Frederieke S. van der Deen and Nick Wilson (on behalf of the other
authors; both from the University of Otago, Wellington, New Zealand)
This electronic letter aims to give readers an update on the smoking
prevalence projections to 2025 and beyond in New Zealand (NZ) that were
provided in the paper by Ikeda et al. NZ is now one of four nations with
an official smokefree goal (others are: Fin...
Frederieke S. van der Deen and Nick Wilson (on behalf of the other
authors; both from the University of Otago, Wellington, New Zealand)
This electronic letter aims to give readers an update on the smoking
prevalence projections to 2025 and beyond in New Zealand (NZ) that were
provided in the paper by Ikeda et al. NZ is now one of four nations with
an official smokefree goal (others are: Finland, Scotland, and Ireland).
In NZ, this goal is generally interpreted as achieving a smoking
prevalence under 5% by the year 2025.
The modelling work by Ikeda et al aimed to explore the feasibility of
achieving this goal under current annual trends in smoking uptake and
cessation (ie, business-as-usual (BAU)). Smoking prevalence data from a
regularly conducted NZ health-related survey between 2002 and 2011 were
used to provide information on recent annual trends in smoking uptake and
cessation as input for future BAU smoking prevalence projections. However,
since this modelling work was first published (as an e-publication in
2013), smoking prevalence data from the 2013 Census has become available.
A larger than expected fall in smoking rates in the general NZ adult
population, but especially in Maori (indigenous population), was observed.
It was therefore decided to update the future BAU smoking prevalence
projections that were provided in the Ikeda et al paper by using smoking
prevalence data from the 2013 Census.
The updated future BAU projected smoking prevalence in 2025 was 8.3%
and 6.4% for non-Maori (Ikeda et al: 10.7% and 8.8%), and 18.7% and 19.3%
for Maori men and women, respectively (Ikeda et al: 30.0% and 37.3%).
Although the updated projections are more favourable from a public health
perspective (especially for Maori) than the previous modelling work, a
smoking prevalence below 5% by 2025 is still not attained by any
demographic group. Achieving the 2025 smokefree goal will most likely
require implementation of more intense existing tobacco control strategies
or potentially even entirely novel measures (eg, major changes in the
tobacco retail environment as per the Tobacco Control themed supplement
for March 2015 'The Pack and the Retail Environment').
Updating the previously published smoking prevalence projections
proved to be a feasible and relatively easy exercise. Projecting and
regularly updating future BAU smoking prevalence projections with most up-
to-date smoking prevalence data, in NZ and in other nations, may assist
policy makers in planning how much more intense tobacco control measures
may need to be to achieve smokefree goals. For more detail around the
methods of updating the previous modelling work by Ikeda et al, we would
refer readers to the recently published paper that describes this work
[1].
Reference
1. van der Deen FS, Ikeda T, Cobiac L, Wilson N, Blakely T (2014)
Projecting future smoking prevalence to 2025 and beyond in New Zealand
using smoking prevalence data from the 2013 census. N Z Med J 127 (1406):
71-79. http://www.otago.ac.nz/wellington/otago083774.pdf
Thomson and colleagues present a novel radical approach for national
tobacco elimination supported by cogent arguments and discussion of the
various pros and cons for such a policy (Tobacco Control 2010;10:431-435).
They discuss, albeit briefly, the importance of best practice cessation
support. However current best practice is not especially effective, and
just as they have argued for a radical policy approach, there sim...
Thomson and colleagues present a novel radical approach for national
tobacco elimination supported by cogent arguments and discussion of the
various pros and cons for such a policy (Tobacco Control 2010;10:431-435).
They discuss, albeit briefly, the importance of best practice cessation
support. However current best practice is not especially effective, and
just as they have argued for a radical policy approach, there similarly
needs to be a more radical and innovative approach to cessation treatments
in terms of access, public awareness and choices of delivery.
Firstly, cessation treatments, particularly Nicotine Replacement
Therapy (NRT) must be more visible and available. Despite strong subsidy
for NRT via prescription and the New Zealand Quitline it remains easier to
obtain a packet of cigarettes that it does to obtain the almost harmless
nicotine equivalent. Nicotine needs to be much more prominently displayed,
and available wherever tobacco is legally sold. When a smoker needs
nicotine they usually need it immediately at the corner shop not after an
appointment with their GP and a pharmacy prescription.. Nicotine needs
marketing in the same proportion that tobacco needs eliminating.
Secondly, there needs to be better education about the relative
safety of NRT compared to continued smoking. More than 50% of smokers
believe that nicotine is the dangerous component of smoking, and so it is
perhaps not surprising that NRT uptake is poor. The merits of NRT should
be discussed at every cessation encounter and much more widely
promulgated. For those unable to quit smoking, the long term use of
nicotine is infinitely preferable to continued smoking, and yet to date
there have been no long term studies designed to explore substitution as
an alternative to cessation.
Lastly, we need fast acting nicotine formulations delivered in a
manner that is both acceptable to smokers and rapidly controls their urges
to smoke. The inhalation route is the obvious one but is more difficult
given the aversiveness of nicotine in the upper airway. Oral liquid
formulations may prove more effective than current NRT, and we should not
write off products such as snus without at least examining their potential
for harm reduction. In addition to considering a sinking lid for tobacco,
we need to take the lid off nicotine, convince smokers that it is not much
more harmful than coffee, and provide a much improved range of products
for cessation or failing that for lifelong use.
Dr Gupta’s comparison of trends in lung cancer mortality and smoking
prevalence in Sweden and Connecticut purports to undermine the claim that
increasing snus use in Sweden has contributed to declining lung cancer
rates there.
Dr Gupta argues that some factor other than snus must have been at
work because the ratio of lung cancers between Sweden and Connecticut has
remained constant despite the large differenc...
Dr Gupta’s comparison of trends in lung cancer mortality and smoking
prevalence in Sweden and Connecticut purports to undermine the claim that
increasing snus use in Sweden has contributed to declining lung cancer
rates there.
Dr Gupta argues that some factor other than snus must have been at
work because the ratio of lung cancers between Sweden and Connecticut has
remained constant despite the large difference in snus use between the two
places. He identifies this “other factor” as a declining cigarette smoking
prevalence that he attributes to tobacco control policies.
We agree that a decline in cigarette smoking in both countries
explains the lung cancer trends but we don’t see how this rules out a role
for snus. This is exactly the mechanism by which proponents of snus would
claim that snus use reduces smoking prevalence, namely, that population
smoking prevalence declines because existing smokers switch to snus and
new tobacco users use snus rather than cigarettes (Ramström and Foulds
2006).
The fact that smoking prevalence declined in Connecticut as a result
of more traditional tobacco control policies simply shows that there is
more than one way to reduce smoking prevalence. The fact that the decline
in cigarette smoking over the time period examined was greater in Sweden (
-13%) than in Connecticut (-8%) supports the hypothesis that the addition
of snus to more conventional tobacco control policies has increased the
decline in smoking prevalence.
We concede that the comparison does not prove that snus was
responsible for the decline in lung cancer rates in Sweden, but it is much
more supportive of the claims for snus than Dr Gupta allows.
Yours sincerely
Coral Gartner and Wayne Hall
References
Ramström, L. M. and J. Foulds (2006). "Role of snus in initiation and
cessation of tobacco smoking in Sweden." Tobacco Control 15(3): 210-214.
Research on waterpipe smoking, also called hookah, is still emerging,
and research on second-hand hookah exposure is still in its nascent
stages. However, after reading the review on the various effects of second
-hand waterpipe smoke exposure by Kumar et al recently published in
Tobacco Control1, we noted several major issues in its execution and have
serious reservations about th...
Research on waterpipe smoking, also called hookah, is still emerging,
and research on second-hand hookah exposure is still in its nascent
stages. However, after reading the review on the various effects of second
-hand waterpipe smoke exposure by Kumar et al recently published in
Tobacco Control1, we noted several major issues in its execution and have
serious reservations about the potential of this review as a tool in the
development of public health policy.
First, the authors failed to synthesize all available research on the
topic into their review, by utilizing only two electronic search
databases. When a search was conducted in CINAHL, we found one more
relevant article that could have been included in this review2. However,
we are unable to judge as the authors don't present the inclusion criteria
for the review. Furthermore, we found another systematic review on this
topic and found that the amount of nicotine absorption resulting from
daily hookah use was similar to that of daily cigarette use3. This is
concerning because the authors did not include the older systematic review
in the narrative nor did they derive information from it; consequently,
calling into question the relevance of the current review. In addition,
the authors were unclear regarding their methodology. They only provided a
list of search terms and failed to specify any inclusion criteria, making
it impossible for anyone to replicate their review.
Second, the authors did not seem to have assessed the scientific quality
of the included studies, negatively affecting the transparency of the
review process. Thus, readers cannot properly assess its quality as a
comprehensive review of the current body of literature or assess the
validity of the findings that were included in the review. They also
failed to assess publication bias, which would have been a relevant issue
as they only included published studies. Given that a number of reporting
guidelines for reviews have been produced, these issues are almost
unjustifiable.
Although the authors examined an important, often overlooked public health
issue, their review suffered from major methodological flaws that could
not be ignored. Unfortunately, the review's weaknesses prevent it from
being a proper synthesis of the current body of research on the effects of
second-hand exposure to hookah smoke and a useful tool for assisting
decision-making in public health policy.
REFERENCES
1 Kumar SR, Davies S, Weitzman M, Sherman S. A review of air quality,
biological indicators and health effects of second-hand waterpipe smoke
exposure. Tob Control. 2015; 24: i54-i59. doi: 10.1136/tobaccocontrol-2014
-052038
2 Aydin A, Kiter G, Durak H, Ucan ES, Kaya GC, Ceylan E. Water-pipe
smoking effects on pulmonary permeability using technetium-99m DTPA
inhalation scintigraphy. Ann Nucl Med. 2004; 18(4): 285-289. doi:
10.1007/BF02984465
3 Neergaard J, Singh P, Job J, Montgomery S. Waterpipe smoking and
nicotine exposure: a review of the current evidence. Nicotine Tob Res.
2007; 9(10): 987-994. doi: 10.1080/14622200701591591
Smokers tend to leave their smoking prints permanently or
semipermanently in buildings where they live and enjoy the taste of smoking
regularly. The nonsmokers, newcomers moving into the said buildings,
dislike smoking leftovers in terms of nicotine and other byproducts of
tobacco use. The comparative analysis of relevant samples from firsthand,
secondhand and thirdhand smokers would have shed some light on the levels
o...
Smokers tend to leave their smoking prints permanently or
semipermanently in buildings where they live and enjoy the taste of smoking
regularly. The nonsmokers, newcomers moving into the said buildings,
dislike smoking leftovers in terms of nicotine and other byproducts of
tobacco use. The comparative analysis of relevant samples from firsthand,
secondhand and thirdhand smokers would have shed some light on the levels
of tobacco byproducts among them and their direct relevance to the serious
or nonserious consequences of tobacco use.
How long and why tobacco byproducts stay in such buildings needs to be
addressed comprehensively. Do we have a decontaminating agent(s)for tobacco
byproducts and hence prevention of THIRDHAND smoke exposure to naive
renters of buildings having nicotine and other smoking byproducts left by
smokers?
NOT PEER REVIEWED This comment summarizes, but mischaracterizes the
findings and conclusions of our study. Our analyses and interpretation are
based strictly on the letter of the Family Smoking Prevention and Tobacco
Control Act (FSPTCA) and its requirements, including Section
911(b)(2)(ii), which bans "the use of explicit or implicit descriptors
that convey messages of reduced risk including 'light', 'mild' and 'low',
o...
NOT PEER REVIEWED This comment summarizes, but mischaracterizes the
findings and conclusions of our study. Our analyses and interpretation are
based strictly on the letter of the Family Smoking Prevention and Tobacco
Control Act (FSPTCA) and its requirements, including Section
911(b)(2)(ii), which bans "the use of explicit or implicit descriptors
that convey messages of reduced risk including 'light', 'mild' and 'low',
or similar descriptions in a tobacco product, label, labeling or
advertising".
The findings demonstrated that manufacturers did not simply remove
descriptors, to be in compliance with the law, but introduced new color-
coded brand name descriptors which smokers were able to recognize and
easily identify the formerly labeled "lights" brands. We did not examine
the use of colors themselves, which may be protected by the First
Amendment, but rather the use of color terms.
The marketing materials examined make explicit the fact that the use of
substituted color terms in brand names is similar to the dropped
"descriptors, so that consumers will continue to recognize these brands as
"lights". The National Cancer Institute previously found that filter
ventilation has been used by manufacturers to delineate the misleading
"lights" categories, which are now color-coded, and which conveyed
messages of reduced risk resulting in increased initiation and reduced
cessation.
Our conclusions are stated in conservative terms that manufacturers appear
to have evaded this critical element of the FSPTCA, which is intended to
protect the public health.
The commentary by Noel, Rees and Connolly on E-cigarettes is truly
remarkable. They appear to draw the conclusion that E-cigarettes represent
a potentially substantial hazard to the American public that requires
"efforts . . . to counteract e-cigarette industry marketing and inform
regulatory strategies," then urge research to justify the conclusions they
have already reached. All this was done without considering the res...
The commentary by Noel, Rees and Connolly on E-cigarettes is truly
remarkable. They appear to draw the conclusion that E-cigarettes represent
a potentially substantial hazard to the American public that requires
"efforts . . . to counteract e-cigarette industry marketing and inform
regulatory strategies," then urge research to justify the conclusions they
have already reached. All this was done without considering the research
already done by the E-cigarette industry and others relative to the
chemical quality of their products and marketing policy.
Questions related to the quality of manufacture or marketing of E-
cigarettes can be resolved by FDA regulating them as the tobacco products
they are intended to be. Under the new FDA tobacco law, FDA has all the
authority it needs to assure quality and consistency of manufacturing and
to regulate marketing as needed to prevent sales to minors. The fact that
FDA has not taken such action is the fault of FDA, not the E-cigarette
manufacturers or vendors. E-cigarettes are intended as a substitute for
cigarettes for smokers unwilling or unable to quit, yet desiring to all-
but-eliminate their exposure to the other toxic substances in cigarette
smoke.1
From February of 2007 through February of 2010, I served as Co-Chair
of the Tobacco Control Task Force of the American Association of Public
Health Physicians. In that context I explored policy options for rapidly
and substantially reducing tobacco-related illness and death among current
American tobacco users. This research led to the conclusion that almost
all tobacco-related illness and death in the United States is due to the
smoking of cigarettes and that alternative smokeless tobacco and nicotine
products, including but not limited to snus, E-cigarettes and the
pharmaceutical NRT products, pose a risk of tobacco-related death less
than 2% the risk posed by cigarettes.2,3 In this context, it seemed clear
that a harm reduction initiative based on informing smokers of the
difference in risk posed by the different types of tobacco/nicotine
products, accompanied by effective FDA regulation of the manufacture and
marketing of all such products held the best possible hope for securing
rapid and substantial reductions in tobacco-related illness and death
among current smokers while minimizing initiation of tobacco use by teens
in the USA.
The "informed public health response" recommended by Noel et al can
be provided by regulation of E-cigarettes by FDA as the tobacco-based
products they are intended to be.
Joel L. Nitzkin, MD
References
1. Nitzkin JL, jln-md@mindspring.com. Citizen Petition (to FDA) to
Reclassify E-Cigarettes from "drug-device combination" to "tobacco
product"
[<http://www.aaphp.org/special/joelstobac/2010/Petition/20100207FDAPetition1.pdf>].
2. Nitzkin JL, Rodu B. AAPHP Resolution and White Paper: The Case for Harm
Reduction for Control of Tobacco-related Illness and Death
[http://www.aaphp.org/special/joelstobac/20081026HarmReductionResolutionAsPassed1.pdf].
3. Rodu B, Nitzkin JL, jln-md@mindspring.com. Update on the Scientific
Status of Tobacco Harm Reduction, 2008-2010 Prepared for the American
Association of Public Health Physicians
[http://www.aaphp.org/special/joelstobac/2010/harmredcnupdatejuly2010.html]
This letter responds to misrepresentations in a recent article by
Daniel Stevens and Stanton Glantz (1). In the article, Stevens and Glantz
question my integrity based on some questions during a 4-day deposition
which I gave in 2014 in a legal proceeding against my employer. These
writers cite snippets from the 1,000+-page transcript of that deposition,
relating the text of a facetious note that I h...
This letter responds to misrepresentations in a recent article by
Daniel Stevens and Stanton Glantz (1). In the article, Stevens and Glantz
question my integrity based on some questions during a 4-day deposition
which I gave in 2014 in a legal proceeding against my employer. These
writers cite snippets from the 1,000+-page transcript of that deposition,
relating the text of a facetious note that I had sent to my boss almost 20
years ago in 1996. The writers use a small portion of that note, together
with my answers to other deposition questions, taken out of context, to
infer that I gave questions from the open-book examination for
recertification to my co-workers to answer for me.
It is well-understood that recertification candidates must complete
the self-assessment examination themselves (2), which is precisely what I
did in both 1992 and 1996. Period. I stand by my sworn testimony that I
did not provide questions from either my 1992 or 1996 recertification
examinations to anyone to answer for me, and that my examination responses
were my own work. This is made clear in the deposition transcript and I
refute this attempt by Stevens and Glantz to suggest otherwise.
I am taken aback by the willingness of Tobacco Control to accept the
sort of "scholarship" pursued by Stevens and Glantz. These authors advise
special scrutiny of my work, with specific mention of my lead authorship
of the Industry Menthol Report that was written at the request of the FDA
(3). I stand by the scientific integrity of and conclusions in that
report, as well as by the comments provided to FDA on the recently-voided
TPSAC menthol report (4), and on FDA's own Preliminary Scientific
Evaluation of menthol (5).
Jonathan Daniel Heck, Ph.D., DABT, ATS
References
1. Stevens D, Glantz S. Tob Control Published Online First: May 12,
2015, doi:10.1136/
tobaccocontrol-2015-052271.
2.http://www.abtox.org/Candidates/ABOT_recertification/ABOT_recertification_policy.aspx
(accessed May 19, 2015)
3
http://www.fda.gov/downloads/AdvisoryCommittees/CommitteesMeetingMaterials/TobaccoProductsScientificAdvisoryCommittee/UCM249320.pdf
(accessed May 19, 2015).
4
http://www.lorillard.com/pdf/fda/Comments_to_FDA_on_TPSAC_Report.pdf
(accessed May 19, 2015)
5. http://www.lorillard.com/wp-content/uploads/2013/11/PSE-
Response_Lorillard_Final.pdf (accessed May 19, 2015)
Conflict of Interest:
I am a full-time employee of the Lorillard Tobacco Company. I have been asked on occasion to provide testimony in litigation involving my employer. I have done so from time to time, and receive no payment for this beyond the normal salary and benefits of my employment
NOT PEER REVIEWED
Funding: While this assessment was funded by RJ Reynolds Tobacco Company, it is the product of independent scientific thought, and it expresses solely the opinions of the authors.
When data are lacking, models that simulate population health events
under different exposure scenarios may serve to inform policy by providing
the basis for decision making. In order for models to be used in this
manner,...
NOT PEER REVIEWED
Funding: While this assessment was funded by RJ Reynolds Tobacco Company, it is the product of independent scientific thought, and it expresses solely the opinions of the authors.
When data are lacking, models that simulate population health events
under different exposure scenarios may serve to inform policy by providing
the basis for decision making. In order for models to be used in this
manner, their underlying assumptions must be as realistic as possible, and
the data used to define the starting point, or "base case", must be
accurate. If these criteria are met, then using the model to describe the
potential effects of extreme scenarios (i.e., "worst case" and "best
case") can provide useful information about the magnitude of effects to be
expected for more reasonable scenarios.
In a recent publication, Mejia et al. described a model using Monte Carlo
simulations, to evaluate the population level health effect that might be
expected if smokeless tobacco products were successfully promoted in the
US as a safer alternative to cigarettes, resulting in substantial changes
in the patterns of use of tobacco products (Mejia, Ling, et al. 2010). The
authors concluded that "promoting smokeless tobacco as a safer alternative
to cigarettes is unlikely to result in substantial health benefits at a
population level". We investigated the methods described by Mejia et al.
(2010), and evaluated their conclusion using three approaches: (1)
critiquing the assumptions underlying the model and its input data; (2)
comparing the published model estimates with estimates developed using the
model as described, but with more realistic input data; and (3) using the
original input data in a more realistic model, and comparing those results
to the published model estimates. We used the results of this
investigation to evaluate the utility of their model.
CRITIQUE OF MODEL ASSUMPTIONS AND INPUT DATA
Model transitions:
Mejia et al. (2010) describe their model as beginning with a
hypothetical population of non-users of tobacco who are then allowed a
very limited number of possible transitions between exposure states.
People are allowed to initiate cigarette smoking or smokeless tobacco
products, cigarette and smokeless tobacco initiators are allowed to
continue use, quit use; switch to the other product, or to become users of
both products ("dual users"). Return to cigarette smoking or smokeless
product use after cessation, switching from continued cigarette use to a
smokeless product or switching from continued smokeless product use to
cigarette smoking are not modeled. The model also does not allow non-
users of tobacco to initiate cigarette smoking.
Transition probabilities:
A crucial aspect of any model-based evaluation of the effectiveness
of a health policy is the model input. Any data selected for the model,
and the rationale for their selection, must be clearly documented for the
model to be useful in evaluating the potential effectiveness of a proposed
policy. In the tobacco harm reduction arena, model results depend heavily
on the transition probabilities selected to describe movement between
different tobacco exposure states that are expected to result from policy
changes. For their base case scenario, Mejia et al. estimated transition
probabilities based on multiple populations that differed with respect to
age, calendar year and region, even though patterns of tobacco use have
been shown to depend strongly on these factors (e.g. (CDC 2007; Gilpin,
Pierce, et al. 1992; Nelson, Mowery, et al. 2006; Roth, Roth, et al. 2005;
Tomar 2003). The estimated probabilities were applied to the entire
hypothetical population, and did not account for age or gender. In
addition, some transition probabilities were based on the estimated
lifetime prevalence of ever use, others on the prevalence of current use,
and yet others on the 2-year incidence of initiation, even though
incidence and prevalence are not interchangeable measures or concepts.
* The incidence of smokeless product initiation (4%) was based on the
arithmetic average of: the prevalence of smokeless product use among
adults in 2005 based on the National Survey on Drug Use and Health (3.3%)
(NSDUH 2005); the prevalence of smokeless product use among adults (2.3%)
based on data from the National Health Interview Survey (NHIS) conducted
in 2000 (Nelson et al., 2006); and the prevalence of smokeless product use
among 9-12th graders in 2003 (6.7%) based on NHIS data (Nelson et al.,
2006). Mejia et al. (2010) averaged these prevalence estimates without
taking the differences between the source populations into account.
* To estimate transition probabilities from smokeless tobacco use to
other exposure states, Mejia et al. used data from Oregon boys in grades 7
and 9 who were followed for 2 years in the late 1990s. The implicit
assumption was that the hypothetical population of smokeless product
"initiators" (which in their example was the population of current
smokeless product users) was like Oregon 7th and 9th grade boys in terms
of their tobacco use patterns.
* The incidence of cigarette smoking initiation was assumed to be
equal to the lifetime prevalence of ever smoking among US adults in 2006
(40%). Mejia et al (2010) then divided the group of cigarette
"initiators" (i.e., ever smokers in 2006) into categories of continuing
smokers, quitters, smokeless product users and dual users based on their
motivation to quit smoking in future. The transition probabilities were
chosen such that "the end state reflected the current smoking and
smokeless use prevalence and quit ratio in the 2006 NHIS survey" (page
298), although the NHIS 2006 survey data were not used by Mejia et al. to
provide estimates of smokeless use. The end state distribution of
continuing smokers and quitters was approximately even (47% and 53%,
respectively) based on the NHIS estimate that 50% of current smokers were
able to quit smoking.
Discussion of the motivation to quit smoking in the future (will
never quit; is health concerned; is affected by smoke-free regulations;
and is price sensitive) comprised a substantial part of the Mejia et al.
paper. However, motivation to quit is irrelevant to the stated purpose of
the model, which was to estimate the population-level health effect to be
expected under different distributions of cigarette smoking and smokeless
tobacco use. The proportions of subjects in each motivation category were
reportedly based on a study of adult smokers who had smoked for at least 5
years in 1987 (Gilpin, Pierce, et al. 1992). This cross-sectional study
used data from the 1987 NHIS and reported the distribution of reported
reasons for quitting smoking in the past 5 years among former smokers, and
not motivation to quit smoking in the future among current smokers. The
Gilpin et al. study did not consider a "smoke-free environment" category,
it included a "health concerned and price sensitive" category because of
considerable overlap between the two categories among their respondents,
and it included several additional categories not considered by Mejia et
al. (e.g., "lost interest" and "miscellaneous", among others). The
proportion of the population of former smokers reporting reasons for
quitting smoking that were not considered by Mejia et al. was almost 50%
in the Gilpin et al. (1992) data. Further, according to Gilpin et al.,
the proportion of subjects that had never tried to quit smoking was 18%
among ever smokers and 33% among current smokers, values that are very
different from the 10% estimated by Mejia et al. (2010).
* Finally, Mejia et al. calculated the probability of remaining a non
-user of tobacco (56%) as the remainder after accounting for the 40% of
the population identified as smoking "initiators" and the 4% of the
population identified as smokeless tobacco "initiators". The model allowed
cigarette "initiators" (i.e., ever smokers) and smokeless product
"initiators" (i.e., current users) to transition to other tobacco exposure
states, but those initially defined as non-users of tobacco were not
allowed to transition into tobacco use.
Tobacco-related health effects:
Mejia et al. created an artificial "tobacco-related health effects"
variable to place the different tobacco exposure categories on a
continuum of risk, where non-users of tobacco were at zero, former
smokers, current smokeless product users and current dual users were log-
normally distributed with means of 5, 11 and 90, respectively, and smokers
were at 100. References to justify these values were only provided for
smokeless product users; even in this case, the value of 11 (standard
deviation = 5) was not directly derived from data but was a consensus
estimate. Neither duration of use nor cessation was considered in
estimating tobacco-related health risk.
Scenarios and results:
Mejia et al. modeled a number of scenarios to represent different
levels of adoption of smokeless tobacco products due to varying
hypothetical levels of successful smokeless product promotion. The
modeled results under each of the scenarios produced wide posterior
intervals that overlapped with one another and the base case scenario,
indicating that none of the point estimates could be interpreted as
demonstrating statistically significant differences in health risk
resulting from differences in the exposure distributions. Under the
"aggressive smokeless promotion" scenario considered by Mejia et al. to be
the most extreme example, the transition probabilities and other
assumptions in the model (e.g. that half the smokeless product users came
from never tobacco users) were so unrealistic that even though a much
lower health risk was assumed for smokeless product users than for
cigarette smokers, the model suggested (statistically non-significant) net
harm at the population level.
Mejia et al. acknowledged that their transition probabilities were
less than ideal, but claimed that better data were unavailable. However,
we found several examples that could have been used: Lundqvist et al.
reported on patterns of tobacco use in a population of middle-aged Swedes
that included initiation, cessation and rates of transition among
cigarettes, smokeless tobacco and dual use over a ten year period
(Lundqvist, Sandstrom, et al. 2009). Transitions between exposure states
among adults in the United States, including cessation of smokeless
tobacco and dual use, were provided by Zhu et al. in analyses of the
Current Population Survey-Tobacco Use Supplement for 2002 and 2003 (Zhu,
Wang, et al. 2009). Smoking initiation rates are available from the
National Health Interview Survey (Escobedo and Peddicord 1997). The
National Survey on Drug Abuse provides estimates of smoking initiation in
the US (Office of Applied Statistics, 1998 and 1999); its successor, the
National Survey of Drug Use and Health, provides estimates of cigarette
and ST initiation for people aged 12 and older as recently as 2008
(http://oas.samhsa.gov/nsduh/2k8nsduh/2k8Results.pdf); and Davis et al.
provided estimates of smoking initiation specifically for youth smokers
(Davis et al., 2009). The study of Oregon teenagers that Mejia et al.
relied on for smokeless tobacco product transition rates (Severson,
Forrester, et al. 2007) also reported the probability of cigarette and
smokeless tobacco initiation and the transition probabilities for those
who used smokeless products at baseline, but these estimates were not used
by Mejia et al.
From these alternative sources, we selected the three papers
(Lundqvist et al., 2009; Severson et al., 2007 and Zhu et al., 2009) that
provided the most complete sets of initiation, cessation and transition
probabilities for comparison with the data used by Mejia et al. (2010).
Compared to the probabilities presented by Lundqvist et al. (2009) for
Swedish adults and the probabilities observed by Severson et al. (2007)
among teenage boys in Oregon, Mejia et al. considerably underestimated the
proportion of persons remaining non-tobacco users and greatly
overestimated the smoking initiation probability among non-tobacco users.
The estimate used by Mejia et al. (2010) was similar to that provided by
Escobedo and Peddicord (1997) based on data from the early 1980s, but
greater than that provided by Davis et al. (2009) based on students in
grades 6-12 who participated in the ALLTURS study between 2000 and 2002.
Further, contrary to evidence reported by Zhu et al. and Lundqvist et al.
(2009), Mejia et al. (2010) assumed that (i) cessation of use was much
lower among smokeless product users than cigarette smokers while
initiation of dual use was much higher among smokeless product users; and
(ii) switching from one product to the other was much more common among
smokeless tobacco users than cigarette smokers.
Model validation:
Mejia et al. did not report any attempt to validate their model,
although they did successfully replicate results, using similar model
input, produced by another technique (Gartner, Hall, et al. 2007). Some
problems underlying the model whose results Mejia et al. chose to
replicate have been discussed elsewhere (Sulsky, Bachand et al., 2010)
SENSITIVITY ANALYSIS
Having identified problems with the data selected as model input by
Mejia et al., we attempted to assess the model assumptions by using more
defensible input and evaluating the difference in results. Although the
authors provided the full model input, via a spreadsheet accessible to
journal (Tobacco Control) subscribers through its web site, the
spreadsheet does not perform any calculations. However, we had already
used the WinBUGS computer program to create a simulation model that
estimates mortality or morbidity for a hypothetical population of persons
who have never used tobacco and who, as they age, may transition into and
out of 33 possible tobacco exposure states, including current and former
smoking or smokeless product use and recidivism for those who had quit. A
brief description of this model is available (Bachand, Curtin, et al.
2010); a full description is currently being prepared for peer review. We
were able to use the data documented in the spreadsheet provided by Mejia
et al. in a simplified form of our simulation model to replicate their
results. We then tested the sensitivity of their model by modifying the
input documented by Mejia et al. and using it in the simplified form of
our model.
Alternative results:
We simplified our model to restrict it to the transitions described
by Mejia et al. (2010). After cigarette smoking initiation, only one
change in tobacco exposure was allowed, and only one change was allowed
after smokeless product initiation unless the subject switched to
cigarettes; in this case, one additional change could be made. For
transitions not modeled by Mejia et al., we used transition probabilities
of 0. Using the model input specified by Mejia et al. (2010) was
difficult to accomplish for several reasons: (i) Mejia et al. did not take
age into account, while our model does; (ii) We did not use prevalence as
an estimate of incidence in our model. Whenever their transition
probabilities were prevalence estimates, we used incidence estimated from
the National Household Survey on Drug Abuse (Office of Applied Studies,
1999), instead; and (iii) The proportions used by Mejia et al. to
describe the distribution of motivations to quit were not useful for the
stated purpose and were not based on reliable information; therefore, we
calculated the weighted average of their transition probabilities for each
of the four end states: quitting, continuing cigarette use, switching to a
smokeless product and dual use.
For this example, we used Mejia et al.'s comparison of the "aggressive
smokeless promotion" scenario to their base case scenario. To approximate
the input used by Mejia et al., we kept the ratios between the transition
probabilities the same as the ratios between the "aggressive smokeless
promotion scenario" and the transition probabilities in their base case
scenario. It is important to keep in mind that their base case scenario
assumed that 4% of the population used smokeless products while we assumed
no form of tobacco use at baseline, but allowed proportions of the
population to initiate cigarette or smokeless tobacco use at user-defined,
age-specific rates.
In our analysis, follow-up started at age 13, the youngest age at which a
non-negligible proportion of tobacco users initiates use, and ended at age
72. The width of each age category was five years. To allow for validation
of the model results against current mortality data accounting for
adequate disease induction time, we based age category-specific smoking
initiation rates on the 1980 National Household Survey on Drug Abuse
(Office of Applied Studies, 1999). Age category-specific smoking
cessation rates for 1980 were based on data from The California Tobacco
Control Program's effect on adult smokers: (1) Smoking cessation (Messer K
et al., 2007). More recent data could be used to model prospective future
population health effects, if desired. For smoking initiation, we used
11.25%, 10%, 1.25% and 0.25% for age categories 13-17, 18-22, 23-27and 28-
32 years, respectively, and 0 for older age categories. For smoking
cessation, we used 2.5% for age 13-17, 4.5 for the next 3 age categories,
5.0 for category 33-37 years, 5.5 for categories 38-42 and 43-47 years,
7.5% for category 48-52 years and 8.5% for the remaining 4 age categories.
Mejia et al. used tobacco use patterns reported by 145 7th and 9th grade
boys to estimate the transition probabilities for the whole population
following the use of a smokeless product. Therefore, we also used the
transition probabilities reported for the 7th and 9th grade boys for all
ages in our model.
Our model uses age-, years of smoking- and years of quitting-specific
mortality rates based on the coefficients from a Poisson model estimated
using data for men from the Kaiser Permanente Cohort study (Friedman,
Tekawa, et al. 1997). The ratio of excess risks for current smokeless
tobacco users versus smokers (0.08) was based on a consensus estimate
reported by Levy et al. (Levy, Mumford, et al. 2004), and the ratio of
excess risks for former smokeless product users versus smokers was set to
0.05. While Mejia et al. combined men and women in their analysis, we
restricted our analysis to men because tobacco use patterns vary
considerably between genders (see paragraph two of "Limitations", page 303
in Mejia et al. and reference numbers 5, 6, 12, 22, 29, 30, 31, and 36
from Mejia et al.).
Using data that replicated, as closely as possible, the flawed input
and transition probabilities used by Mejia et al. to define a "worst-case"
scenario of aggressive smokeless tobacco promotion, we, like them,
observed statistically non-significant net harm. That is, there were more
deaths estimated at the end of follow-up under the test scenario compared
to the base-case, but the difference was not statistically significant.
We then made a slight change in the transition probabilities, such
that the probabilities for transitions from smokeless tobacco use reported
by Severson et al. for 7th and 9th grade boys were applied only to the
youngest two age categories (13-<18 and 18-<23 years). For all other
age groups, we used the transition probabilities reported by Lundqvist et
al. or by Zhu et al. This change resulted in statistically significant net
benefit , i.e., there were fewer deaths estimated at the end of follow-up
under the test scenario compared to the base-case. Thus, running the model
with only slightly more realistic input produced statistically significant
estimates that suggested a benefit of aggressive smokeless tobacco
promotion, rather than harm, at the population level.
As described above, the model used by Mejia et al. incorporated a
very limited number of possible transitions between exposure states.
Therefore, we wanted to determine the effect of using the flawed
transition probabilities suggested by Mejia et al., but allowing all
possible transitions in our model.
For transitions not modeled by Mejia et al., we assumed that transition
probabilities for "no change in tobacco use" were 95%, while transition
probabilities for "changes in tobacco use" were 5%; when more than one
type of change was possible, the transition probability of 5% was divided
between them. For example, the probability of remaining a cigarette smoker
(no change) after several previous changes in tobacco use was set to 95%
while the probability of switching back to a smokeless product and the
probability of quitting were set to 2.5% each. We repeated the analysis
allowing a 25% probability for "change in tobacco use" while the
transition probabilities for "no changes" were 75%.
Allowing for a small degree (5%) of recidivism and switching from one to
the other product after previous changes in tobacco use (while using Mejia
et al.'s input, to the extent possible, for transitions considered in
their model), we observed a net benefit (i.e., a reduction in mortality)
at the population level. The benefit was statistically significant, based
on the 95% posterior intervals, even when the transition probabilities for
the 7th and 9th grade boys were applied to all ages. Allowing for a
greater degree (25%) of recidivism and switching from one to the other
product resulted in an even more pronounced, statistically significant,
population benefit.
CONCLUSIONS
The model proposed by Mejia et al. model is overly simplistic in its
use of only a limited number of exposure states and transitions: 56% of
the starting population, identified as non-tobacco users at baseline, are
not allowed to become tobacco users; no one who quits tobacco use is
allowed to revert to a tobacco use state; the model uses the same
initiation, cessation and transition rates for the whole hypothetical
population, regardless of age or gender; and, the risk of tobacco related
health outcomes "measured" by the health index is assumed to be the same
regardless of duration of tobacco use or cessation.
The sources used by Mejia et al. (2010) to define the initial
exposure distribution and the transition probabilities are difficult to
justify. The authors mixed estimates for adult men and women, drawn from a
nationally representative sample of current and former smokers, and for
145 7th and 9th grade boys who attended secondary school in one of a few
towns in Oregon. The transition probabilities used by Mejia et al.
incorrectly implied that smokeless tobacco users were very unlikely to
quit (a beneficial transition) and very likely to switch to smoking or to
initiate dual use (harmful transitions) while smokers were very likely to
quit or to switch to smokeless tobacco (beneficial transitions) and
unlikely to initiate dual use (a harmful transition).
The health index is of questionable validity, and does not seem to be
based on empirical data. The data purportedly used to justify the values
assigned to the health index comprised a mix of diseases and causes of
death, measures of effect (incidence and prevalence), and exposures
(product types). Furthermore, the Mejia et al. model assumes that risks
associated with each type of tobacco product are the same for all users,
i.e., the risk of experiencing a tobacco-related health outcome "measured"
by the health index is assumed to be the same for males, females, all
ages, and any duration of use or former use of tobacco.
The results reported by Mejia et al. did not indicate statistically
significant differences between exposure groups, yet the authors
interpreted the results as showing no benefit of smokeless tobacco. An
objective interpretation of their results is that the model provides no
evidence for either benefit or harm to the population associated with
increased promotion of smokeless tobacco use.
Due to the significant shortcomings of the methods employed by Mejia
et al., their conclusion that "promoting smokeless tobacco as a safer
alternative to cigarettes is unlikely to result in substantial health
benefits at a population level" does not follow from the results. Small
changes to Mejia et al.'s model input or assumptions led to the opposite
conclusion. Because of its flaws, the simulation model proposed by Mejia
et al. does not provide information that can be used in evaluating or
setting tobacco control policy.
BIBLIOGRAPHY
Bachand AM, Curtin G, et al. 2010. Development of a dynamic
simulation model to estimate population mortality effects resulting from
the availability of smokeless tobacco products. Ann Epidemiol 20: P70.
CDC. 2007. Cigarette smoking among adults--United States, 2006. MMWR Morb
Mortal Wkly Rep 56: 1157-1161.
Escobedo LG, Peddicord JP. 1997. Long-term trends in cigarette smoking
among young U.S. adults. Addict Behav 22: 427-430.
Friedman G, Tekawa IS, Sadler M, Sidney S. 1997. Smoking and mortality:
the Kaiser Permanente experience. In: Shopland DR, Burns DM, Garfinkel L,
Samet J, editors. Changes in Cigarette-Related Disease Risks and Their
Implication for Prevention and Control. Rockville, MD: US Department of
Health and Human Services, Public Health Service, National Institutes of
Health, National Cancer Institute.p 477-499.
Gartner CE, Hall WD, et al. 2007. Assessment of Swedish snus for tobacco
harm reduction: an epidemiological modelling study. Lancet 369: 2010-2014.
Gilpin EA, Pierce JP, et al. 1992. Reasons smokers give for stopping
smoking: do they relate to sucess in stopping? Tob Control 1: 256-263.
Levy DT, Mumford EA, et al. 2004. The relative risks of a low-nitrosamine
smokeless tobacco product compared with smoking cigarettes: estimates of a
panel of experts. Cancer Epidemiol Biomarkers Prev 13: 2035-2042.
Lundqvist G, Sandstrom H, et al. 2009. Patterns of tobacco use: A 10-year
follow-up study of smoking and snus habits in a middle-aged Swedish
population. Scandinavian Journal of Public Health 37: 161-167.
Mejia AB, Ling PM, et al. 2010. Quantifying the effects of promoting
smokeless tobacco as a harm reduction strategy in the USA. Tob Control 19:
297-305.
Nelson DE, Mowery P, et al. 2006. Trends in smokeless tobacco use among
adults and adolescents in the United States
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Roth HD, Roth AB, et al. 2005. Health risks of smoking compared to Swedish
snus
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Severson HH, Forrester KK, et al. 2007. Use of Smokeless Tobacco is a Risk
Factor for Cigarette Smoking. Nicotine Tobacco Research 9: 1331-1337.
Tomar SL. 2003. Trends and patterns of tobacco use in the United States
1. Am J Med Sci 326: 248-254.
Zhu SH, Wang JB, et al. 2009. Quitting Cigarettes Completely or Switching
to Smokeless: Do U.S. Data Replicate the Swedish Results? Tobacco Control
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Conflict of Interest:
Competing interests: The authors are preparing an alternative tobacco harm reduction model. This work was supported by RJ Reynolds Tobacco Company.
NOT PEER REVIEWED "The GC temperature programme for all analyses was: 35C hold for 5???min; 10C/min to 300C; then hold for 3.5???min at 300C."
Water is not dangerous. Yet, if I submerge a human test subject in a container of water for 3.5 minutes, then this water becomes quite lethal. No vaping device is intended to run continuously for longer than a few seconds.
Furthermore, 300C is far too high a temperature for any vaping de...
NOT PEER REVIEWED "The GC temperature programme for all analyses was: 35C hold for 5???min; 10C/min to 300C; then hold for 3.5???min at 300C."
Water is not dangerous. Yet, if I submerge a human test subject in a container of water for 3.5 minutes, then this water becomes quite lethal. No vaping device is intended to run continuously for longer than a few seconds.
Furthermore, 300C is far too high a temperature for any vaping device. If I force a human test subject to drink a large cup of coffee heated to 300C, they will suffer severe injuries, possibly fatal. This does not make coffee consumed at an appropriate temperature and at an appropriate pace dangerous.
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