Center for Global Tobacco Control, Department of Social and Behavioral Sciences, Harvard School of Public Health, Boston, Massachusetts, United States of America ; Smoking and Lung Cancer Research Center, Hellenic Cancer Society, Athens, Greece ; Clinic of Social and Family Medicine, Department of Social Medicine, University of Crete, Heraklion, Greece.
PLoS One. 2013 Sep 4;8(9):e72945. doi: 10.1371/journal.pone.0072945. eCollection 2013.
Successful smoke-free legislation is dependent on political will, enforcement and societal support. We report the success and pitfalls of a non-enforced nationwide smoke-free legislation in Greece, as well as ways in which compliance and enforcement-related factors, including ashtrays and signage, may impact indoor secondhand smoke (SHS) concentrations.
A follow-up study of venues (n=150, at baseline, n=75 at 2-year follow-up) in Greece assessed indoor particulate matter with a diameter less than 2.5 micrometers (PM 2.5 ) concentrations attributable to SHS smoke every six months for two years (n=455 venue/measurements).
Following the implementation of the 2010 smoke-free legislation, mean PM2.5 concentrations attributable to SHS fell from 175.3 µg/m(3) pre-ban to 84.52 µg/m(3) immediately post-ban, increasing over subsequent waves (103.8 µg/m(3) and 158.2 µg/m(3) respectively). Controlling for potential influential factors such as ventilation, time of day, day of week, city and venue type, all post-ban measurements were still lower than during the pre-ban period (Wave 2 beta: -118.7, Wave 3 beta: -87.6, and Wave 4 beta: -69.9). Outdoor or indoor signage banning smoking was not found to affect SHS concentrations (beta: -10.9, p=0.667 and beta: -18.1, p=0.464 respectively). However, ashtray or ashtray equivalents were strong determinants of the existence of indoor SHS (beta: +67 µg/m(3), p=0.017).
While the public may be supportive of smoke-free legislation, adherence may decline rapidly if enforcement is limited or nonexistent. Moreover, enforcement agencies should also focus on the comprehensive removal of ashtray equivalents that could act as cues for smoking within a venue.
成功实施无烟立法取决于政治意愿、执法力度和社会支持。我们报告了希腊一项非强制性全国无烟立法的成功和失败之处,以及合规和执法相关因素(如烟灰缸和标识)如何影响室内二手烟(SHS)浓度。
希腊的一项后续研究对场所(基线时 n=150,2 年随访时 n=75)进行了评估,每六个月对室内小于 2.5 微米的颗粒物(PM 2.5)浓度进行了为期两年的评估(n=455 个场所/测量值)。
在 2010 年无烟立法实施后,立即禁止吸烟后,归因于 SHS 的 PM2.5 浓度从禁令前的 175.3 µg/m3下降到 84.52 µg/m3,随后的几个波次中浓度有所增加(分别为 103.8 µg/m3和 158.2 µg/m3)。控制潜在的影响因素,如通风、一天中的时间、一周中的天数、城市和场所类型,所有禁止吸烟后的测量值仍低于禁令前的时期(波 2 beta:-118.7,波 3 beta:-87.6,波 4 beta:-69.9)。室外或室内禁止吸烟的标识没有发现对 SHS 浓度有影响(beta:-10.9,p=0.667 和 beta:-18.1,p=0.464)。然而,烟灰缸或烟灰缸等效物是室内 SHS 存在的强烈决定因素(beta:+67 µg/m3,p=0.017)。
虽然公众可能支持无烟立法,但如果执法力度有限或不存在,遵守率可能会迅速下降。此外,执法机构还应集中精力全面清除烟灰缸等效物,这些等效物可能成为场所内吸烟的线索。