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The relevance of particle-overload related lung tumors in rats for human risk assessment following chronic inhalation exposures to poorly soluble particulates (PSP) has been a controversial issue for more than three decades. In 1998, an ILSI (International Life Sciences) Working Group of health scientists was convened to address this issue of applicability of experimental study findings of lung neoplasms in rats for lifetime-exposed production workers to PSPs. A full consensus view was not reached by the Workshop participants, although it was generally acknowledged that the findings of lung tumors in rats following chronic inhalation, particle-overload PSP exposures occurred only in rats and no other tested species; and that there was an absence of lung cancers in PSP-exposed production workers. Since the publication of the ILSI Workshop report in 2000, there have been important new data published on the human relevance issue. A thorough and comprehensive review of the health effects literature on poorly soluble particles/lung overload was undertaken and published by an ECETOC (European Centre for Ecotoxicology and Toxicology of Chemicals) Task Force in 2013. One of the significant conclusions derived from that technical report was that the rat is unique amongst all species in developing lung tumors under chronic inhalation overload exposures to PSPs. Accordingly, the objective of this review is to provide important insights on the fundamental differences in pulmonary responses between experimentally-exposed rats, other experimental species and occupationally-exposed humans. Briefly, five central factors are described by the following issues. Focusing on these five interrelated/convergent factors clearly demonstrate an inappropriateness in concluding that the findings of lung tumors in rats exposed chronically to high concentrations of PSPs are accurate representations of the risks of lung cancer in PSP-exposed production workers. The most plausible conclusion that can be reached is that results from chronic particle-overload inhalation studies with PSPs in rats have no relevance for determining lung cancer risks in production workers exposed for a working lifetime to these poorly soluble particulate-types., (Copyright © 2016. Published by Elsevier Ireland Ltd.)

Six pigment-grade (pg) or ultrafine (uf)/nanoscale (anatase and/or rutile) titanium dioxide (TiO2) particulates were evaluated for in vivo genotoxicity (OECD 474 Guidelines) in male and female rats by two different laboratories. All test materials were robustly characterized. The BET surface areas of the pg and uf samples ranged from 7 to 17 m(2)/g and 50 to 82 m(2)/g respectively. The materials were assessed for induction of micronuclei and toxicity in bone marrow by analyzing peripheral blood reticulocytes (RETs) by flow cytometry. Single oral gavage doses of 500, 1000 or 2000 mg/kg body weight (bw) of each material were implemented with concurrent negative (water) and positive controls (cyclophosphamide). Approximately 48 and 72 h after exposure, blood samples were collected and 20,000 RETs per animal were analyzed. For each of the six tests, there were no biologically or toxicologically relevant increases in the micronucleated RET frequency in any TiO2 exposed group at either time point at any dose level. In addition, there were a lack of biologically relevant decreases in %RETs among total erythrocytes. All six TiO2 test substances were negative for in vivo genotoxicity effects; however, it is noted that the exposure to target tissues was likely negligible. One pigment grade and one ultrafine material each were evaluated for potential systemic exposure/uptake from the gastrointestinal tract by analysis of TiO2 into blood and liver. No significant increases in TiO2 over controls were measured in blood (48 or 72 h) or liver (72 h) following exposures to 2000 mg/kg bw TiO2. These data indicate that there was no absorption of the test material from the gastrointestinal tract into the blood circulation and the lack of genotoxic effects is therefore attributed to a lack of exposure due to the inability of the test material to migrate from the gastrointestinal tract into the blood and then into target tissues., (Copyright © 2015 Elsevier Inc. All rights reserved.)

Six different commercial forms and sizes of titanium dioxide particles were tested in separate developmental toxicity assays. The three pigment-grade (pg) or 3 ultrafine (uf)/nanoscale (anatase and/or rutile) titanium dioxide (TiO2) particle-types were evaluated for potential maternal and developmental toxicity in pregnant rats by two different laboratories. All studies were conducted according to OECD Guideline 414 (Prenatal Developmental Toxicity Study). In addition, all test materials were robustly characterized. The BET surface areas of the pg and uf samples ranged from 7 to 17 m(2)/g and 50-82 m(2)/g respectively (see Table 1). The test substances were formulated in sterile water. In all of the studies, the formulations were administered by oral gavage to time-mated rats daily beginning around the time of implantation and continuing until the day prior to expected parturition. In 3 of the studies (uf-1, uf-3, & pg-1), the formulations were administered to Crl:CD(SD) rats beginning on gestation day (GD) 6 through GD 20. In 3 additional studies (uf-2, and pg-2, pg-3 TiO2 particles), the formulations were administered to Wistar rats beginning on GD 5 through 19. The dose levels used in all studies were 0, 100, 300, or 1000 mg/kg/day; control group animals were administered the vehicle. During the in-life portions of the studies, body weights, food consumption, and clinical observations before and after dosing were collected on a daily basis. All dams were euthanized just prior to expected parturition (GD 21 for Crl:CD(SD) rats and GD 20 for Wistar rats). The gross necropsies included an examination and description of uterine contents including counts of corpora lutea, implantation sites, resorptions, and live and dead fetuses. All live fetuses were sexed, weighed, and examined externally and euthanized. Following euthanasia, fresh visceral and head examinations were performed on selected fetuses. The fetal carcasses were then processed and examined for skeletal alterations. There was no evidence of maternal or developmental toxicity at any dose level tested in any of the six studies. Based on these results, the no-observed-adverse-effect level (NOAEL) for titanium dioxide was 1000 mg/kg/day, the highest administered dose, in both the Sprague-Dawley (Crl:CD(SD) and Wistar rat strains., (Copyright © 2015 Elsevier Inc. All rights reserved.)

These studies elucidated mechanisms of inhaled p-aramid respirable fiber-shaped particulates (RFP) biodegradation in the lungs of exposed rats and hamsters. We postulate that lung fluids coat/activate inhaled p-aramid RFP which deposits in the lung and promote enzymatic attack and consequent shortening. p-Aramid or cellulose (biopersistent control) RFP were instilled into the lungs of rats and the lungs digested 24 h later using two different (KOH or enzymatic) digestion techniques. In vivo, the enzyme but not the KOH solution produced shortening of p-aramid but not cellulose RFP recovered from the lungs. For in vitro studies, the two RFP-types were incubated with BAL fluids and underwent simulated digestions; also rat lung epithelial cells, macrophages or co-cultures were incubated with p-aramid and digested at 1, 24, or 168 h postexposure. The results of in vitro acellular studies demonstrated that only p-aramid RFP incubated in BAL fluids and digested by the enzyme method were shortened. In vitro cellular studies demonstrated a shortening of p-aramid RFP in macrophages and co-cultures but not in lung epithelial cells at 24 h and 1 week postexposure. These results demonstrate that lung fluids coat and catalyze the p-aramid RFP as a prelude for shortening and describe a likely mechanism for the biodegradability of inhaled p-aramid RFP in the lungs of exposed animals.

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.

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.

The Workshop on Approaches to Evaluating the Toxicity and Carcinogenicity of Man-Made Fibers (MMF) was held in Durham, North Carolina, on November 11-13, 1991. The goal of the workshop was to reach a consensus, or to determine the extent to which a consensus existed, in two areas. Participants were asked to identify scientifically sound approaches for evaluating the toxicity and carcinogenicity of man-made fibers based on today's science and to determine research appropriate for study during the next 5 years that can provide an improved scientific basis for future revisions of approaches used to evaluate man-made fiber toxicity and carcinogenicity. During the first day, a series of "state of knowledge" presentations were made to provide all participants with a common data base from which to interact and discuss scientific issues. The workshop participants were assigned to one of four discussion groups, which met separately in three half-day sessions following the first day of presentations. All groups discussed the same topics: exposure assessment, hazard identification, and dose-response information needed to integrate to characterize risk in the first session; approaches to obtaining the needed information in the second session; and recommended approaches and guidelines for evaluating the toxicity and carcinogenicity of MMF and research needs in the third session. The workshop participants reconvened as a whole after each discussion session, and one member from each group reported the group's conclusions. A closure period was also included at the end of the workshop for review and discussion of items that had been considered during the workshop. The primary conclusions reached were the following: -All fiber types capable of depositing in the thorax are not alike in their pathogenic potential. -Only fiber samples with dimensions similar to those to which humans can inhale should be tested. -A complete characterization (i.e., dimensions, fiber number, mass, and aerodynamic diameter) of the fiber aerosol and retained dose is essential. -Appropriate aerosol generation methods must be used for inhalation studies in order to preserve fiber lengths. -A tiered approach to toxicity evaluation is recommended that includes: 1. In vitro screening for durability, surface properties, cytotoxicity, and similar properties, etc; 2. Short-term inhalation or other in vivo studies; 3. That chronic inhalation studies are the "gold standard" (i.e., provide most appropriate data for risk characterization). -The rat is the most appropriate species for inhalation studies. -In chronic inhalation studies, animals should be retained to at least 20% survival after 2-year exposure. -Serial lung burden analyses are an essential component of inhalation studies and are essential for understanding exposure-dose-response relationships. -Studies oriented to understanding mechanisms of toxicity and carcinogenicity are important adjuncts to traditional toxicity studies. -Histopathological analyses of tissues of the respiratory tract represent primary endpoints for evaluating effects of inhaled fibers. Major effects include pulmonary fibrosis, lung tumors, and mesotheliomas. Experimental tissues should be archived for future studies; wherever possible, handling and preservation of tissues should be done in a way that maximizes their future use in mechanistic studies. -Potential human exposures throughout the entire life-cycle of the fiber must be considered and fibrous material for toxicologic studies prepared accordingly. -Intracavity studies are inappropriate for risk characterization but can play a useful screening role in assessing fiber toxicity.(ABSTRACT TRUNCATED AT 400 WORDS)

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.

Evaluation of the pulmonary hazards associated with exposure to fibrous materials tends to be more complicated than assessments required for particulate materials. Fibers are defined by aspect ratios and it is generally considered that physical dimensions play an important role in the pathogenesis of fiber-related lung diseases. Several digestion techniques have been used to recover fibers from exposed lung tissue for clearance studies. Because many of the digestion fluids are corrosive (e.g., bleach, KOH), it is conceivable that the dimensions of recovered fibers are modified during the tissue digestion methods to assess whether the physical dimensions of bulk samples of fibers were altered following simulated digestion processing. Aliquots of crocidolite and chrysotile asbestos, Kevlar aramid, wollastonite, polyacrylonitrile (pan)-based carbon, and glass fibers were incubated with either saline, bleach, or KOH and then filtered. Scanning electron microscopy techniques were utilized to measure the physical dimensions (i.e., lengths and diameters) of at least 160 fibers per treatment group of each fiber type. Our results showed that the lengths and diameters of glass fibers and wollastonite were altered after treatment with KOH. In addition, treatment with bleach produced a small reduction in both asbestos fiber-type diameters, and greater changes in Kevlar and wollastonite diameters and carbon fiber lengths (P less than 0.05). These results indicate that lung digestion methods should be carefully assessed for each fiber type before initiating fiber clearance studies.

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 animal's 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.