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Chrysotile asbestos stimulates platelet-derived growth factor-AA production by rat lung fibroblasts in vitro: evidence for an autocrine loop.

We have investigated the mitogenic and chemotactic role of platelet-derived growth factor (PDGF) in pulmonary fibrogenesis induced by chrysotile asbestos. Since fibroblasts phagocytize asbestos in the lung interstitium, we have sought to learn whether the fibers alter the production of PDGF-like molecules by rat lung fibroblasts or induce mitogenesis of these fibroblasts in vitro. Conditioned medium as well as cell lysates from fibroblasts exposed to asbestos contained approximately 4-fold more PDGF than unexposed cells as detected by Western blot. Two distinct molecular weight forms of PDGF (36 and 18 kD) were detected by Western blotting. We postulate that these PDGF-like molecules are homologues of human PDGF-AA since we could not detect any PDGF in a sensitive enzyme immunoassay that recognized only PDGF-BB and PDGF-AB. Furthermore, PDGF-A chain mRNA was readily detected by Northern analysis, whereas PDGF-B chain mRNA was not detected by conventional Northern analysis. However, message amplification using a reverse transcriptase polymerase chain reaction allowed detection of the B-chain message. A significant dose-dependent mitogenic effect of asbestos was found by using both a cell proliferation assay and nuclear labeling with bromodeoxyuridine when fibroblasts were exposed under serum-free conditions. This mitogenesis induced directly by asbestos was blocked almost entirely with an anti-PDGF antibody that neutralized all three PDGF isoforms. Thus, these data support our hypothesis that an autocrine loop for PDGF-AA is operative in vitro following exposure to asbestos in lung fibroblasts, and we suggest that this signaling pathway could be significant in the pathogenesis of pulmonary fibrosis.

Animals↗

Asbestos fibers and interleukin-1 upregulate the formation of reactive nitrogen species in rat pleural mesothelial cells.

Nitric oxide radical (.NO) and peroxynitrite anion (ONOO-) have been implicated in lung inflammation and may be important in pleural injury. The present study was undertaken to determine the effects of asbestos exposure and cytokine stimulation on .NO and ONOO- production by rat pleural mesothelial cells. Accordingly, rat parietal pleural mesothelial cells were cultured for 2 to 72 h with or without 50 ng/ml of recombinant interleukin-1beta (IL-1beta) in the presence (1.05 to 8.4 microg/cm2) or absence of crocidolite or chrysotile asbestos fibers. The effects of asbestos were compared with those of carbonyl iron, a nonfibrogenic particulate. Mesothelial cell messenger RNA (mRNA) expression of the inducible form of .NO synthase (iNOS), assessed with the reverse transcription-polymerase chain reaction (RT-PCR), increased progressively from 2 to 12 h in IL-1beta-containing cultures. Nitrite (NO2-), the stable oxidation product of .NO in mesothelial cell conditioned medium, was assayed through the Griess reaction. Both types of asbestos fibers (chrysotile > crocidolite) upregulated the formation of NO2- in mesothelial cells costimulated with IL-1beta in a concentration-dependent and time-dependent fashion. In contrast, carbonyl iron did not upregulate NO2- formation in IL-1beta-stimulated cells. Both types of asbestos fibers also induced iNOS protein expression and the formation of nitrotyrosine in mesothelial cells and greatly induced the formation of nitrate (NO3-), a surrogate marker of ONOO- formation, in IL-1beta-stimulated cells. However, the effects of chrysotile were notably greater than those of crocidolite. These findings may have significance for the induction of pleural injury by asbestos fibers.

Animals↗

Phagocytosis of crocidolite asbestos induces oxidative stress, DNA damage, and apoptosis in mesothelial cells.

Phagocytosis of asbestos fibers may be a necessary step for asbestos-induced injury to mesothelial cells, but this has not been established because quantification of fiber uptake is difficult and ways to increase fiber phagocytosis without also increasing total dose were not available. We quantified phagocytosis by counting intracellular fibers after removing adherent fibers with trypsin; we selectively increased fiber phagocytosis by coating crocidolite asbestos fibers with the adhesive serum protein vitronectin (VN), which we have shown increases fiber uptake via integrins. We measured various aspects of asbestos-induced cytotoxicity: intracellular oxidation by the shift of fluorescence of cells loaded with an oxidative probe, DNA strand breakage by the alkaline unwinding ethidium bromide fluorometric assay, apoptosis by annexin V binding and by nuclear morphology, and cell-cycle progression. We found that, compared with control fibers or particles, asbestos increased intracellular oxidation, DNA strand breakage, and apoptosis. Selective increases in fiber uptake by VN-coating of the fibers further increased the oxidation, DNA strand breakage, and apoptosis, and induced a cell-cycle arrest in G2/M. Selective decreases in fiber uptake by cytochalasin or by integrin blockade with RGD peptides inhibited several of these measures of injury. We conclude that phagocytosis is important and perhaps necessary for asbestos-induced injury to mesothelial cells.

Animals↗

Matrix metalloproteinases promote inflammation and fibrosis in asbestos-induced lung injury in mice.

Inhalation of asbestos fibers causes pulmonary inflammation and eventual pulmonary fibrosis (asbestosis). Although the underlying molecular events are poorly understood, protease/antiprotease and oxidant/antioxidant imbalances are believed to contribute to the disease. Implicated in other forms of pulmonary fibrosis, the matrix metalloproteinases (MMPs) have not been examined in asbestosis. We therefore hypothesized that MMPs play a pathogenic role in asbestosis development. Wild-type C57BL/6 mice were intratracheally instilled with 0.1 mg crocidolite asbestos, causing an inflammatory response at 1 d and a developing fibrotic response at 7, 14, and 28 d. Gelatin zymography demonstrated an increase in MMP-9 (gelatinase B) during the inflammatory phase, while MMP-2 (gelatinase A) was profoundly increased in the fibrotic phase. Immunohistochemistry revealed MMP-9 in and around bronchiolar and airspace neutrophils that were often associated with visible asbestos fibers. MMP-2 was found in fibrotic regions at 7, 14, and 28 d. No increases in RNA levels of MMP-2, MMP-9, or MMP-8 were found, but levels of MMP-7, MMP-12, and MMP-13 RNA did increase at 14 d. The MMP inhibitors, TIMP-1 and TIMP-2, were also increased at 7-28 d after asbestos exposure. To confirm the importance of MMP activity in disease progression, mice exposed to asbestos were given daily injections of the MMP inhibitor, GM6001. MMP inhibition reduced inflammation and fibrosis in asbestos-treated mice. Collectively, these data suggest that MMPs contribute to the pathogenesis of asbestosis through effects on inflammation and fibrosis development.

Animals↗

Evidence of a role for mesothelial cell-derived interleukin 8 in the pathogenesis of asbestos-induced pleurisy in rabbits.

Although acute asbestos-induced pleurisy is characterized by an influx of neutrophils, the identity of the factors that attract these cells to the pleural space and the source of the factors are unknown. We found that instillation of crocidolite asbestos into the pleural space of rabbits led to the appearance in pleural liquid of chemotactic activity for neutrophils, and that this chemotactic activity was inhibited significantly by a neutralizing antibody to human interleukin 8 (IL-8). Cultured rabbit pleural mesothelial cells incubated with crocidolite asbestos also released chemotactic activity for neutrophils, which was inhibited significantly by the anti-IL-8 antibody. To determine whether rabbit pleural mesothelial cells synthesize IL-8, we generated a probe for rabbit IL-8 mRNA by amplifying cDNA prepared from stimulated pleural mesothelial cells using the polymerase chain reaction (PCR) and primers based on homologous sequences in human and sheep IL-8 cDNAs. Homology-based PCR yielded a single cDNA fragment with a nucleotide sequence 88% identical to that of a corresponding region of human IL-8 cDNA. With the radiolabeled PCR product as a probe, we demonstrated rapid induction of IL-8 mRNA expression in pleural mesothelial cells exposed to asbestos. As expected, tumor necrosis factor-alpha also led to the appearance of IL-8 in the rabbit pleural space and stimulated cultured pleural mesothelial cells to synthesize and release IL-8. We conclude that asbestos directly stimulates pleural mesothelial cells to synthesize IL-8 and that mesothelial cell-derived IL-8 may play an important role in mediating asbestos-induced pleural inflammation.

Animals↗

Asbestos-induced pulmonary toxicity: role of DNA damage and apoptosis.

Asbestos causes asbestosis and various malignancies by mechanisms that are not clearly defined. Here, we review the accumulating evidence showing that asbestos is directly genotoxic by inducing DNA strand breaks (DNA-SB) and apoptosis in relevant lung target cells. Although the exact mechanisms by which asbestos causes DNA damage and apoptosis are not firmly established, some of the implicated mechanisms include the generation of iron-derived reactive oxygen species (ROS) as well as reactive nitrogen species (RNS), alteration in the mitochondrial function, and activation of the death receptor pathway. We focus on the accumulating evidence implicating ROS. DNA repair mechanisms have a key role in limiting the extent of DNA damage. Recent studies show that asbestos activates DNA repair enzymes such as apurinic/apyrimidinic endonuclease (APE) and poly (ADP-ribose) polymerase (PARP). Asbestos-induced neoplastic transformation may result in the setting where DNA damage overwhelms DNA repair in the face of a persistent proliferative signal. Strategies aimed at limiting asbestos-induced oxidative stress may reduce DNA damage and, as such, prevent malignant transformation.

Animals↗

The asbestos war.

That asbestos is still being sold despite overwhelming evidence linking it to debilitating and fatal diseases is testament to the effectiveness of a campaign, spear-headed by Canadian interests, to promote a product already banned in many developed countries. Blessed by government and commercial support, asbestos apologists have implemented a long-term coordinated strategy targeting new consumers in Asia, the Far East and Latin America. At industry-backed "conferences" and on government-funded junkets, they spin a web of deceit, telling all who will listen that "chrysotile (white asbestos) can be used safely." The fact that Canada exports over 95% of all the chrysotile it mines suggests that while chrysotile is supposedly safe enough for foreigners, it is not safe enough for Canadians. Asbestos victims in many countries have struggled to gain public recognition of the human cost of asbestos use. In recent years, nongovernmental organizations working with these groups have created a global anti-asbestos virtual network; with the commitment and support of thousands of "virtual members," this network challenges industry's propaganda and exposes the forces that support its cynical attempt to offload this dangerous substance on developing countries.

Asbestos↗

Asbestos problems yet to explode in Korea.

Although asbestos mining and manufacture has occurred in Korea since the 1920s, it was not until the 1980s that the broader social democratic movement heightened public awareness of the health problems associated with exposure to asbestos. The first systematic national survey of asbestos-related diseases was conducted in 1993. In that year, the first case of asbestos-related disease was compensated by the government. This long-delayed recognition of asbestos-related disease took place in a country that already had more than 100 asbestos factories. About 40 to 50 mesothelioma cases are reported annually through the Korean Cancer Registry. Nonetheless, only six mesothelioma cases have ever been referred to the government for workers' compensation. Lung cancer is the fastest growing cancer in Korea. Over the last 15 years, mortality from lung cancer has more than tripled. Among all these lung cancer cases, only 12 have been recognized as occupational in origin and compensated accordingly.

Asbestos↗

The phase-out of asbestos in the Australian manufacturing environment.

The importation of raw asbestos and asbestos-containing products into Australia was banned at the end of 2003. Despite a high incidence of asbestos-related disease, it was the threat of industrial action that eventually persuaded Australian governments to impose a ban. Significant government-sponsored reports in 1990 and 1999 had not convinced politicians that a phase-out of chrysotile was feasible. An impediment for government and industry was the risk of unemployment of asbestos workers. The threat of future asbestos exposures remains for maintenance workers. An example is given of the need for continued vigilance of workers and their unions before the manufacturing environment can be relatively asbestos-free.

Asbestos↗

[Effects of asbestos on the cell cycle of PHA-stimulated human peripheral blood lymphocytes].

It is well known that persons exposed to asbestos display systemic immunological alterations: impaired lymphocyte response to PHA, the appearance of autoantibodies and elevation of the serum immunoglobulin level. The authors intend in this report to determine whether asbestos fibres (crocidolite, chrysotile and amosite) have any effect on the cell cycle of human lymphocytes after PHA stimulation. Peripheral blood mononuclear (PBM) cells were incubated with 10 micrograms/ml PHA for 2 days. After PHA stimulation, a decrease in the percentage of cells in the G0 phase and an increase in that of cells in the G1A, G1B and S phases was observed. When asbestos fibres or titanium dioxide (TiO2) was added to the culture dish at the beginning of the experiment, the progression of the cell cycle was inhibited only by asbestos fibres, in which case the percentage of cells in the G0 phase was significantly increased, while those of cells in the G1B and S phases were significantly decreased. The experiment for determining the critical period for inhibition of blastogenic response revealed that no inhibition was demonstrable when crocidolite fibre was added at 24 hr after PHA stimulation. Although the mechanisms of asbestos-fibre-mediated suppression remain to be clarified, these results showed that asbestos fibres act at an early stage (G0 phase) of the cell cycle and suppress the PHA stimulation of PBM cells.

Asbestos↗

Increased risk of malignant mesothelioma of the pleura after residential or domestic exposure to asbestos: a case-control study in Casale Monferrato, Italy.

The association of malignant mesothelioma (MM) and nonoccupational asbestos exposure is currently debated. Our study investigates environmental and domestic asbestos exposure in the city where the largest Italian asbestos cement (AC) factory was located. This population-based case-control study included pleural MM (histologically diagnosed) incidents in the area in 1987-1993, matched by age and sex to two controls (four if younger than 60). Diagnoses were confirmed by a panel of five pathologists. We interviewed 102 cases and 273 controls in 1993-1995, out of 116 and 330 eligible subjects. Information was checked and completed on the basis of factory and Town Office files. We adjusted analyses for occupational exposure in the AC industry. In the town there were no other relevant industrial sources of asbestos exposure. Twenty-three cases and 20 controls lived with an AC worker [odds ratio (OR) = 4.5; 95% confidence interval (CI), 1.8-11.1)]. The risk was higher for the offspring of AC workers (OR = 7.4; 95% CI, 1.9-28.1). Subjects attending grammar school in Casale also showed an increased risk (OR = 3.3; 95% CI, 1.4-7.7). Living in Casale was associated with a very high risk (after selecting out AC workers: OR = 20.6; 95% CI, 6.2-68.6), with spatial trend with increasing distance from the AC factory. The present work confirms the association of environmental asbestos exposure and pleural MM, controlling for other sources of asbestos exposure, and suggests that environmental exposure caused a greater risk than domestic exposure.

Aged↗

Mechanisms of the genotoxicity of crocidolite asbestos in mammalian cells: implication from mutation patterns induced by reactive oxygen species.

Asbestos is an important environmental carcinogen in the United States and remains the primary occupational concern in many developing countries; however, the underlying mechanisms of its genotoxicity are not known. We showed previously that asbestos is a potent gene and chromosomal mutagen in mammalian cells and that it induces mostly multilocus deletions. Furthermore, reactive oxygen species (ROS) are associated with the mutagenic process. To evaluate the contribution of ROS to the mutagenicity of asbestos, we examined their generation, particularly hydrogen peroxide, and compared the types of mutants induced by crocidolite fibers with those generated by H(2)O(2 )in human-hamster hybrid (A(L)) cells. Using confocal scanning microscopy together with the radical probe 5,6 -chloromethy-2,7 -dichlorodihydrofluorescein diacetate (CM-H(2)DCFDA), we found that asbestos induces a dose-dependent increase in the level of ROS among fiber-treated A(L) cells, which is suppressed by concurrent treatment with dimethyl sulfoxide. Using N-acetyl-3,7-dihydroxyphenoxazine (Amplex Red reagent) together with horseradish peroxidase, we further demonstrated that there was a dose-dependent induction of H(2)O(2) in crocidolite-treated A(L) cells. The amount of H(2)O(2 )induced by asbestos reached a plateau at a dose of 6 microg/cm(2). Concurrent treatment with catalase (1,000 U/mL) inhibited this induction by 7- to 8-fold. Mutation spectrum analysis showed that the types of CD59(-) mutants induced by crocidolite fibers were similar to those induced by equitoxic doses of H(2)O(2). These results provide direct evidence that the mutagenicity of asbestos is mediated by ROS in mammalian cells.

Animals↗

Assessment of autoimmune responses associated with asbestos exposure in Libby, Montana, USA.

Systemic autoimmune responses are associated with certain environmental exposures, including crystalline particles such as silica. Positive antinuclear antibody (ANA) tests have been reported in small cohorts exposed to asbestos, but many questions remain regarding the prevalence, pattern, and significance of autoantibodies associated with asbestos exposures. The population in Libby, Montana, provides a unique opportunity for such a study because of both occupational and environmental exposures that have occurred as a result of the mining of asbestos-contaminated vermiculite near the community. As part of a multifaceted assessment of the impact of asbestos exposures on this population, this study explored the possibility of exacerbated autoimmune responses. Age- and sex-matched sets of 50 serum samples from Libby and Missoula, Montana (unexposed), were tested for ANA on HEp-2 cells using indirect immunofluorescence. Data included frequency of positive tests, ANA titers, staining patterns, and scored fluorescence intensity, all against known controls. Serum immunoglobulin A (IgA), rheumatoid factor, and antibodies to extractable nuclear antigen (ENA) were also tested. The Libby samples showed significantly higher frequency of positive ANA and ENA tests, increased mean fluorescence intensity and titers of the ANAs, and higher serum IgA, compared with Missoula samples. In the Libby samples, positive correlations were found between ANA titers and both lung disease severity and extent of exposure. The results support the hypothesis that asbestos exposure is associated with autoimmune responses and suggests that a relationship exists between those responses and asbestos-related disease processes.

Asbestos↗

Concentration and size of asbestos in water supplies.

A review of the results of over 1500 asbestos analyses from U.S. water supplies suggests that the majority of water consumers are not exposed to asbestos concentrations in their drinking water over 1 x 10(6) fibers per liter. There are, however, some populations that are exposed to waterborne asbestos concentrations over 10 x 10(6) fibers per liter caused by natural erosion, mine processing wastes, waste pile erosion, corrosion of asbestos cement pipe, or disintegration of asbestos tile roofs running into cisterns. The distribution of fiber sizes in the water is dependent on the source of the fibers. The average length of chrysotile fibers found in an asbestos cement distribution system was 4 micrometers, while the average fiber length of chrysotile fibers contributed to a water supply by natural erosion was 1 micrometer.

Asbestos↗

Use of quantitative analysis of urine to assess exposure to asbestos fibers in drinking water in the Puget Sound region.

An earlier epidemiologic and electron microscopy study of drinking water in the Everett area of Washington State indicated large numbers of naturally occurring chrysotile asbestos fibers in the water. The purpose of the present study was to determine whether significant numbers of asbestos fiber could be demonstrated in the urine of donors residing in that area for less than 3 yr and over 20 yr where the tapwater contained about 200 X 10(6) fibers/L. A control group was obtained from Seattle where the tapwater asbestos fiber content was 100 times less. Urine samples, filtered control water, tapwater samples, and additional controls were processed for transmission electron microscopy by the use of the Nuclepore membrane filter-Jaffe wick procedure. Interference by mucus in the urine was reduced by treatment with hydrogen peroxide. Samples were taken over a period of 21 months. At no time during this period did the asbestos content of the urine samples consistently exceed that of the control waters. There was a significant difference (p less than 0.05) in the asbestos content of urine samples from subjects with less than 3 yr residence times versus greater than 20 yr. Asbestos concentration in urine samples from Everett residents as a whole did not differ significantly from that in samples from Seattle residents. Variable degrees of chrysotile contamination of control water samples and of Nuclepore membrane filters presented a problem. At present, the data are inconclusive but would suggest no relationship between high concentrations of fibers in drinking water and the numbers estimated for voided urine.

Adult↗

Multiple mechanisms for the carcinogenic effects of asbestos and other mineral fibers.

Asbestos and other mineral fibers are carcinogenic to humans and animals but differ from many carcinogens in that they do not induce gene mutations. An understanding of these interesting human carcinogens, therefore, is an important problem in cancer research. Asbestos and other fibers induce predominantly two types of cancers: mesotheliomas and bronchogenic carcinomas. Fiber size is an important factor in the carcinogenic activity of these substances as has been shown for mesothelioma induction. For bronchogenic carcinomas, but not for mesotheliomas, a synergistic effect of asbestos exposure and cigarette smoke has been observed in humans. The mechanisms by which fibers alone versus fibers in concert with other carcinogens induce cancers are probably distinct. In addition to fiber dimensions, fiber durability and surface properties of fibers are important properties affecting carcinogenicity. Evidence exists that asbestos is a complete carcinogen, an initiator and a promoter. Multiple mechanisms must be operative to explain the diverse effects of mineral fibers. Although asbestos is inactive as a gene mutagen, there is now clear evidence that it induces chromosomal mutations (aneuploidy and aberrations) in a wide variety of mammalian cells including mesothelial cells. Asbestos also induces transformation of cells in culture including mesothelial cells and fibroblasts. A mechanism for cell transformation, which is dependent on fiber dimension, has been proposed. The fibers are phagocytized by the cells and accumulate in the perinuclear region of the cells. When the cell undergoes mitosis, the physical presence of the fibers interferes with chromosome segregation and results in anaphase abnormalities. The transformed cells show aneuploidy and other chromosome abnormalities.(ABSTRACT TRUNCATED AT 250 WORDS)

Animals↗

Increased focal adhesion kinase- and urokinase-type plasminogen activator receptor-associated cell signaling in endothelial cells exposed to asbestos.

Exposure of low-passage endothelial cells in culture to nonlethal amounts of asbestos, but not refractory ceramic fiber-1, increases cell motility and gene expression. These changes may be initiated by the fibers mimicking matrix proteins as ligands for receptors on the cell surface. In the present study, 1- to 3-hr exposures of endothelial cells to 5 mg/cm2 of chrysotile asbestos caused marked cell elongation and motility. However, little morphological change was seen when chrysotile was added to cells pretreated with either mannosamine to prevent assembly of glycophosphatidylinositol (GPI)-anchored receptors or with herbimycin A to inhibit tyrosine kinase activity. Affinity purification of GPI-anchored urokinase-type plasminogen activator receptor (uPAR) from chrysotile-exposed cells demonstrated that asbestos altered the profile of proteins and phosphoproteins complexed with this receptor. Tyrosine kinase activities in the complexes were also increased by asbestos. Immunoprecipitations with selective monoclonal antibodies demonstrated that both chrysotile and crocidolite asbestos increase kinase activities associated with p60 Src or p120 focal adhesion kinase (FAK). Further, chrysotile also changed the profile of proteins and phosphoproteins associated with FAK in intact cells. These data suggest that asbestos initiates endothelial cell phenotypic change through interactions with uPAR-containing complexes and that this change is mediated through tyrosine kinase cascades.

Animals↗

Pleural macrophage recruitment and activation in asbestos-induced pleural injury.

The pathogenesis of asbestos-induced pleural fibrosis is poorly understood. Moreover, there has been a long-standing controversy regarding the relative potential of different commercial types of asbestos to cause pleural disease. We postulated that inhaled asbestos fibers translocate to the pleural space where they stimulate the recruitment and activation of pleural macrophages. To test this hypothesis, and to determine whether there are differences between inhaled amphibole and serpentine asbestos, Fischer 344 rats were exposed by intermittent inhalation (6 hr/day for 5 days/week over 2 weeks) to either National Institute of Environmental Health Sciences (NIEHS) crocidolite (average concentration 7.55 mg/m3) or NIEHS chrysotile fibers (average concentration 8.51 mg/m3). Comparisons were made with sham-exposed rats. The rats were sacrificed at 1 and 6 weeks after the cessation of exposure. More pleural macrophages were recovered at 1 and 6 weeks after crocidolite and chrysotile exposure than after sham exposure. Small numbers of crocidolite fibers (approximately 1 per 4000 cells) were detected in the pleural cell pellet of one crocidolite-exposed rat by scanning electron microscopy. Pleural macrophage supernatants were assayed for production of nitric oxide (NO) (by the Griess reaction) and tumor necrosis factor alpha (TNF-alpha) (by an enzyme-linked immunosorbent assay method). Significantly greater amounts of NO as well as TNF-alpha were generated by pleural macrophages at 1 and 6 weeks after either crocidolite or chrysotile inhalation than after sham exposure. Conceivably, translocation of asbestos fibers to the pleural space may provide a stimulus for persistent pleural space inflammation, cytokine production, and the generation of toxic oxygen and nitrogen radicals. Enhanced cytokine secretion within the pleural space may in turn upregulate adhesion molecule expression and the synthesis of extracellular matrix constituents by pleural mesothelial cells. Thus, our findings may have significance for the development of asbestos-induced pleural injury.

Animals↗