Personal exposure to ultrafine particles (UFP) can occur while people are cooking, driving, smoking, operating small appliances such as hair dryers, or eating out in restaurants. These exposures can often be higher than outdoor concentrations. For 3 years, portable monitors were employed in homes, cars, and restaurants. More than 300 measurement periods in several homes were documented, along with 25 h of driving two cars, and 22 visits to restaurants. Cooking on gas or electric stoves and electric toaster ovens was a major source of UFP, with peak personal exposures often exceeding 100,000 particles/cm 3 and estimated emission rates in the neighborhood of 10 12 particles/min. Other common sources of high UFP exposures were cigarettes, a vented gas clothes dryer, an air popcorn popper, candles, an electric mixer, a toaster, a hair dryer, a curling iron, and a steam iron. Relatively low indoor UFP emissions were noted for a fireplace, several space heaters, and a laser printer. Driving resulted in moderate exposures averaging about 30,000 particles/cm 3 in each of two cars driven on 17 trips on major highways on the East and West Coasts. Most of the restaurants visited maintained consistently high levels of 50,000-200,000 particles/cm 3 for the entire length of the meal. The indoor/outdoor ratios of size-resolved UFP were much lower than for PM 2.5 or PM 10 , suggesting that outdoor UFP have difficulty in penetrating a home. This in turn implies that outdoor concentrations of UFP have only a moderate effect on personal exposures if indoor sources are present. A time-weighted scenario suggests that for typical suburban nonsmoker lifestyles, indoor sources provide about 47% and outdoor sources about 36% of total daily UFP exposure and in-vehicle exposures add the remainder (17%). However, the effect of one smoker in the home results in an overwhelming increase in the importance of indoor sources (77% of the total). Keywords: cooking, restaurants, gas stoves, electric stoves, vehicles, tobacco smoke.
IntroductionUltrafine particles (UFP) are increasingly studied because of considerations of their toxicology and possible human health effects (Oberdo¨rster et al., 2005; Bra¨uner et al., 2007a, b;Sto¨lzel et al., 2007). Outdoor UFP concentrations were measured for 1-2 years in several US cities (U.S. EPA Supersites program; Solomon et al., 2008), and near roadways in California (Zhu et al., 2002) and also in Erfurt and Augsberg, Germany (Wichmann et al., 2000). Residential indoor concentrations have also been reported (Abt et al., 2000;Dennekamp et al., 2001;Long et al., 2001;Wallace and Howard-Reed, 2002;Klepeis et al., 2003;He et al., 2004;Wallace, 2000Wallace, , 2005Wallace, , 2006Wallace et al., 2004Wallace et al., , 2008Hoek et al., 2008). A number of studies of exposures while driving have been done (Westerdahl et al., 2005;Fruin et al., 2008;Zhu et al., 2008). However, exposures in locations such as restaurants or while operating everyday sources of UFP close to one's person (stoves, toasters, ovens, hair dryers...