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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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