Emissions of Chromium (VI) from Arc Welding

Abstract The presence of Cr in the +6 oxidation state (Cr[VI]) is still observed in ambient air samples in California despite steps taken to reduce emissions from plating operations. One known source of emission of Cr(VI) is welding, especially with high Cr-content materials, such as stainless steels. An experimental effort was undertaken to expand and update Cr(VI) emission factors by conducting tests on four types of arc-welding operations: gas-metal arc welding (GMAW), shielded metal arc welding (SMAW), flux-core arc welding, and pulsed GMAW. Standard American Welding Society hood results were compared with a total enclosure method that permitted isokinetic sampling for particle size-cut measurement, as well as total collection of the aerosol. The fraction of Cr(VI) emitted per unit mass of Cr electrode consumed was determined. Consistent with AP-42 data, initial results indicate that a significant fraction of the total Cr in the aerosol is in the +6 oxidation state. The fraction of Cr(VI) and total aerosol mass produced by the different arc welding methods varies with the type of welding process used. Self-shielded electrodes that do not use a shield gas, for example, SMAW, produce greater amounts of Cr(VI) per unit mass of electrode consumed. The formation of Cr(VI) from standard electrode wires used for welding mild steel was below the method detection limit after eliminating an artifact in the analytical method used.

[1]  Gael D. Ulrich,et al.  Fume Formation Rates in Gas Metal Arc Welding A new fume chamber design improves the accuracy of fume generation data , 1999 .

[2]  Jenny R. Roberts,et al.  Pulmonary Responses to Welding Fumes: Role of Metal Constituents , 2004, Journal of toxicology and environmental health. Part A.

[3]  S. Mortazavi,et al.  Control of exposure to hexavalent chromium and ozone in gas metal arc welding of stainless steels by use of a secondary shield gas. , 2002, The Annals of occupational hygiene.

[4]  Thomas A. Cahill,et al.  Composition of PM2.5 and PM10 Aerosols in the IMPROVE Network , 1997 .

[5]  I. Kennedy,et al.  The impact of chlorine on chromium speciation in a laminar diffusion flame , 2001 .

[6]  S. Mortazavi,et al.  THE EFFECTS OF WELDING PARAMETERS ON ULTRAVIOLET LIGHT EMISSIONS, OZONE AND Cr VI FORMATION IN MIG WELDING , 1997 .

[7]  K. Ashley,et al.  Determination of hexavalent chromium in industrial hygiene samples using ultrasonic extraction and flow injection analysis. , 1997, The Analyst.

[8]  S. Mortazavi,et al.  Control of occupational exposure to hexavalent chromium and ozone in tubular wire arc-welding processes by replacement of potassium by lithium or by addition of zinc. , 2002, The Annals of occupational hygiene.

[9]  C. Sioutas,et al.  SIZE DISTRIBUTION AND DIURNAL CHARACTERISTICS OF PARTICLE-BOUND METALS IN SOURCE AND RECEPTOR SITES OF THE LOS ANGELES BASIN , 2002 .

[10]  Graeme. Ogilvie,et al.  Pulsed arc welding , 2003 .

[11]  S. Solberg,et al.  Atmospheric Chemistry and Physics , 2002 .

[12]  J. Antonini,et al.  Health Effects of Welding , 2003, Critical reviews in toxicology.