest 2 exposure groups. Progressive pleural fibrosis with mesothelial hypertrophy and hyperplasia was present in the thoracic wall and diaphragm in most animals and increased with time in the recovery hamsters. While no pulmonary neoplasms were observed in the amosite exposed hamsters, a large number of mesotheliomas were found; 25 fibers/cm3, 3.6%; 125 fibers/cm3, 25.9%; and 250 fibers/cm3, 19.5%. For the 3 fiber types, the severity of the lung and pleural lesions generally paralleled the cumulative fiber burden, especially those >20 mum length, in the lung, thoracic wall, and diaphragm. They also inversely paralleled the in vitro dissolution rates; that is, the faster the dissolution, the lower were the cumulative lung burdens and the less severe the effects.     

Toxicological and epidemiological studies on effects of airborne fibers: Coherence and public health implications

Airborne fibers, when sufficiently biopersistent, can cause chronic pleural diseases, as well as excess pulmonary fibrosis and lung cancers. Mesothelioma and pleural plaques are caused by biopersistent fibers thinner than ～0.1 μm and longer than ～5 μm. Excess lung cancer and pulmonary fibrosis are caused by biopersistent fibers that are longer than ～20 μm. While biopersistence varies with fiber type, all amphibole and erionite fibers are sufficiently biopersistent to cause pathogenic effects, while the greater in vivo solubility of chrysotile fibers makes them somewhat less causal for the lung diseases, and much less causal for the pleural diseases. Most synthetic vitreous fibers are more soluble in vivo than chrysotile, and pose little, if any, health pulmonary or pleural health risk, but some specialty SVFs were sufficiently biopersistent to cause pathogenic effects in animal studies. My conclusions are based on the following: 1) epidemiologic studies that specified the origin of the fibers by type, and especially those that identified their fiber length and diameter distributions; 2) laboratory-based toxicologic studies involving fiber size characterization and/or dissolution rates and long-term observation of biological responses; and 3) the largely coherent findings of the epidemiology and the toxicology. The strong dependence of effects on fiber diameter, length, and biopersistence makes reliable routine quantitative exposure and risk assessment impractical in some cases, since it would require transmission electronic microscopic examination, of representative membrane filter samples, for determining statistically sufficient numbers of fibers longer than 5 and 20 μm, and those thinner than 0.1 μm, based on the fiber types.     

Pulmonary and Pleural Responses in Fischer 344 Rats Following Short-Term Inhalation of a Synthetic Vitreous Fiber: II. Pathobiologic Responses

The pleura is a target site for toxic effects induced by a varietyof fibrous particulates, including both natural mineral andman made vitreous fibers. We examined selected cytological andbio chemical indicators of inflammation in both the pleuralcompart ment and pulmonary parenchyma in F344 rats followinginhala tion of RCF-1, a kaolin-based ceramic fiber. Male F344rats were exposed by Inhalation to 89 mg/m³ (2645 WHO fibers/cc)RCF-1 6 hr/day for 5 consecutive days. In lung parenchyma, cytologicaland biochemical inflammatory responses occurred rapidly followingexposure. In contrast, pleural responses were delayed in onsetand of a much smaller magnitude than those observed in lung.At both Day 1 and Day 28 postexposure, increased quantitiesof lactate dehydrogenase, N-acetyl glucosaminidase, alkalinephosphatase, albumin, and neutrophils were present in bronchoalveolarlavage fluid. These responses were attenuated at the lattertime point. No significant responses were detected in pleurallavage fluid until 28 days following exposure, at which timeelevated numbers of macrophages and eosinophils, but not neutrophils,were observed. Increased albumin and fibronectin were also observed in PLF at this latter time point. These findings demonstratethat the onset of pleural and pulmonary responses followinginhalation of RCF-1 are temporally separated and that pleuralinjury may increase in severity with time following exposure.The increase in severity of pleural inflammation found in thepostexposure period cannot be readily explained by fiber translocation.     

Studies on the chronic toxicity (inhalation) of four types of refractory ceramic fiber in male Fischer 344 rats

Abstract Refractory ceramic fibers (RCF) are man-made vitreous fibers used primarily in industrial high-temperature applications, especially for insulation of furnaces and kilns. Because of their increasing use and potential for human exposure, a chronic toxicity/carcinogenicity inhalation study was conducted in Fischer 344 (F344) rats. Five groups of 140 weanling male F344 rats were exposed via noseonly inhalation to either HEPA-filtered air (chamber controls) or 30 mg/m(3) (approximately 220 fibers/cm(3)) of three types [kaolin-based, high-purity, and aluminum zirconia silica (AZS)] of "size-selected" RCF fibers (approximately 1μ in diameter and approximately 20 um in length) and an "after-service" heat-treated (2400°F for 24 h) kaolin-based fiber for 6 h/day, 5 days/wk for 24 mo. They were then held unexposed until approximately 20% survival and then sacrificed at 30 mo. A positive control group of 80 F344 rats was exposed to 10 mg/m(3) chrysotile asbestos. Croups of 3-6 animals were sacrificed at 3, 6, 9, 12, 15, 18, and 24 mo to follow the progression of lesions and to determine fiber lung burdens. Additional groups of 3 rats were removed from exposure at 3, 6, 9, 12, and 18 mo and were held until sacrificed at 24 mo (recovery groups) for similar determinations. Lung burdens increased rapidly for all RCFs, appearing to plateau by about 12 mo. By 24 mo, lung burdens ranged from 2.6 to 9.6 × 10(5) fiberslmg of dry lung tissue for the RCFs tested. Treatment-related lesions were restricted to the lungs. To some extent all types of RCF resulted in macrophage infiltration, bronchiolization of proximal alveoli, and microgranuloma formation by 3 mo of exposure. Interstitial fibrosis was observed at 6 mo for all types of RCF, except the "after-service" fiber where fibrosis was not seen until 12 mo. The lesions progressed in severity until 12-15 mo, after which they plateaued. A minimal amount of focal pleural fibrosis was first observed at 9 mo and progressed to a mild severity by the end of the study. Fxposure-related pulmonary neoplasms (bronchoalveolar adenomas and carcinomas combined) were observed with all 4 types of RCF [kaolin, 16 of 123 (13%); AZS, 9 of 121 (7.4%); high-purity, 19 of 121 (15.7%); and "after-service,"4 of 118 (3.4%)], compared to 2 of 120 (1.5%) in the untreated air controls. Pleural mesotheliomas were observed in two kaolin, three AZS, two high-purity, and one "after-service" exposed rats. A comparable but slightly greater amount of fibrosis was observed in the lungs of the positive (chrysotile asbestos) controls. The incidence of bronchoalveolar neoplasms in the chrysotile exposed rats was 13 of 69 (18.8%), and a mesothelioma occurred in 1 (1.4%) animal. The results of this study showed that the four types of RCF studied had carcinogenic activity in rats at the maximum tolerated dose.     

Quantification of the pathological response and fate in the lung and pleura of chrysotile in combination with fine particles compared to amosite-asbestos following short-term inhalation exposure

The marked difference in biopersistence and pathological response between chrysotile and amphibole asbestos has been well documented. This study is unique in that it has examined a commercial chrysotile product that was used as a joint compound. The pathological response was quantified in the lung and translocation of fibers to and pathological response in the pleural cavity determined. This paper presents the final results from the study. Rats were exposed by inhalation 6?h/day for 5 days to a well-defined fiber aerosol. Subgroups were examined through 1 year. The translocation to and pathological response in the pleura was examined by scanning electron microscopy and confocal microscopy (CM) using noninvasive methods. The number and size of fibers was quantified using transmission electron microscopy and CM. This is the first study to use such techniques to characterize fiber translocation to and the response of the pleural cavity. Amosite fibers were found to remain partly or fully imbedded in the interstitial space through 1 year and quickly produced granulomas (0 days) and interstitial fibrosis (28 days). Amosite fibers were observed penetrating the visceral pleural wall and were found on the parietal pleural within 7 days postexposure with a concomitant inflammatory response seen by 14 days. Pleural fibrin deposition, fibrosis, and adhesions were observed, similar to that reported in humans in response to amphibole asbestos. No cellular or inflammatory response was observed in the lung or the pleural cavity in response to the chrysotile and sanded particles (CSP) exposure. These results provide confirmation of the important differences between CSP and amphibole asbestos.     

Quantification of the pathological response and fate in the lung and pleura of chrysotile in combination with fine particles compared to amosite-asbestos following short-term inhalation exposure

The marked difference in biopersistence and pathological response between chrysotile and amphibole asbestos has been well documented. This study is unique in that it has examined a commercial chrysotile product that was used as a joint compound. The pathological response was quantified in the lung and translocation of fibers to and pathological response in the pleural cavity determined. This paper presents the final results from the study. Rats were exposed by inhalation 6?h/day for 5 days to a well-defined fiber aerosol. Subgroups were examined through 1 year. The translocation to and pathological response in the pleura was examined by scanning electron microscopy and confocal microscopy (CM) using noninvasive methods. The number and size of fibers was quantified using transmission electron microscopy and CM. This is the first study to use such techniques to characterize fiber translocation to and the response of the pleural cavity. Amosite fibers were found to remain partly or fully imbedded in the interstitial space through 1 year and quickly produced granulomas (0 days) and interstitial fibrosis (28 days). Amosite fibers were observed penetrating the visceral pleural wall and were found on the parietal pleural within 7 days postexposure with a concomitant inflammatory response seen by 14 days. Pleural fibrin deposition, fibrosis, and adhesions were observed, similar to that reported in humans in response to amphibole asbestos. No cellular or inflammatory response was observed in the lung or the pleural cavity in response to the chrysotile and sanded particles (CSP) exposure. These results provide confirmation of the important differences between CSP and amphibole asbestos.     

Chronic Inhalation Toxicity of a Kaolin-Based Refractory Ceramic Fiber in Syrian Golden Hamsters

Abstract

Kaolin-based refractory ceramic fiber (RCF) is a man-made vitreous fiber used primarily in industrial high-temperature applications, especially for insulation of furnaces and kilns. Because of its increasing use and potential for human exposure, a chronic toxicity/ carcinogenicity inhalation study was conducted in Syrian golden hamsters. Two groups of 140 weanling male hamsters were exposed via nose-only inhalation to either HEPA-filtered air (chamber controls) or 30 mg/m³ (-220 fibers/cm³) of “size-selected” RCF fibers (1 µm in diameter and -25 /jm in length) for 6 h/day, 5 dayslwk for 18 mo. They were then held unexposed until -20% survival (20 mo). A positive control group of 80 hamsters was exposed to 10 mg/m³ chrysotile asbestos (0.09 µm average diameter and 2.2 µm average length). Groups of 3 hamsters were sacrificed at 3, 6, 9, 12, 15, and 18 mo to follow the progression of lesions. Additional groups of 3 hamsters were removed from exposure at 3, 6, 9, and 12 mo and were held until 18 mo (recovery groups). Treatment-related lesions were restricted to the lungs. RCF exposure resulted in macrophage infiltration, bronchiolization of proximal alveoli, and microgranuloma formation by 3 mo of exposure. Interstitial and focal pleural fibrosis were observed at 6 mo. The pulmonary lesions progressed in severity until 12 mo after which they plateaued. In contrast, pleural fibrosis progressed until the end of the study. In recovery animals, there was no further progression of either pulmonary or pleural lesions following cessation of exposure. While no pulmonary neoplasms were observed in the RCF exposed hamsters, 42 of 102 (41.2%) had pleural mesotheliomas. A greater severity of fibrosis was observed in the lungs of the positive (chrysotile asbestos) controls, but no neoplasms were observed in either the lung or pleura. No neoplasms were found in the lungs or pleura of the chamber air controls.     

Use of Lung Toxicity and Lung Particle Clearance to Estimate the Maximum Tolerated Dose (MTD) for a Fiber Glass Chronic Inhalation Study in the Rat

Short–term toxicity and lung clearance were assessed inrats exposed by inhalation to size-selected fibrous glass (FG)for 13 weeks. Results from this study and from a recent FG chronicinhalation study are presented here as guidelines for the selectionof a maximum tolerated dose (MTD) for chronic inhalation studiesof fibers. Fischer 344 rats were exposed using nose–onlyinhalation chambers, 6 hr/day, 5 days/week, for 13 weeks toone of five concentrations of FG (36, 206, 316, 552, or 714fibers/cc; expressed gravirnetrically, 3, 16, 30, 45, or 60mg/m³) or to filtered air. Rats were then held for an additional10 weeks of postexposure recovery. Test fiber was size–selectedfrom glass wool having a chemical composition representativeof building insulation. Rats were terminated at 7, 13, 19, and23 weeks after the onset of exposure to evaluate pulmonary pathology,lung epithelium cell proliferation, lung fiber burden, and lunglavage cells and chemistry. The effect of fiber inhalation onlung clearance of innocuous microspheres was also evaluated:following fiber exposure, six rats/group were exposed to ⁸⁵Sr–labeled3.0-µm polystyrene microspheres by intratracheal inhalationand then monitored for whole–body radioactivity duringthe 10–week recovery period. Data from the short–termstudy support the choice of 30 mg/m³ as the MTD for the previouschronic FG study and also provide indicators of long–termlung toxicity and functional impairment that can be used toestimate the MTD for future chronic fiber inhalation studies.     

The toxicological response of Brazilian chrysotile asbestos: a multidose subchronic 90-day inhalation toxicology study with 92-day recovery to assess cellular and pathological response

Inhalation toxicology studies with chrysotile asbestos have in the past been performed at exceedingly high doses without consideration of fiber number or dimensions. As such, the exposures have exceeded lung overload levels, making quantitative assessment of these studies difficult if not impossible. To assess the cellular and pathological response in the rat lung to a well-characterized aerosol of chrysotile asbestos, a 90-day subchronic inhalation toxicology study was performed using a commercial Brazilian chrysotile (CA 300). The protocol was based on that established by the European Commission for the evaluation of synthetic vitreous fibers. The study was also designed to assess the potential for reversibility of any such changes and to permit association of responses with fiber dose in the lung and the influence of fiber length. Wistar male rats were randomly assigned to an air control group and to 2 CA 300 exposure groups at mean fiber aerosol concentrations of 76 fibers L > 20 microm/cm3 (3413 total fibers/cm3; 536 WHO fibers/cm3) or 207 fibers L > 20 microm/cm3 (8941 total fibers/cm3; 1429 WHO fibers/cm3). The animals were exposed using a flow-past, nose-only exposure system for 5 days/wk, 6 h/day, during 13 consecutive weeks (65 exposures), followed by a subsequent nonexposure period lasting for 92 days. Animals were sacrificed after cessation of exposure and after 50 and 92 days of nonexposure recovery. At each sacrifice, subgroups of rats were assessed for the determination of the lung burden; histopathological examination; cell proliferation response; bronchoalveolar lavage with the determination of inflammatory cells; clinical biochemistry; and for analysis by confocal microscopy. Through 90 days of exposure and 92 days of recovery, chrysotile at a mean exposure of 76 fibers L > 20 microm/cm3 (3413 total fibers/cm3) resulted in no fibrosis (Wagner score 1.8 to 2.6) at any time point. The long chrysotile fibers were observed to break apart into small particles and smaller fibers. In vitro modeling has indicated that these particles are essentially amorphous silica. At an exposure concentration of 207 fibers L > 20 microm/cm3 (8941 total fibers/cm3) slight fibrosis was observed. In comparison with other studies, chrysotile produced less inflammatory response than the biosoluble synthetic vitreous fiber CMS. As predicted by the recent biopersistence studies on chrysotile, this study clearly shows that at that at an exposure concentration 5000 times greater than the U.S. threshold limit value of 0.1 f(WHO)/cm3, chrysotile produces no significant pathological response.     

A CLEARANCE MODEL OF MAN-MAN VITREOUS FIBERS (MMVFs) IN THE RAT LUNG

Short-term inhalation experiments have been recently performed in rats to evaluate the biopersistence of man-made vitreous fibers (MMVFs). The number and size distribution of inhaled fibers in the rat lung were measured at different postexposure time points. These data were used for developing a mathematical model to describe the clearance kinetics of MMVFs in the rat lung. The model proposed a breakage scheme for long fibers during clearance. The breakage rates for different MMVFs were determined from the fiber size distribution data at different time points. The calculated breakage rate appears to be related to the in vitro dissolution rate; the more soluble a fiber, the faster the fiber breaks.     

Comparison of Calidria Chrysotile Asbestos to Pure Tremolite: Inhalation Biopersistence and Histopathology Following Short-Term Exposure

The differences between chrysotile asbestos, a serpentine mineral, and amphibole asbestos have been debated extensively. Many studies have shown that chrysotile is cleared from the lung more rapidly than amphibole. In order to quantify the comparative clearance of chrysotile and the amphibole asbestos tremolite, both fibers were evaluated in an inhalation biopersistence study that followed the European Commission recommended guidelines. In addition, the histopathological response in the lung was evaluated following the short-term exposure. This article presents the results of this study through 90 days after cessation of exposure. Following the termination of the study, a subsequent article will provide the complete results through 12 mo after cessation of exposure. In order to quantify the dynamics and rate by which these fibers are removed from the lung, the biopersistence of a sample of commercial grade chrysotile from the Coalinga mine in New Idria, CA, of the type Calidria RG144 and of a long-fiber tremolite were studied. For synthetic vitreous fibers, the biopersistence of the fibers longer than 20 µm has been found to be directly related to their potential to cause disease. This study was designed to determine lung clearance (biopersistence) and the histopathological response. As the long fibers have been shown to have the greatest potential for pathogenicity, the aerosol generation technique was designed to maximize the number of long respirable fibers. The chrysotile samples were specifically chosen to have 200 fibers/cm³ longer than 20 µm in length present in the exposure aerosol. These longer fibers were found to be largely composed of multiple shorter fibrils. The tremolite samples were chosen to have 100 fibers/cm³ longer than 20 µm in length present in the exposure aerosol. Calidria chrysotile fibers clear from the lung more rapidly (T_{1/2, fibers L>20 µm} = 7 h) than any other commercial fiber tested including synthetic vitreous fibers. With such rapidly clearing fibers, the 5-day exposure would not be expected to result in any pathological change in the lung, and the lungs of animals that inhaled Calidria chrysotile showed no sign of inflammation or pathology and were no different than the lungs of those animals that breathed filtered air. Following this 5-day exposure to tremolite, the tremolite fibers once deposited in the lung parenchyma do not clear and almost immediately result in inflammation and a pathological response in the lung. At the first time point examined, 1 day after cessation of exposure, inflammation was observed and granulomas were already formed. By 14 days postexposure these microgranulomas had turned fibrotic, and by 90 days postexposure the severity of the collagen deposits had increased and interstitial fibrosis was observed in one of the rats. These findings provide an important basis for substantiating both kinetically and pathologically the differences between chrysotile and the amphibole tremolite. As Calidria chrysotile has been certified to have no tremolite fiber, the results of the current study together with the results from toxicological and epidemiological studies indicate that this fiber is not associated with lung disease.     

Comparison of Calidria chrysotile asbestos to pure tremolite: inhalation biopersistence and histopathology following short-term exposure

The differences between chrysotile asbestos, a serpentine mineral, and amphibole asbestos have been debated extensively. Many studies have shown that chrysotile is cleared from the lung more rapidly than amphibole. In order to quantify the comparative clearance of chrysotile and the amphibole asbestos tremolite, both fibers were evaluated in an inhalation biopersistence study that followed the European Commission recommended guidelines. In addition, the histopathological response in the lung was evaluated following the short-term exposure. This article presents the results of this study through 90 days after cessation of exposure. Following the termination of the study, a subsequent article will provide the complete results through 12 mo after cessation of exposure. In order to quantify the dynamics and rate by which these fibers are removed from the lung, the biopersistence of a sample of commercial grade chrysotile from the Coalinga mine in New Idria, CA, of the type Calidria RG144 and of a long-fiber tremolite were studied. For synthetic vitreous fibers, the biopersistence of the fibers longer than 20 microm has been found to be directly related to their potential to cause disease. This study was designed to determine lung clearance (biopersistence) and the histopathological response. As the long fibers have been shown to have the greatest potential for pathogenicity, the aerosol generation technique was designed to maximize the number of long respirable fibers. The chrysotile samples were specifically chosen to have 200 fibers/cm3 longer than 20 microm in length present in the exposure aerosol. These longer fibers were found to be largely composed of multiple shorter fibrils. The tremolite samples were chosen to have 100 fibers/cm3 longer than 20 microm in length present in the exposure aerosol. Calidria chrysotile fibers clear from the lung more rapidly (T1/2, fibers L > 20 microm = 7 h) than any other commercial fiber tested including synthetic vitreous fibers. With such rapidly clearing fibers, the 5-day exposure would not be expected to result in any pathological change in the lung, and the lungs of animals that inhaled Calidria chrysotile showed no sign of inflammation or pathology and were no different than the lungs of those animals that breathed filtered air. Following this 5-day exposure to tremolite, the tremolite fibers once deposited in the lung parenchyma do not clear and almost immediately result in inflammation and a pathological response in the lung. At the first time point examined, 1 day after cessation of exposure, inflammation was observed and granulomas were already formed. By 14 days postexposure these microgranulomas had turned fibrotic, and by 90 days postexposure the severity of the collagen deposits had increased and interstitial fibrosis was observed in one of the rats. These findings provide an important basis for substantiating both kinetically and pathologically the differences between chrysotile and the amphibole tremolite. As Calidria chrysotile has been certified to have no tremolite fiber, the results of the current study together with the results from toxicological and epidemiological studies indicate that this fiber is not associated with lung disease.     

Use of short-term assays to evaluate the potential toxicity of two new biosoluble glasswool fibers

Two new glasswools were developed for optimal biosolubility in the lung: JM 902, for insulation and filtration; and JM 901F, for standard thermal and acoustical insulation. Both were tested for lung biopersistence and their potential to induce persistent pulmonary inflammation in rats. Their dissolution rate constants (k(dis)) were estimated in vitro. Results for 902 were: in vitro k(dis) (pH 7.4) = 150 ng/cm2/h; after 5 days of fiber inhalation (IH), lung clearance of fibers > 20 microm length (F > 20 microm) indicated a weighted half-time (WT(1/2)) of 6.8 days and 90% clearance time (T90) of 33 days; following intratracheal instillation (IT), lung clearance half-time (T(1/2)) for F > 5 microm was 20 days. Results for 901F were: k(dis) (pH 7.4) = 500-560; after 5 days of fiber inhalation exposure, WT(1/2) (F > 20 microm) = 8.1 days and T90 = 38 days. After 5 days of fiber inhalation, both fibers induced initial pulmonary inflammation followed by return to normal within 3 wk postexposure. Lung clearance half-times for 902 and 901F passed the European Union (EU) criteria for noncarcinogenic fibers (IH WT(1/2) F > 20 microm was < 10 days); 902 passed the noncarcinogenic criterion of the German government (IT T(1/2) F > 5 microm was < 45 days). Thus, carcinogenicity labeling is not required for either fiber in the EU. Short-term test results for 902 and 901F were similar to results for synthetic vitreous fibers (SVFs) that were innocuous in rodent chronic inhalation studies, but short-term test results for 902 and 901F differed sharply from results for other SVFs that were pathogenic in chronic studies. Thus, these short-term tests indicate that 902 and 901F are biosoluble fibers and would be nonpathogenic in the rat exposed by inhalation.     

Interspecies Comparisons of the Toxicity of Asbestos and Synthetic Vitreous Fibers: A Weight-of-the-Evidence Approach

This analysis reviews the available literature on interspecies comparisons of the toxicity of asbestos and synthetic vitreous fibers (SVFs). This topic is of substantial practical importance because most quantitative risk analyses on the effects of inhalation of SVFs are based upon extrapolation of data from rodent inhalation studies. Available information on interspecies comparisons for both dosimetry (the relation between exposure concentration and fiber lung burden) and potency (the relation between lung burden and disease) is summarized. Dosimetry models indicate that, on a normalized basis, fiber deposition and clearance rates are lower in humans than rats. Potency is less well understood than dosimetry, in part because the source of relevant human data is asbestos studies, which are adequate to demonstrate hazard, but are problematic in other regards. There are significant interspecies differences between the mouse, hamster, rat, and human. The available evidence suggests that the rat is preferable as a model for the human. Rats develop fibrosis at comparable lung burdens [10(6) long (> 20 microm length) fibers per gram of dry lung] to those in humans. This analysis concludes that, on a weight-of-evidence basis, there is no reason to conclude that humans are more sensitive to fibers than rats with respect to the development of lung cancer.