SVEP1 influences monocyte to macrophage differentiation via integrin α4ß1/α9ß1 and Rho/Rac signalling.

BACKGROUND: The large extracellular matrix protein SVEP1 mediates cell adhesion via integrin α9ß1. Recent studies have identified an association between a missense variant in SVEP1 and increased risk of coronary artery disease (CAD) in humans and in mice Svep1 deficiency alters the development of atherosclerotic plaques. However how SVEP1 functionally contributes to CAD pathogenesis is not fully understood. Monocyte recruitment and differentiation to macrophages is a key step in the development of atherosclerosis. Here, we investigated the requirement for SVEP1 in this process. METHODS: SVEP1 expression was measured during monocyte-macrophage differentiation in primary monocytes and THP-1 human monocytic cells. SVEP1 knockout THP-1 cell lines and the dual integrin α4ß1/α9ß1 inhibitor, BOP, were utilised to investigate the effect of these proteins in THP-1 cell adhesion, migration and cell spreading assays. Subsequent activation of downstream integrin signalling intermediaries was quantified by western blotting. RESULTS: SVEP1 gene expression increases in monocyte to macrophage differentiation in human primary monocytes and THP-1 cells. Using two SVEP1 knockout THP-1 cells we observed reduction in monocyte adhesion, migration, and cell spreading compared to control cells. Similar results were found with integrin α4ß1/α9ß1 inhibition. We demonstrate reduced activity of Rho and Rac1 in SVEP1 knockout THP-1 cells. CONCLUSIONS: SVEP1 regulates monocyte recruitment and differentiation phenotypes through an integrin α4ß1/α9ß1 dependent mechanism. GENERAL SIGNIFICANCE: These results describe a novel role for SVEP1 in monocyte behaviour relevant to CAD pathophysiology.

The majority of adrenocorticotropin receptor (melanocortin 2 receptor) mutations found in familial glucocorticoid deficiency type 1 lead to defective trafficking of the receptor to the cell surface.

CONTEXT: There are at least 24 missense, nonconservative mutations found in the ACTH receptor [melanocortin 2 receptor (MC2R)] that have been associated with the autosomal recessive disease familial glucocorticoid deficiency (FGD) type 1. The characterization of these mutations has been hindered by difficulties in establishing a functional heterologous cell transfection system for MC2R. Recently, the melanocortin 2 receptor accessory protein (MRAP) was identified as essential for the trafficking of MC2R to the cell surface; therefore, a functional characterization of MC2R mutations is now possible. OBJECTIVE: Our objective was to elucidate the molecular mechanisms responsible for defective MC2R function in FGD. METHODS: Stable cell lines expressing human MRAPalpha were established and transiently transfected with wild-type or mutant MC2R. Functional characterization of mutant MC2R was performed using a cell surface expression assay, a cAMP reporter assay, confocal microscopy, and coimmunoprecipitation of MRAPalpha. RESULTS: Two thirds of all MC2R mutations had a significant reduction in cell surface trafficking, even though MRAPalpha interacted with all mutants. Analysis of those mutant receptors that reached the cell surface indicated that four of six failed to signal, after stimulation with ACTH. CONCLUSION: The majority of MC2R mutations found in FGD fail to function because they fail to traffic to the cell surface.

Why does Kevlar decompose, while Nomex does not, when treated with aqueous chlorine solutions?

Kevlar and Nomex are high-performance polymers which have wide varieties of applications in daily life. Recently, they have been proposed to be biocidal materials when reacted with household bleach (sodium hypochlorite solution) because they contain amide moieties which can be chlorinated to generate biocidal N-halamine functional groups. Although Nomex can be chlorinated without any significant decomposition, Kevlar decomposes under the same chlorination conditions. In this study, two mimics for each of the polymers were synthesized to simulate the carboxylate and diaminophenylene components of the materials. It was found that the p-diaminophenylene component of the Kevlar mimic is oxidized to a quinone-type structure upon treatment with hypochlorous acid, which then decomposes. However, such a mechanism for the Nomex mimic is not possible. In this paper, based upon these observations, a plausible answer will be provided to the title question.

Pulmonary toxicity screening studies in male rats with TiO2 particulates substantially encapsulated with pyrogenically deposited, amorphous silica.

The aim of this study was to evaluate the acute lung toxicity in rats of intratracheally instilled TiO2 particles that have been substantially encapsulated with pyrogenically deposited, amorphous silica. Groups of rats were intratracheally instilled either with doses of 1 or 5 mg/kg of hydrophilic Pigment A TiO2 particles or doses of 1 or 5 mg/kg of the following control or particle-types: 1) R-100 TiO2 particles (hydrophilic in nature); 2) quartz particles, 3) carbonyl iron particles. Phosphate-buffered saline (PBS) instilled rats served as additional controls. Following exposures, the lungs of PBS and particle-exposed rats were evaluated for bronchoalveolar lavage (BAL) fluid inflammatory markers, cell proliferation, and by histopathology at post-instillation time points of 24 hrs, 1 week, 1 month and 3 months. The bronchoalveolar lavage results demonstrated that lung exposures to quartz particles, at both concentrations but particularly at the higher dose, produced significant increases vs. controls in pulmonary inflammation and cytotoxicity indices. Exposures to Pigment A or R-100 TiO2 particles produced transient inflammatory and cell injury effects at 24 hours postexposure (pe), but these effects were not sustained when compared to quartz-related effects. Exposures to carbonyl iron particles or PBS resulted only in minor, short-term and reversible lung inflammation, likely related to the effects of the instillation procedure. Histopathological analyses of lung tissues revealed that pulmonary exposures to Pigment A TiO2 particles produced minor inflammation at 24 hours postexposure and these effects were not significantly different from exposures to R-100 or carbonyl iron particles. Pigment A-exposed lung tissue sections appeared normal at 1 and 3 months postexposure. In contrast, pulmonary exposures to quartz particles in rats produced a dose-dependent lung inflammatory response characterized by neutrophils and foamy (lipid-containing) alveolar macrophage accumulation as well as evidence of early lung tissue thickening consistent with the development of pulmonary fibrosis. Based on our results, we conclude the following: 1) Pulmonary instillation exposures to Pigment A TiO2 particles at 5 mg/kg produced a transient lung inflammatory response which was not different from the lung response to R-100 TiO2 particles or carbonyl iron particles; 2) the response to Pigment A was substantially less active in terms of inflammation, cytotoxicity, and fibrogenic effects than the positive control particle-type, quartz particles. Thus, based on the findings of this study, we would expect that inhaled Pigment A TiO2 particles would have a low risk potential for producing adverse pulmonary health effects.

Biodegradability of para-aramid respirable-sized fiber-shaped particulates (RFP) in human lung cells.

Using both in vivo (inhalation) and in vitro (cell culture) studies, we previously reported that p-aramid respirable fibers (RFP--defined as respirable-sized fiber-shaped particulates) are biodegraded in lungs and lung cells of rats following exposures. The current studies were undertaken to determine whether shortening mechanisms of p-aramid RFP biodegradability are also operative in human lung cells. Cultures of human A549 lung epithelial cells (A549), primary alveolar macrophages (HBAL) (collected via bronchoalveolar lavage [BAL]) from volunteers), and co-cultures (Co) of the A549 and HBAL were incubated with p-aramid RFP for either 1 h, 1 day, or 1 week to assess RFP shortening. Lengths of RFP were measured using scanning electron microscopy (SEM) following fixation, digestion of culture tissue components, and processing. Similar to findings using rat lung cells, only slight RFP shortening was measured in A549 cultures at 1-day and 1-week post-incubation. More importantly, in HBAL and Co groups, greater transverse cleavage of p-aramid RFP was measured at 1-day and 1-week postexposure compared to 1-h HBAL or Co groups, or in any A549 groups. In contrast, cellulose RFP, a biopersistent reference control fiber, were not measurably shortened under similar circumstances. Second, p-aramid RFP were incubated either with phosphate-buffered saline (PBS), or acellular BAL fluids from human volunteers or rats and processed for SEM analysis of RFP lengths. Mean lengths of p-aramid RFP incubated with human or rat BAL fluids were substantially decreased compared to PBS. Similar to our findings with rat lung cells, components of human lung fluids coat the p-aramid RFP as a prerequisite for subsequent enzymatic cleavage by human phagocytic lung cells and this finding reinforces the concept that inhaled p-aramid RFP are likely to be biodegradable in the lungs of humans.

Comparative pulmonary toxicity inhalation and instillation studies with different TiO2 particle formulations: impact of surface treatments on particle toxicity.

Most pigment-grade titanium dioxide (TiO(2)) samples that have been tested in pulmonary toxicity tests have been of a generic variety-i.e., generally either uncoated particles or TiO(2) particles containing slightly hydrophilic surface treatments/coatings (i.e., base TiO(2)). The objectives of these studies were to assess in rats, the pulmonary toxicity of inhaled or intratracheally instilled TiO(2) particle formulations with various surface treatments, ranging from 0-6% alumina (Al(2)O(3)) or alumina and 0-11% amorphous silica (SiO(2)). The pulmonary effects induced by TiO(2) particles with different surface treatments were compared to reference base TiO(2) particles and controls. In the first study, groups of rats were exposed to high exposure (dose) concentrations of TiO(2) particle formulations for 4 weeks at aerosol concentrations ranging from 1130-1300 mg/m(3) and lung tissues were evaluated by histopathology immediately after exposure, as well as at 2 weeks and 3, 6, and 12 months postexposure. In the second study, groups of rats were intratracheally instilled with nearly identical TiO(2) particle formulations (when compared to the inhalation study) at doses of 2 and 10 mg/kg. Subsequently, the lungs of saline-instilled and TiO(2)-exposed rats were assessed using both bronchoalveolar (BAL) biomarkers and by histopathology/cell proliferation assessment of lung tissues at 24 h, 1 week, 1 and 3 months postexposure. The results from these studies demonstrated that for both inhalation and instillation, only the TiO(2) particle formulations with the largest components of both alumina and amorphous silica surface treatments produced mildly adverse pulmonary effects when compared to the base reference control particles. In summary, two major conclusions can be drawn from these studies: (1) surface treatments can influence the toxicity of TiO(2) particles in the lung; and (2) the intratracheal instillation-derived, pulmonary bioassay studies represent an effective preliminary screening tool for inhalation studies with the identical particle-types used in this study.

Comparative pulmonary toxicity assessment of single-wall carbon nanotubes in rats.

The aim of this study was to evaluate the acute lung toxicity of intratracheally instilled single-wall carbon nanotubes (SWCNT) in rats. The lungs of rats were instilled either with 1 or 5 mg/kg of the following control or particle types: (1) SWCNT, (2) quartz particles (positive control), (3) carbonyl iron particles (negative control), (4) phosphate-buffered saline (PBS) + 1% Tween 80, or (5) graphite particles (lung tissue studies only). Following exposures, the lungs of PBS and particle-exposed rats were assessed using bronchoalveolar lavage (BAL) fluid biomarkers and cell proliferation methods, and by histopathological evaluation of lung tissue at 24 h, 1 week, 1 month, and 3 months postinstillation. Exposures to high-dose (5 mg/kg) SWCNT produced mortality in ~15% of the SWCNT-instilled rats within 24 h postinstillation. This mortality resulted from mechanical blockage of the upper airways by the instillate and was not due to inherent pulmonary toxicity of the instilled SWCNT particulate. Exposures to quartz particles produced significant increases versus controls in pulmonary inflammation, cytotoxicity, and lung cell parenchymal cell proliferation indices. Exposures to SWCNT produced transient inflammatory and cell injury effects. Results from the lung histopathology component of the study indicated that pulmonary exposures to quartz particles (5 mg/kg) produced dose-dependent inflammatory responses, concomitant with foamy alveolar macrophage accumulation and lung tissue thickening at the sites of normal particle deposition. Pulmonary exposures to carbonyl iron or graphite particles produced no significant adverse effects. Pulmonary exposures to SWCNT in rats produced a non-dose-dependent series of multifocal granulomas, which were evidence of a foreign tissue body reaction and were nonuniform in distribution and not progressive beyond 1 month postexposure (pe). The observation of SWCNT-induced multifocal granulomas is inconsistent with the following: (1) lack of lung toxicity by assessing lavage parameters, (2) lack of lung toxicity by measuring cell proliferation parameters, (3) an apparent lack of a dose response relationship, (4) nonuniform distribution of lesions, (5) the paradigm of dust-related lung toxicity effects, (6) possible regression of effects over time. In addition, the results of two recent exposure assessment studies indicate very low aerosol SWCNT exposures at the workplace. Thus, the physiological relevance of these findings should ultimately be determined by conducting an inhalation toxicity study.

Pulmonary toxicity studies in rats with triethoxyoctylsilane (OTES)-coated, pigment-grade titanium dioxide particles: bridging studies to predict inhalation hazard.

The aim of this study was to assess and compare the acute lung toxicities of intratracheally instilled hydrophobic relative to hydrophilic surface-coated titanium dioxide (TiO(2)) particles using a pulmonary bridging methodology. In addition, the results of these instillation studies were bridged with data previously generated from inhalation studies with hydrophilic, pigment-grade (base) TiO(2) particles, using the base, pigment-grade TiO(2) particles as the inhalation/instillation bridge material. To conduct toxicity comparisons, the surface coatings of base pigment-grade TiO(2) particles were made hydrophobic by application of triethoxyoctylsilane (OTES), a commercial product used in plastics applications. For the bioassay experimental design, rats were intratracheally instilled with 2 or 10 mg/kg of the following TiO(2) particle-types: (1) base (hydrophilic) TiO(2) particles; (2) TiO(2) with OTES surface coating; (3) base TiO(2) with Tween 80; or (4) OTES TiO(2) with Tween 80. Saline instilled rats served as controls. Following exposures, the lungs of sham- and TiO(2)-exposed rats were assessed both using bronchoalveolar lavage (BAL) biomarkers and by histopathology of lung tissue at 24 hours, 1 week, 1 month, and 3 months post exposure. The results demonstrated that only the base, high-dose (10 mg/kg) pigment-grade TiO(2) particles and those with particle-types containing Tween 80 produced a transient pulmonary inflammatory response, and this was reversible within 1 week postexposure. The authors conclude that the OTES hydrophobic coating on the pigment-grade TiO(2) particle does not cause significant pulmonary toxicity.

Biodegradability of inhaled p-aramid respirable fiber-shaped particulates (RFP): mechanisms of RFP shortening and evidence of reversibility of pulmonary lesions.

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.

Coordination chemistry of silver(I) with the nitrogen-bridged ligands (C(6)H(5))(2)PN(H)P(C(6)H(5))(2) and (C(6)H(5))(2)PN(CH(3))P(C(6)H(5))(2): the effect of alkylating the nitrogen bridge on ligand bridging versus chelating behavior.

The coordination chemistry of silver(I) with the nitrogen-bridged ligands (C(6)H(5))(2)PN(R)P(C(6)H(5))(2) [R = H (dppa); R = CH(3) (dppma)] has been investigated by (31)P NMR and electrospray mass spectrometry (ESMS). Species observed by (31)P NMR include Ag(2)(mu-dppa)(2+), Ag(2)(mu-dppa)(2)(2+), Ag(2)(mu-dppa)(3)(2+), Ag(2)(mu-dppma)(2+), Ag(2)(mu-dppma)(2)(2+), and Ag(eta(2)-dppma)(2)(+). Species observed by ESMS at low cone voltages were Ag(2)(dppa)(2)(2+), Ag(2)(dppa)(3)(2+), Ag(2)(dppma)(2)(2+), and Ag(dppma)(2)(+). (C(6)H(5))(2)PN(CH(3))P(C(6)H(5))(2) showed a strong tendency to chelate, while (C(6)H(5))(2)PN(H)P(C(6)H(5))(2) preferred to bridge. Differences in the bridging versus chelating behavior of the ligands are assigned to the Thorpe-Ingold effect, where the methyl group on nitrogen sterically interacts with the phenyl groups on phosphorus. The crystal structure of the three-coordinate dinuclear silver(I) complex (Ag(2)[(C(6)H(5))(2)PN(H)P(C(6)H(5))(2)](3))(BF(4))(2) has been determined. Bond distances include Ag-Ag = 2.812(1) A, Ag(1)-P(av) = 2.492(3) A, and Ag(2)-P(av) = 2.509(3) A. The compound crystallizes in the monoclinic space group Cc at 294 K, with a = 18.102(4)(o), Z = 4, V = 7261(3) A(3), R = 0.0503, and R(W) = 0.0670.

Biodegradability of inhaled para-aramid respirable-sized fiber-shaped particulates: mechanistic in vivo and in vitro studies.

Biopersistence represents an important health-related issue in fiber toxicology. These studies were undertaken to elucidate the mechanism(s) through which inhaled p-aramid respirable-sized fiber-shaped particulates (RFP) are biodegraded in the lungs of exposed rats and hamsters. Previously, we and others have reported that, following deposition in the lung, long p-aramid RFPs are cleaved into shorter fibrous fragments. To investigate the mechanisms of RFP biodegradation, we have postulated that lung fluids coat/activate p-aramid RFP following deposition in the alveolar regions of the lung, thus predisposing the RFP to enzymatic attack and consequent shortening. This process enhances the rate of clearance of the inhaled RFP. To test this hypothesis, we have conducted both in vivo and in vitro cellular and noncellular investigations. First, p-aramid or cellulose RFP were instilled into the lungs of rats and the lungs were digested 24 h postexposure using two different digestion techniques: (1) a conventional ethanolic KOH method and (2) an enzymatic method that simulates the action of lung enzymes. Cellulose RFP were utilized as a control organic fiber-type that is known to be biopersistent. The results demonstrated that the enzymatic but not the KOH method resulted in transverse cleavage of the p-aramid RFP; the lengths of cellulose RFP recovered from rat lungs were not reduced by either method. Next, standardized preparations of p-aramid RFP or cellulose RFP were incubated with saline or lung fluids and then processed by one of two tissue digestion techniques. Mean lengths of p-aramid RFP incubated with saline and processed with KOH or the enzyme method were not found to be altered. Indeed, only the preparation of p-aramid RFP that had been incubated with bronchoalveolar lavage (BAL) fluids and processed with the enzyme solution resulted in cleavage of p-aramid RFP. Moreover, when the BAL fluids were autoclaved to denature proteins, the length dimensions of p-aramid RFP were intermediate between saline controls and RFP incubated with normal BAL fluids and processed via the enzymatic technique. In contrast to the in vitro noncellular studies with p-aramid RFP, the combination of BAL fluid incubation and enzyme digestion method had no measurable effect on shortening of cellulose RFP, indicating that the results with p-aramid were specific to that fiber-type. In a final set of in vitro cellular studies, cultures of rat lung epithelial cells, alveolar macrophages, or co-cultures of epithelial cells and macrophages were treated with p-aramid RFP for 1 h, 1 day, or 1 week to determine whether RFP shortening occurs directly in the phagocytic cells. The lengths of fibrils were measured using scanning electron microscopy techniques. The results demonstrated that (1) no shortening occurred in the epithelial cell cultures at any time point; however, (2) in the macrophage and cocultures, cleavage of p-aramid RFP was observed at 1 day and 1 week postexposure. Our data suggest that components of lung fluids coat and catalyze the p-aramid RFP as a prerequisite for enzymatic cleavage. This process could play a significant role in facilitating the transverse cleavage or shortening of inhaled p-aramid RFP in the lungs of exposed rats and hamsters.

Man-made respirable-sized organic fibers: what do we know about their toxicological profiles?

Man-made organic fibers (MMOFs) have been manufactured for over 50 years. Until recently, there have been few concerns raised regarding the safety of organic fiber dusts. This is due, in large part, to the perception that the dimensions of most, if not all, of these products were too large to be inhaled into the distal lungs of workers, i.e., were considered to be nonrespirable. A brief review of some of the issues related to organic fiber toxicology is presented herein. Some of the organic fiber-types used in commerce are identified and some fundamental tenets of fiber toxicology are discussed. In addition, the European Union, in their recent consideration for banning chrysotile asbestos fibers, evaluated some organic fiber substitutes and compared them to the hazards of asbestos. A brief review of their conclusions is described below. Finally, the results of some recent studies assessing the mechanisms of biodegradability of para-aramid respirable-sized, fiber-shaped particulates (RFP) are presented. Para-aramid (p-aramid) RFP are the most extensively-studied respirable organic fiber-type and RFP is the new term which describes respirable-sized organic fibers (ECETOC, 1996) (1). The results of these studies provide clues regarding the mechanism(s) of p-aramid RFP shortening in the lungs of exposed animals, and may be relevant for humans.

Biodegradability of inhaled p-aramid respirable fibre-shaped particulates: representative of other synthetic organic fibre-types?

OBJECTIVES: Biopersistence, or alternatively, biodegradability (i.e., low biopersistence) represents an important concept in fibre toxicology. The studies described below were undertaken to investigate the mechanisms through which inhaled para-aramid (p-aramid) respirable, fibre-shaped particulates (RFP) are biodegraded in the lungs of exposed rats and hamsters; in contrast, cellulose fibres, another organic fibre-type, are known to be biopersistent. To investigate the mechanisms of RFP biodegradation, we have hypothesized that lung fluids activate p-aramid RFP following deposition, and the RFP are then vulnerable to enzymatic attack in the lungs. METHODS: To test the hypothesis, p-aramid RFP or cellulose RFP were instilled into the lungs of rats and the lungs digested 24 h post-exposure using two different digestion techniques: (1) a conventional ethanolic KOH method, and (2) an enzymatic method which simulates lung enzymes. RESULTS: The enzymatic but not the KOH method artificially cleaved the p-aramid RFP recovered from rat lungs. Next, p-aramid RFP or cellulose RFP were incubated with saline or lung fluids and then processed by one of the two digestion techniques. Mean lengths of p-aramid RFP processed with KOH and evaluated by SEM were 13.4 microm; in contrast, mean lengths of p-aramid RFP samples, incubated in lung fluids and treated with the enzymatic method were 8.8 microm. The enzymatic digestion method had no discernible effect on shortening of cellulose RFP, indicating that the results with p-aramid were specific. CONCLUSIONS: Our data indicate that components of lung fluids coat and catalyze the p-aramid, thereby predisposing the RFP to enzymatic cleavage. This could play a significant mechanistic role in facilitating the transverse cleavage or shortening of inhaled p-aramid RFP in the lungs of exposed rats and hamsters.

The utilization of a unified pharmacophore query in the discovery of new antagonists of the adenosine receptor family.

Pharmacophore queries from previously known potent selective A3 antagonists were generated by Chem-X. These queries were used to search a pharmacophore database of diverse compounds (CNS-Set). In vitro assays of 186 'hits' yielded over 30 active compounds, for four adenosine receptor subtypes. This search strategy may also be applicable to the discovery of new ligands via receptor homology data.

Time Course of Eosinophilic Recruitment and Pulmonary Toxicity Biomarkers in an Allergic Asthma Model in Brown Norway Rats.

Allergic asthma is a pulmonary disease characterized by antigen-induced pulmonary eosinophilia, airway hyperresponsiveness, antigen-specific IgE antibody responses, and broncho-constriction. In attempting to elucidate mechanisms associated with the pathogenesis of this disease, a number of animal models have been developed. The current studies were undertaken to develop a model of allergic asthma model in Brown Norway rats. Unlike the neutrophilic inflammatory response to inhaled particles in most strains of rats, inhalation of antigens in sensitized Brown Norway rats results in a complex cellular response which is characterized by a variety of inflammatory cell types, and is dependent on the time course of inflammatory cell recruitment. In characterizing this ovalbumin-challenge model of allergic asthma, it was important to assess the time course of pulmonary inflammation, cell proliferation, and apoptosis. Male Brown Norway rats were sensitized and boosted with intraperitoneal injections of ovalbumin in aluminum hydroxide on experimental days 1 and 8. On days 15-17, rats were challenged by an inhalation exposure to 5% ovalbumin and were evaluated by bronchoalveolar lavage (BAL) at 24 or 48 h postexposure (PE). Control rats were similarly treated to ovalbumin aerosol exposures; however, these animals had been sensitized and boosted with aluminum hydroxide (minus the ovalbumin). Cell differential evaluations demonstrated that the rats exposed for 3 days/24 h postexposure and for 2 days/ 48 h postexposure produced the greatest numbers of BAL eosinophils and corresponding indicators of pulmonary toxicity. It was interesting to note that earlier exposure time periods (i.e., 1 day/24 h PE) generated a predominantly neutrophilic inflammatory response, while longer exposure/postexposure time periods (i.e., 3 days/48 h) produced a predominant mononuclear inflammatory response. Subsequent studies demonstrated that the 2-day/ 48-h protocol produced the optimum eosinophilic, cytotoxic, cell proliferative, and apoptotic response. Histopathological evaluations demonstrated a chronically active alveolitis and bronchiolitis, characterized by epithelial cell proliferation in the airways and inflammatory cell proliferation in the alveoli. Studies are ongoing to assess the cell types undergoing apoptosis in both the airway and parenchymal regions to fully characterize this model in order to assess its relevance and utility for studying asthma in humans.