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ro IV. Sampling Parameters:
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Ca5 Parameter Sample Type Indoor/Outdoor Rationale for Selection
Asbestos breathing ht., VO known use in building construction, evidence of O
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time-weighted presence in early air sampling and in seeded dust, o
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air known inhalation carcinogen 3
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on hold?TotaI Suspended breathing ht.. O Characterize amount of airborne dust that is
particulates Continuous, real inhalable (i 100 pm aerodynamic diameter)
time, air
PMlOandPi f2.5 breathing ht.. O Characterize the amount of airborne dust that is
Continuous, real respirable
time, air
Inhalable (<l 00pm)* breathing ht., I/O To determine relative amounts of each fraction present
thoraci c (< 10pm)* time-weighted, and to have each fraction analyzed for silica, gypsum,
respirable (<2.5pm)* air mica, fiberglass, and calcite to qualitatively determine potential
hazards.
Respirable breathing ht., I/O Known component of concrete, evidence of
crystalline silica time-weighted, presence in some settled dust samples, known
air inhalation carcinogen.
pH*’ dust VO Concrete has a high pH, if dust has a high pH, it may be
contributing to reported symptoms of ENT irritation
Asbestos” dust I/O Determine if asbestos is present in dust
gypsum,silica, mica, dust I/O Associated with building materials (concrete,
fiberglass, calcite** drywall) and known to be irritating to ENT
magnesium dust I/O May act as a tracer for WTC-related dust, levels found in
metals analysis of settled dust from 16,000-29,000 ppm
’ results will be used to better understand the potential for ENT and respiratory irritation, and possibly for determining the possibility of acute/chronic health
problems. Results will assist in providing information/recommendations to the public (e.g., what is contributing to irritation, how to reduce exposures)
” to assist in characterizing dust that can become airborne (re-entrainment of settled dust that may be the source of continuing air contamination), and
to make recommendations for outdoor dust remediation
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