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Does the model of comprehensive
    smoke-free ban matter?

       Mark Ward Luke Clancy

   ICO-WHO Tobacco Control Symposium
         Barcelona 5 July 2012
SESL

Secondhand smoke Exposure and
     Smoke-free Legislation
What did SESL aim to do?
SESL aimed to provide evidence to support implementation of
comprehensive Smokefree policy across the European Union in
accordance with Article 8 of the WHO Framework Convention
                    on Tobacco Control



 The clearest and most rapid support in driving advocacy for
 Smokefree and Article 8 of the WHO FCTC is to examine the
 exposure outcome from different models of Smokefree law
Hypothesis

                             (1)
  Comprehensive laws are the only laws to deliver the full
 potential of reduction of exposure to second hand smoke.


                             (2)
 Is the comprehensive nature of the law the only reason for
any observed reduction in SHS or are other factors important.
Overarching Objective


        Examine the relationship between the
           models of Smokefree legislation
                        and the
       level of exposure to secondhand smoke
            in different European countries
to provide the evidence base to enable the legislators to
 make Smokefree laws which give maximal protection to
                     the population
Countries included (8)

Ireland    – C – April 2004
Italy      – C – January 2005
Spain      – P – January 2006   – C – January 2011
Scotland   – C – March 2006
France     – P – January 2007   – C – January 2008
Portugal   – P – January 2008
Greece     – P – July 2009      – C – January 2010
Turkey     – C – July 2009
Table 1: SHS data collection

            Monitor       Duration     Conversion         Date pre       Date post
                                         factor
            Aerocet                                     Jan-Dec 2007    Mar-Nov 2008
France                    Missing
           Met One 531                     8.2
            Sidepak                                     Feb 2006 – Jan April-2010
Greece                    30 mins+        0.32
             AM510                                           2009
            Aerocet                                       Oct-2003     Oct-2004
Ireland                    3hrs+
           Met One 531                     None           Mar-2004     Mar-2005
                                     x=(y+21.01)/4.01   Nov-Dec 2004 Mar-April 2005
            DustTrak
Italy                     20 mins     x=(y+9.1)/ 2.66                  & Nov-Dec
             8520
                                                                         2005
             SidePak                                      April 2009   July 2010
Portugal                  30 mins         0.51
             AM510
             SidePak                                         n/a        Oct-Dec 2007
Spain                     Missing         0.51
             AM510
                                                          April 2009
             SidePak
Turkey                    30 mins         0.23              (Pre)        Sept-2010
             AM510
                                                        Nov-Dec 2009)
             SidePak                                     Jan-March       March-May
Scotland                  30 mins         0.295
             AM510                                          2007           2007
Table 2: Summary of SHS measurements

           Overall       Range                   Sig Test            R
             %          % change
           change
            63%      (-)99% - (+)124    z(112)= -8.364, p < 0.001   -0.54
France

            40%      (-)99% - (+)66%     z(14)= -2.291, p < 0.05    -0.43
Greece

            82%      (-)100% - (-)13    z(42)= -5.648, p < 0.001    -0.62
Ireland

            70%            n/a           U(61) = 267.0, p < 0.01    -0.36
Italy

            41%      (-)81% - (+)67%      z(12)= -2.51, p < 0.05    -0.51
Portugal

            35%      (-)93% - (+)251%   z(12)= -0.941, p = 0.347    n/a
Turkey

            92%      (-)99% - (-)12%    z(53)= -6.334, p < 0.001    -0.61
Scotland
Comparison of PM2.5 concentrations before and after implementation of
                       smoke-free legislation
Table 3: Ecological factors
                            Correlation with       p-value    r2
                            change in PM2.5
Female participation          .460(n=278)          p<0.001   0.21
GDP per capita                .432 (n=278)         p<0.001   0.19
Minimum hourly wage           .404 (n=245)         p<0.001   0.16
GINI coefficient              -.364(n=278)         p<0.001   0.13
Health expenditure as
                              .358(n=278)          p<0.001   0.13
% of GDP
Corruption                    -.300(n=278)         p<0.001   0.09
Trust public institutions     .252 (n=278)         p<0.001   0.06
Life expectancy – Men         .244(n=278)          p<0.001   0.06
Men – Smoking                -.478 (n=278)         p<0.001   0.23
Prevalence
Women – Smoking               n/a(n=278)           p=0.051   n/a
Prevalence
Overall – Smoking            -.171 (n=278)         p<0.01    0.03
Prevalence
Table 4: Regression analysis of country characteristics, level of
          legislation and percentage reduction in PM2.5


                        B                  β
                                                     Final R=.469*
Level of              28.26*             .309        R2=.220
enforcement                                          Adjusted
                                                     R2=.214

Smoking               -1.56*             -.224
prevalence
among men
               Intercept = 98.82*          *p<.001
Key Messages

 Comprehensive Smoke-free laws work.

 Partial smoke-free laws do not work as evidenced by their failure to
reduce SHS significantly in the hospitality sector in Greece, Portugal
and Spain.

 Developments in Greece and Spain have seen stronger smoke-free
laws put in place and these moves represent an important affirmation
of comprehensive laws.

 Any law, regardless of scope must be actively enforced in order to
have the desired impact.

 There is a need to continue surveillance in all countries.

 In particular Greece and Turkey seem to need particular attention .
Fully Comprehensive
                       V
            ‘Fully’ Comprehensive ?

Ire + Sco
Ita + Fra
Acknowledgements

                            SHS data provided by
Prof Nazmi Bilir (Turkey)

Prof José Alberto Gomes Precioso, Dr Jose Luis Castro, Dr Ana Catarina
Samorinha ,(Portugal)

Prof Bertrand Dautzenberg (France)

Dr Francesco Forastiere, Dr Pasquale Valente and Dr Giuseppe Gorini
(Italy)
Professor Pat Goodman and Ms. Marie Mccaffrey (Ireland)
Dr Maria José Lopez (Spain)
Dr Sean Semple (Scotland)
Dr Constantine Vardavas and Prof Panagiotas Behrakis (Greece)
Funding Acknowledgement



       SESL was funded by the a Pfizer
Tobacco Control and Policy Micro-Grant project

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Does the model of comprehensive smoke-free ban matter?

  • 1. Does the model of comprehensive smoke-free ban matter? Mark Ward Luke Clancy ICO-WHO Tobacco Control Symposium Barcelona 5 July 2012
  • 2. SESL Secondhand smoke Exposure and Smoke-free Legislation
  • 3. What did SESL aim to do? SESL aimed to provide evidence to support implementation of comprehensive Smokefree policy across the European Union in accordance with Article 8 of the WHO Framework Convention on Tobacco Control The clearest and most rapid support in driving advocacy for Smokefree and Article 8 of the WHO FCTC is to examine the exposure outcome from different models of Smokefree law
  • 4. Hypothesis (1) Comprehensive laws are the only laws to deliver the full potential of reduction of exposure to second hand smoke. (2) Is the comprehensive nature of the law the only reason for any observed reduction in SHS or are other factors important.
  • 5. Overarching Objective Examine the relationship between the models of Smokefree legislation and the level of exposure to secondhand smoke in different European countries to provide the evidence base to enable the legislators to make Smokefree laws which give maximal protection to the population
  • 6. Countries included (8) Ireland – C – April 2004 Italy – C – January 2005 Spain – P – January 2006 – C – January 2011 Scotland – C – March 2006 France – P – January 2007 – C – January 2008 Portugal – P – January 2008 Greece – P – July 2009 – C – January 2010 Turkey – C – July 2009
  • 7.
  • 8. Table 1: SHS data collection Monitor Duration Conversion Date pre Date post factor Aerocet Jan-Dec 2007 Mar-Nov 2008 France Missing Met One 531 8.2 Sidepak Feb 2006 – Jan April-2010 Greece 30 mins+ 0.32 AM510 2009 Aerocet Oct-2003 Oct-2004 Ireland 3hrs+ Met One 531 None Mar-2004 Mar-2005 x=(y+21.01)/4.01 Nov-Dec 2004 Mar-April 2005 DustTrak Italy 20 mins x=(y+9.1)/ 2.66 & Nov-Dec 8520 2005 SidePak April 2009 July 2010 Portugal 30 mins 0.51 AM510 SidePak n/a Oct-Dec 2007 Spain Missing 0.51 AM510 April 2009 SidePak Turkey 30 mins 0.23 (Pre) Sept-2010 AM510 Nov-Dec 2009) SidePak Jan-March March-May Scotland 30 mins 0.295 AM510 2007 2007
  • 9. Table 2: Summary of SHS measurements Overall Range Sig Test R % % change change 63% (-)99% - (+)124 z(112)= -8.364, p < 0.001 -0.54 France 40% (-)99% - (+)66% z(14)= -2.291, p < 0.05 -0.43 Greece 82% (-)100% - (-)13 z(42)= -5.648, p < 0.001 -0.62 Ireland 70% n/a U(61) = 267.0, p < 0.01 -0.36 Italy 41% (-)81% - (+)67% z(12)= -2.51, p < 0.05 -0.51 Portugal 35% (-)93% - (+)251% z(12)= -0.941, p = 0.347 n/a Turkey 92% (-)99% - (-)12% z(53)= -6.334, p < 0.001 -0.61 Scotland
  • 10. Comparison of PM2.5 concentrations before and after implementation of smoke-free legislation
  • 11. Table 3: Ecological factors Correlation with p-value r2 change in PM2.5 Female participation .460(n=278) p<0.001 0.21 GDP per capita .432 (n=278) p<0.001 0.19 Minimum hourly wage .404 (n=245) p<0.001 0.16 GINI coefficient -.364(n=278) p<0.001 0.13 Health expenditure as .358(n=278) p<0.001 0.13 % of GDP Corruption -.300(n=278) p<0.001 0.09 Trust public institutions .252 (n=278) p<0.001 0.06 Life expectancy – Men .244(n=278) p<0.001 0.06 Men – Smoking -.478 (n=278) p<0.001 0.23 Prevalence Women – Smoking n/a(n=278) p=0.051 n/a Prevalence Overall – Smoking -.171 (n=278) p<0.01 0.03 Prevalence
  • 12. Table 4: Regression analysis of country characteristics, level of legislation and percentage reduction in PM2.5 B β Final R=.469* Level of 28.26* .309 R2=.220 enforcement Adjusted R2=.214 Smoking -1.56* -.224 prevalence among men Intercept = 98.82* *p<.001
  • 13. Key Messages  Comprehensive Smoke-free laws work.  Partial smoke-free laws do not work as evidenced by their failure to reduce SHS significantly in the hospitality sector in Greece, Portugal and Spain.  Developments in Greece and Spain have seen stronger smoke-free laws put in place and these moves represent an important affirmation of comprehensive laws.  Any law, regardless of scope must be actively enforced in order to have the desired impact.  There is a need to continue surveillance in all countries.  In particular Greece and Turkey seem to need particular attention .
  • 14. Fully Comprehensive V ‘Fully’ Comprehensive ? Ire + Sco Ita + Fra
  • 15. Acknowledgements SHS data provided by Prof Nazmi Bilir (Turkey) Prof José Alberto Gomes Precioso, Dr Jose Luis Castro, Dr Ana Catarina Samorinha ,(Portugal) Prof Bertrand Dautzenberg (France) Dr Francesco Forastiere, Dr Pasquale Valente and Dr Giuseppe Gorini (Italy) Professor Pat Goodman and Ms. Marie Mccaffrey (Ireland) Dr Maria José Lopez (Spain) Dr Sean Semple (Scotland) Dr Constantine Vardavas and Prof Panagiotas Behrakis (Greece)
  • 16. Funding Acknowledgement SESL was funded by the a Pfizer Tobacco Control and Policy Micro-Grant project

Editor's Notes

  1. Source: Smoke free Partnership: http://www.smokefreepartnership.eu/Smoke-free-legislation-in-the-EU
  2. % reduction is the key here.Range % change refers to the variation in reduction/increase in PM2.5 for the venues included in each country. Significance level should be clear.R is a measure of effect size. – indicates a decrease from T1 to T2. The closer to -1 the value the greater the decrease. So Ireland and Scotland the greatest decrease in average PM2.5 with the smallest decrease observed in Italy. Also note: Due to the non-normal distribution of the measurements, non-parametric tests were used. A Wilcoxon signed rank test, which is the non-parametric equivalent of the parametric paired sample T-test, was used where both pre and post smoke-free legislation measurements were recorded at the same venue. In the case of Italy a Mann-Whitney U Test was used as not all the same venues were included in pre and post-ban data collection. The change in Turkey was not significant p=0.347. The report has a full explanation of why this is the case.
  3. Different monitors used and different conversion factors mean that PM2.5 levels themselves are not directly comparable. For this reason we compared the % change in each country
  4. A final OLS multiple regression analysis was performed with percentage change in PM2.5 concentrations the outcome of interest and the independent variables consisting of those shown earlier to be significant predictors and also the season in which pre and post-ban measurements were taken, the lag time between implementation of smoke-free and measurement. The level of legislation (partial or comprehensive) and the level of enforcement were also included in the initial solution. Due to there being fourteen independent variables it was not feasible to use the ‘stepwise’ method which requires a ratio of 40:1 (cases: IV’s) so the ‘enter’ method was used instead (Tabachnick and Fidell, 2007). Screening of the solution indicated that there was not enough statistical power to include all of the independent variables desired and so a final model with sufficient power was designed and contained the following six independent variables: (1)prevalence rate among men, (2)female legislators, senior officials and managers, (3) the life expectancy of men, and (4)enforcement, (5) the level of legislation and (6) the lag time between implementation of smoke-free legislation and data collection. Using the ‘stepwise’ method, the final mode included only the enforcement level and the smoking prevalence rate among men prior to implementation of smoke-free. The model explained 22% (22.4% adjusted) of the variance in percentage change in PM2.5 concentration which was significantly greater than zero [F(2, 268)=37.69, p&lt;.001]. As can be seen in Table 19 lower smoking prevalence among men and stronger enforcement of smoke-free legislation was associated with higher percentage changes (reduction) in PM2.5 concentrations. The level of enforcement made a stronger contribution to the final model.