Smoke Exposure Analysis
|Smoke exposure from a smoke plume from an uncontrolled fire contains particles and gases as it leaves the combustion zone. The gases include water vapor, carbon dioxide, carbon monoxide, nitrogen oxides if the combustion zone is hot enough, and volatile organic compounds. The volatile organic compounds begin as gases but much of those materials will condense or sorb onto the particles in the plume. Some will stay in the gaseous state. The particles from combustion include charred and coked fuel, pyrolyzed associated materials, and agglomerates of “soot” and condensed organic compounds. The distribution of the materials associated with the plume at the receptor site will depend on the size of the particles, their sticking coefficient relative to the surface they contact, distance from the fire, and time of transit from the combustion zone to the receptor. The particles from the smoke plume leave a signature at the receptor site that can often be used to determine the impact of the fire at that location. The signature at the receptor site will change with time so sampling at the receptor site soon after exposure is most desirable, though some evidence of exposure may persist for years.
The materials covered here are related to uncontrolled fires and not controlled combustion sources. Emissions from internal combustion and diesel engines, boilers of all types, and smoking of tobacco or other plants are not included here. Emissions from fireplaces, wildfires, house fires, industrial fires, field burning, and yard waste fires are included. Wildfires include forest fires and brush fires.
Backdrafting in the fireplace or a leaking chimney will emit materials from the fire in the fireplace into the living zone of the building. Fireplace emissions are dominated by spalled coked wood cells and a relative absence of other charred plant material. The intent of burning wood in a fireplace is to consume all of the core of the wood. This is distinct from a wildfire that burns the outside of the plant and tends to leave the charred core. Fireplace debris is deficient in pyrolyzed phytoliths and burnt clay compared to forest fire smoke. Burning waste materials in the fireplace will add to the complexity of the emissions but will not add phytoliths or burnt clay.
Wildfires create strong winds and updrafts that carry large amounts of burnt soil, charred bark, charred wood, charred leaves, other charred plant material, pyrolyzed phytoliths, and other charred biologicals in their plume. With forest fires and brush fires, the plants burn from the outside in rather than from the inside out, as in a fireplace. As a result phytolith rich bark generally provides a strong source for pyrolyzed phytoliths. The type and frequency of phytolith will depend on the fuel at the location of the fire. Fire retardant aerosol particles may also be present as part of the assemblage.
House fire particles tend to be dominated by charred Douglas fir or Pine, high hydrocarbon content soot agglomerates from burning plastics and synthetic fibers, charred paint, and soot coated glass fiber. The agglomerated soot tends to be absent in wildfires, fireplace emissions, field burning, and the backyard burning of leaf and plant trimming.
Fire retardant spheres can generally be distinguished from red spray paint spheres by the larger crystals and lower vehicle content of the fire retardant. The vehicle content of most paints is about 20% but gel in the fire retardant is about 5%. The mineral filler in spray paint tends to be quite small while the crystals in fire retardant grow as the water evaporates and tend to be much larger than the pigment (iron oxide). Most of the fire retardant used for wildfires is pigmented with red iron oxide (hematite) so other colors of spray paint won’t interfere.
Smoke damage contains a particle signature of the source. House fires, forest fires, brush fires, fireplace smoke, industrial fires, cigarettes, trucks, kitchen fires, etc. all leave a characteristic signature.
We can identify the source and if the environment (i.e home, office, school) has been impacted by smoke from that particular source.
For more information please contact us.
SMOKE EXPOSURE ANALYSIS RATES
Tapelift Analysis ……………………………10 Days $360.00 (Per Sample Site)
Expedited (5 days) $560.00
Deposit each Sample in separate plastic sandwich bags. Label each sample according to where it was taken.
Please remember to include your name and e-mail or home address.
For more sampling instructions refer to “Sampling Methods“.