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Empowering individuals to influence their environment
both at home and in public is
the purpose of The
Breathing Association’s
advocacy activities. The
Breathing Association works with
the EPA (Environmental Protection Agency) promoting the Smoke
Free Home Pledge program. This program asks adults
to sign a pledge to keep their home smoke free. By taking the pledge
adults agree that they will ask their friends, family, and any guest
to refrain from smoking while in their home. An extension of the
pledge...making your car smoke free as well, can be part of your
commitment to providing a better environment for the children,
ill and elderly in your care.
The
Breathing Association encourages individuals to take the Smoke
Free Pledge and keep their car and home smoke free. Click
here to sign up for a free pledge kit.
In public places as a member of the Tobacco
Free Collaborative, The
Breathing Association promotes
the Eat, Breathe and Dine Smoke
Free program. Other advocacy activities include The
Great American Smoke-Out, Operation
Storefront, and Smoke
Free Restaurants Are Clearly Better.
A Brief
Review of the Science and Epidemiology of Secondhand Smoke
Despite two decades
of research and more than 1000 scientific studies that overwhelmingly
demon–strate the substantial and varied injuries caused by secondhand
smoke, some people still believe tobacco industry-generated propa–ganda
that secondhand smoke is not a major health problem. Not surprisingly, the dialogue between clean indoor air advocates
and tobacco industry supporters often gets heated, and both sides can
be drawn into “blowing smoke” by citing secondary and exaggerated
source material, primarily from activist web sites. In an effort to “clear
the air,” and counter factual misstatements by opponents, SmokeFree
Columbus has undertaken a systematic and extensive litera–ture
review. The result is pre–sented below: a synopsis of the available
primary sources that provide an accurate view of the strengths and limitations
of the current science of passive smoking.
Introduction
Over the seventeen years since the first Surgeon General’s report[i] on
hazards of secondhand smoke, epidemiologists and medical scientists have
developed an even more extensive body of evidence about its noxious and
deadly effects. We now understand
much more about the chemistry of smoke itself, its effect on human tissues
and the considerable injury secondhand smoke imposes on the human body
both in the long and short term.
Secondhand
Smoke Constituents
As is often cited, secondhand smoke contains nearly 4000 chemicals and
organic compounds, two hundred of which are known poisons and over 50
show carcinogenic potential.[ii] Nine
of these are classified by the US Environmental Protection Agency (EPA)
as Group A carcinogens[iii] where
there is sufficient evidence from epidemiologic
studies to support a casual association between exposure to the agents
and cancer. The EPA also classifies
secondhand smoke itself as a Group A carcinogen.
The smoke that comes off the end of a cigarette is different than mainstream
smoke. Without inhalation,
burning is slower and cooler; combustion is less complete, and the smoke
does not pass through the body of the cigarette or the filter. As
such "sidestream"
smoke generally contains more nicotine, more carbon monoxide, more carcinogens
and more irritant particles and gasses than does the smoke a smoker actively
inhales[iv]. Another
often overlooked aspect of secondhand smoke exposure
is that smokers tend to develop a level of tolerance to the drug effects
of nicotine, the inflammatory effects of irritant tars, and the oxygen
reduction caused by carbon monoxide. Nonsmokers
who are not so accustomed may therefore have more intense, violent and
even lethal reactions[v],[vi].
Effects
When human tissues are exposed to levels of secondhand smoke commonly
found in the home of a smoker or a bar or restaurant where smoking is
occurring, there are a variety of both immediate and long term effects. Oral
and pharyngeal membranes react with tissue swelling and increased mucous
production. Respiratory cilia, the small moving wave of hairs in the lung
passages, are paralyzed, thereby preventing the efficient removal of
irritant particles, viruses and bacteria.[vii],[viii] Spasm
may occur in the smallest lung passages, the bronchioles. The
larger airways experience the most overt reactions of sneezing and coughing. In
susceptible individuals these effects of secondhand smoke may precipitate
a serious or deadly asthma attack, while the chronic irritation and inflammation
wrought by secondhand smoke is
thought to be responsible for lung cancer.[ix]
Less overt is the effect secondhand smoke has on the cardiovascular system. The
levels of nicotine and carbon monoxide found in secondhand smoke cause
arteriolar constriction and an increase in heart rate and blood pressure
in susceptible individuals. The
lining of the blood vessels and the clotting factors in blood may be
inflamed or disturbed. These
effects combined with the reduction of oxygen caused by carbon monoxide’s
effect on blood hemoglobin is probably why secondhand smoke exposure
is so strongly linked to coronary heart disease, angina and sudden unexplained
death.[x]
Measuring Exposure
How do we know how much smoke and its toxic ingredients are actually in
an environment where people are smoking? How
can we gauge if nonsmokers are actually exposed in a public place or
a workplace setting? We
have several valuable tools. We
can directly measure the some of the constituents of secondhand
smoke in the air and we can assay biologic markers
within bodily fluids. Measurements
of nicotine, particulate matter and other noxious gasses have been utilized
in a variety of studies.
Obviously, ambient indoor air conditions vary widely, but typically concentrations
of nicotine in residences where smoking occurs tend to run between 2
and 10 micrograms per cubic meter. Smoking
sections of bars, however, may run as high as 50-75 mg/m3. [xi] There
is no reliable way to ascertain what is a safe level of this dangerous
and addictive drug.
The second direct measure of secondhand smoke has
been to look at respirable suspended particles (RSP). These particles are not specific to secondhand smoke and therefore
RSP measurements must be compared between smoking and non-smoking environments. Variations
in settings cause variations in measurements but in general RSP's run
somewhere between 10% and 300% higher in smoking environments.[xii]
Measuring other air pollutants associated with secondhand smoke is complicated because like RSP's there are often other sources of these
gasses in the indoor environment. Polycyclic
aromatic hydrocarbons have been studied extensively in home environments. These
are known carcinogens and were found to be 1.5 to 4 times higher in homes
with no other known combustion source other than smoking as compared
to similar homes without smoking.[xiii]
More important perhaps are the biologic markers of secondhand smoke. These are measures of toxins found in nonsmokers who are exposed
to secondhand smoke compared
to nonsmokers who are not exposed. The
most important tools have been measurement of cotinine, a long lasting
metabolite of nicotine, and various direct and indirect measures of carbon
monoxide.
The biologic half life (the time it takes for the level of a substance
to drop to half its original level in the body) for cotinine is similar
for most bodily fluids – approximately 15-19 hours.[xiv] Generally,
significant cotinine does not come from any other source other than tobacco,
tobacco smoke or nicotine replacement products, and is therefore an excellent
indicator of specific exposure in an involuntary smoker.[xv] Whereas
smokers attain much higher levels of cotinine than do involuntary smokers,
the presence of cotinine does indicate that a nonsmoker has been substantially
exposed.
Carbon monoxide and blood hemoglobin bound to carbon monoxide (carboxyhemoglobin)
are excellent indicators of the amount and intensity of a smoker's habit. However,
carbon monoxide can come from any combustion source and only in very
heavy secondhand smoke exposures
can one distinguish carbon monoxide levels between secondhand
smoke exposed and unexposed people.
Other important measures of exposure to secondhand smoke are quantitative
surveys of exposure at home, work or public places.. Historically
the main focus of large population-based studies has been on active smoking,
however, more recent studies have examined secondhand smoke exposure
for a variety of sub populations. As an example, in California in 1990,
a large survey showed that 42% of adult nonsmokers were exposed to secondhand
smoke [xvi] and
the average exposure was 250 minutes per day[xvii]. One
suspects that theses estimates have dropped especially in California
where all public places are now legally smokefree. Of
interest is the fact that many nonsmokers who do not recall an exposure
to secondhand smoke are
found to have significant levels of cotinine in their bodily fluids. This
suggests that there may be substantial underreporting of secondhand
smoke exposure.
The
Human Toll
There have now been
several hundred scientific studies examining the adverse medical effects
of secondhand smoke. Scientists have defined several broad categories of human
injury provoked by secondhand smoke. These
include prenatal and perinatal deaths, sudden infant death syndrome (SIDS);
respiratory health effects including asthma, infections, irritation,
reduced lung function, sickle cell crises and chronic pulmonary disease;
carcinogenic effects focusing on lung and breast cancer; and cardiovascular
effects including myocardial infarction, coronary artery disease, angina
pectoris and sudden unexplained
death.
The effects on children are myriad. Fetuses
exposed by virtue of paternal smoking have higher rates of spontaneous
abortion[xviii] while
children born to mothers exposed at work are smaller[xix] and
have higher rates of stillbirth.[xx] The
two best studies to date on SIDS suggest that babies exposed to secondhand
smoke have at least twice the rate of death from this devastating disease.[xxi],[xxii]
A Chinese study of infants born to nonsmoking mothers,
but exposed to secondhand smoke at
home, concluded that 9% of the total costs of medical care for this
age group and over 1500 extra hospital admissions was attributed to
tobacco smoke in Hong Kong.[xxiii]
Asthma affects 5 million American children is the most common chronic
condition of childhood. It
accounts for more than $3.2 billion in health care costs for children
alone.[xxiv] There
seems to be little question, involuntary smoking exacerbates asthma and
provokes specific attacks in both children and adults.[xxv],[xxvi] In
addition, there is suggestive data that secondhand smoke actually
induces new cases of asthma at a rate twice that of nonsmoking homes.[xxvii]
Moreover more than 10 different studies demonstrate that secondhand
smoke provokes significant increases
in otitis media, upper respiratory illness, pneumonia and school absence
in children.3,[xxviii] In
California alone secondhand smoke related
otitis media causes 78-188,000 office visits per year for children under
three and 18-36,000 cases of bronchitis or pneumonia. [xxix] Secondhand
smoke may also have a terrible effect on children already debilitated
by disease. A recent study demonstrates that children with sickle cell
disease are twice as likely to suffer a painful and dangerous sickle
cell crisis if they are exposed to secondhand smoke.[xxx]
Lung cancer is the most deadly of all human cancers, and the causal relationship
between active smoking and carcinoma of the lung is now unquestioned. Beginning
with the sentinel study by Hiryama[xxxi] more
than 20 years ago and continuing through 30 other retrospective and case
control studies, the risk of lung cancer to a nonsmoker is now shown
to be 20% higher if he or she lives with a smoker.28 For
some time we have also known that smoking causes breast cancer, but just
as worrisome is the new and surprising discovery that breast cancer occurs
significantly more often in women exposed to secondhand smoke.[xxxii]
Most convincing of all, however, is the case that secondhand smoke causes substantial and deadly heart disease in nonsmoking adults. In
the last two decades more than 20 studies point to excess coronary morbidity
and mortality in nonsmokers exposed to secondhand smoke.28,[xxxiii],[xxxiv] Moreover
there is an expanding body of evidence in both animal and human studies
that underscore pathologic changes in body chemistry and function when
exposed to secondhand smoke and
help explain why secondhand smoke can
be so devastating to the cardiovascular system. "At
least five interrelated processes have been proposed to contribute to
the clinical manifestations of MI [heart attack], including: atherosclerosis,
thrombosis, coronary artery spasm, cardiac arrhythmia and reduced capacity
of blood to deliver oxygen"[xxxv]
Virtually all of the studies of heart disease, either case-controlled
or cohort, prospective or retrospective, have looked at individuals exposed
at home or work, based on their individual life and work styles. What
we, however, are proposing is regulation of a toxic exposure that will
cause a. community-wide shift not only in exposures to non-smokers but
also a decrease in use by smokers. Several
states and cities have taken these steps and their experience has been
studied.
As a result of its comprehensive tobacco control program that has at
its cornerstone a ban on workplace exposure to secondhand smoke, California estimates that 33,000 lives are spared annually from cardiovascular
disease.[xxxvi] The
most recent and compelling story is that of Helena, Montana.[xxxvii] For
the last 6 months of 2002, Helena enforced strict workplace ban until
it was preempted by industry sponsored state legislation. During
the time of the ban, admissions for heart attack at one large hospital
dropped 60%. After the law
was reversed, they resumed their previous level. Statistical
analysis including surrounding communities that were unaffected by the
ban demonstrated this effect to be both valid and profound.
Summary:
The evidence is now undeniable and overwhelming. Smoking
in homes, workplaces and public places endangers not only smokers but
also those who are exposed to secondhand smoke. In
the past twenty-five years more than 1000 papers and studies have been
published on this issue. Not
all have shown equal effects primarily because of the difficulty of measuring
ongoing socio/biologic behavior, but there is clear and convincing evidence
that public health and safety are jeopardized by secondhand smoke. Moreover,
banning smoking in workplaces unmistakably reduces deaths and injuries
not just for nonsmokers but for smokers themselves. In
Central Ohio, we have both an opportunity and a duty to respond to these
facts.
[i] U.S.
Department of Health and Human Services (U.S. DHHS, 1986). The
HealthConsequences of Involuntary Smoking: A Report of the Surgeon
General. U.S. DHHS, Public Health Service, Office on Smoking
and Health
[ii] International
Agency for Research on Cancer (IARC, 1986). Evaluation of the
CarcinogenicRisk of Chemicals to Humans--Tobacco Smoking. IARC
Monographs Volume 38, Lyon, France.
[iii] U.S.
Environmental Protection Agency (U.S. EPA, 1992). Respiratory
Health Effects of Passive Smoking: Lung Cancer and Other Disorders. U.S.
EPA Publication No. EPA/600/6-90/006F.
[iv] Baker
RR (1981). Product formation mechanisms inside a burning cigarette. Progr
EnergyCombustion Sci 7:135-153 (as cited in IARC, 1986).
[v] U.S.
Department of Health and Human Services (U.S. DHHS, 1990). U.S.
Public Health Service: The
Health Benefits of Smoking Cessation. A Report of the Surgeon General.
DHHS (CDC) 90-8416.
[vi] Leone
A, Mori L, Bertanelli F, Fabiano P, Filippelli M (1991). Indoor
passive smoking: Its effect on cardiac performance. Int J Cardiol 33:247-252.
[vii] Battista
SP (1976). Ciliatoxic components of cigarette smoke. In: Wynder
EL, Hoffman D, Gori GB (Eds). Smoking and Health. I. Modifying
the Risk for the Smoker. DHEW Publ. No. (NIH) 76-1221, pp.
517-534.
[viii] Wanner
A (1977). State of the art: Clinical aspects of mucociliary transport. Am
Rev Respir Dis116:73-125.
[ix] Cardenas
VM, Thun MJ, Austin H, Lally CA, Clark WS, Greenberg RS, Heath
CW Jr. (1997). Environmental tobacco smoke and lung cancer mortality
in the American Cancer Society’s Cancer Prevention Study
II. Cancer Causes and Control 8:57-64.
[x] Glantz
SA and Parmley WW (1995). Passive smoking and heart disease. Mechanisms
and risk. JAMA 273: 1047-1053.
[xi] U.S.
Environmental Protection Agency (U.S. EPA, 1992). Respiratory
Health Effects of Passive Smoking: Lung Cancer and Other Disorders.
EPA/600/6-90/006F. EPA Office of Research and Development, Washington,
DC.
[xii] Guerin
MR, Jenkins RA, Tomkins BA (1992). The Chemistry of Environmental
Tobacco Smoke: Composition and Measurement. Lewis Publishers,
Boca Raton.
[xiii] Sheldon
L, Clayton A, Keever J, Perritt R, Whitaker D (1993). Indoor
Concentrations of Polycyclic Aromatic Hydrocarbons in California
Residences. Draft Final Report, Contract No. A033-132.
Research Triangle Institute.
[xiv] Jarvis
M, Russell MAH, Benowitz NL, Feyerabend C (1988). Elimination of
cotinine from body fluids: implications for noninvasive measurements
of tobacco smoke exposure. Am J Public Health 78:696-698.
[xv] Benowitz
NL, Jacob P III (1994). Metabolism of nicotine to cotinine studied
by a dual stable isotope method. Clin Pharmacol Ther 56:483-493.
[xvi] Jenkins
PL (1992). Activity Patterns of Californians: Reported Exposures
to ETS. Presented at the Workshop on Health Effects of Environmental
Tobacco Smoke, Oakland, CA, October 14, 1992.
[xvii] Lum
S (1994a). “Duration and location of ETS exposure for the
California population,” memorandum from S Lum, Indoor Exposure
Assessment Section, Research Division, California Air Resources
Board, to L Haroun, Reproductive and Cancer Hazard Asssessment
Section, Office of Environmental Health Hazard Assessment, February
3.
[xviii] Windham
GC, Swan SH, Fenster L (1992). Parental cigarette smoking and the
risk of spontaneous abortion. Am J Epidemiol 135(12):1394-1403.
[xix] Martin
TR, Bracken MB (1986). Association of low birthweight with passive
smoke exposure in pregnancy. Am J Epidemiol 124(4):633-642.
[xx] Ahlborg
G Jr., Bodin L (1991). Tobacco smoke exposure and pregnancy outcome
among working women. A prospective study at prenatal care centers
in Orebro County, Sweden. Am J Epidemiol 133(4):338-347.
[xxi] Klonoff-Cohen
HS, Edelstein SL, Lefkowitz ES, Srinivasan IP, Kaegi D, Chang JC,
Wiley, KJ (1995). The effect of passive smoking and tobacco exposure
through breast milk on sudden infant death syndrome. JAMA 273:795-798.
[xxii] Blair
PS, Fleming PJ, Bensley D, Smith I, Bacon C, Taylor E, Berry J,
Golding J, Tripp J (1996). Smoking and the sudden infant death
syndrome: results from 1993-5 case-control study for confidential
inquiry into stillbirths and deaths in infancy. BMJ 313:195-198.
[xxiii] Leung
GM, Ho LM, Lam TH 2003 The economic burden of environmental tobacco
smoke in the first year of life. Arch Dis Chld: 2003 Sep;88(9):767-71.
[xxiv] Asthma's
impact on children and adolescents. National Center for Environmental
Health. 6/23/03 http://www.cdc.gov/nceh/airpollution/asthma/children.htm
[xxv] Evans
D, Levison MJ, Feldman CH, Clark NM, Wasilewski Y, Levin B, Mellins
RB (1987). The impact of passive smoking on emergency room visits
of urban children with asthma. Am Rev Respir Dis 135:567-572.
[xxvi] Murray
AB, Morrison BJ (1989). Passive smoking by asthmatics: its greater
effect on boys than on girls and on older than on younger children. Pediatrics 84(3):451-459.
[xxvii] Burchfiel
CM, Higgins MW, Keller JB, Howatt WF, Butler WJ, Higgins IT (1986).
Passive smoking in child-hood. Respiratory conditions and pulmonary
function in Tecumseh, Michigan. Am Rev Respir Dis 133(6):966-973.
[xxix] California
Environmental Protection Agency, Office of Environmental Health
Hazard Assessment (1997) Health effects of exposure to environmental
tobacco smoke, final report. pp 6-68.
[xxx] West DC, Romano PS, Azari
R, et al Impact of environmental
tobacco smoke on children with sickle cell disease..
Arch Pediatr Adolesc Med. 2003;157:1197-1201.
[xxxi] Hirayama
T (1981). Non-smoking wives of heavy smokers have a higher risk
of lung cancer. Br Med J 282:183-185.
[xxxii] California EPA. Proposed
identification of environmental tobacco smoke as a toxic air contaminent. Public
review draft, November 2003. Section
7.
[xxxiii] Svendson,
KH, Kuller LH, Martin MJ, Ockene JK (1987). Effects of passive
smoking in the multiple risk factor intervention trial. Am
J Epidemiol 126(5): 738-795
[xxxiv] Steenland
K, Thun M, Lally C Jr (1996). Enviornmental tobacco smoke and coronary
heart disease in the American Cancer Society CPS-II Cohort. Circulation
89:2260-2265
[xxxv] California
Environmental Protection Agency, Office of Environmental Health
Hazard Assessment (1997) Health Effects of Exposure to Environmental
Tobacco Smoke. Final Report.
[xxxvi] Fichtenberg
CM, Glantz SA. Association of the California Tobacco Control
Program with declines in cigarette consumption and mortality
from heart disease. N Engl J Med. 2000 Dec 14;343(24):1772-7.
[xxxvii] Sargent
RP, Shepard R, Glantz S. Myocardial
infarctions in Helena, Montana before, during and after a citywide
workplace smoking ban. Presentation to the Annual College of Cardiology
Scientific Session. 4/1/03.
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