Pulmonary toxicity and extrapulmonary tissue distribution of metals after repeated exposure to different welding fumes.

Welders are exposed to fumes with different metal profiles. The goals of this study were to compare lung responses in rats after treatment with chemically different welding fumes and to examine the extrapulmonary fate of metals after deposition in the lungs. Rats were treated by intratracheal instillation (0.5 mg/rat, once a week for 7 weeks) with gas metal arc-mild steel (GMAW-MS) or manual metal arc-hardsurfacing (MMAW-HS) welding fumes. Controls were treated with saline. At 1, 4, 35, and 105 days after the last treatment, lung injury and inflammation were measured, and elemental analysis of different organs was determined to assess metal clearance. The MMAW-HS fume was highly water-soluble and chemically more complex with higher levels of soluble Mn and Cr compared to the GMAW-MS fume. Treatments with the GMAW-MS fume had no effect on toxicity when compared with controls. The MMAW-HS fume induced significant lung damage early after treatment that remained elevated until 35 days. Metals associated with each fume sample was cleared at different rates from the lungs. Mn was cleared from the lungs at a faster rate and to a greater extent compared to the other metals over the 105-day recovery period. Mn and Cr in the MMAW-HS fume translocated from the respiratory tract and deposited in other organs. Importantly, increased deposition of Mn, but not other metals, was observed in discrete brain regions, including dopamine-rich areas (e.g., striatum and midbrain).

Pneumotoxicity and pulmonary clearance of different welding fumes after intratracheal instillation in the rat.

The objectives of this study were to compare different welding fumes in regard to their potential to elicit lung inflammation or injury and to examine possible mechanisms whereby welding fumes may damage the lungs. Fume was collected on filters from conventional spray [mild steel (MS-SPRAY) or stainless steel (SS-SPRAY) electrode wire] or pulsed current [mild steel (MS-PULSE) electrode wire] gas-shielded metal arc welding. Rats were given one of the three welding fume samples by intratracheal instillation (1.0 mg/100 g body wt). Other rats received a relatively inert dust (iron oxide), a pneumotoxic dust (crystalline silica), or a vehicle control (saline). Bronchoalveolar lavage (BAL) was performed 1, 7, 14, and 35 days postinstillation, and indicators of pulmonary damage [cellular differential, albumin, as well as, tumor necrosis factor-alpha (TNF-alpha), interleukin-1 beta (IL-1 beta), lactate dehydrogenase, and beta-n-acetyl glucosaminidase release] were assessed. One day postinstillation, some evidence of lung inflammation (more neutrophils) was observed for all particle groups, while increased BAL TNF-alpha and IL-1 beta were observed only in the SS-SPRAY and silica groups. By 14 days, lungs appeared normal among the MS-SPRAY, MS-PULSE, and iron oxide groups. At 14 and 35 days postinstillation, elevated pulmonary responses persisted for the animals exposed to silica and the SS-SPRAY welding fume. By 35 days, however, the SS-SPRAY group approached control levels, while the injury induced by silica increased. Using magnetometric estimates of welding fumes, we observed that MS-SPRAY fume was cleared from the lungs at a faster rate than the SS-SPRAY particles. We have demonstrated that the SS-SPRAY fume has more pneumotoxicity than MS fumes. This difference may reflect a greater retention of the SS-SPRAY particles in the lungs and different elemental composition of the fume. The SS-SPRAY fume also had enhanced release of TNF-alpha and IL-1 beta from lung cells soon after fume instillation. In contrast, we saw no influence of the power supply on particle size, composition, or toxicity.