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. Author manuscript; available in PMC: 2011 Mar 1.
Published in final edited form as: J Expo Sci Environ Epidemiol. 2009 Dec 30;21(2):123–132. doi: 10.1038/jes.2009.68

Table 1.

Summary of house-dust PAH measurements for nine PAHs.

Individual PAH Molecular
weight
Missing Below
detection
Percent
detected
Non-missing and
above detection
Concentration (ng PAH per g dust)
Min. Median Max.
Benzo(a)anthracenea,b,c 228 1 5 99.1% 577 <2 25 834
Chrysenea,b,c 228 1 0 100.0% 582 7 73 1547
Benzo(a)pyrenea,b,c 252 16 9 98.4% 558 <2 40 1948
Benzo(b)fluoranthenea,b,c 252 5 1 99.8% 577 <2 59 2450
Benzo(k)fluoranthenea,b,c 252 11 0 100.0% 572 3 40 814
Indeno(1,2,3-c,d)pyrenea,b,c 276 0 1 99.8% 582 <2 53 2371
Dibenzo(a,h)anthracenea,b,c 278 6 35 93.9% 542 <2 14 393
Coronened 300 25 8 98.6% 550 <4 94 636
Dibenzo(a,e)pyrened 302 5 4 99.3% 574 <4 27 713

PAH, polycyclic aromatic hydrocarbons.

a

Detection limit 2 ng per g dust.

b

Classified as probable human carcinogen by US Environmental Protection Agency.

c

Used in EPA’s 2002 National-Scale Air Toxics Assessment outdoor PAH model.

d

Detection limit 4 ng per g dust.