Environmental monitoring of secondhand smoke exposure
Identifieur interne : 000398 ( Main/Exploration ); précédent : 000397; suivant : 000399Environmental monitoring of secondhand smoke exposure
Auteurs : Benjamin J. Apelberg [États-Unis] ; Lisa M. Hepp [États-Unis] ; Erika Avila-Tang [États-Unis] ; Lara Gundel [États-Unis] ; S Katharine Hammond [États-Unis] ; Melbourne F. Hovell [États-Unis] ; Andrew Hyland [États-Unis] ; Neil E. Klepeis [États-Unis] ; Camille C. Madsen [États-Unis] ; Ana Navas-Acien [États-Unis] ; James Repace [États-Unis] ; Jonathan M. Samet [États-Unis] ; Patrick N. Breysse [États-Unis]Source :
- Tobacco Control [ 0964-4563 ] ; 2013-05.
Abstract
The complex composition of secondhand smoke (SHS) provides a range of constituents that can be measured in environmental samples (air, dust and on surfaces) and therefore used to assess non-smokers' exposure to tobacco smoke. Monitoring SHS exposure (SHSe) in indoor environments provides useful information on the extent and consequences of SHSe, implementing and evaluating tobacco control programmes and behavioural interventions, and estimating overall burden of disease caused by SHSe. The most widely used markers have been vapour-phase nicotine and respirable particulate matter (PM). Numerous other environmental analytes of SHS have been measured in the air including carbon monoxide, 3-ethenylpyridine, polycyclic aromatic hydrocarbons, tobacco-specific nitrosamines, nitrogen oxides, aldehydes and volatile organic compounds, as well as nicotine in dust and on surfaces. The measurement of nicotine in the air has the advantage of reflecting the presence of tobacco smoke. While PM measurements are not as specific, they can be taken continuously, allowing for assessment of exposure and its variation over time. In general, when nicotine and PM are measured in the same setting using a common sampling period, an increase in nicotine concentration of 1 μg/m3 corresponds to an average increase of 10 μg/m3 of PM. This topic assessment presents a comprehensive summary of SHSe monitoring approaches using environmental markers and discusses the strengths and weaknesses of these methods and approaches.
Url:
DOI: 10.1136/tobaccocontrol-2011-050301
Affiliations:
- États-Unis
- Californie, Illinois, Maryland, État de New York
- Baltimore, Los Angeles
- Université de Californie du Sud
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Monitoring SHS exposure (SHSe) in indoor environments provides useful information on the extent and consequences of SHSe, implementing and evaluating tobacco control programmes and behavioural interventions, and estimating overall burden of disease caused by SHSe. The most widely used markers have been vapour-phase nicotine and respirable particulate matter (PM). Numerous other environmental analytes of SHS have been measured in the air including carbon monoxide, 3-ethenylpyridine, polycyclic aromatic hydrocarbons, tobacco-specific nitrosamines, nitrogen oxides, aldehydes and volatile organic compounds, as well as nicotine in dust and on surfaces. The measurement of nicotine in the air has the advantage of reflecting the presence of tobacco smoke. While PM measurements are not as specific, they can be taken continuously, allowing for assessment of exposure and its variation over time. In general, when nicotine and PM are measured in the same setting using a common sampling period, an increase in nicotine concentration of 1 μg/m3 corresponds to an average increase of 10 μg/m3 of PM. This topic assessment presents a comprehensive summary of SHSe monitoring approaches using environmental markers and discusses the strengths and weaknesses of these methods and approaches.</div></front></TEI><affiliations><list><country><li>États-Unis</li></country><region><li>Californie</li><li>Illinois</li><li>Maryland</li><li>État de New York</li></region><settlement><li>Baltimore</li><li>Los Angeles</li></settlement><orgName><li>Université de Californie du Sud</li></orgName></list><tree><country name="États-Unis"><region name="Maryland"><name sortKey="Apelberg, Benjamin J" sort="Apelberg, Benjamin J" uniqKey="Apelberg B" first="Benjamin J" last="Apelberg">Benjamin J. Apelberg</name></region><name sortKey="Avila Tang, Erika" sort="Avila Tang, Erika" uniqKey="Avila Tang E" first="Erika" last="Avila-Tang">Erika Avila-Tang</name><name sortKey="Avila Tang, Erika" sort="Avila Tang, Erika" uniqKey="Avila Tang E" first="Erika" last="Avila-Tang">Erika Avila-Tang</name><name sortKey="Breysse, Patrick N" sort="Breysse, Patrick N" uniqKey="Breysse P" first="Patrick N" last="Breysse">Patrick N. Breysse</name><name sortKey="Breysse, Patrick N" sort="Breysse, Patrick N" uniqKey="Breysse P" first="Patrick N" last="Breysse">Patrick N. Breysse</name><name sortKey="Gundel, Lara" sort="Gundel, Lara" uniqKey="Gundel L" first="Lara" last="Gundel">Lara Gundel</name><name sortKey="Hammond, S Katharine" sort="Hammond, S Katharine" uniqKey="Hammond S" first="S Katharine" last="Hammond">S Katharine Hammond</name><name sortKey="Hepp, Lisa M" sort="Hepp, Lisa M" uniqKey="Hepp L" first="Lisa M" last="Hepp">Lisa M. Hepp</name><name sortKey="Hovell, Melbourne F" sort="Hovell, Melbourne F" uniqKey="Hovell M" first="Melbourne F" last="Hovell">Melbourne F. Hovell</name><name sortKey="Hyland, Andrew" sort="Hyland, Andrew" uniqKey="Hyland A" first="Andrew" last="Hyland">Andrew Hyland</name><name sortKey="Klepeis, Neil E" sort="Klepeis, Neil E" uniqKey="Klepeis N" first="Neil E" last="Klepeis">Neil E. Klepeis</name><name sortKey="Madsen, Camille C" sort="Madsen, Camille C" uniqKey="Madsen C" first="Camille C" last="Madsen">Camille C. Madsen</name><name sortKey="Navas Acien, Ana" sort="Navas Acien, Ana" uniqKey="Navas Acien A" first="Ana" last="Navas-Acien">Ana Navas-Acien</name><name sortKey="Repace, James" sort="Repace, James" uniqKey="Repace J" first="James" last="Repace">James Repace</name><name sortKey="Samet, Jonathan M" sort="Samet, Jonathan M" uniqKey="Samet J" first="Jonathan M" last="Samet">Jonathan M. Samet</name></country></tree></affiliations></record>Pour manipuler ce document sous Unix (Dilib)
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