This paper models nicotine dose and ultraviolet-absorbing particulate matte
r (UVPM) alveolar lung burden resulting from exposure to environmental toba
cco smoke (ETS) for nonsmokers in workplaces where smoking was reported not
to occur. Data were obtained from personal monitoring of ETS in 16 U.S. ci
ties [Jenkins R.A., Guerin M.R., Palausky A., Counts R.W., Bayne C.K., and
Dindal A.B. Determination of human exposure to environmental tobacco smoke
(ETS): a study conducted in 16 U.S, cities. Draft final report by Oak Ridge
National Laboratory for Center for Indoor Air Research, Linthicum, MD, 199
6a; Jenkins R.A., Palausky A., Counts R.W., Bayne C.K., Dindal A.B., and Gu
erin M.R. Exposure to environmental tobacco smoke in sixteen cities in thee
United States as determined by personal breathing zone air sampling. J. Ex
pos. Anal. Environ. Epidemiol. 1996b: 6(4): 473 -502.]. This is a continuat
ion of earlier analyses focusing on nonsmokers in smoking workplaces (SWs)
[LaKind J.S., Graves C.G., Ginevan M.E., Jenkins R.A., Naiman D.Q., and Tar
diff R.G. Exposure to environmental tobacco smoke in the workplace and the
impact of away - from - work exposure. Risk Anal. 1999a: 19 (3): 349-358; L
aKind J.S., Jenkins R.A., Naiman D.Q., Ginevan M.E., Graves C.G., and Tardi
ff R.G. Use of environmental tobacco smoke constituents as markers for expo
sure. Risk Anal. 1999b: 19(3): 359-373; LaKind J.S., Ginevan M.E., Naiman D
.Q., James A.C., Jenkins R.A., Dourson M.L., Felter S.P., Graves C.G., and
Tardiff R.G. Distribution of exposure concentrations and doses for constitu
ents of environmental tobacco smoke. Risk Anal. 1999c: 19(3) : 375-390.]. E
ven though study participants characterized their workplaces as nonsmoking,
some individuals reported observing cigarettes in the workplace. Individua
ls observing six or more cigarettes were excluded from the analysis on the
grounds that they were in de facto SWs. Exposure to ETS was lower in nonsmo
king than SWs, but even with this exclusion, exposure was not zero. Distrib
utions were selected for each model input, and at least 2000 iterations of
the model were made for each dose or lung burden characterization (e.g., fo
r females, for males). In these nonsmoking workplaces (NSWs), neither nicot
ine nor UVPM concentrations were lognormally distributed. Hence, observed c
oncentrations were used directly via bootstrap sampling (nicotine) or a con
stant number of times (UVPM) as input to the models. As in SWs, individuals
from smoking homes (SHs) experienced greater exposure in NSWs to both nico
tine and UVPM than did individuals from nonsmoking homes (NSH; P<0.001). Th
e distributions of modeled nicotine dose and UVPM lung burden were highly s
kewed, with most individuals receiving relatively low exposure to ETS in th
e workplace. Comparing doses from NSWs modeled here to doses from SWs model
ed previously, less difference between smoking and NSWs was apparent in UVP
M levels than in nicotine levels. For average exposure, UVPM alveolar lung
burdens were approximately 10-fold higher in smoking than NSWs, while avera
ge nicotine doses were 20-25 times higher in smoking than NSWs. These findi
ngs are in the range observed by other investigators and are partly explain
ed by very low denominators in the ratios (i.e., very low levels experience
d in NSWs). For upper bound exposure, the nonsmoking-to-smoking ratios rema
ined about the same for UVPM. For nicotine, the upper bound ratios remained
the same for people from NSHs but were halved for people from SHs.