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Passive Smoking and Heart Disease: Epidemiology, Physiology, and Biochemistry.
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CR900213R3
In press
Circulation
PASSIVE SMOKIr1G AND HEART DISEASE:
EPIDEMIOLOGY, PHYSIOLOGY, AND BIOCHEMISTRY
Stanton A. Glantz, PhD
William W. Parmley, MD
Division of Cardiology, Department of Medicine
Cardiovascular Research Institute
University of California
San Francisco, CA 94143
Short title: Passive Smoking and Heart Disease
This manuscript is based on a background paper prepared for the U.S. Environmental Protection
Agency. It was
also presented at the Seventh World Conference on Tobacco and Health, Perth, Australia, April 1-5,
1990, and the
World Conference on Lung Health, Boston, MA, May 20-24, 1990.
Address for Correspondence and Reprints: Stanton A. Glantz, Ph.D.
Professor of Medicine
Division of Cardiology
~ Box 0124 M1186
University of California
San Francisco, CA 94143-0124
(415) 476-3893
FAX: (415) 476-0424

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ABSTRACT
The evidence that environmental tobacco smoke (ETS) increases risk of death from heart disease is
similar
to that which existed in 1986 when the Surgeon General concluded that ETS caused lung cancer in
healthy
nonsmokers. Eleven epidemiological studies, done in a variety of locations, reflect a 3096 increase
in risk of death
from ischemic heart disease or myocardial infarction in nonsmokers living with smokers. The larger
studies
demonstrate a dose-response effect. The epidemiological studies are complemented by a variety of
physiological
and biochemical data from human studies which show that ETS adversely affects platelet function and
damages
arterial andothelium, increasing the risk of heart disease. ETS also exerts adverse effects on
exercise capability of
healthy people and those with heart disease by reducing the body's ability to deliver and use
oxygen. In animal
experiments, ETS also depresses cellular respiration at the level of mitochondria. The polycyclic
aromatic
hydrocarbons in ETS also accelerate, and may initiate, the development of itherosclerotic plaque.
Nonsmokers.
appear to be more sensitive to ETS than smokers. In terms of cardiovascular disease, it is incorrect
to compute
"cigarette equivalents" for passive exposure to ETS, then try to extrapolate the effects of this
exposure on
nonsmokers from the effects of direct smoking on smokers. ETS causes heart disease, and ETS-induced
heart
disease may account for about ten times as many deaths as ETS-induced lung cancer. ETS is the third
leading
preventable cause of death, after primary smoking and alcohol.
CONDENSED ABSTRACT
The evidence that environmental tobacco smoke (ETS) increases risk of death from heart disease is
similar
to that available when the Surgeon General concluded that ETS caused lung cancer in healthy
nonsmokers. ETS
increases risk of death from heart disease by 3096 among nonsmokers living with smokers. ETS
adversely affects
platelet function and damages arterial endothelium. ETS significantly reduces exercise capability of
healthy people
and those with heart disease, as well as mitochondrial respiration. The polycyclic aromatic
hydrocarbons in ETS
accelerate the development of atherosclerotic plaque. ETS causes heart disease and is the third
leading preventable
cause of death, after active smoking and alcohol.
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Key Words
artherosclerosis myocardial infarction
bentio(a)pyrene passive smoking
carbon monoxide platelets
environmental tobacco smoke polycyclic aromatic hydrocarbons
epidemiology secondhand smoke
mitochrondia tobacco smoke pollution

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The first disease linked definitively to active smoking was lung cancer. It is, therefore, not
surprising that
the first disease identified as caused by passive smoking was also lung cancer'. Before the advent
of mass marketed
cigarettes, lung cancer was a rare disease. Since smoking is the primary cause of lung cancer,
identication of this
link - for both active2 and passive smoking' - was relatively straightforward. This situation
contrasts with heart
disease, which has many risk factors. It is not surprising that it took longer for the scientific
community to
conclude that active smoking caused heart disease. Once the link between smoking and heart disease
was
established, it became clear that smoking killed more people by causing or aggravating heart disease
than did the
lung cancer. In fact, smoking is the most important preventable cause of coronary disease. Exposure
to
environmental tobacco smoke (ETS) has now been linked to heart disease in nonsmokersxa.
Much of the evidence for this link has appeared since the US Surgeon General' and National Academy
of.
Sciences7 reviewed the evidence on the health effects of ETS in 1986. Based on the information
available then, both
reports concluded that the evidence linking ETS and heart disease was equivocal and that more
research was
necessary before any definitive statements could be made. These conclusions were reasonable in 1986.
In the four
years since these reports were written, considerable information on both the epidemiology and
biological
mechanisms by which ETS causes heart disease has accumulated. Most of the results presented here
were published
after the 1986 Surgeon General and National Academy of Science reports.
There are now eleven epidemiological studies on the relationship between exposure to environmental
tobacco
smoke in the home and the risk of heart disease in the nonsmoking spouse of a smoker. All but one of
these studies
yielded relative risks or odds ratios greater than 1.0. There are several lines of biological
evidence which make this
association plausible. There is evidence that exposure to ETS reduces exercise tolerance of both
healthy individuals
as well as people with existing coronary artery disease. Such reduced exercise capability is one of
the landmarks
of acute compromises to the coronary circulation. There is good evidence, from both human and animal
studies,
that exposure to tobacco smoke, including passive smoking, increases aggregation of blood platelets.
Such increases
in platelet aggregation are an important step in the genesis of atherosclerosis. In addition,
increasing platelet
aggregation contributes to risk of coronary thrombosis, i cause of acute myocardial infarction.
Finally, carcinogenic
agents in ETS, including benzo(a)pyrene have been shown to produce injuries to the endothelial cells
which line
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arteries. Such injuries are the first step in the development of atherosclerosis. Thus, exposure to
ETS can
contribute to both short term and long term insults to the coronary circulation and the heart. It is
not surprising,
therefore, that epidemiological studies have identified an increase in the risk of coronary artery
disease in
nonsmokers living with smokers.
Effects of Primary Smokina
Before reviewing the evidence linking ETS with coronary artery disease, it is worth summarizing the
evidence linking active smoking with coronary artery disease. This evidence was summarized in the
1983 Surgeon
General's Report, which was devoted entirely to cardiovascular disease; it concluded that cigarette
smoking is one
of the three major independent heart disease risk factors. It also concluded that the magnitude of
the risk associated
with cigarette smoking is similar to that associated with the other two major heart disease risk
factors, hypertension
and hypercholesterolemia; however, because cigarette smoking is present in a larger percentage of
the U.S.
population than either hypertension or hypercholesterolemia, cigarette smoking ranks as the largest
preventable cause
of heart disease in the United States. Since 1983, evidence has also mounted that the polycyclic
aromatic
hydrocarbons in cigarette smoke can injure the arterial endothelium and initiate the atherosclerotic
process.
All the compounds implicated as damaging to the cardiovascular system of smokers have been
identified in
ETS'.'.
Epidemiological Studies on ETS and Heart Disease
Since 1984, the epidemiological evidence linking exposure to ETS with heart disease has rapidly
accumulated. The results of the eleven published studies'''= are summarized in Table 1 and Figure 1;
four studies
present data on men, nine on women, and one on both sexes combined. Despite minor differences in
methodology
or end points (some used death from ischemic heart disease of any origin and some were limited to
death from
myocardial infarction), the results of these studies are remarkablly consistent. All the studies on
men yielded
relative risks of death from heart disease exceeding 1.0 when a nonsmoking man was married to a
woman who
smoked, with a median risk of 1.2. All but one of the studies on women' yielded relative risks
exceeding 1, with
a median relative risk of 1.4. Several studies'a""a0 have also suggested an increase in the risk
of nonfatal coronary
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symptoms. Consistency of an observation across different studies increases the confidence one can
have that an
association is causal.
Several authors also observed a dose-response relationship between increasing amounts of smoking by
the
spouse and the risk of heart disease in the nonsmoking spouse'"13`5'", which in most cases was
statistically
significant. The presence of such dose-response effects across multiple studies, done in different
locations with
different criteria, supports the hypothesis that ETS causes heart disease in nonsmokers.
While all but one of the studies in Table 1 and Figure 1 yielded relative risks greater than 1.0,
the fact
remains that 3 of the studies in men and 5 of the studies in women had 95 96 confidence intervals
for the relative
risk of passive smoking for heart disease that included 1.0, meaning that the risk was not
statistically significantly
elevated above 1.0 (with P <.05). It is important to note that the 95 96 confidence intervals do not
lie symmetrically
about 1.0, but rather are skewed towards higher risks. Exn*+,ining the confidence intervals leads to
the conclusion
that exposure to ETS elevates the risk of heart disease (Figure 1). It is also possible to combine
the results of these
studies in a formal analysis to derive a global estimate of the relative risk and associated 95 96
confidence interval.
By combining the studies, the sample size and so the power to detect an effect increases. Wells'
used several of
the studies in Table 1''''"' to compute a pooled relative risk of 1.3 (95% confidence interval 1.1
to 1.6) for men
and and 1.2 (95 96 confidence interval 1.1 to 1.4) for women. A similar analysis using all the
studies in Table 1
yields a relative risk of 1.3 (with a 95 96 confidence interval from 1.1 to 1.6).
When interpreting the results of such epidemiological studies, it is always important to consider
biological
plausibility and potential confounding variables which could explain the results. Aside from noting
that the
compounds in mainstream smoke that have been implicated in heart disease are in ETS, we will defer
the discussion
of biological plausibility until we discuss the effects of ETS on platelets and the atherogenic
agents in ETS. For
now, we will concentrate on potential confounding variables, such as the possible confounding effect
of a correlation
of spouses' poor health behaviors (e.g., diet high in animal fat). These confounders are
particularly important in
a disease like heart disease, because it is known to be caused by multiple risk factors.
All the studies controlled for the most important confounding variable, age, and several"'`"
controlled
for known risk factors for coronary artery disease, in particular levels of serum or plasma
cholesterol, blood
pressure and body mass. Most of the studies also included one or more measures of socioeconomic
status, such
as the nature of the housing or amount of education. Indeed, studies that estimated the relative
risk both with and
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without taking these confounding variables into account found an increase in risk associated with
ETS after taking
the confounding variables into account'a's.
Lee='" has suggested that the elevated risk of heart (and other) disease with passive smoking could
be due
to misclassification of nonsmokers who are really smokers. In addition, Wale has noted that some
people who
say they live with nonsmokers have detectable levels of the nicotine metabolite cotinine in their
blood, indicating
that they are actually exposed to ETS, either at work or at home. The former type of
misclassification would tend
to lead to an overesdmate of the risks associated with ETS and the latter would lead to an
underestimate of the risk.
Careful analysis of the question of misclassification - which applies generally to studies of ETS -
have
demonstrated that the observed risks cannot be explained by this problems-2`a.
There is always the possibility that there is some other confounding variable relating to cultural
factors, such
as the nature of housing or employment or the nature of time spent outside the home. The fact that
results from
all over the world in widely varying cultural settings - including several regions in the United
States, the United.
Kingdom, Japan, and China - argues against this concern.
One can assess formally how confident one can be in reaching a negative conclusion by computing the
power
of the study to detect an effect of specified siuP. Table 1 shows estimates of the power of each of
the studies to
detect a 20% increase in risk of heart disease (i.e., a relative risk of 1.2) with the available
samples. The power
was computed as described in Muhm and Olshan30, using a two-sided test for the relative risk with a
Type I risk
of 5% (i.e., requiring the 95% confidence interval for the relative risk to exclude 1.0 before
concluding a
statistically significant elevation in risk in an individual study). Most of the studies have low to
moderate power.
All fourl','4,'5," that have power above 4096 identified significant increases of heart disease risk
with ETS exposure.
Examining Table 1 reveals that the greater the power of the study to detect an effect, the more
likely it was to find
a significant adverse effect of ETS.
Finally, it is worth noting that all these studies are based on the smoking habits of the
nonsmoker's sQousc,
and so exposure to ETS at home. Household exposures to ETS at home are generally much smaller than
exposures
at work, where the density of smokers is generally higher"X. As a result, these studies generally
underestimate the
risk and attendant public health burden due to ETS-induced heart disease. Kawachi at alm have
adjusted Wells's
relative risks to account for workplace exposures to ETS and found that the relative risks increase
to 2.3 (95 96 Cl
1.4 - 3.4) for men and 1.9 (95% Cl 1.4 - 2.5) for women. Thus, any potential confounding of the
results due to
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exposure to ETS outside the home will tend to produce underestimates rather than overestimates of
the effect of
ETS. Likewise, estimates of public health impact based on risks computed from household exposures'
will be lower
than the true public health impact. In addition, Wellss and Kawachi et al-" indicate that the number
of heart disease
deaths due to passive smoking is an order of magnitude greater than then number of lung cancer
deaths due to
passive smoking. Even though the relative risks for heart disease and lung cancer caused by ETS are
similar (about
1.3 for both diseases), the attributable deaths for heart disease is greater since heart diease is
much more common
than lung cancer. Of 53,000 annual deaths in the U.S. attributed to passive smokings, 37,000 are
attributed to heart
disease, compared with 3,700 for lung cancer (Figure 2).
These epidemiological studies demonstrate a connection between ETS exposure and death from heart
disease.
We now turn our attention to possible physiological and biochemical mechanisms which could explain
these
observations.
Acute Effects of ETS Exposure
Chronic exposure to ETS exerts carcinogenic effects by increasing the cumulative risk of a molecule
of one
of the carcinogens in the ETS damaging a cell and initiating or promoting the carcinogenic process.
The situation
with heart disease is different. In heart disease there are both important chronic changes (i.e.,
the development of
atherosclerotic lesions) and acute changes. The latter include an increase in myocardial oxygen
demand which may
outstrip the oxygen supply and produce ischemia, and increased platelet aggregation which can lead
to coronary
thrombosis and acute myocardial infarction.
When the coronary circulation cannot provide enough oxygen to the myocardium to meet the demand, the
result is ischemia which can be silent or result in aaginal chest pain. Earlier onset of angina or
hypotension during
exercise is a reflection of more severe heart disease. Oxygen supply can be reduced by
atherosclerotic narrowing
or vasoconstriction of the coronaries or by reducing the oxygen carrying capacity of the blood by
forming
carboxyhemoglobin. Khalfen and Klochkov" confirmed earlier work by Aronow" demonstrating that
exposure to
ETS significantly reduced exercise ability in patients with coronary artery disease and the rate
pressure product
(heart rate times systolic blood pressure). In both studies, patients were exposed to realistic
levels of ETS by simply
sitting in a waiting room while someone was smoking. '1'hese effects were present in both smokers
and
nonsmokers" and regardless of whether or not the room was ventilated"-'s. Exposure to ETS also
increased resting
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heart rate and systolic and diastolic blood pressure, and resulted in a lower heart rate at the
onset of angina's. Blood
carboxyhemoglobin was increased by about 196 after exposure to ETS'3. Thus, acute exposure to ETS
leads to an
imbalance between myocardial oxygen supply and demand during exercise in patients with coronary
artery disease.
While this discussion has concentrated on the carbon monoxide in ETS as the active agent, it is
possible that some
other component of the ETS is causing or contributing to this effect.
The effects of ETS on cardiac performance are, in fact, severe enough to affect exercise performance
in
young healthy subjects with no evidence of heart disease. McMurray et al" exposed young healthy
women to pure
air and air contaminated with ETS while they exercised on a treadmill. The results were similar to
those observed
in patients with coronary artery disease. Resting heart rate was increased during exposure to ETS,
which increased
blood carboxyhemoglobin by about 196. Exposure to ETS significantly reduced maximum oxygen uptake
(by
0.251/min and time to exhaustion (by 2.1 min). Exposure to ETS also increased the perceived level of
exertion
during exercise, maximum heart rate, and CO2 output. It also significantly increased levels of
lactate in venous
blood (from a mean of 5.5 mM during control period to 6.8 mM after exposure to ETS). This greater
lactate at
a lower oxygen consumption during the passive smoking trials indicates a greater reliance on
anaerobic metabolism.
The combined effect of the reduced oxygen carrying capacity and increased lactate resulted in a
reduction in
maximal aerobic power and the duration of exercise. Thus, even in healthy subjects, exposure to ETS
adversely
affects exercise performance. Lamb" has suggested that at maximal exertion levels, up to 90% of the
oxygen
carrying capacity of the blood may be needed. Probably because of carbon monoxide, ETS reduces this
capacity,
so the muscle cannot maintain its high rate of aerobic metabolism unless cardiac output is further
increased; people
with heart disease and reduced ventricular reserve have difficulty meeting this demand. In sum,
exposure to ETS
increases the demands on the heart during exercise and reduces the capacity of the heart to respond.
This imbalance
increases the ischemic stress of exercise in patients with existing coronary artery disease and can
acutely precipitate
symptoms.
Moskowitz et al" found evidence that adolescent children of parents who smoked may suffer from
chronic
tissue hypoxia such as that observed in anemia, chronic pulmonary disease, cyanotic heart disease or
high altitude.
These children had significantly elevated levels of 2,3-diphosphoglycerate (DPG), even after
correcting for age,
weight, height and sex. 2,3-DPG acts as a physiologic modulator of hemoglobin oxygen affinity. It
binds to
specific amino acid sites and increases the P., (lowers the oxygen affinity), thus making more
oxygen available to
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peripheral tissues. This observatiion suggests that the body is attempting to compensate for hypoxia
by increasing
DPG level in blood to meet tissue oxygen requirements, The changes were dose-dependent; the greater
the exposure
to ETS (measured both in terms of parental smoking and serum thiocyanate in the children), the
greater the increase
in DPG.
There is also evidence that acute exposure to ETS directly affects respiration of the myocardium at
a cellular
level. GvotdjQkovli et al" exposed rabbits in a 50 liter child's incubator to the smoke of three
burning cigarettes
smoked over a 30 minute period and measured several variables related to the metabolism of cardiac
mitochondria.
They had three groups of rabbits: one group exposed to a single dose of ETS, one group exposed to 30
min of ETS
twice daily for two weeks, and one group exposed to 30 minutes of ETS twice daily for eight weeks.
They
measured mitochondrial respiration as the consumption of oxygen after adding ADP to a vessel
containing
mitochondrial fragments. Using pyruvate as a substrate, mitochondrial respiration was reduced
significantly
compared to control (pure air) for all doses of ETS, by even a single exposure; to about half the
control value. The
oxidative phosphorylation rate was also reduced significantly at all exposures by about one-third.
There were no
significant changes in the coefficient of oxidative phosphorylation with ETS exposure. Gvozdjikovi
et al"
concluded that pyruvate as a substrate was a sensitive indicator of the toxic action of the ETS on
the oxidative
process.
Later, to further isolate where in the process of mitochondrial respiration, the ETS acted, GvozdjQk
et al'0."
reported data on succinate, NADH, and cytochrome oxidase activity in the mitochondria in the four
groups of
rabbits. Exposure to ETS affects the activity of NADH oxidase, succinate oxidase and cytochrome
oxidase of
myocardial mitochondria. The activity of the first two oxidases exhibited no changes compared with
the control
group - neither after a single exposure to ETS or following exposures up to 2 weeks. Cytochrome
oxidase activity
decreased both after a single exposure to ETS and over time, with increasing effects as the duration
of exposure to
ETS is extended. The observation that cytochrome oxidase and not NADH or succinate oxidase activity
was
affected by ETS suggests that the deleterious effects of ETS on myocardial mitochondrial respiration
occur at the
terminal segment of the mitochondrial respiration process. Prolonged exposure to carbon monoxide has
been shown
to induce ultrastructural changes in myocardium4z'' and may account for the adverse effects of ETS
exposure on
mitochondrial function.
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Thus, acute exposure to ETS not only increases the demand and compromises the supply of oxygen to
the
heart, but also reduces the myocardium's ability to use the oxygen to create ATP to provide energy
to support the
heart's pumping activity.
Effects on Platelets
The action of ETS to increase platelet aggregation is another way in which ETS can acutely increase
the risk
of a coronary event. Platelets are important for the normal process of hemostasis, to prevent blood
loss after an
injury. When blood platelets aggregate inappropriately and form a thrombus in the coronary
circulation, they can
precipitate a myocardial infarction. Hemostasis depends on complex interactions among the dynamics
of blood flow,
components of the vessel wall, platelets and plasma proteins. Definitive evidence has confirmed that
platelets play
a major role in thrombus formation and embolization, especially in the arterial system. In addition,
increasing
evidence has shown that platelet deposition and thrombus formation can contribute to the growth and
progressioa
of atherosclerotic plaques". An arterial thrombus appears to develop in three phases: platelet
adhesion, platelet
aggregation, and activating of clotting mechanisms. Passive smoking increases platelet aggregation
and so increases
the likelihood of thrombus formation and myocardial infarction.
Table 2sum*^9rizes the results of several studies by Davis et al"" on the effects of cigarette smoke
on
platelet aggregation and damage to the arterial endothelium. Davis et alsl also measured platelet
aggregate ratios
and eadothelial cell counts in nonsmokers before and after being exposed to 20 minutes of ETS while
sitting in a
hospital atrium. The platelet aggregate ratio in these studies is the ratio of the platelet count of
platelet rich plasma
prepared from blood mixed immediately with EDTA and formaldehyde to the same mixture without
formaldehyde.
This method assumes that platelet aggregates circulating in blood are fixed in the EDTA-formaldehyde
solution, and
break apart in the EDTA solution. Thus, a decrease in the platelet aggregate ratio reflects an
increased formation
of platelet aggregates. Mean values before and after passive smoking were 0.87 and 0.78 (P=.002) for
platelet
aggregate ratios and 2.8 and 3.7 (P=.002) for counts of anuclear endothelial cell carcasses in
venous blood. These
changes are intermediate between the effects observed after nonsmokers smoked two tobacco cigarettes
and the
effects observed after smoking two non-tobacco cigarettes'r and similar to the values observed in
nonsmokers who
smoked two cigarettes while trying not to inhale°. These effects were not correlated with the level
of nicotine in
the blood of the experimental subjects in any of these or other'°'"; related studies on how drugs
modify platelet
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aggregation and endothelial cell counts. In particular, the effects observed in nonsmokers smoking
without inhaiing
were similar to the effects on smokers smoking two cigarettes, despite the fact that the plasma
nicotine levels in the
nonsmokers were a factor of 5 smaller than those observed in the smokers". Other work in the same
laboratory
comparing smoking with snuff use revealed similar changes in platelet function in response to these
two forms of
tobacco useP. This result, combined with the finding that smoking non-tobacco cigareites" failed to
produce
changes in platelet function as large as observed with tobacco cigarettes, suggests that nicotine is
an important active
agent. Since non-tobacxo cigarettes also affected platelet aggregation somewhat, however, it is
possible that carbon
monoxide or other combustion products are also influencing the platelets.
Sinzinger and KefalidesA measured platelet sensitivity to antiaggregatory prostaglandins (E 12,
and D2)
before, during and after 15 minutes of exposure to ETS in healthy nonsmokers and smokers. Passive
smoking
reduced platelet sensitivity to the antiaggregatory prostaglandins IZ and E, significantly (P <.01)
by a factor of about
2 by the end of 15 minutes exposure to ETS among nonsmokers. This effect persisted at 20 minutes
after the end
of exposure, and was gone by 40 minutes. Platelet response to prostaglandin D2 changed modestly in a
similar
pattern, but did not reach statistical significance. Among smokers, the control level of platelet
aggregation was
higher (P <.01) and the prostaglandins had no significant effects on platelet aggregation over time
during or
following exposure to ETS. Sinzinger and Virgolini-4 also showed that repeated exposure to ETS for
one hour per
day for ten days produced lasting changes in platelet function in nonsmokers similar to that
observed in smokers.
Thus, nonsmokers' platelets seem much more sensitive to a single exposure to ETS than do smokers'
platelets, with
platelet sensitivity to disaggregating prostaglandins having similar effects in nonsmokers acutely
exposed to ETS
as it does on the chronic levels of platelet aggregation observed chronically in smokers.
Further evidence from the same laboratory that passive smoking increases platelet aggregation comes
from
work by Burghuber at a1", who had smokers and nonsmokers smoke two cigarettes and also exposed a
different
group of smokers and nonsmokers to ETS in an 18 m3 room in which 30 cigarettes had been smoked just
before
exposing the nonsmokers. They measured the sensitivity of platelets to the disaggregating substance
prostaglandin
12 which is released by endothelium and inhibits platelet aggregation. Figure 3 shows the results of
this experiment.
In smokers, neither smoking nor passive smoking affected the sensitivity of the platelets to the
disaggregating effect
of prostaglandin 12. The sensitivity of platelets in smokers. was also significantly lower than
nonsmokers. In
contrast, platelets were more sensitive to prostaglandin 12 in nonsmokers, with both smoking and
passive smoking
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producing similar reduction in platelet sensitivity to prostaglandin 12. These results suggest that
the platelets of
smokers are already desensitized to the anti-aggregatory substance prostaglandin 12, so that no
further decrease in
aggregation is seen. The significant decrease in platelet sensitivity to prostaglandin after acute
exposure to ETS
suggests that after ETS exposure platelets are more likely to aggregate, with adverse consequences.
Earlier work by Saba and Mason" also indicated that nicotine increased a variety of measures of
platelet
aggregation in nonsmokers and smokers. While the in vitro effects of nicotine on platelets from
smokers was
greater than in nonsmokers, the effect generally did not vary with dose (between 2z10'9 and 2z10'4
molar),
suggesting that the effects of nicotine on platelets occur at low doses and that the system
saturates quickly. This
observation may explain why passive and active smoking have such similar effects on plateletss'~.
The probable link between nicotine and adverse physiologic effects is nicotine-induced release of
catecholamines. Catecholamines are then responsible for increased platelet aggregation. This
reasoning suggests
that beta blockers might provide some protection in smokers. This premise is borne out by a trial
comparing the
effects of the beta blocker metoprolol to a thiazide diuretic in the control of moderate
hypertension., For the same
reduction in blood pressure, the metoprolol treated group had a significantly lower mortality rate
than the thiazide
treated group. Virtually all of this reduction in mortality, however, was seen in smokers, and not
nonsmokers.
This study provides evidence that blocking the effects of catecholamines (released by nicotine) was
the cause of the
reduced mortality in smokers who were receiving metoprolol.
In sum, passive smoking increases platelet aggregation, with a magnitude similar to that observed in
active
smoking. Moreover, the response of nonsmokers to both active and passive smoking appears to be
different from
smokers, with nonsmokers being more sensitive to low exposures to cigarette smoke than smokers. This
observation
suggests that the pharmacology of ETS in nonsmokers may be different than in smokers, with
nonsmokers being
more sensitive to low doses of ETS. In particular, it invalidates attempts to estimate "cigarette
equivalent' doses
of ETS in nonsmokers or extrapolating from risks of smoking in smokers to effects of ETS on
nonsmokers". The
resulting increase in platelet aggregation can contribute to acute thrombus formation and myocardial
infarction.
In addition to the role of platelets in acute thrombus formation, platelets are also important in
the
development of atherosclerosis's. Once there is damage to the arterial endothelium, either through
mechanical or
chemical factors, platelets interact with or adhere to subeadothelial connective tissue and initiate
a sequence which
leads to atherosclerotic plaque. When platelets interact with or adhere to subendocardial connective
tissue, they are
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stimulated to release their granule contents. Endothelial cells normally prevent platelet adherence
because of the
nonthrombogenic character of their surface and their capacity to form antithrombotic substances such
as prostacyclin.
Once the endothelial cells have been damaged, the platelets can stick to them. Once the platelets
are bound to the
endothelium, they release mitogens such as platelet-derived growth factor (PDGF), which encourage
migration and
proliferation of smooth muscle cells in the region of the endothelial injury". If platelet
aggregation is increased
because of exposure to ETS, the chances of platelets building up at an endothelial injury will be
increased. Thus,
in addition to contributing to acute effects through increasing the likelihood of thrombus
formation, the effects of
ETS on platelets also increase the chances that endothelial injury will lead to arterial plaque.
ETS also plays a role in causing damage to the endothelium and initiating the atherosclerotic
process. As
discussed above, Davis et al found that acute exposure to ETSs', like active smoking'l-" and use of
chewing
tobacco-'2, lead to a significant increase (P <.002) in the appearance of anuclear endothelial cell
carcasses in the
blood of people exposed to ETS (or tobacco or tobacco smoke) constituents. The appearance of these
cell carcasses
indicates damage to the endothelium, which is the initiating step in the atherosclerotic process. As
noted above,
the appearance of endothelial cells following passive smoking is almost as great as following
primary smoking
~ (Table 2). Exposure to ETS has been shown to produce injuries similar to those oliserved with
exposure to primary
smoke and also affects platelets in a way that increases the chances that they will bind to the
injured area and
promote growth of smooth muscle cells'6.
The Role of the Polvcvclic Aromatic Hydrocarbons in ETS
Many atherosclerotic plaques in humans are either monoclonal or possess a predominantly monoclonal
component°D, which indicates that the smooth muscle cells of each plaque have a predominant cell
type. Several
aaimal studies have also shown that injections of polycyclic aromatic hydrocarbons (PAHs), in
particular 7,12-
dimethylbenz(a,h)anthracene (DMBA), benzo(a)pyrene°i-" accelerate the development of
atherosclerosis.
Benzo(a)pyrene is an important element in ETS'. The effects of PAHs or other carcinogenic or
mutagenic elements
in ETS66 relate directly to the response .to injury theory of atherogenesis discussed above. Changes
in the
underlying smooth muscle stimulated by these agents could then initiate the "injury" that leads to
platelet
aggregation and plaque formation. Thus, chronic exposure to ETS could have effects on plaque
formation through
mechanisms similar to that by which long term exposures produce cancer in other organs.
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Albert et ai6t gave chickens weekly intramuscular injections of DBMA and benzo(a)pyrene for up to 22
weeks, then killed the chickens at various times beginning after 13 weeks and measured the plaque
volume in the
chickens' aortas. They found that both DBMA and benzo(a)pyrene significantly increased the volume of
plaque
compared to control chickens who had just received injections of the solvent used to carry these
agents. This study
provided the first evidence that known carcinogenic chemicals could be atherogenic as well.
Penn et al°' extended this result in a similar experiment by showing that the effects of DBMA on
the extent
of plaque buildup in chickens was dose-dependent. The median cross-sectional area of plaques on
individual aortic
segments and the plaque volume index (an approximate measure of the total volume of placjue per
aorta) increased
in a nearly linear fashion with DBMA dose. In contrast to the marked increase in plaque area in the
DBMA-treated
aaimals, there was only a slight increase in the percentage of aortic sections with plaques in
carcinogen-treated
animals than in controls. Plaques with a small cross sectional area were present in all animals.
Lesions of widely
differing cross sectional areas appeared to be similar histologically under the 'light microscope.
Together, these data suggest strongly that a major effect of chronic DBMA exposure is to increase
the size
of spontaneous aortic lesions. Rather than inducing some sort of cancer-like change in an individual
cell that begins
the process which ultimately leads to formation of a plaque, Penn et al suggested that chronic DBMA
exposure
causes preferential division of individual cells or patches of cells within the preexisting
spontaneous lesions. From
this perspective, DBMA and other exogenous compounds would be acting as a mitogen, similar to that
released by
activated platelets, to stimulate division of aortic smooth muscle.
Revis et al'2 found similar results in White Carneau pigeons injected with DMBA and benzo(a)pyrene
weekly
for 6 months, beginning when the pigeons were 3 months old. Compared with the work described above,
they
found a greater effect on atherogenesis of benzo(a)pyrene than DBMA, and also failed to observe a
dose-response
relationship between the dose given and the amount of aortic plaque. These differences from the work
just described
may be related to species differences, differences in the carrier used to inject the PAHs (DMSO in
the previous
studies vs. corn oil in this one) or differences in the age of the pigeons or dosing schedule. They
also found an
increase in aortic plaques in pigeons treated with the PAH 3-methylcholanthrene, but not the
carcinogen 2,4,6-
trichlorophenol or the PAH benzo(e)pyrene, which is not considered a carcinogen. This result
suggests that
carcinogenic PAHs, rather than carcinogens or PAHs in general, are implicated in the atherosclerotic
process.
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Revis et al°2 also studied the distribution of these compounds after they had been radiolabelled.
Forty-eight
hours after the injection of PAHs, radioactivity in the liver, aorta and lung accounted for 7596 of
the injected dose,
whereas in animals injected with 2,4,6-trichlorophenol, radioactivity in the liver and kidney
accounted for 8096 of
the dose. In addition, 80% of the radioactivity observed in the plasma immediately following
injection of
radiolabelled PAHs was associated with the LDL and HDL cholesterol fractions, compared with only 24%
of the
2,3,6-trichlorophenol, suggesting that plasma lipoproteins are an important vehicle for transporting
PAHs to their
sites of activation in the arteries.
There is also evidence that ETS directly affects plasma lipoproteins. Moskowitz et al" showed that
adolescent children whose parents smoked had elevated levels of cholesterol and depressed levels of
HDL, even after
correcting for age, weight, height and sex. These effects were dose dependent; the greater the
exposure to ETS,
the greater the changes in these variables. Pomrehn et al .7 observed similar effects of ETS on HDL
in children
whose parents smoked, even in children who smoked or crewed tobacco themselves. High cholesterol and
low HDL
are important for the development of plaque. Data on cholesterol and HDL from adults married to
smokers is
mixed`a's.
To further elucidate the possible mechanisms by which PAHs induce atherosclerotic changes, Majesky
et
alo gave White Carneau and Show Racer pigeons a single injection of benzo(a)pyrene, then looked for
metabolites
of the benzo(a)pyrene in aortic and hepatic tissues 48 hours later. White Carneau pigeons develop
severe
atherosclerosis by the time they are 3 years old, whereas Show Racer pigeons are relatively
resistant to aortic
atherosclerosis. Aortic preparations of the White Carneau strain exhibited a much greater
inducibility of the
microsomal monooxygenase system than did those of the Show Racer strain, particularly in young
pigeons. Aortic
tissues from White Carneau pigeons aged 6-12 months exhibited a 3-12 fold inducibility whereas
aortic tissues from
the same strain at 2-5 years of age exhibited only minor (maximum of 3.3 fold) and, for the most
part, statistically
insignificant increases. No age differences in inducibility could be detected in the Show Racer
strain. Interestingly,
the differences in inducibility manifest in aortic tissues were greater in aortic tissues than in
hepatic tissues from
the same birds. Thus, the PAHs seem to accelerate any preexisting tendency to develop
atherosclerosis.
Regardless of the ultimate mechanism by which PAHs exhibit atherogenic effects, it seems logical to
suppose
that the reactive intermediary metabolites of these chemicals are the proximate atherogenic or
co-atherogenic agents
since the parent compounds are relatively inert both chemically and biologically. Thus,
bioactivation and
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inactivation (and regulatory control of these processes) may be presumed to play extremely important
roles in their
atherogenic properties. Bioactivated chemicals vary in their stability and reactivity according to
four general
categories: (i) those which are extremely unstable and persist only at the immediate site (enzyme)
of bioactivation,
(ii) those which persist only within cells in which bioactivation occurs, (iii) those which persist
primarily only
within tissues in which bioactivation occurs, and (iv) those capable of being transferred in the
circulation from one
organ to another. For the first three of these four categories, biotransformation in the aorta per
se (target tissue
activation) would be of prime interest and importance. Thus, it appears that PAHs could be playing
either a
mutagenic or mitogenic role in beginning the atherosclerotic process in susceptible cells or
individuals, depending
on how the PAHs in ETS are metabolized in the aorta.
The finding that enzymes that metabolize DMBA and benzo(a)pyrene are in the artery wall led Penn et
ah`
to search for specific molecular events in plaque cells that would lead to DNA changes similar to
those previously
found in tumors. Identification of such processes would be supportive of the monoclonal hypothesis
of
atherogenesis. They obtained human DNA samples from coronary artery plaques as well as DNA from
normal
sections of the coronary arteries at surgery to remove the plaque. These DNA samples were tested
with the NIH
3T3 cell transection assay. Foci arose in cells transfected with each of the DNA samples obtained
from the human
coronary plaque, with an efficiency (number of foci per ug of DNA) ranging from 0.016 to 0.060 (mean
0.036).
The transfection efficiencies for DNA's from normal coronary artery, liver, spleen, lung, kidney and
trachea were
all below 0.008. The transformed cells were also injected into the scalps of nude mice, where they
developed
tumors. These results provide direct evidence for similarities on the molecular level in the
development of plaques
and tumors. Human coronary artery plaque DNA contains sequences capable of transforming NIH 3T3
cells and
these transformed cells can cause tumors after injection into nude mice. Control experiments
verified that the
transforming cells did indeed contain human DNA and that the tumorigenic (or transforming) activity
was not due
to the as oncogene family. Although these results clearly demonstrate that human plaque DNA has
transforming
ability, the temporal expression of this activity in vivo is not known. The plaques were taken from
adult patients
in late stages of vascular disease. Thus, we cannot determine from these samples whether the
manifestation of
transformation is a relatively late event in plaque development or an early but stable event.
Oncogene activation
and expression is an important early event in transformation and tumor genesis. These results
identify specific
molecular events that may underlie the proliferation of smooth muscle cells that is a hallmark of
atherosclerotic
c:1`lantzlmanuscriletaheut.doc 14

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plaque development and demonstrates that plaque cells exhibit molecular alterations that had
previously only been
thought to be present in cancer-cell transformation and tumorigenesis. These results provide direct
support for the
monoclonal hypothesis.
Randerath et e also demonstrated that constituents of cigarette "tar," including benzo(a)pyrene, are
preferentially attracted to the heart and damage DNA there. They studied molecular mechanisms of
smoking-related
carcinogenesis by examining the induction and distribution of covalent DNA damage in internal organs
of the mouse
following topic application of cigarette smoke condensate daily for 1, 3, or 6 days then killed 24
hr later. DNA
samples were obtained from skin, lung, heart, kidney, liver, and spleen. Adducts containing
benzo(a)pyrene-derived
moieties were identified, together with others. At all three times, the number of adducts in heart
and lung DNA
was about five times higher than that in liver and slightly higher than that in skin. Covalent DNA
damage was
estimated to be 6.2, 5.7, 3.9, and 1.9 times higher, respectively, in lung, heart, skin and kidney
than in liver,
ranging from approximately 1 adduct in 5.4x106 DNA nucleotides in lung to 1' adduct in 3.3x10' DNA
nucleotides
in liver. Spleen DNA was virtually adduct free. While the DNA adduct profiles resembled each other
qualitatively
among the different tissues, there were major quantitative differences between the different
tissues, with the highest
DNA binding occurring in the lung and heart. The reasons for the high incidence of DNA adducts in
the heart are
not known, but may be related to the role of plasma lipids in transporting PAHs such as
benzo(a)pyrene and binding
of these lipids to coronaries arteries.
In sum, there is a growing body of evidence at a molecular level supporting the nonoclonal
hypothesis of
atherogenesis, with compounds in tobacco smoke and ETS strongly implicated as agents which stimulate
the
development of coronary lesions. Regardless of whether the monoclonal hypothesis proves to be true
(or, more
likely, one of several initiators of the atherosclerotic process), the fact is that there is clear
evidence that components
of ETS, in particular PAHs such as benzo(a)pyrene, initiate or accelerate the development of plaque.
These
biochemical findings are consistent with the epidemiological finding that chimney sweeps, which are
exposed to high
levels of PAHs in soot, have an increased risk of heart disease (as well as cancer) and tend to
develop these diseases
younger than other, comparable, occupations which avoid exposure to PAHe. The PAHs in ETS are
clearly
implicated at epidemiological, physiological and biochemical levels in the genesis of heart disease.
cASlauiCtlmanu.cektuheart.doc 15

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The evidence that ETS increases risk of death from heart disease is similar to that which existed in
1986
when the Surgeon General concluded that ETS caused lung cancer in healthy nonsmokers`. There are
eleven
epidemiological studies, done in a variety of locations, which reflect about a 30% increase in risk
of death from
ischemic heart disease or myocardial infarction among nonsmokers living with smokers. The larger
studies also
demonstrate a statistically significant dose-response effect, with larger exposure to ETS being
associated with greater
risks of death from heart disease.
These epidemiological studies are complemented by a variety of physiological and biochemical data
which
show that ETS adversely affects platelet function and damages arterial endothelium in a way that
increases the risk
of heart disease. Moreover, ETS, in realistic exposures, also exerts significant adverse effects on
exercise capability
of both healthy people and those with heart disease by reducing the body's ability to deliver and
utilize oxygen.
In animal experiments, ETS also depresses cellular respiration at the level of mitochondria. The
polycyclic aromatic
hydrocarbons in ETS also accelerate, and may initiate, the development of atherosclerotic plaque.
It is also important to note that the cardiovascular effects of ETS appear to be different in
nonsmokers and
smokers. Nonsmokers appear to be more sensitive to ETS than smokers, perhaps because some of the
affected
systems are sensitive to low doses of the compounds in ETS, then saturate and also perhaps because
of physiological
adaptions smokers undergo as a result of chronic exposure to the toxins in cigarette smoke. In any
event, these
findings indicate that, in terms of cardiovascular disease, it is incorrect to compute "cigarette
equivalents' for
passive exposure to ETS, then try to extrapolate the effects of this exposure on nonsmokers from the
effects of direct
smoking on smokers.
These results combine to suggest that heart disease is an important consequence of exposure to ETS.
The
combination of epidemiological studies with demonstration of physiological changes with exposure to
ETS, together
with biochemical evidence that elements of ETS have significant adverse effects on the
cardiovascular system, lead
to the conclusion that ETS causes heart disease. This increase in risk translates into about 10
times as many deaths
from ETS-induced heart disease as lung cancer; these deaths contribute greatly to the estimated
53,000 deaths
annually from passive smokings. This toll makes passive smoking the third leading preventable cause
of death in
the United States today, behind active smoking70 and alcohol't
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AclrnowledQements
We thank James Stoughton for assistance in library work, A. Judson Wells, Donald Shopland, James
Repace,
Neil Benowitz, Takeshi Hirayama and the Tobacco Institute for their comments on drafts of the
manuscript, Voij tech
Licho and Art Sussnman for translating foreign language articles, and Jerry Simnitt for typing.

CR900213R3
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Toxicol. 1987; 61:89-104.
67. Pomerehn P, Hollarbush J, Clarke W, Lauer R: Childrens' HDL-chol: The effects of tobacco;
Smoking,
smokeless and parental smoking. Circulation 1990; 81:720 (abstract).
68. Randerath E, Mittal D, Randerath K: Tissue distribution of covalent DNA damage in mice treated
dermally
with cigarette 'tar': preference for lung and heart DNA. Carcinogenesis 1988; 9:75-80.
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69. Hansen E: Mortality from cancer and ischemic heart disease in Danish chimney sweeps: A five-year
follow-up. Am. J. Epidemiol. 1983; 117:160-164.
70. USPHS: I3educinQ the health conseauences of smoking: 25 vears o grqg ,ss. A report of the
Surgeon
General. 1989; DHHS(CDC) 89-8411.
71. NIAAA: Sixth ispport to the U.S. ConQress on alcohol and health from the Secretary of Health and
Human Services. U.S. Dept. of Health and Human Services, Public Health Service, Alcohol, Drug Abuse,
and Mental Health Administration, National Institute on Alcohol Abuse and Alcoholism, 1987;
DHHS(ADM) 87-1519.
o:\;l.ntz\,n.nusctilsdheut.doo 23

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Table 1
Epidemiological Studies of Environmental Tobacco Smoke and Coronary Heart Disease Death
Author Type' Location Deaths Relative 95% Dose Power` Controlling for:
or Risk Confidence Response?b
Cases Intervat MENEM
Males
Gillis at ats P Scotland 32 1.3 0.7 - 2.6 - 4% age
(1984)
Lee et al9 C United 41 1.2 0.5 - 2.6 - 10% age, marital status
(1986). Kingdom
Svendsen et P United States 13 2.1 0.7 - 6.5 Yes 18% age, blood pressure,
at10 (1987)° serum cholesterol,
weight, education,
alcohol
Helsing et P Maryland 370 1.3 1.1 - 1.6 No 27% age, marital status,
al~~ (1988) housing, education
Ferles
Hirayama12 P Japan 494 1.2 0.9 - 1.4 Yes 32% age, diet
(1984)
Gillis et ata P Scotland 21 3.6 0.9 -13.8 - 15% age
(1984)
Garland et P California 19 2.7 0.9 -13.6 - 23% age, blood pressure,
att3 (1985) plasma cholesterol,
weight, years of marriage
Lee et als C United 77 0.9 0.7 - 1.3 - 3% age, marital status
(1986) Kingdom
Martin et a114 C Utah 23 2.6 1.2 - 5.7 - 44% age, family history of
(1986) CHD, hypertension,
diabetes, weight,
alcohol exercise
Helsing at P Maryland 988 1.2 1.1 - 1.4 Yes 98% age, housing, marital
at" (1988) status, education
He (1989) is C China 34 1.5 1.2 - 1.8 Yes 74% age, race, residence,
occupation, hypertension,
family history of
hypertension or CHD,
alcohol, exercise,
h rli idemia
Humble et atls P Geor9ia 76 1.6 1.0 - 2.6 Yes 30% age, serum cholesterol,
(1990) blood pressure, weight
Butler~i P California 64 1.4 0.5 - 3.8 - 4% age
(1990)
ioth sexes ca.bined
Hote et al17 P Scotland 84 2.0 1.2 - 3.4 - 87% age, sex, social class,
C1989)' blood pressure,
cholesterol, weight
'P = Prospective cohort, C= Case control
bHo entry in this column indicates no coanknt on the presence or absence of dose-response
relationship
`Power to detect relative risk of 1.2 with 95% confidence
dHigh risk population; members of MRFIT trial
'This report is a tater follow-up of the population reported in Gittis et als
50778 2005
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Table 2
Effect of Passive and Active Smoking on Platelet Aggregation and Endothelial Cell Damage
Platelet A re ate Ratio Endothelial Cell Count n
Before After Change Before After Change
Passive Smoking .87 .78 -.09 2.8 3.7 0.9 10
(nonsmoker)
Tobaccoa(nonsmoker) .80 .65 -.15 2.3 4.8 2.5 20
vs.
Non-tobacco .81 .78 -.03 2.5 3.0 0.5
cigarette
(nonsmoker)
Inhale cigarette .81 .68 -.13 4.0 5.4 1.4 24
(smoker) vs.
Not inhale cigarette .82 .73 -.09 3.3 4.7 1.4 22
(nonsmoker)
Smoke (smoker) vs. .85 .70 -.15 4.4 6.4 2.0 17
Snuff (smoker) .82 .76 -.06 J 1 3.9 4.7 0.8
Notes: All studies are paired and reflect significant differences (P<.005). Platelet aggregate ratio
is the ratio of platelet count of platelet-rich plasaw, prepared immediately after venipuncture with
a
sotution containing edetic acid and formaldehyde, to that of pLateLet-rich plasma prepared in the
same
manner, except for the absence of formaldehyde. A decrease in the platelet aggregate ratio reflects
an
increased formation of platelet aggregates. Endoth ~ti
a
~~ ell count is mean number of anuctear cell
~
~
carcasses in 0.9 µl chambers. Source: Davis et al
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FIGURE LEGENDS
Figure 1: Relative risk in epidemiological studies of the risk of death from coronary heart disease
or myocardial
infarction among nonsmokers living with smokers compared with nonsmokers living with nonsmokers.
Lines
indicate 95 96 confidence intervals. (Note that two studies have upper bounds to the 95 96
confidence interval off
the scale of the graph.)
Figure 2: Heart disease accounts for the majority of annual deaths attributed to environmental
tobacco smoke.
Source: Wells26.
Figure 3: Effect of active (left) and passive (right) smoking on platelet aggregation in smokers and
nonsmokers.
The sensitivity index. SIpGu, is defined as the inverse of the concentration of *prostaglandin I;
necessary to inhibit
ADP-induced platelet aggregation by 50%. Lower values of SI,,u indicate greater platelet
aggregation. Source:
Burghuber et al-" Figures 3 and 4.
c:\glantz\rtunu.crikuheart.doc 26

Relative Risk
N) W .A UT d) --1
i
~ Gillis (1984)
I
Lee (1988)
. Svendsen (1987)
J
1
Aft
I
-}- Helsing (1988)
T~ Hirayama (1984)
I
.:
Gillis (1984) ~
Garland (1985)
I
I
'
-{-!- Lee (1988)
~-- Martin (1986)
-}- Helsing (1988)
-}~- He (1989)
Butler (1990)
-}- Humble (1990)
Hole (1989)

. s
N
~
~
~D

,
.
PGh
I
PcAI 0.5
1PcA3
SMOKEft
0
8EF0RE AFTER
0
BEFORE
Pc.01
AFTER
