Table 1.
Summary statisticsa for NCCLS and FOX study dust samplesb, compared to results from similar studies. All concentrations in ng/g. GM/GSD = geometric mean/geometric standard deviation
Northern California Childhood Leukemia Study 2010 (n=59) |
Firefighter Occupational Exposure Study Southern California 2010-2011 (n = 27) |
Boston, MA Area Homes (Stapleton and others 2008) 2006 (n=7-10) |
San Francisco Bay Area, CA Homes (Dodson and others 2012); 2006 (n=16) |
San Francisco Bay Area, CA Homes(Dodson and others 2012) 2011 (n=16) |
Vancouver, BC, homes (Shoeib and others 2012) 2007-2008 n=116 |
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% Detect |
Blankc (ng, n=7) |
GM | GSD | Mina | Median | Max | % Detect |
Blankc (ng, n =3) |
GM | GSD | Mina | Median | Max | GM | GSD | Min | Max | Min | Median | Max | Min | Median | Max | Min | Median | Max | |
β-DBE-DBCH | 54.2 | <0.64 | 1.46 | 3.46 | <0.64 | 0.91 | 359 | 21.7 | <0.64 | 0.76 | 1.47 | <0.64 | <0.64b | 2.33 | <2 | <2 | 11 | <2 | <2 | 16 | |||||||
α-DBE-DBCH | 54.2 | <0.64 | 1.38 | 3.34 | <0.64 | 0.75 | 307 | 21.7 | <0.64 | 0.74 | 1.42 | <0.64 | <0.64b | 2.07 | <2 | <2 | 13 | <2 | <2 | 25 | |||||||
BATE | 0.0 | <0.64 | <0.64 | 1.00 | <0.64 | <0.64 | <0.64 | 4.3 | <0.64 | 0.66 | 1.16 | <0.64 | <0.64 | 1.28 | – | – | – | – | – | – | <0.08 | 0.9 | 4.6 | ||||
PBT | 28.8 | <0.64 | 0.87 | 1.92 | <0.64 | <0.64 | 7.87 | 73.9 | <0.64 | 1.30 | 1.84 | <0.64 | 1.39b | 5.28 | <0.02 | 0.30 | 12 | ||||||||||
PBEB | 44.1 | <0.64 | 1.26 | 2.60 | <0.64 | <0.64 | 12.8 | 82.6 | <0.64 | 1.79 | 2.53 | <0.64 | 1.89b | 21.4 | <0.07 | 0.5 | 4.1 | ||||||||||
TBP-DBPE | 28.8 | <0.64 | 0.79 | 1.58 | <0.64 | <0.64 | 4.21 | 73.9 | <0.64 | 1.24 | 1.93 | <0.64 | 1.01b | 4.68 | <2 | <2 | 2 | - | - | - | <0.30 | 1.5 | 1,200 | ||||
HBB | 81.4 | <0.64 | 2.02 | 2.53 | <0.64 | 1.85 | 16.3 | 91.3 | <0.64 | 7.78 | 2.84 | <0.64 | 9.40b | 27.4 | <2 | 1 | 8 | <2 | <2 | 13 | <0.02 | 3.7 | 130 | ||||
EH-TBB | 93.2 | <0.64 | 310 | 8.59 | <0.64 | 337 | 19198 | 91.3 | 0.88 | 1400 | 17.3 | <0.64 | 2687b | 29007 | 91.1 | 2.6 | 35.7 | 669 | 4 | 48 | 740 | 45 | 100 | 5900 | <0.30 | 120 | 18,000 |
BEH-TEBP | 93.2 | 0.99 | 144 | 5.94 | <0.64 | 186 | 3483 | 91.3 | <0.64 | 1096 | 12.0 | <0.64 | 2076b | 11422 | 65.8 | 1.7 | 24.3 | 111 | 36 | 140 | 1900 | <2 | 260 | 3800 | 10 | 99 | 6,400 |
BTBPE | 93.2 | <0.64 | 21.8 | 4.41 | <0.64 | 22.3 | 1505 | 91.3 | <0.64 | 31.3 | 4.84 | <0.64 | 28.4 | 626 | 17.7 | 3.6 | 2.5 | 219 | 7 | 30 | 220 | 3 | 12 | 130 | 1.8 | 30 | 610 |
DBDPE | 78.0 | <2.60 | 53.5 | 6.40 | <2.60 | 82.8 | 5564 | 82.6 | <2.60 | 96.5 | 5.99 | <2.60 | 161b | 1650 | 39.4 | 6.7 | <10 | 262 | <10 | 51 | 430 | 18 | 140 | 2800 |
Summary statistics calculated using value of LOD for non-detects.
Dust-NBFR concentrations differed between the NCCLS and FOX study using the non-parametric Wilcoxon–Mann–Whitney test, p<0.05
< X.X – Below lowest calibration standard converted to ng/g