Toxicity and recovery in the pregnant mouse after gestational exposure to the cyanobacterial toxin, cylindrospermopsin.

Cylindrospermopsin (CYN) is a tricyclic alkaloid toxin produced by fresh water cyanobacterial species worldwide. CYN has been responsible for both livestock and human poisoning after oral exposure. This study investigated the toxicity of CYN to pregnant mice exposed during different segments of gestation. The course of recovery and individual responses to the toxin were evaluated. Adverse effects of CYN were monitored up to 7 weeks post-dosing by clinical examination, histopathology, biochemistry and gene expression. Exposure on gestational days (GD) 8-12 induced significantly more lethality than GD13-17 exposure. Periorbital, gastrointestinal and distal tail hemorrhages were seen in both groups. Serum markers indicative of hepatic injury (alanine amino transferase, aspartate amino transferase and sorbitol dehydrogenase) were increased in both groups; markers of renal dysfunction (blood urea nitrogen and creatinine) were elevated in the GD8-12 animals. Histopathology was observed in the liver (centrilobular necrosis) and kidney (interstitial inflammation) in groups exhibiting abnormal serum markers. The expression profiles of genes involved in ribosomal biogenesis, xenobiotic and lipid metabolism, inflammatory response and oxidative stress were altered 24 h after the final dose. One week after dosing, gross, histological and serum parameters had returned to normal, although increased liver/body weight ratio and one instance of gastrointestinal bleeding was found in the GD13-17 group. Gene expression changes persisted up to 2 weeks post-dosing and returned to normal by 4 weeks. Responses of individual animals to CYN exposure indicated highly significant inter-animal variability within the treated groups.

Induction of pulmonary matrilysin expression by combustion and ambient air particles.

The molecular mechanism(s) by which chemically complex air pollution particles mediate their adverse health effects is not known. We have examined the ability of combustion and ambient air particles to induce pulmonary matrilysin expression due to the well-documented role of matrix metalloproteinases in tissue injury and repair responses. Rats were exposed to saline, residual oil fly ash (2.5 mg/rat), or ambient air particles (2.5 mg/rat) via intratracheal instillation and examined 3-72 h after exposure. Saline-exposed animals had low levels of matrilysin mRNA, whereas the animals exposed to either complex particle showed an early induction of pulmonary matrilysin gene expression as well as of the 19-kDa activated form of matrilysin. Immunocytochemistry and in situ hybridization analyses identified the alveolar macrophages and monocytes as primary sources of air pollution particle-induced matrilysin expression. Matrilysin gene induction and protein activation by combustion and ambient air particles correlated with the early histopathological changes produced by these particles. These results demonstrate the ability of combustion and ambient air particles to induce pulmonary matrilysin expression and suggest a role for this matrix metalloproteinase in the initiation of lung injury produced by these particles.

Particulate Matter Induction of Pulmonary Gelatinase A, Gelatinase B, and Tissue Inhibitor of Metalloproteinase Expression.

Gelatinase A and gelatinase B are matrix metalloproteinases (MMPs) that are capable of degrading type IV collagen as well as other major components of basement membranes. These MMPs are also involved in modulating inflammation and tissue remodeling. Previous studies have shown the induction of pulmonary matrilysin, another MMP, following exposure to either combustion or ambient particulate matter (PM). In the present study, we examined whether gelatinase A, gelatinase B, or tissue inhibitor of metalloproteinase (TIMP) was affected following exposure to PM. Sprague-Dawley rats were exposed to a combustion PM (residual oil fly ash, ROTA, 2.5 mg/rat) or saline by intratracheal instillation and examined at 6 to 72 h postexposure. Changes in gelatinase A, gelatinase B, and TIMP-1 and -2 m RNA levels were determined using reverse transcription (RT) polymerase chain reaction (PCR). ROTA exposure increased the mRNA levels of gelatinase A and TIMP-1. However, gelatinase B mRNA, not expressed in control animals, was significantly induced from 6 to 24 h following ROFA exposure. Western blot analysis confirmed the presence of gelatinase A and B protein in lung tissue following ROFA exposure. Immunocytochemical analysis revealed that alveolar epithelial cells and inflammatory cells were major cellular sources for the pulmonary gelatinase A and B expression. To compare the effects of ambient PM with that of combustion PM and to further examine effects of ambient PM size on MMP induction, animals were treated with the same dose of the size-fractionated ambient PM [PM1.7, PM1.7-3.7, PM37.20 (size indicated in micrometers) collected from Washington, DC], Gelatinase A, gelatinase B, and TIMP gene expression and cellular distributions were assessed using RT-PCR and immunocytochemistry, respectively. Interestingly, gelatinase B was significantly induced to the same extent by all three size-fractionated ambient PM. Celatinase A and TIMP-1 expression were not changed, while TIMP-2 expression was slightly decreased by PM1.7 and PM1.7-3.7. Immunocytochemically, gelatinase A, gelatinase B, and TIMP-2 expression were localized mainly to the terminal bronchiole region and associated with inflammatory cells in ambient PM exposed animals. Thus, we have provided further evidence that MMP and TIMP expression are altered following exposure to either combustion or ambient PM supporting the hypothesis that MMP may be involved in pathogenesis of PM-induced lung injury.

Cytokine mediation of ozone-induced pulmonary adaptation.

Previous studies have shown that a single exposure of animals to ozone (O3) can induce protection or adaptation to the acute injurious effects of a subsequent O3 challenge. Although a number of mechanisms have been proposed to account for this response, none appear to be fully explanatory. We examined the role interleukin (IL)-6 may play in the induction of adaptation to O3-induced pulmonary injury. A statistically significant 29-fold increase in bronchoalveolar lavage fluid IL-6 levels was observed in rats exposed to 0.5 ppm O3 during nighttime hours when compared with daytime hours even though similar kinetics of inflammation were induced by each exposure. Animals receiving an initial nighttime O3 exposure showed a lesser degree of inflammation following a subsequent O3 exposure when compared with animals which received an initial daytime exposure. Rats pretreated with IL-6 both intratracheally and intraperitoneally and subsequently exposed to O3 showed a lesser degree of cellular inflammation when compared with respective controls. Pretreatment of rats with anti-IL-6-receptor antibodies (ra) prior to the nighttime O3 exposure completely abrogated the O3-induced cellular adaptive response without effecting the inflammatory response induced by the initial nighttime O3 exposure. In fact, administration of anti-IL-6ra augmented the neutrophil influx following the second O3 exposure. Anti-IL-6ra treatment did not alter the pulmonary edema adaptive response, suggesting that the O3-induced cellular and edema adaptive responses are regulated by different mechanisms. Our data indicate that mobilization of pulmonary antioxidants does not play a role in the IL-6-mediated early cellular adaptive response and suggest that IL-6 is an essential mediator of the O3-induced cellular adaptive response.

Genetic variability in combustion particle-induced chronic lung injury.

Occupational exposure to anthropogenic particles is associated with lung injury in humans. We hypothesized that residual oil fly ash (ROFA), an emission source particulate, may induce acute lung injury and fibrosis in sensitive rat strains and that fibronectin (Fn) gene expression will correspond to the development of fibrosis. Male Sprague-Dawley (SD), Wistar (WIS), and Fischer 344 (F-344) rats (60 days old) were exposed to saline or ROFA (8.3 mg/kg) by intratracheal instillation and examined for up to 12 wk. Histology indicated focal areas of lung damage showing inflammatory cell infiltration as well as alveolar, airway, and interstitial thickening in all three rat strains during 1-7 days postexposure. Trichrome staining of the lung sections indicated a sporadic incidence of focal alveolar fibrosis at 1, 3, and 12 wk in SD rats, whereas WIS and F-344 rats showed only a modest increase in trichrome staining in the septal areas. Of all Fn mRNA isoforms examined by polymerase chain reaction, only EIIIA(+) was upregulated during 6 h-1 wk in ROFA-exposed SD and WIS rats but not in F-344 rats. In situ hybridization analysis in SD rats revealed Fn mRNA expression by macrophage and alveolar and airway epithelium and within fibrotic areas. Immunohistochemical analysis revealed increased presence of Fn EIIIA(+) protein in the areas of fibrotic injury and basally to the airway epithelium. In summary, Fn EIIIA(+) increases early in the course of particle-induced lung injury and remodeling, which may or may not result in discernible alveolar fibrosis. There is a rat strain variation in ROFA-induced fibrosis and associated Fn EIIIA(+) expression.

Soluble transition metals mediate residual oil fly ash induced acute lung injury.

Identification of constituents responsible for the pulmonary toxicity of fugitive combustion emission source particles may provide insight into the adverse health effects associated with exposure to these particles as well as ambient air particulate pollution. Herein, we describe results of studies conducted to identify constituents responsible for the acute lung injury induced by residual oil fly ash (ROFA) and to assess physical-chemical factors that influence the pulmonary toxicity of these constituents. Biochemical and cellular analyses performed on bronchoalveolar lavage fluid obtained from rats following intratracheal instillation of ROFA suspension demonstrated the presence of severe inflammation, an indicator of pulmonary injury, which included recruitment of neutrophils, eosinophils, and monocytes into the airway. A leachate prepared from ROFA, containing predominantly Fe, Ni, V, Ca, Mg, and sulfate, produced similar lung injury to that induced by ROFA suspension. Depletion of Fe, Ni, and V from the ROFA leachate abrogated its pulmonary toxicity. Correspondingly, minimal lung injury was observed in animals exposed to saline-washed ROFA particles. A surrogate transition metal sulfate solution containing Fe, V, and Ni largely reproduced the lung injury induced by ROFA. Metal interactions and pH were found to influence the severity and kinetics of lung injury induced by ROFA and soluble transition metals. These findings provide direct evidence for the role of soluble transition metals in the pulmonary injury induced by the combustion emission source particulate, ROFA.

Eosinophilic lung inflammation in particulate-induced lung injury: technical consideration in isolating RNA for gene expression studies.

Particulate and other pollutant exposures are associated with lung injury and inflammation. The purpose of this study was to develop an approach by which intact RNA could be obtained from inflamed lung tissue from particulate-exposed animals in order to correlate injury with specific gene expression. Male Sprague Dawley (SD) and Fischer-344 (F-344) rats were intratracheally instilled with saline or residual oil fly ash (ROFA) particles, 8.3 mg/kg body weight in saline. At various time points following ROFA instillation, lungs were either lavaged or used for RNA isolation. ROFA exposure produced an increase in bronchoalveolar lavage fluid (BALF) neutrophils in both SD and F-344 rats. A time-dependent increase in eosinophils occurred only in SD rats but not in F-344 rats. Extraction of inflamed pulmonary tissue having a high influx of eosinophils for RNA using the conventional acid guanidinium thiocyanate phenol-chloroform (AGPC) procedure failed to provide undegraded RNA suitable for RT-PCR and Northern blot analysis of beta-actin mRNA expression. Mixing intact total RNA from saline control rat lungs with degraded RNA samples from inflamed lung yielded a gel profile of degraded RNA, indicating the presence of ribonuclease-like activity in the RNA extracted from lung tissues having eosinophil influx. Evidently, the conventional AGPC procedure failed to completely remove ribonuclease activity associated with ROFA-induced pulmonary eosinophil influx. This study reports a single-step modification to the AGPC extraction method that does not require additional reagents or additional precipitation steps for extracting undegraded RNA from nuclease-rich inflamed lung tissue. The aqueous layer resulting from mixing homogenate and chloroform is extracted a second time using an equal volume of AGPC buffer followed by addition of chloroform and centrifugation. The second aqueous phase is then treated as described in the conventional RNA extraction protocol. This simple and convenient modification does not require multiple precipitations of RNA and yields undegraded RNA from inflamed lung tissue with a slightly higher A260/A280 ratio without affecting overall RNA recovery. The results indicate that undegraded RNA could not be isolated using the routine AGPC-based isolation technique from lung tissue containing eosinophils following ROFA exposure. The degraded RNA preparations were unsuitable for gene expression studies. However, undegraded RNA can be isolated from these tissues by modifying the original AGPC RNA extraction procedure, which is suitable for gene expression analysis using northern blot and RT-PCR techniques.

Temporal expression and cellular distribution of pulmonary fibronectin gene induction following exposure to an emission source particle.

This study examines the ability of an emission source particle, residual oil fly ash (ROFA), to influence pulmonary fibronectin (Fn) gene expression. Fn is an extracellular matrix (ECM) protein involved in a variety of cellular functions, including inflammation, cell proliferation, and fibrosis. Temporal expression and spatial distribution of Fn gene induction were assessed by in situ hybridization in rat lung during acute phase of lung injury occurring 6 to 72 h following intratracheal instillation of ROFA. Fn mRNA was not detected in rat lungs treated with either saline or at 6 h after ROFA treatment. However, Fn mRNA was induced in airway epithelial cells 24 h after ROFA instillation. Histopathology showed peribronchial inflammation and focal edema. Diffuse inflammation in alveolar region with limited expression of Fn mRNA was evident 48 h after ROFA exposure, occurring mainly in proliferating epithelial cells. Extensive Fn mRNA expression was seen in proliferating fibroblasts and in hyperplastic epithelial cells within incipient fibrotic lesions 72 h after exposure, while the intensity of expression in the airway epithelial cells was decreased. Therefore, Fn mRNA induction was associated with inflammatory and incipient fibrotic lesions, indicating its possible involvement in airway hyperreactivity and initiation of fibrogenesis.

Lung injury after silica instillation is associated with an accumulation of iron in rats.

It has been postulated that the incomplete complexation of host iron by the surface of mineral oxides is essential in in vivo lung injury after exposure to these dusts. We investigated the associations between in vivo iron accumulation after intratracheal instillation of silica dust in rats and 1) concentrations of antioxidants and oxidized products in the lung and 2) an index of chronic fibrotic injury. Fifty milligrams of minusil were intratracheally instilled into 60-day-old, male Sprague-Dawley rats. Ionizable Fe3+ complexed to the surface of silica increased from 12.7 +/- 1.4 mumol/g to values as high as 42.5 +/- 9.1 mumol/g dust after instillation. Corresponding to this elevation of surface-adsorbed metal, concentrations of iron in bronchoalveolar lavage fluid, lung tissue, plasma, and liver tissue all increased. Antioxidant molecules in lung tissue, including ascorbate, urate, and glutathione, all decreased, whereas superoxide dismutase increased. Oxidized products in the lung tissue, measured as thiobarbituric acid-reactive products, similarly increased, reflecting an oxidant stress. Dietary depletion of iron stores before instillation of silica dust resulted in low iron stores (hematocrit values of 21.8 +/- 1.9) and low iron concentrations in lavage fluid, lung tissue, and liver tissue. Rats on iron-depleted diets demonstrated a diminished fibrotic injury after dust instillation. Complexation of iron by the dust surface may be central in collagen deposition after silica exposure.

Toxicity of an anthraquinone violet dye mixture following inhalation exposure, intratracheal instillation, or gavage.

Anthraquinone dyes are utilized by the military in colored-smoke grenades. During production, workers in munitions plants may be exposed to fugitive emissions of these dyes or mixtures thereof. The effects of a prototype violet dye mixture (VDM) consisting of Disperse Red 11 (DR11), [1,4-diamino-2-methoxy-anthraquinone] and Disperse Blue 3 (DB3) [1-methylamino-4-hydroxyethylamino-anthraquinone] on F344 male and female rats have been investigated. Acute 1-day inhalation exposures (6 hr) to VDM were conducted at 1000, 300, 100, 70, 40, and 10 mg/m3, with an additional exposure to 40 mg/m3 6 hr/day for 5 days; 4.22 +/- 2.1 microns (MMAD +/- delta g). Lung burdens of dye, general histopathology, and/or liver function were evaluated at 0, 3, and 7 days postexposure. Unexpected lethality due to severe liver damage was observed with acute exposures of > or = 300 mg/m3 and in the 5-day 40 mg/m3 exposures. Centrilobular degeneration and necrosis of liver cells was concentration-dependent with inhalation of VDM > or = 40 mg/m3. In addition, nasal olfactory epithelium exhibited degeneration and necrosis with acute exposures > or = 10 mg/m3. Lung instillations at 250, 500, and 1000 micrograms of the VDM revealed no lung or liver toxicity. Because per os exposure due to preening was suspected as a major exposure route, a gavage study with the VDM and its two component dyes DR11 and DB3 (800 mg/kg) was undertaken. One day following gavage with DR11 or DB3, serum enzymes indicative of liver toxicity (LDH, SGPT, SDH, and ICDH) were slightly elevated (1-6x control). However, rats gavaged with VDM had serum enzyme levels 10-100x control by Day 1 after gavage, indicating acute liver toxicity. Activities of liver enzymes involved in xenobiotic and glutathione metabolism were also acutely affected. All of the dyes caused various degrees of induction of glucose-6-phosphate dehydrogenase, glutathione reductase, glutathione peroxidase, and nonprotein sulfhydryls. The enzymes involved in xenobiotic metabolism (glutathione S-transferase, NADPH cytochrome-c reductase, and P450) were also elevated by the two component dyes, in contrast to their significant depression with VDM treatment. The similarity between the liver and olfactory epithelium effects of these compounds and the lack of pulmonary tissue effects is not fully understood, but the interaction of the individual dyes as VDM emphasizes the need to assess chemicals such as the anthraquinones as their likely-to-be-encountered mixtures.

Enhanced mortality and liver damage in virus-infected mice exposed to p-xylene.

This study assessed effects of exposure to p-xylene, a ubiquitous air pollutant, on mice infected with murine cytomegalovirus (MCMV), a mouse model for a common human virus. It was postulated that adverse health effects could occur as a result of (1) enhanced infection due to xylene-induced immune suppression, (2) increased p-xylene toxicity due to viral suppression of cytochrome P-450 (P-450), and/or (3) additive or synergistic effects on liver function due to tissue injury by both p-xylene and MCMV. Mice were exposed to filtered air, 600 or 1200 ppm p-xylene 6 h/d for 4 d and infected with a sublethal dose of MCMV after the first exposure. No deaths occurred among uninfected, p-xylene-exposed mice or infected, air-exposed mice; 34% and 0% mortality occurred respectively in infected mice exposed to 1200 and 600 ppm p-xylene. Virus titers in the liver and splenic natural killer cell activity were unaffected by exposure to 1200 ppm p-xylene. Small but significant increases in serum aspartate aminotransferase, alanine aminotransferase, and lactate dehydrogenase activities, indicators of liver damage, were observed at 4 d postinfection. p-Xylene exposure had no effect on these serum enzyme activities in uninfected mice, but 1200 ppm potentiated this effect in infected mice. MCMV significantly suppressed and p-xylene significantly increased total P-450 levels in the liver, but there was no significant interaction between the two. Isozymes 1A1, 2B1/B2, and 2E1 were decreased to a similar degree, suggesting that the virus does not target specific isozymes. Enhanced mortality was not due to immune suppression. While p-xylene potentiated liver damage was caused by the virus, the magnitude of serum enzyme activities indicates that this damage was not a likely cause of death. The cause of deaths is unclear, results were consistent with the hypothesis that enhanced mortality was related to enhanced xylene toxicity due to suppression of P-450, although additive or synergistic damage to tissues other than liver cannot be ruled out.

Effects of inhaled phosgene on rat lung antioxidant systems.

A concentration-response and C x T study were undertaken to determine the effect of phosgene (COCl2) inhalation on pulmonary antioxidant processes as determined by changes in endogenous glutathione (GSH) and antioxidant-associated enzymes (GSH peroxidase, GSH reductase, glucose-6-phosphate dehydrogenase, and superoxide dismutase). Rats were exposed to 0.0, 0.1, 0.25, 0.5, and 1.0 ppm phosgene for 4 hr and 0.25 ppm phosgene for 8 hr. The endpoints were assayed at 0, 1, 2, 3 and 7 days after exposure cessation. The lowest effective concentration was 0.1 ppm phosgene (increases in measured variables from 8 to 35% above control values). At all concentrations, major effects were observed 1 to 2 days after exposure (12 to 159% above control), peaking at 2 to 3 days postexposure (11 to 253% above control), and in some cases were still evident 7 days (10 to 65% above control) after exposure. The C x T study using the same dose (120 ppm-min), but different times and concentration (0.25 ppm for 8 hr and 0.5 ppm for 4 hr), showed a concentration dependence. The peak antioxidant enzyme changes observed for the higher concentration (0.5 ppm) were at least double those observed for the lower concentration (0.25 ppm). These enzyme changes were similar to those reported for the oxidants O3 and NO2. Although the suspected mechanism of initial damage between phosgene and these oxidants is different (acylation vs oxidation) the biological result is similar (i.e., damage, repair, and influx of cells), thus eliciting similar biochemical changes in response to pulmonary injury.(ABSTRACT TRUNCATED AT 250 WORDS)

Glutathione peroxidase and glutathione transferase activity in rat lung and liver following cadmium inhalation.

A 2-h inhalation exposure to 4.6 mg Cd/m3 decreased pulmonary total glutathione peroxidase (GSH Px) activity and non-selenium peroxidase (GSH non-Se-Px) activity but had no effect on GSH selenium peroxidase (Se-Px) activity. Seventy-two hours after exposure there was an increase in total GSH Px and GSH Se-Px activity and a decrease in GSH non-Se-Px activity. Exposure to 0.44 mg Cd/m3 for 2 h caused no effect on GSH Se-Px at either 0 or 72 h post exposure, but total GSH Px and GSH non-Se-Px activities were decreased up to 72 h post exposure. Exposure to 4.6 mg Cd/m3 caused an increase in hepatic GSH Se-Px activity 72 h post exposure, but no other significant changes were observed in the liver. Changes in GSH non-Se-Px activity did not relate to changes in GSH transferase (Tr) activity. The data suggest that alterations in GSH Px activity by Cd2+ may be due to changes in GSH non-Se-Px activity and that changes in pulmonary GSH Tr and GSH non-Se-Px activities may not be as closely linked as in the liver.

A comparative study of the effects of inhaled cadmium chloride and cadmium oxide: pulmonary response.

The effects of aerosols of cadmium chloride (CdCl2) and cadmium oxide (CdO) on pulmonary biochemical function were compared. Rats and rabbits were exposed to 0.25, 0.45, or 4.5 mg Cd/m3 for 2 h. Pulmonary toxicity was determined histologically and biochemically. Cadmium chloride and CdO showed a deposition response that was linearly related to the chamber concentration. Both compounds caused multifocal, interstitial pneumonitis 72 h after exposure, but the CdO lesion was more severe with proliferation of fibrocytic-like cells as well as pneumocytes. Comparing the two Cd compounds at the highest concentration (4.5 mg Cd/m3), the biochemical responses in the rat were similar. The majority of the effects occurred 72 h after exposure, with significant increases in lung weight, lung-to-body weight ratio, GSH reductase, GSH transferase, and G-6-PDH. However, GSH peroxidase was inhibited immediately after the CdO exposure. Cadmium oxide-related alterations in the parameters studied could easily be distinguished from those of CdCl2 at the exposure concentration of 0.45 mg Cd/m3. The response pattern in the rabbit resembled that of the rat. In both species Cd had a consistent inhibitory effect on pulmonary GSH peroxidase, even at the lowest concentration of 0.25 mg Cd/m3. Based on these findings, inhaled CdO appeared to be more toxic to the lung than inhaled CdCl2.

A model of the regional uptake of gaseous pollutants in the lung. I. The sensitivity of the uptake of ozone in the human lung to lower respiratory tract secretions and exercise.

An ozone (O3) dosimetry model is presented that takes into account convection and diffusion of O3 in the lumen and airspaces of the lower respiratory tract and transport and chemical reactions in the mucous and surfactant layers and in the underlying tissue and capillaries. The model was applied to human airway morphometric data. Values for the chemical and physical parameters that define the liquid tissue and blood compartments were based on reported experimental data. Simulation results illustrate the variability of results due to an uncertainty in the knowledge of transport parameters, liquid, tissue, and blood compartment thicknesses, and chemical reaction rates. Results were most sensitive to mucous compartment thickness and reaction rate constant and least sensitive to transport and blood parameters. Exercise was simulated, showing little effect on tracheobronchial uptake but a pronounced effect on pulmonary uptake.

An automated analysis of glutathione peroxidase, S-transferase, and reductase activity in animal tissue.

A centrifugal analyzer and a spectrophotometer were compared for routine analysis of xenobiotic metabolizing enzymes glutathione (GSH) peroxidase, GSH-S transferase, and GSH reductase. Lung, liver, and kidney from 60-day-old male rats were used as the source of enzymes. Linear regression analysis was used to assess the accuracy and precision of the centrifugal analyzer method in measuring enzyme activities. Biologically and statistically, the centrifugal analyzer proved to be acceptable for routine measurement of these GSH-dependent enzymes.