5 shared non-person entities · 1 shared topics · similarity 0.951
machine-extracted · confidence unavailable · Check page ↗NYC-WTC_000209427
Label derived from the City's folder field. The City does not supply document titles.NYC-WTC_000209427–000209449
OCR status: ok · source: pdftotext
NYC 9/11 Public Portal Document
Region 1 ’s Technical Appendix for the Brookfield School System^® states the following:
The results ... of the fifty-one (51) Method D5755-95 samples were compared to the benchmark chosen by EPA based on the asbestos fiber levels found in ambient (outside) air measured by Transmission Electron Microscopy (TEM), within the range 0.01 - 0.045 fibers/structures per cubic centimeter (f/cc) [this is the same as structures per mitiiiiter, or s/mL]... In order to compare the benchmark levels from cubic centimeter(cc) to settled dust levels in square centimeter (cm2) and allowing for the aerodynamic properties of these fibers, a K-factormust be applied. After the application of the appropriate K-factor we calculated a benchmark of 45,000 structures per square centimeter (s/cm2).
EPA established benchmark levels of ambient (outside) air measured by Transmission Electron Microscopy (TEM) within the range 0.01 - 3.045 fibers/structures per cubic centimeter (f/cc)
More recent studies in which asbestos air and surface dust levels were measured by TEM have been used to calculate additional K-factors.. Based on these controlled studies for reentrainment of settled fibers into air, the K-factor of 10-6 [ten to the minus six, or 0.000001] was used. As shown in Section 7.0, the 0.045 f/cc corresponds to 45,000 s/cm2 after the application of the K- factor.
The problems with Region I's risk assessment are discussed below:
Region 1 misrepresentation of background air levels and safety levels
Region 1 knowing used a false value for the at'erage or background level of asbestos in “ambient” outside air for its risk assessment. The level of 0.045 s/mL came from the one, outlying highest level found in an early 1983 study of outside air.^’ There was actually a wide range of values, most of which showed no dehxtable asbestos whatsoever. This one high value of 0.045 s/mL was an outlier, the highest recorded. It could well have been measured near an asbestos mine or processing facility, or near a natural rock outcropping of an asbestos mineral deposit.
It is unconscionable for Region 1 to have used the 0.045 s/mL highest outlier value from the study. At a minimum, it should have used the mean (average) for all of the measurements, most of which showed no asbestos at all.
Since 1983, however, much more definitive studies with increased sensitivity have become available for background air levels. Region 1 should have used the peer reviewed level for ambient outside air fi-om these more recent sIndies established by the Agency for Toxic Substances and Disease Registry (ATSDR) of the Centers for Disease Control (CDC). The ATSDR is an authoritative source for this infonnation for EPA, and is funded through EPA statutes to develop this information in a Toxicological Profile for Asbestos.^* The early 1983 study used by Region 1 was not even mentioned by the ATSDR.
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NYC-WTC_000209439
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