Collection and analysis of Nicotine as a marker for environmental tobacco smoke
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Exposure to secondhand and thirdhand smoke in private vehicles: Measurements in air and dust samples
2023, Environmental ResearchDevelopment of a passive sampler for analysis of nicotine in non-smoking areas
2023, Microchemical JournalMeasurement of airborne nicotine, as a marker of secondhand smoke exposure, in homes with residents who smoke in 9 European countries
2023, Environmental ResearchCitation Excerpt :To the best of our knowledge, this is of the largest studies providing objective data on SHS exposure in households with residents who smoke in Europe. Following a previously employed (Arechavala et al., 2017) and validated methodology (Hammond et al., 1987), we measured vapor-phase nicotine concentrations in a type of household that might be more reluctant to become smoke-free. Unlike PM2.5, released while smoking but also by other sources of combustion like some household appliances (furnaces, heaters, and stoves), airborne nicotine is unique to tobacco smoke, and thus, a specific marker to SHS (Hammond et al., 1987; Apelberg et al., 2013).
Establishment of a method to expose and measure pollution in excised porcine skin with electron paramagnetic resonance spectroscopy
2022, Ecotoxicology and Environmental SafetySecondhand smoke exposure assessment in outdoor hospitality venues across 11 European countries
2021, Environmental ResearchCitation Excerpt :For the environmental monitoring, we used airborne nicotine which is an objective and specific marker of SHS (Apelberg et al., 2013). Moreover, all countries shared a common protocol designed in accordance with a previously validated methodology (Hammond et al., 1987). Finally, the present analyses yield new insights regarding the main factors contributing to SHS concentrations on a set of highly frequented outdoor venues.
Secondhand smoke exposure in outdoor children's playgrounds in 11 European countries
2021, Environment InternationalCitation Excerpt :It is also the first study that objectively measures SHS exposure in playgrounds by monitoring airborne nicotine, a tobacco-specific constituent (Apelberg et al., 2013). The procedure for nicotine sampling has been previously validated (Hammond et al., 1987) and several studies have used this tracer previously to estimate SHS exposure in outdoor settings (López et al., 2012; Fu et al., 2016). Furthermore, we examined SHS exposure as a function of a wide range of contextual variables, providing new information about factors influencing SHS exposure in outdoor playgrounds at a local and national level.