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HEXAVALENT
CHROMIUM
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Welding
Welding refers to the use
of any electric or gas welding or cutting equipment. Over 500,000
U.S. workers regularly perform welding or torch cutting operations.
Another 2 million perform these operations intermittently. These
employees may be at risk for exposure to hexavalent chromium and many
other hazardous substances in the fumes from these operations.
There are numerous ways that welding or cutting can produce fumes
containing hexavalent chromium.
Fumes
Welding joins or cuts
apart metal using intense heat from either a gas fired flame or electric
arc. This heat can bring a metal to above its boiling point.
This superheating converts small metal particles into metal vapor.
Fumes are formed when the vapor cools and condenses back into particles.
Fumes may be visible or invisible. Welding smoke is an example of
visible fumes. Regardless if the fumes can be seen particles can
still be present.
Particles
Metal particles in welding
fumes can come from several sources and can vary in size from 0.00 µm - 20
µm.
These sources include,
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the base metal
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coatings, residues or
paint
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electrode material
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flux material
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filler metal
The boiling point for chromium
is 2672 oC (4841 oF).
Since the heat of welding or cutting can exceed 3000 oC (5432
oF) chromium particles can easily vaporize and then condense into
fumes.
Chemical
Reaction
Chromium particles generated
in welding fumes can undergo a chemical reaction to become hexavalent
chromium particles. There are many variables that can play a part in
this chemical reaction. These variables include,
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electrical current
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voltage
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electrode diameter
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droplet size
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surface temperature
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evaporation rate
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shielding gas
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arc length
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microspatter
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ultraviolet radiation
Detection
Monitoring for exposure from
welding fumes is accomplished by drawing air from a worker's breathing zone
through a filter. The filter is then processed in a lab to determine
the amount of hexavalent chromium and other metals, such as lead and
cadmium, to which the employee was exposed. This is expressed as an
8-hour time weighted average (TWA). While important this monitoring
alone will not provide information on the origin of the hexavalent chromium.
The origin of most particles in welding fumes is the metal being cut or
welded and/or the paint, coatings or other substances on the surface of the
metal. This also applies to metal that is coated or contaminated with
hexavalent chromium compounds. Yet as explained above chromium
particles generated during welding can be changed to hexavalent chromium
particles.
Questions?
How can you determine which of
the many factors contribute to the chemical reaction that forms hexavalent
chromium in a specific welding/torching operation?
Why would you want to know
this?
Explanation
OSHA has established a permissible exposure limit (PEL) of 5 micrograms of
hexavalent chromium per cubic meter of air (5 µg/m3) as an 8-hour
TWA. OSHA has also established a PEL of 50 µg/m3 of
lead as an 8-hr TWA. A look at the periodic table of elements shows
the atomic weight (rounded up) for chromium is 52 while the atomic weight
for lead (Pb) is 207. So the atomic weight for lead is approximately
four times that of chromium.
Now take a scenario where
there is both lead and chromium in a metal alloy or a paint or coating.
Torch cutting or welding will generate particles of both metals in the
fumes. According to the atomic weights, at a minimum, there should be
four times the amount of lead than chromium in the fumes. If the
chromium is converted to hexavalent chromium the same proportion should
apply.
It is then possible to
simultaneously have an exposure below the PEL for lead (<50 µg/m3) yet above
the PEL for chromium (5 µg/m3) [Example: particulate composition
in torch/welding fumes of 40 µg/m3 of lead could also have 1/4 that amount
of chromium or 10 µg/m3]. It is also possible to have particulate
composition for lead that is below the OSHA action level for that metal (30
µg/m3 ) and still be above the PEL for chromium [Example:
particulate composition in torch/welding fumes of 28 µg/m3 of
lead could also have 1/4 that amount of chromium or 7 µg/m3]
Answers
We have answered the second question first.
"Why would you want to know
this?
It is possible to have exposure levels below the PEL or Action Level for
lead yet above the PEL or Action Level for hexavalent chromium. You
could then be faced with needing respirator protection for the hexavalent
chromium level yet not for the lead. Reducing the hexavalent chromium
exposure could eliminate the need for respirator use. Yet to do this
it may be necessary to first determine where the hexavalent chromium is
coming from.
This brings us to the first
question.
"How can you determine which of the many factors contribute to the chemical
reaction that forms hexavalent chromium in a specific welding/torching
operation?"
HSR Consulting
has researched this issue extensively. We have partnered with a
national testing lab to offer a specific type of air monitoring that could
provide these answers. This monitoring is conducted simultaneously
with the OSHA required monitoring.
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Hexavalent Chromium Standard
Final Rule
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Initial Requirements Effective
November 27,
2006
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INDUSTRY-SPECIFIC
STANDARDS
General Industry
Construction
Shipyards
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