Hexavalent Chromium Exposure Factors from Welding Operations

By Jerome E. Spear, CSP, CIH

Chromium has been used commercially in the U.S. for more than 100 years. Chromium occurs mainly in three forms, described by its valence state. Metallic chromium (Cr[0]) is a steel-gray solid with a high melting point that is used to make steel and other alloys. Chromium metal does not occur naturally but is produced from chrome ore. Trivalent chromium (Cr[III]) occurs naturally in rocks, soil, plants, animals, and volcanic emissions. Cr(III) is used industrially as brick lining for high-temperature industrial furnaces and to make metals, metal alloys, and chemical compounds. Cr(III) is also believed to be an essential nutrient but in only trace amounts. Most diets tend to be deficient in Cr(III). Hexavalent chromium (Cr[VI]) occurs through the oxidation of chromium compounds with lower valence states. Cr(VI) is considered the greatest occupational and environmental health concern, as it is the most toxic. Other valence states are unstable so they are less common. They will most likely be quickly converted to either Cr(III) or Cr(VI).

This article summarizes common welding processes, relative fume generates, and the primary Cr(VI) exposure factors from welding operations.

Hexavalent Chromium in Welding Fumes

Chromium metal is found in stainless steel and many low-alloy materials, electrodes, and filler materials. The chromium that is present in electrodes, welding wires, and base materials is in the form of Cr(0). Therefore, welders do not ordinarily work with materials containing Cr(VI). But rather, the high temperatures created by welding oxidize chromium in steel to the hexavalent state. The majority of the chromium found in welding fume is typically in the form of Cr2O3 and complex compounds of Cr(III). Some of the metal oxides in its hexavalent form are also in the form of CrO3. Pure CrO3 is extremely unstable; however, other metal oxides, especially alkali metals, tend to stabilize Cr(VI) compounds (Fiore, 2006).

Welding fume is a complex mixture of metal oxides. Fumes from some processes may also include fluorides. The predominant metal fume generated from mild, low alloy, and stainless steel welding is iron oxide. Oxides of manganese are also typically present. Fumes from stainless steel and some low-alloy steel welding also typically contain chromium and nickel. Chromium is typically not intentionally added to mild steels or mild steel consumables but due to the use of scrap steel in the steel production process, some low levels of chromium metal may be present. However, in most mild steel welding, the exposure limits for fume constituents other than Cr(VI) (such as manganese) will be exceeded before the PEL for Cr(VI) is reached (Fiore, 2006).

Common Welding Processes

Different welding processes have different fume generation rates (FGR). Having a basic understanding of the welding processes and their relative fume generation rates is important in order to assess the risk of exposures to welding fumes and gases. An overview of common welding processes and their relative fume generation rates is provided below:

Shielded Metal Arc Welding (SMAW, “stick welding”) is commonly used for mild steel, low alloy steel, and stainless steel welding. In SMAW, the electrode is held manually, and the electric arc flows between the electrode and the base metal. The electrode is covered with a flux material, which provides a shielding gas for the weld to help minimize impurities. The electrode is consumed in the process, and the filler metal contributes to the weld. SMAW can produce high levels of metal fume and fluoride exposure; however, SMAW is considered to have little potential for generating ozone, nitric oxide and nitrogen dioxide gases.

Gas Metal Arc Welding (GMAW) is also known as metal inert gas (MIG) welding. GMAW is typically used for most types of metal and is faster than SMAW. This process involves the flow of an electric arc between the base metal and a continuously spool-fed solid-core consumable electrode. Shielding gas is supplied externally, and the electrode has no flux coating or core. Although GMAW requires a higher electrical current than SMAW, GMAW produces fewer fumes since the electrode has no fluxing agents. However, due to the intense current levels, GMAW produces significant levels of ozone, nitrogen oxide, and nitrogen dioxide gases.

Fluxed-Cored Arc Welding (FCAW) is commonly used for mild steel, low alloy steel, and stainless steel welding. This welding process has similarities to both SMAW and GMAW. The consumable electrode is continuously fed from a spool and an electric arc flows between the electrode and base metal. The electrode wire has a central core containing fluxing agents and additional shielding gas may be supplied externally. This welding process generates a substantial amount of fume due to the high electrical currents and the flux-cored electrode. However, FCAW generates little ozone, nitric oxide, and nitrogen dioxide gases.

Gas Tungsten Arc Welding (GTAW) is also known as tungsten inert gas (TIG) welding. GTAW is used on metals such as aluminum, magnesium, mild steel, stainless steel, brass, silver and copper-nickel alloys. This technique uses a non-consumable tungsten electrode. The filler metal is fed manually and the shielding gas is supplied externally. High electrical currents are used, which causes this process to produce significant levels of ozone, nitric oxide, and nitrogen dioxide gases. However, GTAW produces very little fumes.

Submerged Arc Welding (SAW) is another common welding process used to weld thick plates of mild steel and low alloy steels. In this welding process, the electric arc flows between the base metal and a consumable wire electrode; however, the arc is not visible since it is submerged under flux material. This flux material keeps the fumes low since the arc is not visible. There are also little ozone, nitric oxide and nitrogen dioxide gases that are generated. The major potential airborne hazard with SAW is the fluoride compounds generated from the flux material.

Factors Affecting Fume Generation Rates (FGR)

The primary sources of information when determining the components likely to be in the fume is the Safety Data Sheet (SDS) and/or the manufacturer’s technical data sheet of the consumable electrode/wire. About 90 to 95 percent of the fumes are generated from the filler metal and flux coating/core of consumable electrodes (Lyttle, 2004). Since the base metal weld pool is much cooler than the electrode tip, the base metal contributes only a minor amount of the total fumes. However, the base metal may be a significant factor of the fume exposure if the metal or surface residue contains a highly toxic substance (such as chromate-containing coatings, lead-based paint, etc.).

In addition to the welding process, studies have shown that the FGR is also influenced by the following factors:

Electrical current: In general, the fume generation rate is exponentially proportional to the current.
Arc voltage: The fume generation rate generally increases when the arc voltage increases.
Electrode diameter: In general, a small diameter electrode has a higher FGR than a large diameter electrode because of the differences in voltage and current. However, the voltage is typically adjusted up when larger diameter electrodes are used. Therefore, when considering the typical increase in voltage for larger electrodes, the electrode diameter has only a modest effect, if any, on the fume generation rate in practical applications.
Electrode angle: The angle of the electrode to the workpiece has a slight (but unpredictable) affect on the fume generation rate.
Shielding gas: In gas-shielding arc welding, the FGR tends to be greater when 100% carbon dioxide (CO₂), as compared to argon, is used as the shielding gas.
Speed of welding: As the welding rate increases, the fume generation rate obviously increases.
GMAW transfer mode: GMAW has three transfer modes. Short-circuit GMAW is where the wire actually touches the puddle. It results in the lowest heat input so also has the lowest fume levels. But its use is limited to the sheet metal industry due to its low penetration resulting in a high defect rate on heavy, industrial welding. Globular transfer mode is where the droplets are greater than the diameter of the electrode and has moderate heat input. Spray transfer mode is where the diameter of the droplets are smaller than the diameter of the wire and has the highest heat input and highest fume levels. Both spray mode and globular transfer are the most difficult to weld out of position.
Steady or pulsed current GMAW: Technology has advanced to power sources that have pulsing capabilities for GMAW applications. GMAW pulse current operates in spray mode for a short period of time (e.g., one droplet per pulse) then the wire cools off. This allows GMAW to operate at a lower temperature per unit time. Studies have shown that utilizing a pulsing current generates fewer fumes than under steady current welding processes, all else remaining equal.

In general, FCAW produces the greatest fume generation rate (for mild steel) and is closely followed by SMAW. However, when welding chromium-containing steel, Cr(VI) contained in the fumes generated from SMAW tends to be greater than Cr(VI) generated from FCAW. Alkali metals, such as sodium and potassium, stabilize Cr(VI). These metals and are often SMAW electrode coatings and may also be present in FCAW flux (Fiore, 40), which may explain why Cr(VI) concentrations from SMAW operations are often higher than Cr(VI) concentrations from FCAW. GMAW tends to have a moderate relative fume generation rate. GTAW and SAW are inherently low fume generating processes.

Other ancillary process (such as air arc gouging and plasma arc cutting) can also generate a significant amount of fumes and gases (e.g., carbon monoxide, ozone, etc.) due to the high electrical current and arc voltage associated with these processes. Potential exposures to not only the operator but also other personnel in the work area can be significant from such processes, especially in enclosed and confined spaces. Few research studies are available that examine potential Cr(VI) exposure associated with air arc gouging and plasma cutting operations.

Cr(VI) Exposure Factors

Welding fume exposure tends to be highly variable due to several exposure factors. These factors should be considered when assessing potential exposures to Cr(VI). The primary Cr(VI) exposure factors are described below.

Welding process: As discussed above, the welding process used has a significant effect on the fume generation rate.
Chromium content and flux ingredients in the consumable: Stainless steel and chromium alloys typically contain between 11.5% and 30% chromium, by weight. Obviously, as the chromium content in the consumable increases, the amount of Cr(VI) emitted from the welding process will likely increase. Other ingredients in the electrode may also have some affect in stabilizing Cr(VI) resulting in higher Cr(VI) concentrations.
Chromate coatings on base material: Chromates may be contained in pigments in coatings and paints to provide corrosion resistant properties. When performing repair work on painted structures, be sure to analyze bulk samples of the coating to ensure the paint or coating does not contain chromates.
Welding rate: High welding rates obviously increases the fumes generated. However, information pertaining to an individual’s welding or production rate is seldom accurately and consistently measured in exposure monitoring efforts. Consider utilizing an arc timer during exposure monitoring to accurately collect and document actual welding time, which may prove useful in explaining unusually high or low exposure monitoring results and/or in better categorizing similar exposure groups (SEGs).
Relative welding position: The welding position plays a significant role in welding fume exposure primarily due to the plume’s path of travel. Welding in a down-flat position (such as a tank bottom or where the workpiece is positioned below the welder’s waist) tends to present the highest potential fume exposures. Welding in a horizontal direction (such as when welding the girth seam of a tank) can also create relatively high fume exposures depending on plume’s path of travel in relation to the welder’s breathing zone. Welding in a vertical direction (such as a vertical seam of a tank shell) tends to have the lowest potential fume exposure since the welder’s breathing zone is typically not in the plume’s travel path and the plume stays close to the heat-affected zone as it naturally rises.
Local exhaust ventilation (LEV): Studies have shown that the use of LEV can lower fume exposure. However, the effectiveness of LEV depends on several factors, including work practices and proper maintenance of the LEV units.
Welding environment (inside or enclosed space): Welding inside buildings or an enclosed space presents the potential for an accumulation of fumes that may increase exposures not only to the welder but also other personnel inside the building or enclosed space.
General/dilution ventilation and natural air currents: Although general/dilution ventilation is often used when welding indoors or inside enclosed spaces, local exhaust ventilation is preferred for fume control since it attempts to capture fumes at the source. The effect on the plume’s travel path is unpredictable when using general ventilation.
Other welding (or ancillary/allied processes) performed in the area: Finally, the amount of welding or other related activities (such as air arc gouging and/or plasma cutting) may obviously affect potential exposures to welding fumes and Cr(VI) inside enclosed spaces, especially if the space is poorly ventilated.

References

Fiore, S. R. (2006). Reducing exposure to hexavalent chromium in welding fumes. Welding Journal, 38-42.

Lyttle, K. A. (2004, March/April). Optimizing consumable selection increases productivity, decreases fumes. Gases & Welding Distribution, 45-47.

Spear, J. E. (2004). Welding Fumes: Protect Your Employees and Your Company. Tools of the Trade, 3(4), 10-13.

Spear, J. E. (2010, September). Welding Safety: Assessing and Controlling Exposures to Hexavalent Chromium. American Society of Safety Engineers, 22-31.

Wallace, M., & Fischbach, T. (2002). Effectiveness of local exhaust for reducing welding fume exposure during boiler rehabilitation. (D. Tharr, Ed.) Applied Occupational and Environmental Hygiene, 17(3), 145-151.

Wallace, M., Landon, D., Song, R., & Echt, A. (2001). A field evaluation of the effect of pulsed arc welding technique on reducing worker exposures. Applied Occupational and Environmental Hygiene, 16(2), 93-97.