Inhalation toxicity of potassium octatitanate fibers (TISMO) in rats following 13 weeks of aerosol exposure

One hundred and forty male and 140 female rats were divided into 1 control and 3 test groups of 35 rats each, per sex, and exposed by whole-body inhalation to test compound at target concentrations of 0, 1 mg/m(3) (1700 fibers/cm(3), 123 WHO fibers/cm(3)), 10 mg/m(3) (5900 fibers/cm(3), 952 WHO fibers/cm(3)), and 100 mg/m(3) (112,700 fibers/cm(3), 7440 WHO fibers/cm(3)) for 6 h/day, 5 days/wk for 13 wk. Ten rats from each group were killed after 13 wk of exposure and 13 wk of recovery, respectively, for histopathological evaluation. The other 15 rats from each group were killed to study lung clearance after 91 days of exposure, and approximately 1.5 and 3 mo of recovery following the end of the 13 wk of exposure. The mean fiber length of the chamber atmosphere was 2.8, 2.7, and 2.8 microm, while the mean fiber width was 0.48, 0.48, and 0.45 microm for the 1-, 10-, and 100-mg/m(3) chambers, respectively. In the 1-mg/m(3) (123 WHO fibers/cm(3)) exposure group, inhaled particles were mostly retained in a few fiber-laden alveolar macrophages (AMs) within the alveoli adjacent to alveolar ducts without any adverse tissue response throughout 13 wk of exposure and following 13 wk of recovery. This exposure concentration was considered to be a no-observable-adverse-effect level (NOAEL), since the alveoli containing fiber-laden AMs preserved normal structure. After 13 wk of exposure to 10 mg/m(3) (952 WHO fibers/cm(3)), fiber-laden AMs were mainly retained at the alveoli adjacent to the alveolar ducts. Infrequently, slight fibrotic thickening was observed in the alveolar ducts and adjoining alveoli, with proliferating fibroblasts and hyperplastic Type II pneumocytes, and microgranulomas. Occasionally, trace amounts of collagenous material were deposited in the thickened alveolar ducts and adjoining alveolar walls. In addition, minimal alveolar bronchiolarization was occasionally found in the alveoli adjacent to the terminal bronchioles. The peribronchial lymphoid tissue and thymic lymph nodes contained migrated fiber-laden AMs. After 13 wk of recovery, fiber-laden AMs had mostly disappeared from alveoli located in the peripheral acini, but they localized in the alveolar ducts region, suggesting there was active lung clearance of fibers by the AMs via airways. Thickened alveolar ducts and adjacent alveoli were decreased in thickness, a reversible change manifested by reduction of proliferating Type II pneumocytes and fibroblasts. Collagenized fibrosis was slightly more pronounced in the thickened alveolar ducts and adjoining alveoli. The lung response following 13 wk of exposure to 100 mg/m(3) (7440 WHO fibers/cm(3)) and after 13 wk of recovery was similar to those findings of the 952 WHO fibers/cm(3) group but more pronounced, demonstrating a clear concentration-related response. Alveolar ducts and adjoining alveolar walls in the central acini were irregularly thickened with more frequent evidence of minimal collagenized fibrosis. The lung burden and clearance of fibers were estimated by measuring the total content of titanium (Ti) in the lungs, but high variability of Ti content in control and exposed groups prevented meaningful lung clearance analysis.     

INHALATION TOXICITY OF POTASSIUM OCTATITANATE FIBERS (TISMO) IN RATS FOLLOWING 13 WEEKS OF AEROSOL EXPOSURE

One hundred and forty male and 140 female rats were divided into 1 control and 3 test groups of 35 rats each, per sex, and exposed by whole-body inhalation to test compound at target concentrations of 0, 1 mg/m³ (1700 fibers/cm³, 123 WHO fibers/cm³), 10 mg/m³ (5900 fibers/cm³, 952 WHO fibers/cm³), and 100 mg/m³ (112,700 fibers/cm³, 7440 WHO fibers/cm³) for 6 h/day, 5 days/wk for 13 wk. Ten rats from each group were killed after 13 wk of exposure and 13 wk of recovery, respectively, for histopathological evaluation. The other 15 rats from each group were killed to study lung clearance after 91 days of exposure, and approximately 1.5 and 3 mo of recovery following the end of the 13 wk of exposure. The mean fiber length of the chamber atmosphere was 2.8, 2.7, and 2.8 µm, while the mean fiber width was 0.48, 0.48, and 0.45 µm for the 1-, 10-, and 100-mg/m³ chambers, respectively. In the 1-mg/m³ (123 WHO fibers/cm³) exposure group, inhaled particles were mostly retained in a few fiberladen alveolar macrophages (AMs) within the alveoli adjacent to alveolar ducts without any adverse tissue response throughout 13 wk of exposure and following 13 wk of recovery. This exposure concentration was considered to be a no-observable-adverse-effect level (NOAEL), since the alveoli containing fiber-laden AMs preserved normal structure. After 13 wk of exposure to 10 mg/m³ (952 WHO fibers/cm³), fiber-laden AMs were mainly retained at the alveoli adjacent to the alveolar ducts. Infrequently, slight fibrotic thickening was observed in the alveolar ducts and adjoining alveoli, with proliferating fibroblasts and hyperplastic Type II pneumocytes, and microgranulomas. Occasionally, trace amounts of collagenous material were deposited in the thickened alveolar ducts and adjoining alveolar walls. In addition, minimal alveolar bronchiolarization was occasionally found in the alveoli adjacent to the terminal bronchioles. The peribronchial lymphoid tissue and thymic lymph nodes contained migrated fiber-laden AMs. After 13 wk of recovery, fiber-laden AMs had mostly disappeared from alveoli located in the peripheral acini, but they localized in the alveolar ducts region, suggesting there was active lung clearance of fibers by the AMs via airways. Thickened alveolar ducts and adjacent alveoli were decreased in thickness, a reversible change manifested by reduction of proliferating Type II pneumocytes and fibroblasts. Collagenized fibrosis was slightly more pronounced in the thickened alveolar ducts and adjoining alveoli. The lung response following 13 wk of exposure to 100 mg/m³ (7440 WHO fibers/cm³) and after 13 wk of recovery was similar to those findings of the 952 WHO fibers/cm³ group but more pronounced, demonstrating a clear concentration-related response. Alveolar ducts and adjoining alveolar walls in the central acini were irregularly thickened with more frequent evidence of minimal collagenized fibrosis. The lung burden and clearance of fibers were estimated by measuring the total content of titanium (Ti) in the lungs, but high variability of Ti content in control and exposed groups prevented meaningful lung clearance analysis.     

Pulmonary response of rats exposed to titanium dioxide (TiO2) by inhalation for two years

Rats were exposed to TiO2 by inhalation exposure to concentrations of 0, 10, 50, and 250 mg/m3 for 6 hr/day, 5 days/week for 2 years. There were no abnormal clinical signs, body weight changes, or excess mortality in any exposed group. Exposed groups showed slight increases in the incidence of pneumonia, tracheitis, and rhinitis with squamous metaplasia in the anterior nasal cavity. The pulmonary response at 10 mg/m3 satisfied the biological criteria for a "nuisance dust." The lung reaction was characterized by dust-laden macrophage (dust cell) infiltration in the alveolar ducts and adjoining alveoli with hyperplasia of Type II pneumocytes. Rats at 50 and 250 mg/m3 exposure concentrations revealed a dose-dependent dust cell accumulation, a foamy macrophage response, Type II pneumocyte hyperplasia, alveolar proteinosis, alveolar bronchiolarization, cholesterol granulomas, focal pleurisy, and dust deposition in the tracheobronchial lymph nodes. Minute collagenized fibrosis occurred in the alveolar walls enclosing large dust cell aggregates. The pulmonary lesions with massive dust accumulation appeared to be the result of an overwhelmed lung clearance mechanism at 250 mg/m3 exposure. Bronchioloalveolar adenomas and cystic keratinizing squamous cell carcinomas occurred at 250 mg/m3 exposure, while no compound-related lung tumors were found in rats exposed to either 10 or 50 mg/m3. In addition to excessive dust loading in the lungs of rats exposed chronically at 250 mg/m3, the lung tumors were different from common human lung cancers in terms of tumor type, anatomic location, tumorigenesis, and were devoid of tumor metastasis. Therefore, the biological relevance of these lung tumors and other pulmonary lesions for man is negligible.     

Inhalation toxicity study on rats exposed to titanium tetrachloride atmospheric hydrolysis products for two years

Rats were exposed to TiCl4 hydrolysis products by inhalation exposure at aerosol concentrations of 0, 0.1, 1.0, and 10 mg/m3 for 6 hr/day, 5 days/week for 2 years. There were no abnormal clinical signs, body weight changes, or excess mortality in any exposed groups. No pathological changes other than a mild rhinitis were observed at 0.1 mg/m3. At 1.0 mg/m3, the incidence of mild rhinitis and tracheitis was increased. The lungs showed a minute dust-laden macrophage (dust cell) reaction with slight Type II pneumocyte hyperplasia in alveoli adjacent to the alveolar ducts. The pulmonary response at the 1.0 mg/m3 satisfied the biological criteria for a nuisance dust. At 10 mg/m3, extrapulmonary particle deposition occurred in the tracheobronchial lymph nodes, liver, and spleen without any tissue response. An increased incidence of rhinitis, tracheitis, and dust cell response with Type II pneumocyte hyperplasia, alveolar bronchiolarization, foamy dust cell accumulation, alveolar proteinosis, cholesterol granuloma, and focal pleurisy was also observed. The pulmonary lesions developed in the alveolar duct region where dust cells had accumulated and had provoked a chronic tissue response. In addition, a few well-differentiated, cystic keratinizing squamous carcinomas were developed from alveoli showing bronchiolarization with squamous metaplasia in the alveolar duct region. No tumor metastasis was found in other organs. The lung tumors were a unique type of experimentally induced tumor and have not been seen usually in man or animals. Therefore, the relevance to man of this type of lung tumor is highly questionable.     

Effects of Inhaled Chromium Dioxide Dust on Rats Exposed for Two Years

Effects of Inhaled Chromium Dioxide Dust on Rats Exposed forTwo Years. LEE, K. P., ULRICH, C. E., GEIL, R. G., AND TROCHIMOWICZ,H. J. (1988). Fundam. Appl. Toxicol 10, 125–145. Ratswere exposed by inhalation to chromium dioxide (C1O2) dust atdesign concentrations of 0, 0.5 mg/m³(stabilized and unstabilized,respectively), or 25 mg/m³ (stabilized) for 6 hr/day, 5 days/weekfor 2 years. No dust-exposure-related pathological changes otherthan lung lesions were observed in all exposed rats. There wereno significant differences in pulmonary responses between unstabilizedand stabilized CrC>2 at the 0.5 mg/m³ exposure level. Thelungs showed minute dust deposition in the alveoli adjacentto the alveolar ducts, but maintained an intact general architecture.The pulmonary responses satisfied the biological criteria fora nuisance dust. At 25 mg/m³, dust deposition was sharply confinedto the alveoli in the alveolar duct region. Alveolar walls enclosingdust-laden macrophage (dust cell) aggregates were thickenedwith hyperplastic Type II pneumocytes and slightly collagenizedfibrosis. Alveoli adjacent to the terminal bronchioles werelined with bronchiolar epithelium (alveolar bronchiolar-ization).In addition, lungs showed foamy macrophage response, cholesterolgranulomas, alveolar protoeinosis, and minute fibrotic pleurisy.These pulmonary lesions occurred predominantly in female rats.Of 108 female rats, 6 developed keratin cysts and 2 had cystickeratinizing squa-mous cell carcinoma (CKSCC). None of 106 malerats had either a keratin cyst or a CKSCC. The lung tumors developedfrom metaplastic squamous cells in the areas of alveolar bronchio-larizationat the alveolar duct region. The lung tumors were well differentiatedand devoid of characteristics of true malignancy. The CKSCCis an experimentally induced, unique tumor type and is differentfrom the type of spontaneous lung tumor seen in man or animals.The relevance to man of this type of lung tumor appears to benegligible.     

The Pulmonary Response and Clearance of Ludox Colloidal Silica after a 4-Week Inhalation Exposure in Rats

Rats were exposed to Ludox colloidal silica (CS) at concentrationsof 0, 10, 50, and 150 mg/m³ for 6 hr/day, 5 days/week for 4weeks. Rats were killed after 4 weeks of exposure and 10 daysor 3 months post exposure (PE). The exposure concentration of10 mg/m³ Ludox CS is considered to be the no-effect concentration.There were no exposure-related clinical signs in any group.After 4 weeks exposure, lung weights were increased significantlyin rats exposed to 50 and 150 mg/m³ Ludox CS, but lung weightswere similar to those of controls at 3 months PE. After 4 weeksexposure to 50 mg/m³ Ludox CS, a slight alveolar macrophageresponse, polymorphonuclear leukocytic infiltration, and TypeII pneumocyte hyperplasia in alveolar duct regions were present.After 3 months PE, these pulmonary lesions had almost disappearedwith removal of most dust-laden alveolar macrophages (AMs).The pulmonary response to 150 mg/m³ Ludox CS was similar incharacter but increased in magnitude from that seen at 50 mg/m³At 3 months PE, most particleladen AMs had disappeared and theremaining AMs were aggregated and sharply demarcated. A fewaggregates of particle-laden AMs appeared to transform intosilicotic nodules comprising macrophages, epithelioid cells,and lymphocytic infiltration in some animals. Some silicoticnodules showed reticular fiber networks with minute collagenfiber deposition. Tracheobronchial lymph nodes were enlargedwith aggregates of particle-laden AMs and hyperplastic histiocyticcells. Lung-deposited Ludox cleared rapidly from the lungs withhalf-times of approximately 40 and 50 days for the 50 and 150mg/m³ groups, respectively.     

Chronic Inhalation Toxicity and Carcinogenicity Study on Potassium Octatitanate Fibers (TISMO) in Rats

A chronic inhalation toxicity/carcinogenicity study of potassium octatitanate fibers (TISMO) was conducted in male Fischer 344 rats. Groups of 135 rats were exposed via whole-body inhalation to 0, 20, 60, or 200 WHO fibers/cc of TISMO, 6 h/day, 5 days/w for 24 mo. Six of 30 subgroup rats were killed after 3, 6, 12, 18, and 24 mo of exposure for lung burden evaluations. Another 30 subgroup rats were removed from the exposure chambers after 6 mo of exposure, placed in clean air, and from this group 6 rats were killed at 3, 6, 9, 12, and 18 mo later to study lung clearance. The remaining 75 rats in each group were subjected to 24 mo of exposure for chronic toxicity and carcinogenicity study. Rats exposed to HEPA-filtered air (chamber control) were used as a negative control in each study. The lung burden results indicated that a time point of equilibrium between lung burden and lung clearance at 20 WHO fibers/cc exposure was attained after approximately 18 mo of exposure. There was no difference in the number of WHO fiber from the lungs between 18 and 24 mo at 20 WHO fibers/cc exposure. But disproportional rapid increase in lung burden at 200 WHO fibers/cc exposure appeared to be saturation of lung clearance mechanism resulting from lung overloading. At 200 WHO fibers/cc exposure, approximately 22.9 and 70.5 million WHO fibers were retained in the lung after 3 and 6 mo of exposure, respectively, but lungs revealed normal in appearance. However, alveolar walls enclosing aggregated TISMO-laden alveolar macrophages (AMs) showed fibrotic thickening and approximately 197.3 million WHO fibers were retained in the lungs after 18 mo of exposure. Inhaled fibers were rapidly cleared during 3- and 6-mo recovery periods, and thereafter gradually progressive fiber reduction was observed throughout 18 mo of recovery. The number of WHO fibers decreased by approximately 72%, 74%, and 79% in the 200, 60, and 20 WHO fibers/cc groups, respectively, at the end of the 18-mo recovery period following 6 mo of exposure. Although inhaled TISMO fibers in the 20 WHO fibers/cc exposure group were phagocytized by alveolar macrophages (AMs) the lung morphology appeared normal throughout 24 mo of exposure. At 60 WHO fibers/cc exposure, a slight dose- and time-dependent increase in TISMO-laden AMs was observed throughout 3, 6, and 12 mo of exposure and some alveoli containing aggregated TISMO-laden AMs showed alveolar wall thickening at 18 mo of exposure and minimal alveolar fibrosis at 24 mo of exposure. The exposure concentration is interpreted as a borderline effect level. At 200 WHO fibers/cc exposure, lungs preserved normal architecture at 3 and 6 mo of exposure. Some alveolar walls enclosing aggregates of TISMO-laden AMs were slightly thickened after 12 mo of exposure and revealed slight alveolar fibrosis after 18 and 24 mo of exposure. Neither exposure related-pulmonary neoplasm nor mesothelioma was observed in 24 mo of exposure. The 20 WHO fibers/cc exposure concentration is considered to be a no-observable-adverse-effect level (NOAEL). TISMO exposure limits of 1 WHO fiber/cc would not impose a significant health hazard to humans in the workplace based on the animal experiments and medical surveys on workers.     

Chronic inhalation toxicity and carcinogenicity study on potassium octatitanate fibers (TISMO) in rats

A chronic inhalation toxicity/carcinogenicity study of potassium octatitanate fibers (TISMO) was conducted in male Fischer 344 rats. Groups of 135 rats were exposed via whole-body inhalation to 0, 20, 60, or 200 WHO fibers/cc of TISMO, 6 h/day, 5 days/w for 24 mo. Six of 30 subgroup rats were killed after 3, 6, 12, 18, and 24 mo of exposure for lung burden evaluations. Another 30 subgroup rats were removed from the exposure chambers after 6 mo of exposure, placed in clean air, and from this group 6 rats were killed at 3, 6, 9, 12, and 18 mo later to study lung clearance. The remaining 75 rats in each group were subjected to 24 mo of exposure for chronic toxicity and carcinogenicity study. Rats exposed to HEPA-filtered air (chamber control) were used as a negative control in each study. The lung burden results indicated that a time point of equilibrium between lung burden and lung clearance at 20 WHO fibers/cc exposure was attained after approximately 18 mo of exposure. There was no difference in the number of WHO fiber from the lungs between 18 and 24 mo at 20 WHO fibers/cc exposure. But disproportional rapid increase in lung burden at 200 WHO fibers/cc exposure appeared to be saturation of lung clearance mechanism resulting from lung overloading. At 200 WHO fibers/cc exposure, approximately 22.9 and 70.5 million WHO fibers were retained in the lung after 3 and 6 mo of exposure, respectively, but lungs revealed normal in appearance. However, alveolar walls enclosing aggregated TISMO-laden alveolar macrophages (AMs) showed fibrotic thickening and approximately 197.3 million WHO fibers were retained in the lungs after 18 mo of exposure. Inhaled fibers were rapidly cleared during 3- and 6-mo recovery periods, and thereafter gradually progressive fiber reduction was observed throughout 18 mo of recovery. The number of WHO fibers decreased by approximately 72%, 74%, and 79% in the 200, 60, and 20 WHO fibers/cc groups, respectively, at the end of the 18-mo recovery period following 6 mo of exposure. Although inhaled TISMO fibers in the 20 WHO fibers/cc exposure group were phagocytized by alveolar macrophages (AMs) the lung morphology appeared normal throughout 24 mo of exposure. At 60 WHO fibers/cc exposure, a slight dose- and time-dependent increase in TISMO-laden AMs was observed throughout 3, 6, and 12 mo of exposure and some alveoli containing aggregated TISMO-laden AMs showed alveolar wall thickening at 18 mo of exposure and minimal alveolar fibrosis at 24 mo of exposure. The exposure concentration is interpreted as a borderline effect level. At 200 WHO fibers/cc exposure, lungs preserved normal architecture at 3 and 6 mo of exposure. Some alveolar walls enclosing aggregates of TISMO-laden AMs were slightly thickened after 12 mo of exposure and revealed slight alveolar fibrosis after 18 and 24 mo of exposure. Neither exposure related-pulmonary neoplasm nor mesothelioma was observed in 24 mo of exposure. The 20 WHO fibers/cc exposure concentration is considered to be a no-observable-adverse-effect level (NOAEL). TISMO exposure limits of 1 WHO fiber/cc would not impose a significant health hazard to humans in the workplace based on the animal experiments and medical surveys on workers.     

Pulmonary cellular effects in rats following aerosol exposures to ultrafine Kevlar aramid fibrils: evidence for biodegradability of inhaled fibrils.

Previous chronic inhalation studies have shown that high concentrations of Kevlar fibrils produced fibrosis and cystic keratinizing tumors in rats following 2-year inhalation exposures. The current studies were undertaken to evaluate mechanisms and to assess the toxicity of inhaled Kevlar fibrils relative to other reference materials. Rats were exposed to ultrafine Kevlar fibers (fibrils) for 3 or 5 days at concentrations ranging from 600-1300 fibers/cc (gravimetric concentrations ranging from 2-13 mg/m3). A complete characterization of the fiber aerosol and dose was carried out. These measurements included gravimetric concentrations, mass median aerodynamic diameter, fiber number, and count median lengths and diameters of the aerosol. Following exposures, cells and fluids from groups of sham- and fiber-exposed animals were recovered by bronchoalveolar lavage (BAL). Alkaline phosphatase, lactate dehydrogenase (LDH), protein, and N-acetyl glucosaminidase (NAG) values were measured in BAL fluids at several time points postexposure. Alveolar macrophages were cultured and studied for morphology, chemotaxis, and phagocytosis by scanning electron microscopy. The lungs of additional exposed animals were processed for deposition, cell labeling, retained dose, and lung clearance studies, as well as fiber dimensions (from digested lung tissue), histopathology, and transmission electron microscopy. Five-day exposures to Kevlar fibrils elicited a transient granulocytic inflammatory response with concomitant increases in BAL fluid levels of alkaline phosphatase, NAG, LDH, and protein. Unlike the data from silica and asbestos exposures where inflammation persisted, biochemical parameters returned to control levels at time intervals between 1 week and 1 month postexposure. Macrophage function in Kevlar-exposed alveolar macrophages was not significantly different from sham controls at any time period. Cell labeling studies were carried out immediately after exposure, as well as 1 week and 1 month postexposure. Increased pulmonary cell labeling was measured in terminal bronchiolar cells immediately after exposure but returned to control values 1 week later. Fiber clearance studies demonstrated a transient increase in the numbers of retained fibers at 1 week postexposure, with rapid clearance of fibers thereafter. The transient increase in the number of fibers could be due to transverse cleaving of the fibers, since the average lengths of retained fibers continued to decrease over time. In this regard, a progressive decrease in the mean lengths and diameters of inhaled fibers was measured over a 6-month postexposure period.(ABSTRACT TRUNCATED AT 400 WORDS)     

Are alveolar macrophages translocated to the lymph nodes?

Hilar lymph nodes from 5 rabbits exposed for 3 months (5 days/week, 6 h/day) to metallic nickel dust (1.2 mg/m³) and from 2 controls were studied with electron microscopy. Some lymph node macrophages were filled with laminated bodies and had a vesiculated cytoplasm, a well developed endoplasmic reticulum and a few of them contained nickel particles as well. This means that they appeared identical to macrophages found in alveoli in nickel exposed rabbits. We propose that there is a transport of alveolar macrophages to the lymph nodes in nickel exposed rabbits.     

Ninety-day inhalation toxicity study with a vapor grown carbon nanofiber in rats

A subchronic inhalation toxicity study of inhaled vapor grown carbon nanofibers (CNF) (VGCF-H) was conducted in male and female Sprague Dawley rats. The CNF test sample was composed of > 99.5% carbon with virtually no catalyst metals; Brunauer, Emmett, and Teller (BET) surface area measurements of 13.8 m2/g; and mean lengths and diameters of 5.8 μm and 158 nm, respectively.Four groups of rats per sex were exposed nose-only, 6 h/day, for 5 days/week to target concentrations of 0, 0.50, 2.5, or 25 mg/m3 VGCF-H over a 90-day period and evaluated 1 day later. Assessments included conventional clinical and histopathological methods, bronchoalveolar lavage fluid (BALF) analysis, and cell proliferation (CP) studies of the terminal bronchiole (TB), alveolar duct (AD), and subpleural regions of the respiratory tract. In addition, groups of 0 and 25 mg/m3 exposed rats were evaluated at 3 months postexposure (PE). Aerosol exposures of rats to 0.54 (4.9 f/cc), 2.5 (56 f/cc), and 25 (252 f/cc) mg/m(3) of VGCF-H CNFs produced concentration-related small, detectable accumulation of extrapulmonary fibers with no adverse tissue effects. At the two highest concentrations, inflammation of the TB and AD regions of the respiratory tract was noted wherein fiber-laden alveolar macrophages had accumulated. This finding was characterized by minimal infiltrates of inflammatory cells in rats exposed to 2.5mg/m(3) CNF, inflammation along with some thickening of interstitial walls, and hypertrophy/hyperplasia of type II epithelial cells, graded as slight for the 25mg/m(3) concentration. At 3 months PE, the inflammation in the high dose was reduced. No adverse effects were observed at 0.54mg/m(3). BALF and CP endpoint increases versus controls were noted at 25mg/m(3) VGCF-H but not different from control values at 0.54 or 2.5mg/m(3). After 90 days PE, BALF biomarkers were still increased at 25mg/m(3), indicating that the inflammatory response was not fully resolved. Greater than 90% of CNF-exposed, BALF-recovered alveolar macrophages from the 25 and 2.5mg/m(3) exposure groups contained nanofibers (> 60% for 0.5mg/m(3)). A nonspecific inflammatory response was also noted in the nasal passages. The no-observed-adverse-effect level for VGCF-H nanofibers was considered to be 0.54mg/m(3) (4.9 fibers/cc) for male and female rats, based on the minimal inflammation in the terminal bronchiole and alveolar duct areas of the lungs at 2.5mg/m(3) exposures. It is noteworthy that the histopathology observations at the 2.5mg/m(3) exposure level did not correlate with the CP or BALF data at that exposure concentration. In addition, the results with CNF are compared with published findings of 90-day inhalation studies in rats with carbon nanotubes, and hypotheses are presented for potency differences based on CNT physicochemical characteristics. Finally, the (lack of) relevance of CNF for the high aspect ratio nanomaterials/fiber paradigm is discussed.     

Lung Response to Ultrafine Kevlar Aramind Synthetic Fibrills Following 2-Year Inhalation Exposure in Rats

Lung Response to Ultrafine Kevlar Aramid Synthetic Fibrils following2-Year Inhalation Exposure in Rats. LEE K. P., KELLY D.P. O'NEALF. O., STADLER, J. C., AND KENNEDY G. L., JR (1988). Fundam.Appl. Toxicol. 11, 1-20. Four groups of 100 male and 100 femalerats were exposed to ultrafine Kevlar fibrils at concentrationsof 0, 2.5,25, and 100 fibrils/cc for 6 hr/day, 5 days/week for2 years. One group was exposed to 400 fibrils/cc for 1 yearand allowed to recover for 1 year. At 2.5 fibrils/cc, the lungshad normal alveolar architecture with a few dust-laden macrophages(dust cell response) in the alveolar airspaces. At 25 fibrils/cc,the lungs showed a dust cell response, slight Type II pneumocytehyperplasia, alveolar bronchiolariation, and a negligible amountof collagenized fibrosis in the alveolar duct region. At 100fibrils/cc, the same pulmonary responses were seen as at 25fibrilsol;cc. In addition, cystic keratinizing squa- mous cellcarcinoma (CKSCC) was found in 4 female rats, but not in malerats. Female rats had more prominent foamy alveolar macrophages,holesterol granulomas, and alveolar bronchio-larization. Thesepulmonary lesions were related to the development of CKSCC.The lung tumors were derived from metaplastic squamous cellsin areas of alveolar bronchiolarization. At 400 fibrils/cc following1 year of recovery, the lung dust content, average fiber length,and the pulmonary lesions were markedly reduced, but slightcentriacinar emphysema and minimal collagenized fibrosis werefound in the alveolar duct region. One male and 6 female ratsdeveloped CKSCC. The lung tumors were a unique type of experimentallyinduced tumors in the rats and have not been seen as spontaneoustumors in man or animals. Therefore, the relevance of this typeof lung tumor to the human situation is minimal.     

Pattern of deposition of stainless steel welding fume particles inhaled into the respiratory systems of Sprague-Dawley rats exposed to a novel welding fume generating system

In order to investigate occupational diseases related to welding fume exposure, such as nasal septum perforation, pneumoconiosis and manganese intoxication, we built a welding fume exposure system that included a welding fume generator, exposure chamber and fume collector. The fume concentrations in the exposure chamber were monitored every 15 min during a 2-h exposure. Fume (mg/m(3)) concentrations of major metals, including Fe, Mn, Cr, and Ni were found to be consistently maintained. An acute inhalation toxicity study was conducted by exposing male Sprague-Dawley rats to the welding fumes generated in this apparatus by stainless steel arc welding. The rats were exposed in the inhalation chamber to a welding fume with a concentration of 62 mg/m(3) total suspended particulates for 4 h. Animals were sacrificed at 4 h and at 1, 3, 7, 10, and 14 days after exposure. Histopathological examinations were conducted on the animals' upper respiratory tracts, including the nasal pathway and the conducting airway, and on the gas exchange region including the alveolar ducts, alveolar sacs, and alveoli. Diameters of fume particles varied from 0.02 to 0.81 microm and were distributed log normally, with a mean diameter of 0.1 microm and geometric standard deviation of 1.42. Rats exposed to the welding fume for 4 h did not show any significant respiratory system toxicity. The mean particle diameter of 0.1 microm resulted in little adsorption of the welding fume particles in the upper respiratory tract. Particle adsorption took place principally in the lower respiratory tracts, including bronchioles, alveolar ducts, alveolar sacs, and alveoli.     

Chronic pulmonary effects in guinea pigs from prolonged inhalation of cotton dust

Inhalation of cotton dust has been associated with development of byssinosis. An animal model has been described recently in which guinea pigs exposed to cotton dust for a 6-week period demonstrated acute respiratory reactions consisting of increased breathing frequency, reduced tidal volume, and airflow fluctuations most prominent on the first day of exposure following a period without exposure, often referred to as a "Monday" response (Ellakkani et al., 1984). The current study examined the effects of cotton dust inhalation for 52 weeks in order to evaluate the animal model for ability to demonstrate more chronic effects of cotton dust exposure. Twenty guinea pigs were exposed to 21 mg/m3 cotton dust for 6 hr/day, 5 days/week, for 52 weeks. Twenty control animals received sham exposure. Parameters used to indicate chronic effects included respiratory measurements, weight gain, lung volume and weight, and histopathological evaluation. Respiratory measurements were taken while animals were breathing ambient air and also while breathing a mixture of 10% CO2, 20% O2, and 70% N2. Pulmonary effects were noted to change during the 12 months of exposure. For the first 3 months experimental animals displayed an increase in breathing frequency and a decrease in breathing volume measured as whole-body plethysmographic pressure. These effects were pronounced on the "Monday" of each week. During Months 3-6, reactions occurred on each day of exposure, although Monday responses were most severe. After 6 months, respiratory reactions were pronounced daily. Other indications of a chronic effect of exposure were increased lung volume, measured by water displacement, 15.0 +/- 3.3 ml (mean +/- SD) for the exposed group, compared with 9.8 +/- 2.0 ml for the controls; increased lung weight 9.4 +/- 1.5 g vs 7.0 +/- 0.8 g; and bronchiolar epithelial hyperplasia and hyperplasia of alveolar type II cells. Additionally, a histomorphometric study of the lungs performed by others (Coulombe et al., 1986) detected changes in the peripheral conducting airways, including increased thickness of bronchiolar epithelium and increased thickness of septa at the alveolar level, denoting chronic exposure. Taken together, these results indicated chronic respiratory effects in guinea pigs as a result of 52 weeks of continued exposure to cotton dust. The parallel in development of symptoms in guinea pigs and in humans exposed to cotton dust indicates that the guinea pig is a suitable model for byssinosis.     

A review of the fate of inhaled α-quartz in the lungs of rats

The distribution of dust particles within the lungs and their excretion are highly associated with their pulmonary toxicity. Literature was reviewed to discern pulmonary translocation pathways for inhaled α-quartz compared to those for inhaled TiO₂. Accordingly, it was hypothesized α-quartz particles in the alveoli were phagocytized by alveolar macrophages but silica-containing macrophages remained in the alveoli for longer time in contrast to the rapid elimination from the alveoli seen for TiO₂-containing macrophages. In addition, it was presumed that free silica particles are translocated in the interstitium, possibly through the cytoplasm of Type I epithelial cells, as observed with TiO₂. Free silica particles are presumed to be phagocytized by interstitial macrophages soon after the particles penetrate the interstitium; these dust cells are then translocated to the ciliated airway regions in the lumen through bronchus-associated lymphoid tissue (BALT). The pulmonary retention half-time of dust particles in rats exposed to α-quartz is several times longer than that of rats exposed to TiO₂, as long as the lung dust burden is ≈ 3?mg. The reduced pulmonary particle clearance ability in rats exposed to α-quartz aerosol is presumably attributed to the long-term retention of dust cells both in the alveoli and in the interstitium; this retention may be caused by the reduced chemotactic abilities of α-quartz-containing dust cells. However, the accumulation of α-quartz-containing dust cells in the lungs is not associated with the occurrence of pulmonary inflammation.     

Pneumotoxicity of butylated hydroxytoluene applied dermally to CD-1 mice

Pneumotoxicity of butylated hydroxytoluene (BHT) applied to the skin of CD-1 mice was investigated and compared with that of butylated hydroxyanisole (BHA). To 6 groups of 10 male mice and 10 female mice 0.1 ml of dimethylsulfoxide (DMSO) solutions containing 0, 5, 10, 20, or 30 mg of BHT or 30 mg of BHA were topically applied 3 times weekly for 4 weeks. Between the 4th and 8th day BHT-treated mice exhibited respiratory distress with subsequent dose-dependent mortality. At autopsy dead animals were found to have congestion and enlargement of the lung with oozing of froth from the trachea. Histologically, collapse of the alveoli and dilatation of the alveolar ducts associated with degeneration or necrosis of type I alveolar epithelial cells were evident. The lethal effect of BHT was more manifest in female than in male mice. In contrast, none of the BHA-treated or control mice showed lung abnormalities. In another series of experiments to study the species difference of BHT pneumotoxicity, F-344 rats of both sexes and male Syrian golden hamsters were exposed to BHT by dermal application 3 times weekly for 4 weeks at a dose of 240 mg in rats or 480 mg in hamsters. However, no pulmonary alterations were observed in either species.     

Toxicity of gallium oxide particles following a 4-week inhalation exposure

To evaluate the inhalation toxicity of Ga2O3, F344 rats were exposed nose-only to 0.2 micron Ga2O3 particles 2 h/day, 5 days/week for 4 weeks. The exposure concentration was 23 +/- 5 mg/m3 (mean +/- SD) resulting in lung burdens of 0.8 +/- 0.1 mg Ga2O3/lung (mean +/- SE) at the end of 4 weeks of exposure. Analysis of bronchoalveolar lavage fluid of exposed rats showed marked responses. One day after termination of exposure, lactate dehydrogenase was increased 6-fold, and the lysosomal enzyme, beta-glucuronidase, was increased 38-fold in rats exposed to Ga2O3 compared to sham exposed controls. Alkaline phosphatase, glutathione reductase, glutathione peroxidase, white blood cells, acid proteinase, and protein were increased 3- to 4-fold. Responses remained elevated 6 and 12 months after exposure. Lung clearance of radiolabeled tracer particles was evaluated 4 days and 6 months after the end of 4 weeks of Ga2O3 exposures. Long-term clearance half-times were significantly longer (3-4 fold, P less than 0.01) in rats exposed to Ga2O3 than in the sham-exposed control rats at both 4 days and 6 months, indicating persistent impairment of particle clearance. Histopathological lesions consisted primarily of alveolar proteinosis 1 day after 4 weeks exposure, progressing in severity to large focal lesions of alveolar histiocytosis and septal fibrosis 6 and 12 months after exposure. Inhaled Ga2O3 produced cytotoxic, inflammatory, and fibrogenic responses of comparable or greater magnitude than those seen after similar exposures of rats to inhaled quartz particles in other studies. These data show that inhaled Ga2O3 particles produce considerable toxicity and exposures in the work place should be limited.     

Pulmonary toxicity of polymeric hexamethylene diisocyanate aerosols in mice

The acute pulmonary response of male C57BL/6 mice exposed to respirable polymeric hexamethylene diisocyanate biuret trimer aerosol (HDI-BT), a component of polyurethane spray paints, was examined. Mice were exposed to concentrations of 1 and 10 mg/m(3) HDI-BT for 5 h and were evaluated 6, 18, 42, 90, 186, and 378 h after the end of exposure. Mice exposed to 1 or 10 mg/m(3) HDI-BT exhibited dose-dependent lung function impairment, edema, neutrophilic inflammation, cellular proliferation, and histologic lesions in terminal bronchioles and alveolar ducts. Impairment of pulmonary function, indicated by decreased frequency and increased enhanced pause (Penh), was maximal immediately after exposure and progressively recovered at later time points. Lung weight and lavage fluid protein content peaked at 6 and 18 h after exposure, respectively. Total cells and macrophages recovered in lavage fluid peaked 90 h after exposure. Neutrophils recovered in lavage fluid peaked between 18 and 42 h after exposure. Proliferative lesions, as identified histologically and by bromodeoxyuridine incorporation, were maximal 90 h after exposure. In contrast, no inflammatory cell influx, protein leakage, or lung pathology were observed in mice exposed to 360 ppb HDI monomer vapor. This model will be useful for investigating molecular mechanisms by which HDI-BT causes lung injury, which is known to occur in humans exposed occupationally to this pulmonary toxicant.     

Subchronic inhalation toxicity of amorphous silicas and quartz dust in rats.

The inhalation toxicity of three amorphous silicas (Aerosil 200, Aerosil R 974 and Sipernat 22S) was compared with that of quartz dust. Rats were exposed to 1, 6 or 30 mg Aerosil 200/m3, 30 mg Aerosil R 974/m3, 30 mg Sipernat 22S/m3 or 60 mg quartz/m3 for 6 hr/day, 5 days/wk for 13 wk. Some rats were killed at the end of the exposure period and some were killed 13, 26, 39 or 52 wk after the end of exposure. Clinical signs, body weight, haematology, biochemistry, urinalyses, organ weights, retention of test material in the lungs and regional lymph nodes, collagen content of the lungs, and gross and microscopic pathology were determined in order to disclose possible adverse effects and to study the reversibility, stability or progression of the effects. All test materials induced increases in lung weight, and pulmonary lesions such as accumulation of alveolar macrophages, inflammation, alveolar bronchiolization and fibrosis. In addition, rats exposed to Aerosil 200, Aerosil R 974 or quartz developed granulomatous lesions. Silicosis was observed only in quartz-exposed animals. At the end of the exposure period, Aerosil 200 and quartz had induced the most severe changes. Quartz dust was hardly cleared from the lungs and the changes in the lungs progressed during the post-treatment period, and eventually resulted in lesions resembling silicotic nodules and in one squamous cell carcinoma. Although Aerosil 200 was very quickly cleared from the lungs and regional lymph nodes, the changes in these organs were only partly reversed during the post-exposure period in rats exposed to 30 mg/m3. Aerosil R 974 and the lower levels of Aerosil 200 resulted in less severe, and mostly reversible, changes. The slightest changes were found after exposure to Sipernat 22S, notwithstanding the persistence of this silica in the lungs during the major part of the post-treatment period. The results of this study revealed that only quartz induced progressive lesions in the lungs resembling silicotic nodules. Of the amorphous silicas examined Aerosil 200 induced the most severe changes in the lungs, which only partly recovered, whereas Sipernat 22S induced the least severe, completely reversible lung changes.     

Inhalation toxicity and carcinogenicity studies of cobalt sulfate.

Cobalt sulfate is a water-soluble cobalt salt with a variety of industrial and agricultural uses. Several cobalt compounds have induced sarcomas at injection sites in animals, and reports have suggested that exposure to cobalt-containing materials may cause lung cancer in humans. The present studies were done because no adequate rodent carcinogenicity studies had been performed with a soluble cobalt salt using a route relevant to occupational exposures. Groups of 50 male and 50 female F344/N rats and B6C3F1 mice were exposed to aerosols containing 0, 0.3, 1.0, or 3.0 mg/m3 cobalt sulfate hexahydrate, 6 h/day, 5 days/week, for 104 weeks. Survival and body weights of exposed rats and mice were generally unaffected by the exposures. In rats, proteinosis, alveolar epithelial metaplasia, granulomatous alveolar inflammation, and interstitial fibrosis were observed in the lung in all exposed groups. Nonneoplastic lesions of the nose and larynx were also attributed to exposure to all concentrations of cobalt sulfate. In 3.0 mg/m3 male rats and in female rats exposed to 1.0 or 3.0 mg/m3, the incidences of alveolar/bronchiolar neoplasms were increased over those in the control groups. Lung tumors occurred with significant positive trends in both sexes. The incidences of adrenal pheochromocytoma in 1.0 mg/m3 male rats and in 3.0 mg/m3 female rats were increased. Nonneoplastic lesions of the respiratory tract were less severe in mice than in rats. In mice, alveolar/bronchiolar neoplasms in 3.0 mg/m3 males and females were greater than those in the controls, and lung tumors occurred with significantly positive trends. Male mice had liver lesions consistent with a Helicobacter hepaticus infection. Incidences of liver hemangiosarcomas were increased in exposed groups of male mice; however, because of the infection, no conclusion could be reached concerning an association between liver hemangiosarcomas and cobalt sulfate. In summary, exposure to cobalt sulfate by inhalation resulted in increased incidence of alveolar/bronchiolar neoplasms and a spectrum of inflammatory, fibrotic, and proliferative lesions in the respiratory tracts of male and female rats and mice. Adrenal pheochromocytomas were increased in female rats, and possibly in male rats.