Effects of quartz, airborne particulates and fly ash fractions from a waste incinerator on elastase release by activated and nonactivated rabbit alveolar macrophages

Effects of heavy metal ions on resting and antigen-activated CD4(+) T cells

Heavy metal environmental pollutants increase susceptibility of affected individuals to bacterial and viral infections, but the mechanisms responsible for this effect are not known. We established cellular in vitro systems to identify molecular targets for the action of heavy metal ions. We used two model systems to determine the effects of heavy metal ions on antigen-induced T lymphocyte responses. The first system was representative of primary antigen responses and utilized CD4(+) primary T lymphocytes derived from DO.11.10 T cell receptor transgenic mice. The second system represented a memory T cell phenotype and utilized the CD4(+) T helper 1 clone, pGL2. We measured the effects of the four heavy metals cadmium, lead, mercury, and vanadium on cytokine and proliferation responses by purified CD4(+) T cell to antigenic stimulation. Cytokine responses were differentially affected by lead and vanadium at concentrations that did not affect T cell proliferation in response to antigen. We also determined whether the metal ions induced apoptotic cell death. Mercury induced apoptosis at concentrations as low as 0.5 microM, whereas cadmium required a concentration of 100 microM. Lead (maximal concentration tested was 200 microM) and vanadium (100 microM) did not induce apoptosis. The results suggested that the different heavy metal ions differentially affected antigen-stimulated responses in T helper cells. These in vitro systems can now be applied to test whether heavy metal ions alter antigen-induced T cell signal transduction pathways in CD4(+) T helper cells.

Increase of bovine alveolar macrophage superoxide anion and hydrogen peroxide release by dusts of different origin

The release of reactive oxygen intermediates (ROI) from bovine alveolar macrophages (BAM) after stimulation with heavy metal-containing dusts was investigated. BAM were obtained by postmortem lavages of bovine lungs. The dusts were collected from waste incineration, sewage sludge incineration, an electric power station, and from two different factories. Three quartz dusts were used as heavy metal-free controls. The dusts were fractionated by sieving and sedimentation and analyzed by electron microscopy, atomic absorption spectrometry (AAS), and atomic emission spectrometry with inductively coupled plasma (AES-ICP). Incubation of BAM with the dusts (12.5-1000 micrograms/ml medium) led to concentration-dependent increases in ROI release. The secretion of ROI was already seen after 15 min and lasted throughout the experiment up to 90 min, with the exception of a waste incinerator ash, which contained the highest contents of some heavy metals and where the release of ROI ceased after 60 min. We suggest that this dust exhibits simultaneously stimulating and inhibiting effects. The ratio of the secreted O2- and H2O2 varied, depending on the dust being investigated. The release of hydrogen peroxide correlated best, in descending order, with the content of iron, manganese, chromium, vanadium, and arsenic in the dusts.

A rabbit lung model for testing reaction to inhaled dental restorative particles

A study was designed to test the outcome of the deposition of particles of plastic composite dental restorative material in rabbit lungs. Grinding and polishing these restorations in situ produces some particles in the 0.5- to 10-microns size range that easily enter and remain in human lungs and are associated with industrial lung disease. Dental restorative plastic material was ground in the laboratory, suspended in saline solution, and injected transtracheally into four New Zealand white rabbits. Two control rabbits were similarly injected with saline solution transtracheally. Twenty-four hours later, the rabbits were injected with 1 mCi of 67Ga citrate intravenously and subsequently reanesthetized for scanning. Baseline scans were obtained in the six animals prior to the injection of the test particles. Positive gallium scans were obtained 72 h after the administration of particulate material in the four test rabbits. The gallium scans of the control rabbits remained no different from baseline. The study was repeated one month later. The animals were killed seven days after the last gallium scan. Light microscopy and transmission electron microscopy of the lungs of the test animals showed foci of chronic inflammation around particles of the restorative material. Particles were in vacuoles within alveolar macrophages and also free in interstitium. Control animals had normal histologic conditions. Silver amalgam and gold dental restorations have years of clinical use but the new plastic composite restorative materials are rapidly being introduced into human clinical dental practice. Normal use involves polymerization, grinding, and polishing of the material within the mouth. The chronic inflammation in the lungs of rabbits indicates a need to test dental restorative material for lung biocompatibility before further, extensive clinical use.