Mitochondrial-derived oxidants and quartz activation of chemokine gene expression.

Macrophage inflammatory protein 2 (MIP-2) is a chemotactic cytokine which mediates neutrophil recruitment in the lung and other tissues. Pneumotoxic particles such as quartz increase MIP-2 expression in rat lung and rat alveolar type II epithelial cells. Deletion mutant analysis of the rat MIP-2 promoter demonstrated quartz-induction depended on a single NFkappaB consensus binding site. Quartz activation of NFkappaB and MIP-2 gene expression in RLE-6TN cells was inhibited by anti-oxidants suggesting the responses were dependent on oxidative stress. Consistent with anti-oxidant effects, quartz was demonstrated to increase RLE-6TN cell production of hydrogen peroxide. Rotenone treatment of RLE-6TN cells attenuated hydrogen peroxide production, NFkappaB activation and MIP-2 gene expression induced by quartz indicating that mitochondria-derived oxidants were contributing to these responses. Collectively, these findings indicate that quartz and crocidolite induction of MIP-2 gene expression in rat alveolar type II cells results from stimulation of an intracellular signaling pathway involving increased generation of hydrogen peroxide by mitochondria and subsequent activation of NFkappaB.

Production of the acute-phase protein lipopolysaccharide-binding protein by respiratory type II epithelial cells: implications for local defense to bacterial endotoxins.

This study demonstrates for the first time that respiratory epithelial cells are able to produce the acute phase protein lipopolysaccharide (LPS)-binding protein (LBP), which is known to play a central role in the defense to bacterial endotoxins (or LPS). Indications for local presence of LBP in human lung was obtained via reverse transcriptase/polymerase chain reaction that showed LBP messenger RNA (mRNA) expression. Therefore, LBP production by the human lung epithelial cell line A549, a human adenocarcinoma with features of type II pneumocytes, was studied. These cells produced LBP in response to interleukin (IL)-1beta, IL-6, and tumor necrosis factor- alpha, a response that was strongly enhanced by dexamethasone. In addition, LBP mRNA was detected in A549 cells, in increasing amounts as a result of stimulation. The pattern of cytokine-induced LBP production in A549 cells was similar to the pattern in the human liver epithelial cell line HuH-7. Moreover, the molecular weight of A549-derived LBP was approximately 60 kD, which is similar to HuH-7-derived LBP. Biologic activity of LBP produced by A549 cells was evaluated on the basis of its ability to interact with LPS. Further indications that type II alveolar epithelial cells are able to produce LBP were obtained from the observations that the murine lung type II epithelial cell line C10 produced murine LBP, and that isolated human primary type II pneumocytes expressed LBP mRNA, which was enhanced after stimulation of cells. The local production of this endotoxin binding protein by lung epithelial cells might contribute to a highly specific response at the site of exposure to bacteria and bacterial endotoxins.

Nuclear factor kappa B activity in response to oxidants and antioxidants.

The goal of this chapter was to review the current protocols that are available to measure the activation of NF-kappa B. The methods discussed all have their pitfalls when used in isolation. To obtain meaningful information, nuclear translocation and transcriptional activation should be studied in conjunction. Study of NF-kappa B regulated protein expression is the most physiologically relevant approach to monitoring the transcription regulatory effect of NF-kappa B. Because of the limitations of transcriptional analysis in primary cell cultures or tissues, incorporation of multiple approaches is recommended when the involvement of NF-kappa B in a disease process is evaluated.

Depletion of nitric oxide causes cell cycle alterations, apoptosis, and oxidative stress in pulmonary cells.

Nitric oxide (NO.) is important in the regulation of mitochondrial function, cell signaling, and gene expression. To elucidate how endogenous NO. regulates the function of airway epithelial cells, we used carboxy-PTIO, a hydrophilic, negatively charged NO. trap, to scavenge NO. from rat lung epithelial (RLE) and rat pleural mesothelial (RPM) cells and to determine the elicitation of cell cycle alterations, apoptosis, and oxidative stress. The reaction of NO. with PTIO causes the formation of PTI, which is measured by electron spin resonance (ESR) and is a quantitative measure of NO. formation. ESR spectroscopy revealed the production of NO. in RLE or RPM cells over a period from 1 to 24 h of exposure, indicating scavenging of NO. by PTIO. Cycle analyses in confluent RLE or RPM cells revealed two- to threefold increases in S and G2/M phases after exposure to 100-200 microM PTIO as well as increases in the fraction of cells undergoing apoptosis. Direct addition of PTI to cells failed to elicit cell cycle perturbations or apoptosis. The guanylyl cyclase inhibitor ODQ mimicked the effects of PTIO. 8-Bromo-cGMP but not 8-bromo-cAMP ameliorated the PTIO- or ODQ-mediated cell cycle perturbations and apoptosis, suggesting that cGMP-dependent pathways are involved in these cell cycle perturbations. Treatment of log-phase cells with PTIO resulted in more dramatic cell cycle perturbations compared with cells treated at confluence. Assessment of 5-bromo-2'-deoxyuridine incorporation to measure DNA synthesis demonstrated decreases in PTIO-treated compared with sham cells in addition to a cell cycle arrest in late S or G2/M phase. Last, incubation with dichlorofluorescin diacetate revealed oxidative stress in PTIO- but not in PTI-exposed RLE or RPM cells. We conclude that the depletion of endogenous NO. induces oxidative stress, cell cycle perturbations, and apoptosis. Our findings illustrate the importance of endogenous NO. in the control of cell cycle progression and survival of pulmonary and pleural cells and that a critical balance between NO. and superoxide may be necessary for these physiological events.

Crocidolite activates NF-kappa B and MIP-2 gene expression in rat alveolar epithelial cells. Role of mitochondrial-derived oxidants.

Nuclear factor kappa B (NF-kappa B) is a transcription factor that regulates expression of several genes coding for inflammatory and immunoregulatory proteins including the neutrophil chemotactic cytokine MIP-2. In previous studies we found that crocidolite asbestos activates the nuclear translocation of NF-kappa B as well as MIP-2 gene expression in rat alveolar type II cells. Here we report that both crocidolite-induced NF-kappa B activation of MIP-2 gene expression can be attenuated by the antioxidant tetramethylthiourea, suggesting the dependence of these responses on oxidative stress. Crocidolite exposure of RLE-TN cells also increased production of H2O2, a response that was inhibited by the mitochondrial respiratory chain inhibitor thenoyltrifluoroacetone (TTFA). TTFA treatment of RLE-6TN cells also inhibited crocidolite-induced nuclear translocation of NF-kappa B and MIP-2 gene expression. These results indicate crocidolite exposure of rat alveolar type II cells results in increased production of mitochondrial-derived hydrogen peroxide and that mitochondrial-derived oxidants contribute to crocidolite activation of NF-kappa B and increases in MIP-2 gene expression.

Modulation of mitochondrial gene expression in pulmonary epithelial cells exposed to oxidants.

Oxidants are important in the regulation of signal transduction and gene expression. Multiple classes of genes are transcriptionally activated by oxidants and are implicated in different phenotypic responses. In the present study, we performed differential mRNA display to elucidate genes that are induced or repressed after exposure of rat lung epithelial (RLE) cells to H2O2 or crocidolite asbestos, a pathogenic mineral that generates oxidants. After 8 or 24 hr of exposure, RNA was extracted, reverse transcribed, and amplified by polymerase chain reaction with degenerate primers to visualize alterations in gene expression. The seven clones obtained were sequenced and encoded the mitochondrial genes, NADH dehydrogenase subunits ND5 and ND6, and 16S ribosomal RNA. Evaluation of their expression by Northern blot analysis revealed increased expression of 16S rRNA after 1 or 2 hr of exposure to H2O2. At later time periods (4 and 24 hr), mRNA levels of 16S rRNA and NADH dehydrogenase were decreased in H2O2-treated RLE cells when compared to sham controls. Crocidolite asbestos caused increases in 16S rRNA levels after 8 hr of exposure, whereas after 24 hr of exposure to asbestos, 16S rRNA levels were decreased in comparison to sham controls. In addition to these oxidants, the nitric oxide generator spermine NONOate caused similar decreases in NADH dehydrogenase mRNA levels after 4 hr of exposure. The present data and previous studies demonstrated that all oxidants examined resulted in apoptosis in RLE cells during the time frame where alterations of mitochondrial gene expression were observed. As the mitochondrion is a major organelle that controls apoptosis, alterations in expression of mitochondrial genes may be involved in the regulation of apoptosis.

GRP78, HSP72/73, and cJun stress protein levels in lung epithelial cells exposed to asbestos, cadmium, or H2O2.

Occupational exposure to crocidolite asbestos is associated with the development of nonmalignant and malignant pulmonary disease. Considerable evidence indicates that the mechanisms of asbestos-induced toxicity involve the production of active oxygen species (AOS). Production of AOS in excess of cellular defenses creates an environment of oxidative stress and stimulates the expression of a number of different genes whose products may be involved in mediating responses from oxidant injury. To further investigate the mechanisms of asbestos-induced pathogenicity, we have examined by Western blot analyses the induction of the stress response proteins GRP78 and HSP72/73 in rat lung epithelial cells (RLE) exposed to crocidolite asbestos. In comparative studies, we also examined GRP78, HSP72/73, and cJun expression in RLE cells exposed to equitoxic concentrations of cadmium chloride (CdCl2) and hydrogen peroxide (H2O2). Our results demonstrate that asbestos and H2O2 do not alter GRP78 or HSP72/73 protein levels in RLE cells, but do increase levels of cJun protein. Increases by asbestos and H2O2 were not accompanied by alterations in cellular glutathione levels in this cell type, but asbestos caused elevations in protein levels of manganese-containing superoxide dismutase (MnSOD), an indirect indicator of oxidant stress. In contrast, exposure of cells to CdCl2 led to no changes in MnSOD protein levels, but increases in GRP78, HSP72/73, and cJun proteins as well as significant increases in oxidized and reduced thiol pools. Results suggest that environmental agents causing oxidative injury to lung epithelium elicit different patterns of stress responses.

Increased epidermal growth factor-receptor protein in a human mesothelial cell line in response to long asbestos fibers.

Epidermal growth factor (EGF) is a potent mitogen for human mesothelial cells, and autophosphorylation of the EGF receptor (EGF-R) occurs in these cell types after exposure to asbestos, a carcinogen associated with the development of mesothelioma. Here, the intensity and distribution of EGF-R protein was documented by immunocytochemistry in a human mesothelial cell line (MET5A) exposed to various concentrations of crocidolite asbestos and man-made vitreous fibers (MMVF-10). Whereas cells in contact with or phagocytizing shorter asbestos fibers (<60 microm length) or MMVF-10 at a range of concentrations showed no increase in EGF-R protein as determined by immunofluorescence, elongated cells phagocytizing and surrounding longer fibers (> or =60 microm) showed intense staining for EGF-R. In contrast, human A549 lung carcinoma cells showed neither elongation nor increased accumulation of EGF-R protein in response to long fibers. Patterns of aggregation and increases in EGF-R protein in mesothelial cells phagocytizing long asbestos fibers were distinct from diffuse staining of phosphotyrosine residues observed in asbestos-exposed cultures. These studies indicate that aggregation of EGF-R by long fibers may initiate cell signaling cascades important in asbestos-induced mitogenesis and carcinogenesis.

Asbestos increases mammalian AP-endonuclease gene expression, protein levels, and enzyme activity in mesothelial cells.

Only two DNA repair enzymes, DNA polymerase beta and O6-methylguanine-DNA methyltransferase, have been shown to be inducible in mammalian cells by genotoxic agents. We show here that crocidolite asbestos induces the DNA repair enzyme, apurinic/apyrimidinic (AP)-endonuclease, in isolated mesothelial cells, the progenitor cells of malignant mesothelioma. Asbestos at nontoxic concentrations of 1.25 and 2.5 microg/cm2 significantly increased AP-endonuclease mRNA and protein levels as well as enzyme activity (P < 0.05) in a dose-dependent manner in rat pleural mesothelial cells. These increases were persistent from 24 to 72 h after initial exposure to fibers. Changes were not observed with glass beads, a noncarcinogenic particle. Confocal scanning laser microscopy showed that AP-endonuclease was primarily localized in the nucleus but also in mitochondria. Our data are the first to demonstrate the inducibility of AP-endonuclease by a human class I carcinogen associated with oxidant stress in normal cells of the lung.

Role of extracellular signal-regulated protein kinases in apoptosis by asbestos and H2O2.

Stimulation of cell signaling cascades by oxidants may be important in the pathogenesis of pulmonary and pleural diseases. Here, we demonstrate in rat pleural mesothelial cells that apoptotic concentrations of crocidolite asbestos and H2O2 induce phosphorylation and activation of extracellular signal-regulated protein kinases (ERK). Activation of c-jun-NH2-terminal protein kinases (JNK)/stress-activated protein kinases was also observed in response to H2O2. In contrast, asbestos caused more protracted activation of ERK without JNK activation. Both H2O2- and asbestos-induced activation of ERK was abolished by catalase. Moreover, chelation of surface iron from crocidolite fibers or addition of N-acetyl-L-cysteine prevented ERK activation and apoptosis by crocidolite, indicating an oxidative mechanism of cell signaling. The MEK1 inhibitor PD-98059 abrogated asbestos-induced apoptosis, confirming a causal relationship between ERK activation and apoptosis. These results suggest that distinct cell-signaling cascades may be important in phenotypic responses elicited by oxidant stresses.

Simultaneous triple fluorescence detection of mRNA localization, nuclear DNA, and apoptosis in cultured cells using confocal scanning laser microscopy.

We describe a multifluorescence labeling technique for simultaneous detection of mRNA, nuclear DNA, and apoptosis in cultured cells. Digoxigenin-labeled cRNA probes were used to study proto-oncogene expression in rat pleural mesothelial cells undergoing apoptosis following exposure to crocidolite asbestos or hydrogen peroxide (H2O2). Hybridized cRNA probe was detected by immunolocalization with an anti-digoxigenin monoclonal primary and fluorophore-conjugated anti-mouse secondary antibody. Cells undergoing apoptosis were simultaneously identified by the TdT-mediated biotin-dUTP nick-end labeling (TUNEL) method and a streptavidin-conjugated far-red fluorophore, and nuclear DNA was stained with oxazole yellow dimer (YOYO-1). With confocal scanning laser microscopy, we demonstrated increased c-jun mRNA expression within the cytoplasm of both TUNEL-positive and non-apoptotic cells following exposure to either crocidolite asbestos or H2O2. Thus, this technique represents a useful in vivo approach for evaluating apoptosis-associated gene expression with confocal scanning laser microscopy.

Differential induction of c-fos, c-jun, and apoptosis in lung epithelial cells exposed to ROS or RNS.

Reactive oxygen (ROS) or nitrogen (RNS) species can affect epithelial cells to cause acute damage and an array of pulmonary diseases. The goal of this study was to determine patterns of early response gene expression and functional end points of exposure to nitric oxide (NO.), H2O2, or peroxynitrite (ONOO-) in a line of rat lung epithelial (RLE) cells. Our focus was on c-fos and c-jun protooncogenes, as these genes play an important role in proliferation or apoptosis, possible end points of exposure to reactive metabolites in lung. Our data demonstrate that NO. generated by spermine 1,3-propanediamine N-14-[1-(3-aminopropyl)-2-hydroxy-2-nitrosohydrazino]-butyl] or S-nitroso-N-acetylpenicillamine as well as H2O2 cause increased c-fos and c-jun mRNA levels, nuclear proteins, and complexes binding the activator protein-1 recognition sequence in RLE cells. These agents also lead to apoptosis and increased membrane permeability. In contrast, exogenously administered ONOO- or 3-morpholinosydnonimine do not induce protooncogenes or apoptosis in RLE cells despite nitration oftyrosines. We conclude that ROS and RNS can elicit distinct molecular and phenotypic responses in a target cell of pulmonary disease.

Novel cell imaging techniques show induction of apoptosis and proliferation in mesothelial cells by asbestos.

We developed in situ dual-fluorescence detection techniques for measuring apoptosis and proliferation simultaneously in single dishes of cells. The deoxyribonucleic acid (DNA)-specific labeling method, terminal deoxynucleotidyl transferase (TdT)-mediated deoxyuridine triphosphate nick-end labeling (TUNEL), first was used in conjunction with a 4',6-diamidino-2-phenylindole (DAPI) counterstain to detect and measure morphologic characteristics of apoptotic rat pleural mesothelial (RPM) cells isolated from Fischer 344 rats and exposed to 300 microM hydrogen peroxide (H2O2). For this purpose, 100 TUNEL-positive nuclei were measured while being viewed with DAPI counterstaining for area, perimeter, longest diameter, and average diameter, using imaging software and an image-collection apparatus. We then exposed cells to a range of concentrations of crocidolite asbestos and putative apoptotic and mitogenic agents. Exposure to crocidolite asbestos (5 microg/cm2) caused a striking dose-dependent apoptotic response at 24 h, 48 h, and 72 h. The nonfibrous crocidolite analogue riebeckite failed to induce apoptosis. At 24 h, tumor necrosis factor-alpha (TNF-alpha) (10 ng/ml) caused an increase in apoptotic nuclei. A second method, utilizing an antibody to 5'-bromodeoxyridine (BrdU) and oxazole yellow homodimer (YOYO), showed a dose-dependent increase in proliferation occurring in cells exposed to asbestos (5 microg/cm2) at 48 h and 72 h. In addition, increased numbers of rat pleural mesothelial (RPM) cells exposed to 12-O-tetradecanoylphorbol-13-acetate (TPA), TNF-alpha, and epidermal growth factor (EGF) exhibited incorporation of BrdU at these time points, although total numbers of cells per unit area were unchanged. Results indicate a dynamic balance between apoptosis and increased DNA synthesis after exposure of mesothelial cells to asbestos.

Inhibition of protein kinase C prevents asbestos-induced c-fos and c-jun proto-oncogene expression in mesothelial cells.

Asbestos and the phorbol ester tumor promoter, 12-O-tetradecanoylphorbol-13-acetate (TPA), increase c-fos and c-jun mRNA levels and AP-1 DNA binding activity in rat pleural mesothelial (RPM) cells, a target cell of asbestos-induced mesotheliomas (N. H. Heintz et al., Proc. Natl. Acad. Sci. USA, 90: 3299-3303, 1993). Because protein kinase C (PKC) is the intracellular receptor of phorbol ester tumor promoters and asbestos is a putative tumor promoter in the respiratory tract, we hypothesized that PKC might play a critical role in asbestos-induced cell signaling pathways associated with regulation of proto-oncogenes. Using a panel of PKC antibodies, we identified PKC alpha as the major PKC isozyme in RPM cells. We then pretreated cells with phorbol ester dibutyrate to down-modulate PKC or with calphostin C, a specific PKC inhibitor, to determine if depletion of PKC alpha could block asbestos-induced c-fos/c-jun expression. Quantitation of Northern blots showed that fiber-associated c-fos/c-jun mRNA levels were significantly lower either after PKC alpha down-modulation or pretreatment with calphostin C. In addition, to determine whether tyrosine kinases also were involved in proto-oncogene activation by asbestos, tyrphostin AG82 or herbimycin A was added to RPM cells before exposure to asbestos. These inhibitors decreased crocidolite-induced c-fos but not c-jun levels, suggesting that tyrosine kinases have different regulatory roles in asbestos-induced c-fos versus c-jun signaling pathways. The ability to block induction of asbestos-induced proto-oncogene expression using pharmacological intervention may be important in prevention and treatment of asbestos-induced proliferative diseases including lung cancers, mesothelioma, and pulmonary fibrosis.

Asbestos causes translocation of p65 protein and increases NF-kappa B DNA binding activity in rat lung epithelial and pleural mesothelial cells.

The mechanisms of cell signaling and altered gene expression by asbestos, a potent inflammatory, fibrogenic, and carcinogenic agent, are unclear. Activation of the transcription factor, nuclear factor (NF)-kappa B, is critical in up-regulating the expression of many genes linked to inflammation and proliferation. Inhalation models of crocidolite- and chrysotile-induced inflammation and asbestosis were used to study the localization of p65, a protein subunit of the NF-kappa B transcription factor, in sham control rats and those exposed to asbestos. In addition, we investigated, using electrophoretic mobility shift analysis, whether in vitro exposure of rat lung epithelial cells and rat pleural mesothelial cells to asbestos increased binding of nuclear proteins, including p65, to the NF-kappa B DNA response element. Furthermore, translocation of p65 into the nucleus was determined by confocal microscopy. In comparison with sham animals, striking increases in p65 immunofluorescence were observed in airway epithelial cells of rats at 5 days after inhalation of asbestos. These increases were diminished by 20 days, the time period necessary for development of fibrotic lesions. In contrast, although inter-animal variability was observed, immunoreactivity for p65 was more dramatic in the interstitial compartment of asbestos-exposed rat lungs at both 5 and 20 days. Changes in p65 expression in pleural mesothelial cells exposed to asbestos in inhalation experiments were unremarkable. Exposure to asbestos also caused significant increases in nuclear protein complexes that bind the NF-kappa B consensus DNA sequence in both rat lung epithelial and rat pleural mesothelial cells. Using confocal microscopy, we observed partial nuclear translocation of p65 in rat pleural mesothelial cells exposed to asbestos. This partial response contrasted with the effects of lipopolysaccharide, which caused rapid and complete translocation of p65 from cytoplasm to nucleus. Our studies are the first to show the presence of the NF-kappa B system in lung tissue and evidence of activation in vitro and in vivo after exposure to a potent inflammatory, fibrinogenic, and carcinogenic environmental agent.

Patterns of inflammation, cell proliferation, and related gene expression in lung after inhalation of chrysotile asbestos.

Biochemical and molecular markers of inflammation, cell proliferation, and pulmonary fibrosis were studied in lungs and bronchoalveolar lavage preparations from Fischer 344 rats at time periods from 3 to 20 days after inhalation of two airborne concentrations (0.18 and 8.2 mg/m3 air) of chrysotile asbestos. Additional groups of animals were examined for lung histopathology and cell proliferation with an antibody to 5-bromo-2'-deoxyuridine after exposure to asbestos for 5 and 20 days and after 20 days of exposure followed by an additional 20 days in room air. Exposure to chrysotile at the higher concentration caused protracted increases in steady-state mRNA levels of manganese-containing superoxide dismutase and elevation in glyceraldehyde-3-phosphate dehydrogenase mRNA at 3 days, but levels of mRNAs encoding copper-zinc-containing superoxide dismutase, ornithine decarboxylase, and the proto-oncogene, c-jun were not statistically elevated from levels occurring in lung homogenates from sham control rats. Differential cell counts in bronchoalveolar lavage revealed an early infiltration of neutrophils that correlated with focal areas of increased cellularity and fibrosis in rat lungs at the higher concentrations of asbestos. However, elevations in lung hydroxyproline were not observed. Significant increases in epithelial cells of the bronchi, the interstitial compartment of the lung, and mesothelial cells incorporating 5-bromo-2'-deoxyuridine, an indication of DNA synthesis, were noted in the higher chrysotile group at 5 days, but labeling in all cell compartments was comparable with that occurring in sham controls at later time points. Indicators of inflammation, increased cell proliferation, and pulmonary fibrosis were not observed in the lungs of rats exposed to the lower concentration of chrysotile. Thus, results indicate that cellular and molecular markers of inflammation and proliferation in lung are dose-related and indicative of the histopathological development of asbestosis.

Asbestos induces nuclear factor kappa B (NF-kappa B) DNA-binding activity and NF-kappa B-dependent gene expression in tracheal epithelial cells.

Nuclear factor kappa B (NF-kappa B) is a transcription factor regulating expression of genes intrinsic to inflammation and cell proliferation--features of asbestos-associated diseases. In studies here, crocidolite asbestos caused protracted and dose-responsive increases in proteins binding to nuclear NF-kappa B-binding DNA elements in hamster tracheal epithelial (HTE) cells. This binding was modulated by cellular glutathione levels. Antibodies recognizing p65 and p50 protein members of the NF-kappa B family revealed these proteins in two of the DNA complexes. Transient transfection assays with a construct containing six NF-kappa B-binding DNA consensus sites linked to a luciferase reporter gene indicated that asbestos induced transcriptional activation of NF-kappa B-dependent genes, an observation that was confirmed by northern blot analyses for c-myc mRNA levels in HTE cells. Studies suggest that NF-kappa B induction by asbestos is a key event in regulation of multiple genes involved in the pathogenesis of asbestos-related lung cancers.

Induction of c-fos and c-jun proto-oncogene expression by asbestos is ameliorated by N-acetyl-L-cysteine in mesothelial cells.

Asbestos fibers cause dose-dependent, persistent increases in mRNA levels of c-jun and c-fos proto-oncogenes in rat pleural mesothelial (RPM) cells, the progenitor cells of asbestos-induced mesothelioma (N. Heintz, Y. M. W. Janssen, and B. T. Mossman. Proc. Natl. Acad. Sci. USA, 90: 3299-3303, 1993). Here we report that addition of N-acetyl-L-cysteine decreases asbestos-mediated induction of c-fos and c-jun mRNA levels in a dose-dependent fashion. Exposure of RPM cells to asbestos causes depletion of total cellular glutathione, a response that can be abolished by pretreatment with N-acetyl-L-cysteine. Pretreatment of cells with buthionine sulfoximine, an agent which diminishes glutathione pools, increases the magnitude of induction of c-fos and c-jun mRNA by asbestos. To determine whether asbestos-induced effects on proto-oncogene expression could be attributed to extracellular generation of active oxygen species (AOS), RPM cells were exposed to H2O2 or xanthine and xanthine oxidase, a generating system of AOS. These oxidant stresses did not decrease cellular glutathione levels nor alter mRNA levels of c-fos or c-jun. However, increased mRNA levels of manganese-containing superoxide dismutase and heme oxygenase were observed, indicating that RPM cells respond to AOS by increased expression of genes encoding antioxidant enzymes. These data indicate that the signaling pathways leading to c-fos/c-jun proto-oncogene induction by asbestos are not triggered directly by formation of extracellular AOS. However, intracellular thiol levels appear to influence the expression of c-fos and c-jun, suggesting a redox-sensitive component in the signaling cascade which modulates gene expression of c-fos and c-jun by asbestos.

Oxygen radicals and asbestos-mediated disease.

Asbestos fibers are potent elaborators of active oxygen species whether by reactions involving iron on the surface of the fiber, or by attempted phagocytosis of fibers by cell types resident in the lung. The link between production of active oxygen species and the pathogenesis of asbestos-mediated disease has been highlighted by studies outlined here exploring the use of antioxidant scavengers which inhibit the cytotoxic effects of asbestos both in vitro and in vivo. The use of antioxidant enzymes ameliorates the induction of certain genes necessary for cell proliferation, such as ornithine decarboxylase, implicating oxidants as causative factors in some abnormal cell replicative events. Based on these observations, antioxidant enzymes likely represent an important lung defense mechanism in response to oxidative stress. In addition, their gene expression in lung or in cells from bronchoalveolar lavage might be a valuable biomarker of chronic inflammation and pulmonary disease after inhalation of oxidants.

Induction of c-fos and c-jun proto-oncogenes in target cells of the lung and pleura by carcinogenic fibers.

To study mechanisms of cell proliferation by asbestos and nonasbestos fibers, we examined the effects of these agents on the mRNA levels of c-fos and c-jun and ornithine decarboxylase (ODC) in hamster tracheal epithelial (HTE) cells and rat pleural mesothelial (RPM) cells, the progenitor cells of bronchogenic carcinoma and mesothelioma, respectively. In comparison with crocidolite asbestos, increases in c-jun mRNA were less striking in HTE cells after exposure to man-made vitreous fiber-10 (MMVF-10) or refractory ceramic fiber-1 (RCF-1). No c-fos mRNA was detected in HTE cells after exposure to particulates, but exposure of HTE cells to H2O2 caused striking increases in c-fos and c-jun, which preceded increases in ODC mRNA. Increases in ODC mRNA were also observed in HTE cells after exposure to nonasbestos fibers, whereas only crocidolite asbestos caused elevations in ODC mRNA in RPM cells. In RPM cells, crocidolite and chrysotile asbestos caused increases in mRNA levels of both c-fos and c-jun. No increases in proto-oncogene induction were observed using MMVF-10 or RCF-1 at nontoxic concentrations (< or = 5 micrograms/cm2 dish). Moreover, erionite, a fiber extremely potent in the causation of mesothelioma in humans, caused more dramatic elevations in c-fos and c-jun. Nonfibrous particles (riebeckite, polystyrene beads) did not alter proto-oncogene expression in these cell types, suggesting that the fibrous geometry of particulates is critical in the induction of c-fos and c-jun.