Mark A. Hartsky

Development of a short-term inhalation bioassay to assess pulmonary toxicity of inhaled particles: Comparisons of pulmonary responses to carbonyl iron and silica

This paper describes a short-term inhalation bioassay for evaluating the lung toxicity of inhaled particulate materials. To validate the method, rats were exposed for 6 hr or 3 days to various concentrations of either aerosolized alpha-quartz silica or carbonyl iron particles. Cells and fluids from groups of sham- and dust-exposed animals were recovered by bronchoalveolar lavage (BAL). Alkaline phosphatase, lactate dehydrogenase (LDH), and protein values were measured in BAL fluids at several time points postexposure. Cells were identified, counted, and evaluated for viability. Pulmonary macrophages (PM) were cultured and studied for morphology, chemotaxis, and phagocytosis by scanning electron microscopy. The lungs of additional exposed animals were processed for histopathology and transmission electron microscopy. Brief exposures to silica elicited a sustained granulocytic inflammatory response (primarily neutrophils) with concomitant increases in alkaline phosphatase, LDH, and protein in the lavage fluids (p less than 0.05). In addition, PM functional capacity was depressed (p less than 0.05) and histopathologic lesions were observed within 1 month after exposure. In contrast, 6-hr or 3-day exposures to CI produced no cellular, cytotoxic, or alveolar/capillary membrane permeability changes at any time postexposure. PM function was either enhanced or unchanged from controls. These data demonstrate that short-term, high-dose inhalation exposures of silica produce effects similar to those previously observed using intratracheal instillation or chronic inhalation models, and lend support to this method as a reliable short-term bioassay for evaluating the pulmonary toxicity and mechanisms associated with exposures to new and untested materials.

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)

Attenuation of perfluoropolymer fume pulmonary toxicity: Effect of filters, combustion method, and aerosol age

Thermal decomposition products of some perfluorinated polymers are toxic to experimental animals in small-scale combustion toxicity tests; the toxicity is dependent upon the heating procedure, combustion temperature, and other experimental conditions. In the current studies we investigated the time course of fume generation and exposure on pulmonary effects in rats following a 30-min exposure to perfluoropolymer decomposition products (i.e., fume concentration = 0.2 mg/m3 of tetrafluoroethylene/hexafluoropropylene copolymer (FEP)) pyrolyzed with either static or dynamic airflows. In the first set of experiments, five different groups of rats were exposed to FEP fumes in a static combustion toxicity test system. Three groups were exposed to unfiltered FEP fumes during 0- to 15-, 15- to 30-, and 0- to 30-min intervals, respectively, and one to a filtered (particle-free) atmosphere of combusted FEP for 30 min. Sham-exposed rats constituted the control group. Immediately after exposure, the rats were sacrificed and their lungs weighed and lavaged or perfused to assess indices of cytotoxicity. Our results showed that lung weights, markers of inflammation, and pulmonary hemorrhage and alkaline phosphatase, beta-glucuronidase, lactate dehydrogenase, and protein levels in bronchoalveolar lavage fluids were significantly elevated in all unfiltered FEP-exposed groups compared to those in either the rates exposed through filters or controls (P less than 0.01). In a second set of experiments using a dynamic pyrolysis toxicity test system, rats were exposed for 30 min to FEP-pyrolyzed fumes which were either freshly generated or aged for 1 or 5 min prior to delivery to the animals breathing zone. Subsequently, lung cytotoxicity parameters were measured. Rats exposed directly to the fresh fumes demonstrated toxic effects consistent with those described above (P less than 0.01), but the pulmonary toxicity of aged (i.e., 1 or 5 min delay) FEP fumes was diminished in a time-dependent manner, suggesting that the toxicant was unstable. Histopathological studies correlated with biochemical results and revealed that inhalation of unfiltered or freshly generated FEP fumes produced a severe lung injury characterized by the development of alveolar and interstitial edema, intraalveolar hemorrhage, congestion, and fibrin deposition. Electron microscopy studies demonstrated severe damage to terminal bronchiolar cells and detachment of Type I epithelial and endothelial cells in pulmonary regions. The severity of pathology observed in lungs of rats exposed to 1-min aged fumes was intermediate between unfiltered/unaltered fume-exposed animals and sham controls. The results of these studies demonstrate that the lung toxicity of perfluoropolymer fumes is associated with the aerosol phase generated in perfluoropolymer pyrolysis.

TIME COURSE OF QUARTZ AND TiO2 PARTICLE-INDUCED PULMONARY INFLAMMATION AND NEUTROPHIL APOPTOTIC RESPONSES IN RATS

Apoptosis, or programmed cell death, has been reported to play an important role in the resolution of pulmonary inflammation. This study was undertaken to investigate the role of apoptosis in resolving particle-induced lung inflammatory responses in exposed rats, using a dose-response / time course experimental design. Groups of rats were exposed via intratracheal instillation to 0, 0.5, 1, 5, 10, or 50 mg/kg body weight of quartz (i.e., crystalline silica) particles or to 0, 0.5, 1, 5, 10, 20, or 50 mg/kg of pigment-grade titanium dioxide (TiO 2) particles and evaluated for lung inflammation parameters and evidence of apoptosis of inflammatory cells at 24, 48, 72, or 168 hours post exposure. At each post exposure evaluation period, bronchoalveolar lavage (BAL)-recovered cells from control and particle-exposed rats were assessed for apoptosis using 4 different techniques. The results in silica-exposed rats demonstrated a significant dose-related increase in inflammation concomitant with apoptosis of pulmonary inflammatory cells at 24 to 48 hours post exposure. At later postexposure time points, both the silica-induced inflammatory responses and apoptotic levels of inflammatory cells at higher doses (i.e., ≥ 5 mg/kg) were reduced but persisted through 1 week. TUNEL (TdT-mediated dUTP nick end-labeling) assay studies confirmed that the vast majority of apoptotic cells were neutrophils. In contrast, titanium dioxide particle exposures produced transient pulmonary inflammation but only small measurable and nonsignificant apoptotic responses at higher exposure concentrations. These results suggest that the sustained lung inflammatory response in rats exposed to ≥ 5 mg/kg silica may be related to the ineffectiveness of the normal apoptotic mechanisms associated with resolution of inflammation. However, because quartz particles are known to be cytotoxic to alveolar macrophages and other lung cells, normal apoptotic mechanisms may have limited utility for resolving particle-induced inflammation, particularly because silica may not be representative of other particle-types. Alternatively, it seems unlikely that apoptosis served to promote silica-induced lung inflammatory responses because the initial increase of apoptosis in inflammatory cells was subsequently correlated with a reduction of the pulmonary inflammatory response in silica-exposed rats. The findings from this in vivo study demonstrate that the neutrophil, and not the alveolar macrophage, is the primary inflammatory cell-type that undergoes apoptosis in response to particles. Furthermore, at doses causing similar degrees of inflammation at 24 hours post exposure, the magnitude of apoptosis induced by silica is significantly larger than that induced by TiO 2, indicating that there are potency differences in lung inflammation as well as apoptotic responses among different particle-types.

Species Comparisons of Proximal Alveolar Deposition Patterns of Inhaled Particulates

Previous studies have shown that inhaled particles and fibers that are small enough to pass through the conducting airways deposit preferentially at alveolar duct bifurcations in the distal lungs of exposed rats. Because it is well documented that anatomic and physiologic differences exist among common experimental animals that may influence deposition patterns, we compared inhaled particle deposition patterns in alveolar regions of four rodent species. Proximal alveolar regions of hamsters and guinea pigs contain rudimentary respiratory bronchioles, whereas in rats and mice, terminal bronchioles lead directly into alveolar ducts. Groups of animals from one strain each of rats, mice, hamsters, and guinea pigs were exposed to aerosols of carbonyl iron (CI) particles for 1 h at design concentrations of 100 mg/m3. Immediately after exposure, the lungs of sham- and CI-exposed animals were perfusion fixed through the vasculature. Subsequently, lung tissues from exposed animals was analyzed for iron concentration; data indicated that total lung deposition of iron particles was highest in mice and hamsters. In addition, scanning electron microscopy of dissected lung tissue revealed that particle deposition patterns in the proximal regions of the distal lung were similar for all species, although greater numbers of CI particles per bifurcation were deposited in rats and mice compared to hamsters (p less than 0.05) and greater numbers were deposited in hamsters compared to guinea pigs (p less than 0.05). The data suggest that the presence of undeveloped respiratory bronchioles in the lungs of hamsters and guinea pigs has little influence on distal lung particle deposition patterns. It remains to be determined whether inhaled particles are deposited at similar sites in the lungs of species with well-developed respiratory bronchioles such as cats, nonhuman primates, and humans.

Subchronic inhalation of high concentrations of low toxicity, low solubility participates produces sustained pulmonary inflammation and cellular proliferation

Long-term inhalation exposures to high dust burdens can produce tumors or proliferative keratin cysts in the lungs of exposed rats. We hypothesized that dust burdens which overwhelm lung clearance mechanisms are associated with sustained cellular proliferation responses and pulmonary inflammation. Male rats were exposed to titanium dioxide (TiO2) or carbonyl iron (CI) particles for 4 weeks at concentrations of 5, 50 and 250 mg/m3. Following completion of exposure, the lungs of sham and dust-exposed animals were lavaged or assessed for cell proliferation or particle clearance immediately after, as well as 1 week, 1, 3 and 6 months postexposure. Exposures to TiO2 or CI at 250 mg/m3 produced persistent pulmonary inflammatory responses and increased BrdU labeling of terminal airway and pulmonary parenchymal cells. The results of this study clearly demonstrate that exposure to excessive dust concentrations of two low toxicity, low solubility particle-types produced sustained pulmonary inflammation, enhanced pulmonary cell labeling, impairment of particle clearance, and the development of pulmonary lesions.

Pulmonary effects in rats inhaling size-separated chrysotile asbestos fibres or p-aramid fibrils: differences in cellular proliferative responses

This study was designed to compare the pulmonary cellular proliferative effects of inhaled, size-separated preparations of chrysotile asbestos fibres with similar aerosol fibre concentrations of para-aramid fibrils. Following fibre preparation, rats were exposed for 2 weeks to aerosols of p-aramid fibrils or chrysotile asbestos fibres at design fibre concentrations of 750 and 400 f/cc. Two week exposures to p-aramid fibrils produced transient pulmonary inflammatory and cell labeling responses in terminal bronchiolar and subpleural regions. Similar to p-aramid, exposure to chrysotile produced a transient increase in neutrophils. In contrast, however, substantial increases compared to controls in pulmonary cell labeling indices were measured on terminal bronchiolar, parenchymal, subpleural, and mesothelial surfaces immediately after exposure, and some increases persisted for 3 months postexposure. In complementary studies we demonstrated that p-aramid is biodegradable in the lungs of exposed rats; in contrast, the clearance of long chrysotile fibres was slow or insignificant, resulting in a pulmonary retention of long chrysotile asbestos fibres. The dimensional changes of asbestos fibres as well as the pulmonary cell labeling data indicate that chrysotile asbestos fibres may produce greater long-term pulmonary effects when compared to inhaled para-aramid fibrils.

Four-week inhalation toxicity study with ludox colloidal silica in rats : pulmonary cellular responses

This study was designed to complement a traditional subchronic inhalation toxicity study with Ludox colloidal silica. CD rats were exposed nose-only for 2 or 4 weeks at concentrations of 0, 10, 50, and 150 mg/m3 Ludox (dried SiO2). Additional groups of rats exposed for 4 weeks were given a 3-month recovery period. Following exposure and/or recovery, fluids and cells were recovered from the lungs by bronchoalveolar lavage (BAL) and measured for cellular and biochemical parameters. Additional groups of animals were processed for cell labeling studies or lung deposition studies. Inhaled doses of Ludox colloidal silica were measured after 4-week exposures and were found to be 489 micrograms/lung (10 mg/m3 group), 2418 micrograms/lung (50 mg/m3), and 7378 micrograms/lung (150 mg/m3), respectively. Results showed that exposures to 150 mg/m3 Ludox for 2 or 4 weeks produced pulmonary inflammation along with increases in BAL protein, LDH, and alkaline phosphatase values (p less than 0.05) and reduced macrophage phagocytosis. Inflammatory responses, evidenced by increased numbers of neutrophils, were also measured in the lungs of the 50 mg/m3 group following 2 and/or 4 weeks of exposure. Most biochemical parameters for all groups returned to control values following a 3-month recovery period. Autoradiographic studies demonstrated that the labeling indices of terminal bronchiolar and lung parenchymal cells were generally increased in the 50 and 150 mg/m3 groups after 2 and 4 weeks of exposure but, with one exception, returned to normal levels following a 3-month postexposure period. No significant alterations in any measured parameters were detected in rats exposed to 10 mg/m3 Ludox at any time postexposure. The determination of a no-observable-effect level (NOEL) of 10 mg/m3 was consistent with results obtained by conventional toxicology methods and affirms the utility of these biochemical, cellular, and autoradiographic techniques for providing a predictive screen to assess the toxicity of inhaled particles.

Complement facilitates macrophage phagocytosis of inhaled iron particles but has little effect in mediating silica-induced lung inflammatory and clearance responses

Complement-mediated mechanisms are known to play a role in pulmonary inflammation and clearance responses to some types of inhaled particles. The present studies were undertaken to investigate the role of complement in mediating pulmonary inflammation and/or phagocytosis as a function of particle clearance in rats exposed to silica or carbonyl iron (CI) particles. Both particle types were shown to be weak activators of serum complement in vitro. In these studies, normal and complement-depressed (CVF-treated) rats were exposed to aerosols of CI or silica particles for 6 hr at 100 mg/m3. Following exposure, alveolar fluids and cells from sham and dust-exposed animals were recovered by bronchoalveolar lavage (BAL) at several time periods postexposure and measured for a variety of biochemical and cellular indices. In addition, pulmonary macrophages were cultured and studied for morphology and phagocytosis. Our results showed that CI exposure did not produce cellular or biochemical indices of pulmonary inflammation, either in normal or complement-depleted rats. However, fewer phagocytic macrophages were recovered from the lungs of CVF-treated, CI-exposed rats than from normal exposed animals. In contrast, silica inhalation produced a sustained PMN inflammatory response in the lungs of exposed rats, measured up through 1 month postexposure, along with significant increases in BAL fluid levels of LDH, protein, and alkaline phosphatase (P less than 0.05) and deficits in pulmonary macrophage phagocytic functions. Cobra venom factor (CVF) treatment prior to exposure in rats had no significant effect upon the silica-induced parameters, suggesting that complement may not play an important role in the acute pulmonary response to silica. The results indicate that complement may play a role in mediating CI-related macrophage clearance responses but has little effect upon sustained silica-induced pulmonary inflammatory parameters.

Acute Pulmonary Effects of Inhaled Wollastonite Fibers are Dependent on Fiber Dimensions and Aerosol Concentrations

Occupational exposure to asbestos fibers has been associated with the development of pulmonary fibrosis (i.e., asbestosis), bronchogenic carcinoma and mesothelioma. Therefore, the commercial use of asbestos is likely to be curtailed or limited in the near future and mineral fiber substitutes are currently being promoted to fill the void. Wollastonite fibers are natural acicular calcium silicate minerals which have been proposed as alternatives for asbestos in applications such as brake linings, wallboard and insulation materials. Wollastonite fiber diameters are generally in the 1–10 µm range with an average diameter of 3.5 µm (Vu, 1988).