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o IV. Sampling Parameters: CT
o rarameter Sample Type Indoor/Outdoor Rationale for Selection o'
cn breathing ht., VO known use in building construction, evidence of ■D
Ca5 Asbestos O
ro
tn time-weighted presence in early air sampling and in settled dust, 3.
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air known inhalation carcinogen 91
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Total Suspended breathing ht.. o Characterize amount of airborne dust that is c
particulates Continuous, real inhalable (<100 pm aerodynamic diameter) 3
CD
time, air
PMlOand PM2.5 breathing ht.. O Characterize the amount of airborne dust that is
Continuous, real respirable
time, air
Inhalable (< 100 pm)’ breathing ht., VO To determine relative amounts of each fraction present
thoracic (<10pm)’ time-weighted, and to have each fraction analyzed for silica, gypsum,
respirable (<4pm)’ air asbestos, mica, fiberglass, and calcite to qualitatively
determine potential hazards.
Respirable breathing ht., VO 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 VO Determine if asbestos is present in dust
Delete? gypsum, mica, dust VO Associated with building materials (concrete,
fiberglass, calcite” drywall) and known to be irritating to ENT
magnesium dust VO 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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