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. 2011 Feb 12;17(1):57–121. doi: 10.1080/10807039.2010.534722

Table 2.

Recommended airborne (inhalation, ocular) pre-planning clearance goals for transit passengers as well as various airport employees and personnel for selected CWAs and TICs.a

Reasonable maximum clearance goals (mg/m3)
Alternative clearance goals (mg/m3)
CWA or TIC <8-h durationb exposure >8 but <24-h duration exposure
Tabun (GA) < 0.0010c < 0.0003e
Sarin (GB) < 0.0010c < 0.0003e
Soman (GD) and Cyclosarin (GF) < 0.00050c < 0.0002e
VX < 0.000071c < 0.000024e
Sulfur mustard (H/HD) < 0.008c < 0.003e
Hydrogen cyanide (AC) < 1.1d < 0.37e
Cyanogen chloride (CK) < 0.25f < 0.08f
Phosgene (CG) < 0.08g < 0.03g

aChemical formulae: tabun, C5H11N2O2P (NATO code GA); sarin, C4H10FO2P (NATO code GB); soman, C7H16FO2P (NATO code GD); cyclosarin, C7H14FO2P (NATO code GF); VX, C11H26NO2PS (NATO code VX); sulfur mustard, C4H8Cl2S (NATO code HD); hydrogen cyanide, HCN (NATO code AC); cyanogen chloride, CNCl (NATO code CK); phosgene, COCl2 (NATO code CG).

bMay also be used as appropriately protective and health-based vapor screening criteria for releasing items, equipment, and facilities that have not been exposed to liquid or heavy aerosol forms of the chemical of concern; these screening criteria would also be useful for evaluating non-porous items and surfaces that have undergone decontamination. If these vapor screening criteria are attained, such decontaminated items would not be expected to pose a vapor exposure hazard (DA 2008, Table C-5).

eProposed >8 but ≤24-h protective estimates presented for use in this analysis are derived by straight-line extrapolation from the 8-h AEGL-1 values and follow standard protocols (NRC/COT 2001).

fIn the absence of a previously derived CK exposure guideline comparable to AEGL-1, these estimates were calculated for use in the current assessment (see text for details of derivation. and Wood 1997). 8-h estimate is derived from experimental data with straight-line extrapolation to 24 h. This derivation is considered a reasonable approach given the absence of published AEGL-1 values for cyanogen chloride.

gIn the absence of a previously derived phosgene (agent CG) exposure guideline comparable to the AEGL-1, these estimates were calculated for use in the current assessment (see text for details of derivation). 8-h estimate is derived as 50% of 8-h AEGL-2 for phosgene (NRC/COT 2002), with straight-line extrapolation to 24 h. This derivation is considered a reasonable approach given the absence of published AEGL-1 values for phosgene.