NYC 9/11 Public Portal Document
Air sampling was conducted to determine the actual levels of fibers, dust, and crystalline
minerals in the air at the time of settled surface dust sampling. Where feasible, these results
are correlated to the settled surface dust results.
/. Fibers in Air
Samples for airborne fibers were first analyzed by phase contrast microscopy (PCM) to
count all fibers present according to the National Institute for Occupational Safely and
Health (NIOSH) Method 7400 counting rules. Phase contrast microscopy identifies fibers
based on size and shape, but not the specific type of fiber. Therefore, the fibers seen by
PCM include asbestos fibers as well as other fibers, such as textiles, fiberglass, and
cellulose that might be present. Any sample with airborne fibers above the highest PCM
levels found in the comparison locations was re-analyzed by transmission electron
microscopy (TEM) and scanning electron microscopy (SEM). The TEM methodology can
distinguish what types of fibers are in a sample, particularly asbestos fibers. The SEM
method identifies SVF. Some fibers present in the settled dust of the area may become
suspended in the air and be present in the air sample.
a. Indoor Air
Fiber levels in air are expressed as the number of fibers in each cubic centimeter (cc) of
air or fibers per cc (fZee). Low levels of fibers were found in the comparison areas above
59th Street homes, where fiber levels ranged from less than 0.001 fee (<0.001 f/cc) to
0.003 fee. Because no asbestos was detected in the settled surface dust of the comparison
areas above 59th Street, these fibers are not likely to have been asbestos. SEM analysis
showed they were not SVF. Figure 7 shows all airborne fiber levels determined by PCM in
the lower Manhattan area with respect to ihe fiber levels found in the comparison areas
above 59th Street. These data represent all fibers found according to the analytical method
used (NIOSH 7400) and are not specific to asbestos or SVF.
The majority of the lower Manhattan air samples from indoor areas without asbestos in the
dust were within the range of fibers found in the comparison areas above 59th Street
(<0.001 to 0.003 f/cc). Six of these air samples (from 3 common areas and 3 residences)
had higher levels of fibers in air than the comparison areas above 59th Street (Table 8).
Four of these areas had measurable levels of SVF in the settled surface dust. All six-air
samples were re-analyzed by TEM to determine if the fibers present included asbestos
fibers. Asbestos fibers were not found in these six air samples (Table 8). A third analysis
was done by SEM to determine if SVF fibers were present in those air samples from areas
with SVF in the settled surface dust. SVF fibers were found in three of these air samples at
concentrations from 0.000037 f/cc to 0.000255 f/cc. Although SEM is a more sensitive
method, detecting thinner fibers than PCM, reported SVF levels were well below the PCM
method detection limit of O.OOlf/cc. SVF fiber concentrations in the comparison areas
above 59th Street ranged from none detected to 0.000087 fee. Although air samples from
comparison areas above 59th Street were not re-analyzed by TEM, no asbestos fibers were
noted on the subsequent SEM analysis for SVF. Therefore the six air samples that had total
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