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Environmental Health Criteria 214

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HUMAN EXPOSURE ASSESSMENT<br />

to better understand the VOC contributions of specific sources,<br />

Wallace et al. (1989) had 7 volunteers undertake about 25 activities.<br />

A number of these activities (using bathroom deodorizers, washing<br />

dishes, cleaning an automobile carburettor) resulted in 10-1000-fold<br />

increases in 8-h exposures to certain VOCs.<br />

A recent study of benzene and toluene in 293 California homes<br />

(Wilson et al., 1993a, b; 1995; Colome et al., 1994) resulted in some<br />

interesting differences between the two agents. For benzene, 48-h<br />

average indoor concentrations correlated fairly well with outdoor<br />

levels, but for toluene almost no correlation was observed. This is<br />

probably due to the much wider use of toluene in consumer products.<br />

Major variables associated with higher net indoor benzene levels were<br />

presence of a gas heating furnace and having two cars parked in an<br />

attached garage. For toluene, a particular brand of furnace had the<br />

highest partial correlation with net indoor toluene concentrations;<br />

apartments also had higher concentrations.<br />

A study of 170 homes in Avon, England found mean indoor levels of<br />

benzene to be 8 µg/m 3 , compared to outdoor concentrations of 5 µg/m 3<br />

(Brown & Crump, 1996). The study employed passive Tenax tubes to<br />

collect 28-day indoor and outdoor samples. These results were in good<br />

agreement with the levels of 10 µg/m 3 indoors and 6 µg/m 3 outdoors<br />

at 50 homes in Los Angeles measured over two seasons in 1987 (Wallace<br />

et al., 1991).<br />

Table 39. Weighted estimates of air and breath concentrations of 11 prevale<br />

residents (fall 1981); 110 000 residents (summer 1982); and 49 000 re<br />

Compound Personal Fall Breath Personal Summer<br />

air outdoor (300) air outdoor<br />

(n = 340) air (150) air<br />

(86) (60)<br />

1,1,1-Trichloroethane 94 a 7.0 a 15 b 67 12<br />

m,p-Dichlorobenzene 45 1.7 8.1 50 1.3<br />

m,p-Xylene 52 11 9.0 37 10<br />

Tetrachloroethylene 45 6.0 13 11 6.2<br />

Benzene 28 9.1 19 NC c NC<br />

Ethylbenxene 19 4.0 4.6 9.2 3.2<br />

o-Xylene 16 4.0 3.4 12 3.6<br />

Trichloroethylene 13 2.2 1.8 6.3 7.8<br />

Chloroform 8.0 1.4 3.1 4.3 13<br />

Styrene 8.9 0.9 1.2 2.1 0.7<br />

Carbon tetrachloride 9.3 1.1 1.34 1.0 1.0<br />

http://www.inchem.org/documents/ehc/ehc/ehc<strong>214</strong>.htm<br />

Page 216 of 284<br />

6/1/2007

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