Effects of different amosite preparations on macrophages, lung damages, and autoimmunity.

The underlying mechanisms of asbestos-related autoimmunity are poorly understood. As the size, surface reactivity, and free radical activity of asbestos particles are considered crucial regarding the health effects, this study aims to compare the effects of exposure to pristine amosite (pAmo) or milled amosite (mAmo) particles on lung damage, autoimmunity, and macrophage phenotype. Four months after lung exposure to 0.1 mg of amosite, BAL levels of lactate dehydrogenase, protein, free DNA, CCL2, TGF-ß1, TIMP-1, and immunoglobulin A of pAmo-exposed C57Bl/6 mice were increased when compared to fluids from control- and mAmo-exposed mice. Effects in pAmo-exposed mice were associated with lung fibrosis and autoimmunity including anti-double-strand DNA autoantibody production. mAmo or pAmo at 20 µg/cm2 induced a pro-inflammatory phenotype characterized by a significant increase in TNFα and IL-6 secretion on human monocyte-derived macrophages (MDMs). mAmo and pAmo exposure induced a decrease in the efferocytosis capacities of MDMs, whereas macrophage abilities to phagocyte fluorescent beads were unchanged when compared to control MDMs. mAmo induced IL-6 secretion and reduced the percentage of MDMs expressing MHCII and CD86 markers involved in antigen and T-lymphocyte stimulation. By contrast, pAmo but not mAmo activated the NLRP3 inflammasome, as evaluated through quantification of caspase-1 activity and IL-1ß secretion. Our results demonstrated that long-term exposure to pAmo may induce significant lung damage and autoimmune effects, probably through an alteration of macrophage phenotype, supporting in vivo the higher toxicity of entire amosite (pAmo) with respect to grinded amosite. However, considering their impact on efferocytosis and co-stimulation markers, mAmo effects should not be neglected. KEY MESSAGES: Lung fibrosis and autoimmunity induced by amosite particles depend on their physicochemical characteristics (size and surface) Inhalation exposure of mice to pristine amosite fibers is associated with lung fibrosis and autoimmunity Anti-dsDNA antibody is a marker of autoimmunity in mice exposed to pristine amosite fibers Activation of lung mucosa-associated lymphoid tissue, characterized by IgA production, after exposure to pristine amosite fibers Pristine and milled amosite particle exposure reduced the efferocytosis capacity of human-derived macrophages.

Sorption of nonpolar aromatic contaminants by chlorosilane surface modified natural minerals.

The efficacy of the surface modification of natural diatomite and zeolite material by chlorosilanes is demonstrated. Chlorosilanes used were trimethylchlorosilane (TMSCI), tert-butyldimethylchlorosilane (TBDMSCI), dimethyloctadecylchlorosilane (DMODSCI), and diphenyldichlorosilane (DPDSCI) possessing different headgroups and chemical properties. Silanol groups of the diatomite and zeolite were modified by chemical reaction with the chlorosilanes resulting in a stable covalent attachment of the organosilanes to the mineral surface. The alteration of surface properties of the modified material was proved by measurements of water adsorption capacity, total organic carbon (TOC) content, and thermoanalytical data. The surface modified material showed great stability even when exposed to extremes in ionic strength, pH, and to pure organic solvents. Sorption of toluene, o-xylene, and naphthalene from water was greatly enhanced by the surface modification compared to the untreated materials which showed no measurable sorption of these compounds. The enhanced sorption was dependent on the organic carbon content as well as on chemical characteristics of the chlorosilanes used. Batch sorption experiments showed that the phenyl headgroups of DPDSCI have the best affinity for aromatic compounds. Removal from an aqueous solution of 10 mg/L of naphthalene, o-xylene, and toluene was 71%, 60%, and 30% for surface modified diatomite and 51%, 30%, and 16% for modified clinoptilolite, respectively. Sorption data were well described by the Freundlich isotherm equation, which indicated physical adsorption onto the lipophilic surface rather than partitioning into the surface organic phase. The chlorosilane modified materials have an apparent potential for application in environmental technologies such as permeable reactive barriers (PRB) or wastewater treatment.

Tenascin and fibronectin expression in human mesothelial cells and pleural mesothelioma cell-line cells.

Fibronectin (Fn) and tenascin (Tn) are two major extracellular matrix (ECM) glycoproteins that may have important roles both in fibrotic lung diseases and in lung tumors. The significance of Fn and Tn in human pleural mesothelial cells and pleural diseases is unclear. Transformed human pleural mesothelial cells (Met5A), primary cultures of mesothelial cells, and cultured mesothelioma cell lines were investigated for Fn and Tn immunoreactivity. Mesothelial cells were exposed for 48 to 96 h to transforming growth factor-beta (TGF-beta), tumor necrosis factor-alpha (TNF-alpha), amosite asbestos fibers, or oxidants (H2O2 and menadione, a compound that auto-oxidizes to produce superoxide). Immunofluorescence and Western blotting with monoclonal anti-Fn and anti-Tn antibodies, and Northern blotting with a complementary DNA (cDNA) probe for Tn showed that mesothelial cells are capable of producing Fn and Tn. The mRNA level and immunoreactivity of Tn was enhanced by TGF-beta and TNF-alpha, whereas Fn was intensified only by TGF-beta. A wide range of amosite, H2O2, or menadione concentrations had no clear effect on Fn or Tn reactivity. Fn and Tn were present at low or undetectable concentrations in five of six mesothelioma cell lines, whereas the organization of Fn immunoreactivity in these cell lines was variable. Furthermore, results obtained with the tumor tissue of these same mesothelioma patients suggested that Fn and Tn expressions do not necessarily parallel either each other or results obtained with the cultured cells.

Asbestos-induced lung epithelial permeability: potential role of nonoxidant pathways.

Asbestos fibers are an important cause of lung fibrosis; however, the biological mechanisms are incompletely understood. The lung epithelium serves an important barrier function in the lung, and disrupting the epithelial barrier can contribute to lung fibrosis. Lung epithelial permeability is increased in patients with asbestosis, and asbestos fibers increase permeability across cultured human lung epithelium. However, the mechanism of this increased permeability is not known. Many of the biological effects of asbestos are postulated to be due to its ability to generate oxidants, and oxidants are known to increase epithelial permeability. However, we previously reported that altering the iron content of asbestos (important in oxidant generation) had no effect on its ability to increase permeability. For that reason, we undertook these studies to determine whether asbestos increases epithelial permeability through nonoxidant pathways. Both extracellular (H2O2) and intracellular (menadione) oxidants increase paracellular permeability across human lung epithelial monolayers. Extracellular catalase but not superoxide dismutase prevented increased permeability after both oxidant exposures. However, catalase offered no protection from asbestos-induced permeability. We next depleted the cells of glutathione or catalase to determine whether depleting normal cellular antioxidants would increase the sensitivity to asbestos. Permeability was the same in control cells and in cells depleted of these antioxidants. In addition to generating oxidants, asbestos also activates signal transduction pathways. Blocking protein kinase C activation did not prevent asbestos-induced permeability; however, blocking tyrosine kinase with tyrophostin A25 did prevent asbestos-induced permeability, and blocking tyrosine phosphatase with sodium vanadate enhanced the effect of asbestos. These data demonstrate that asbestos may increase epithelial permeability through nonoxidant pathways that involve tyrosine kinase activation. This model offers an important system for studying pathways involved in regulating lung epithelial permeability.

Effects of cigarette smoke and asbestos on airway, vascular and mesothelial cell proliferation.

In order to determine whether exposure to both cigarette smoke and asbestos leads to enhanced cell proliferation, and whether pleura cell proliferation reflects the presence of fibres at or near the pleura, rats were exposed to air (control), daily cigarette smoke, a single intratracheal instillation of amosite asbestos, or a combination of smoke and asbestos. Dividing cells were labelled with bromodeoxyuridine (BrdU) and animals were sacrificed at 1, 2, 7 or 14 days. Both cigarette smoke and asbestos produced increases in the labelling index of small airway wall, epithelial cells and pulmonary artery cells. In the small airways there was a brief marked positive synergistic interaction between these two agents, but synergism was not seen in the vessels. Cigarette smoke did not increase the labelling of mesothelial or submesothelial cells, whereas asbestos caused a persisting increase in mesothelial cell labelling. There was no correlation between the number of BrdU labelled mesothelial or submesothelial cells and the number of fibres touching the pleura, or located within 180 microns of the pleura. We conclude that the combination of cigarette smoke and asbestos exposure produces a complex set of interactions and has the potential to markedly increase cell proliferation in the parenchyma, an effect that may be important in both fibrogenesis and carcinogenesis. In contrast to the diminishing effects over time of a single dose of asbestos on cell proliferation in the small airways and vessels, the same dose of asbestos leads to sustained mesothelial cell proliferation. However, the latter process does not correlate with local accumulation of asbestos fibres.

Asbestos causes DNA strand breaks in cultured pulmonary epithelial cells: role of iron-catalyzed free radicals.

Asbestos causes pulmonary fibrosis and various malignancies by mechanisms that remain uncertain. Reactive oxygen species in part cause asbestos toxicity. However, it is not known whether asbestos-induced free radical production causes alveolar epithelial cell (AEC) cytotoxicity by inducing DNA strand breaks (DNA-SB). We tested the hypothesis that asbestos-induced AEC injury in vitro is due to iron-catalyzed free radical generation, which in turn causes DNA-SB. We found that amosite asbestos damages cultured human pulmonary epithelial-like cells (WI-26 cells) as assessed by 51Cr release and that an iron chelator, phytic acid (500 microM), attenuates these effects. A role for iron causing these effects was supported by the observation that ferric chloride-treated phytic acid did not diminish WI-26 cell injury. Production of hydroxyl radical-like species (.OH) was assessed based upon the .OH-dependent formation of formaldehyde (HCHO) in the presence of dimethyl sulfoxide. A variety of mineral dusts induced significant levels of .OH formation (nmol HCHO at 30 min: carbonyl iron, 85 +/- 21; amosite asbestos, 14 +/- 2; chrysotile asbestos, 7 +/- 1; titanium dioxide, 2.5 +/- 0.5). Phytic acid significantly diminished the asbestos-induced .OH production. DNA damage to AEC was assessed by the alkaline unwinding, ethidium bromide fluorometric technique. Hydrogen peroxide caused dose-dependent DNA-SB in WI-26 cells after a 30-min exposure period [50% effective dose (ED50): 5 microM] that was similar to other cell lines. Amosite asbestos induced dose-dependent DNA-SB in WI-26, A549, and primary isolated rat alveolar type II cells maintained in culture for 7-10 days (alveolar type I-like). Lower doses of amosite (0.5-5 micrograms/ml or 0.25-2.5 micrograms/cm2) caused significant WI-26 cell DNA-SB after prolonged exposure periods (> or = 2 days). Phytic acid ameliorated DNA damage in all three cultured AEC. There was a direct correlation between mineral dust-induced .OH production at 30 min and DNA-SB in WI-26 cells at 4 h (P < 0.0005). These data suggest that mineral dusts can be directly genotoxic to relevant target cells of asbestos, AEC. Furthermore, these results provide additional support for the premise that iron-catalyzed free radicals mediate asbestos-induced pulmonary toxicity.

DNA strand breaks following in vitro exposure to asbestos increase with surface-complexed [Fe3+].

Surface functional groups on silicate dusts complex iron cations which can cycle through reduction and oxidation states to generate free radicals. These oxidants have a capacity to produce DNA strand breaks and mutations which are primary events in cancer induction. A differential in the capacity of fibrous silicates to produce carcinoma is recognized with the amphiboles demonstrating a greater biologic effect than the serpentine fiber chrysotile. We tested the hypothesis that the differences in genotoxicity of these fibrous silicates correspond to varying concentrations of iron complexed to the surface. Relative to chrysotile, the amphibole fibers complexed greater amounts of iron cations from both inorganic and in vivo sources. Increased concentrations of surface-complexed iron were associated with greater oxidant generation, measured as thiobarbituric acid-reactive products of deoxyribose, and more covalently closed, circular DNA strand scission. These results indicate that genotoxic effects of these fibers may correspond to their capacity to complex iron at the surface.