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There
is mounting evidence that exposure to higher levels of air pollution is
associated with adverse cardiovascular consequences. A recent scientific
statement from the American Heart Association concluded that transient
changes in air pollution are associated with a short-term increased risk
of cardiovascular disease and death.1 There is also convincing evidence
for an association between air pollution and myocardial ischemia and infarction,
ventricular arrhythmia, heart failure exacerbation, and stroke.1,2,3,4,5
Mechanisms that have been proposed as possible explanations for these
associations include direct effects from agents that cross the pulmonary
epithelium into the circulation, including gases and the soluble constituents
of particles such as transition metals.1 Activation of pulmonary reflexes
may lead to alterations in autonomic balance that may in turn alter coronary
tone and result in a higher risk of arrhythmia and the disruption of vulnerable
plaque.6 The heightened risk that begins early after exposure to high
levels of particulate air pollution appears to persist over days and may
be related to pulmonary oxidative stress leading to enhanced systemic
inflammation and altered hemostaticfibrinolytic balance.7,8,9 These
putative pathways may act separately or in concert, be associated with
different outcomes, and be activated by different components of ambient
pollution. These acute and transient effects of particulate air pollution
should be distinguished from the heightened long-term, chronic risk of
adverse cardiovascular outcomes associated with living in areas with higher
mean levels of air pollution; this long-term risk has been demonstrated
in several large cohort studies, including a recent report from the Women's
Health Initiative.10
In this issue of the Journal, Mills and colleagues11 report the results
of a double-blind, randomized, crossover study of 20 men with a history
of myocardial infarction exposed to either dilute diesel exhaust
at a level similar to what might be routinely experienced when driving
in traffic or filtered air. During each exposure period, subjects
exercised on a bicycle ergometer to a target of 5 to 7 metabolic equivalents
for two 15-minute periods separated by 15-minute rest periods. The researchers
found that although the heart-rate response to exercise was not different
across exposure periods, myocardial ischemia, which was detected in all
patients, was associated with significantly greater ST-segment depression
and a greater ischemic burden during exposure to diesel exhaust than during
exposure to filtered air. Interestingly, Mills and colleagues did not
find that exposure to dilute diesel exhaust had an effect on the degree
of endothelium-dependent or endothelium-independent vasodilatation in
response to provocative testing performed 6 hours after exposure. In addition,
exposure to dilute diesel exhaust had no effect on the basal concentration
of plasma tissue plasminogen activator (t-PA) or plasminogen activator
inhibitor type 1 at 6 hours after exposure, although exposure did significantly
suppress net t-PA release in response to bradykinin infusion, indicating
a proclivity to impaired fibrinolytic activity.
The pathways linking air pollution exposure to the increased severity
of exercise-induced ischemia observed in this study are unclear. One potential
mechanism is decreased myocardial oxygen supply, perhaps related to vasoconstriction
or transient thrombus formation. Another is decreased oxygen-carrying
capacity caused by higher levels of carbon monoxide or by increased demand
reflected in a higher rate-pressure product or altered myocardial energetics.
Mills and colleagues found no effect on peripheral vascular reactivity
measured 6 hours after exposure; however, this does not preclude an effect
on the coronary vasculature during exposure. It is unlikely that the observed
effect was a result of carbon monoxide exposure, since its level in the
dilute diesel exhaust was quite low. Increased myocardial oxygen demand
also seems unlikely because no significant difference in heart-rate response
was observed during either exercise period. Still, this possibility cannot
be excluded, since data on other relevant hemodynamic measures, such as
blood pressure and rate-pressure product, were not provided. Mills and
colleagues did not directly assess the propensity for transient intracoronary
thrombus formation or altered myocardial energetics that may have occurred
during exposure.
This study may provide insight into the mechanism responsible for the
reported association between transient exposure to higher levels of ambient
air pollution and the onset of acute cardiovascular events. Furthermore,
the study suggests that the risk of exertion-triggered acute cardiovascular
events12 may be heightened when vigorous exertion is undertaken in the
presence of high levels of air pollution. For example, the susceptibility
to more severe exercise-induced ischemia, regardless of the pathway, may
be one mechanism leading to acute decompensation among patients with heart
failure as well as to the onset of ventricular arrhythmias. Whether this
is related to the onset of myocardial infarction is less clear, but the
changes in t-PA release may create a predisposition to occlusive thrombus
formation when vulnerable atherosclerotic plaque is disrupted, and short-term
effects on coronary tone have not been ruled out.
The study was specific in evaluating the effects of dilute diesel exhaust,
an extremely complex mixture of particles and gases; it is not possible
to glean which constituents of diesel exhaust were responsible for the
observed effects. Complicating matters further, ambient air pollution
is a heterogeneous mixture of gases and particulate matter, of which diesel
exhaust is only one of many components.1,13 There is a growing body of
evidence that other mobile and stationary sources of combustion-related
pollution are likely contributors to adverse cardiovascular effects. Identifying
the specific sources and constituents responsible for the reported acute
cardiovascular effects of air pollution is an important goal for future
investigations.
There are some important limitations to the study with respect to generalizability.
For example, different engines, fuels, and loads will result in different
outputs. In addition, the study does not directly address the cardiovascular
consequences of air pollution from sources other than diesel combustion.
Furthermore, the findings can be directly applied only to men with a history
of myocardial infarction and evidence of inducible ischemia on exertion.
Nonetheless, if such exposures are causal, these findings may represent
the tip of an iceberg constituting the effects of transient changes in
exposure to elevated levels of air pollution on cardiovascular risk. It
is likely that patients with established coronary disease who have not
experienced a myocardial infarction would respond similarly to transient
exposure to air pollution. More speculative are the effects of exposure
in the vast numbers of people with risk factors for coronary disease,
many of whom have subclinical disease and perhaps vulnerable plaque that
may serve as a substrate for acute coronary events.
The evidence from Mills and colleagues suggests that the risk of having
an acute cardiovascular event triggered by vigorous exertion13,14 may
be heightened with exposure to high levels of air pollution. Considering
the unequivocal benefit of habitual exercise,14 including its established
role in decreasing the risk that isolated episodes of exertion may trigger
the onset of an acute cardiovascular event, the riskbenefit ratio
may be optimized if people exercise away from traffic when possible.
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