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Tobacco and Public Health - TCSC Indonesia

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portable piezobalance to sample aerosols in restaurants, bars, <strong>and</strong> other locations. In<br />

the places sampled, respirable particulate levels ranged up to 700 µg/m 3 , <strong>and</strong> the levels<br />

varied with the intensity of smoking. Similar data have been reported for the office<br />

environment (National Research Council 1986; US Department of <strong>Health</strong> <strong>and</strong> Human<br />

Services 1986; National Cancer Institute 1999; Jenkins et al. 2000). Recent studies<br />

indicate low concentrations in many workplace settings, reflecting declining smoking<br />

prevalence in recent years <strong>and</strong> changing practices of smoking in the workplace. Using<br />

passive nicotine samplers, Hammond (1999) showed that worksite smoking policies<br />

can sharply reduce ETS exposure.<br />

Transportation environments may also be polluted by cigarette smoking.<br />

Contamination of air in trains, buses, automobiles, airplanes, <strong>and</strong> submarines has been<br />

documented (National Research Council 1986; US Department of <strong>Health</strong> <strong>and</strong> Human<br />

Services 1986). A National Research Council report (National Research Council 1986)<br />

on air quality in airliners summarized studies for tobacco smoke pollutants in commercial<br />

aircraft. In one study, during a single flight, the NO 2 concentration varied with<br />

the number of passengers with a lighted cigarette. In another study, respirable particles<br />

in the smoking section were measured at concentrations five or more times higher<br />

than in the nonsmoking section. Peaks as high as 1000 µg/m 3 were measured in the<br />

smoking section. Mattson et al. (1989) used personal exposure monitors to assess<br />

nicotine exposures of passengers <strong>and</strong> flight attendants. All persons were exposed to<br />

nicotine, even if seated in the nonsmoking portion of the cabin. Exposures were<br />

much greater in the smoking than in the nonsmoking section <strong>and</strong> were also greater in<br />

aircraft with recirculated air. Fortunately, with the banning of tobacco smoking on all<br />

domestic flights in 1987 <strong>and</strong> on all flights into <strong>and</strong> out of the United States in 1999, the<br />

issue has for the most part been resolved, as reflected in the National Research<br />

Council’s 2002 updated report (National Research Council 2002).<br />

<strong>Health</strong> effects of passive smoking<br />

JONATHAN M. SAMET 297<br />

Overview<br />

Evidence on the health risks of passive smoking comes from epidemiologic studies,<br />

which have directly assessed the associations of measures of secondh<strong>and</strong> smoke exposure<br />

with disease outcomes. Judgments about the causality of associations between<br />

secondh<strong>and</strong> smoke exposure <strong>and</strong> health outcomes are based not only on this epidemiologic<br />

evidence, but also on the extensive evidence derived from epidemiologic <strong>and</strong><br />

toxicologic investigation on the health consequences of active smoking. To date, the<br />

evidence has supported causal conclusions on a range of acute <strong>and</strong> chronic adverse<br />

effects in children <strong>and</strong> adults (Table 17.1). This paper provides an overview of the now<br />

extensive data on adverse health effects of passive smoking on women <strong>and</strong> children,<br />

drawing on various synthesis reports <strong>and</strong> other reviews (Samet <strong>and</strong> Wang 2000). The<br />

evidence is reviewed separately for adults <strong>and</strong> children.

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