Smog Exposure Linked to Premature Death |
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Smog Exposure Linked to Premature Death
April 2008 - Exposures of less than 24 hours to
current levels of ground-level ozone in many areas are likely to
contribute to premature deaths, finds a new National Research Council
report.
Ozone, a key component of smog, can cause respiratory problems and other
health effects. In addition, evidence of a relationship between exposures
of less than 24 hours and mortality has been mounting, but interpretations
of the evidence have differed, prompting the U.S. Environmental Protection
Agency, EPA, to request the Research Council report.
The committee that wrote the report was not asked to consider how evidence
has been used by the EPA to set ozone standards, including the new public
health standard set by the agency last month.
But the evidence is strong enough that the EPA should include
ozone-related mortality in health-benefit analyses related to future ozone
standards, says the committee, which is chaired by John C. Bailar III,
professor emeritus, Department of Health Studies at the University of
Chicago.
In addition to scientists specializing in environment, public health, and
statistics and from across the United States, the committee includes
scientists from Canada and Spain.
Based on a review of recent research, the committee found that deaths
related to ozone exposure are more likely among people with pre-existing
diseases and other factors that could increase their susceptibility. But,
the committee said, premature deaths are not limited to people who are
already within a few days of dying.
The EPA asked the committee to analyze the ozone-mortality link and assess
methods for assigning a monetary value to lives saved for the
health-benefits assessments.
Like other federal agencies, the EPA is required to carry out a
cost-benefit analysis on mitigation actions that cost more than $100
million per year.
The EPA recently used the results of population studies to estimate the
number of premature deaths that would be avoided by expected ozone
reductions for different policy choices, and then assigned a monetary
value to the avoided deaths by using the value of a statistical life, VSL.
The VSL is derived from studies of adults who indicate the "price" that
they would be willing to pay - that is, what benefits or conveniences
someone would be willing to forgo - to change their risk of death in a
given period by a small amount.
The monetary value of the improved health outcome, or VSL, is based on the
value the group places on receiving the health benefit; it is not the
value selected by policymakers or experts.
The EPA applies the VSL to all lives saved regardless of the age or health
status, so a person who is 80 years old in poor health is estimated to
have the same value of a statistical life as a healthy two-year-old.
To determine if an approach that accounts for differences in remaining
life expectancy could be supported scientifically, the EPA asked the
committee to examine the value of extending life.
For example, EPA could calculate VSL to estimate the value of remaining
life, so a two-year-old would have a higher VSL than an 80-year-old.
It is plausible that people with shorter remaining life expectancy would
be willing to devote fewer resources to reducing their risk of premature
death than those with longer remaining life expectancy.
By contrast, if the condition causing the shortened life expectancy could
be improved and an acceptable quality of life can be preserved or
restored, people may put a high value on extending life, even if they have
other health impairments or are elderly.
The committee concluded that EPA should not adjust the value of a
statistical life because current evidence is not sufficient to determine
how the value might change according to differences in remaining life
expectancy and health status.
However, the committee did not reject the idea that such adjustments may
be appropriate in the future.
The committee examined research based on large population groups to find
out if there is a threshold - a concentration of ozone below which
exposure poses no risk of death. The committee concluded that if a
threshold exists, it is probably at a concentration below the current
public health standard.
"Even in many areas EPA currently considers safe, the science clearly
shows that the air is too often dangerous to breathe, particularly for
those with lung disease," said American Lung Association Chair Terri
Weaver last May when releasing the association's annual ranking of air
pollution in U.S. cities.
"The good news is that there's less ozone everywhere. Yet, we remain
concerned because the science shows that millions are still at risk from
ozone that exceeds acceptable levels," Dr. Weaver said.
"Breathing ozone smog threatens serious health risks, including new
evidence that links it to premature death," she said. "We're calling on
EPA to set new standards for ozone at levels that would protect public
health as the Clean Air Act requires."
As people have individual susceptibilities to ozone exposure, not everyone
may experience an altered risk of death if ozone air concentration
changes, the committee said in today's report.
Further research should explore how personal thresholds may vary and the
extent to which they depend on a person's frailty, the committee said.
The research on short-term exposure does not account for all ozone-related
mortality, and the estimated risk of death may be greater than if based
solely on these studies, the committee noted.
To better understand all the possible connections between ozone and
mortality, future research should address whether exposure for more than
24 hours and long-term exposure - weeks to years - are associated with
mortality, including how ozone exposure could impact life expectancy.
For example, deaths related to short-term exposure may not occur until
several days afterward or may be associated with multiple short-term
exposures, the committee said.
The EPA was advised to monitor ozone during the winter months when it is
low and in communities with warmer and cooler winters to better understand
seasonal and regional differences in risk.
The committee said further research also could look at how other
pollutants, such as airborne particulate matter, may affect ozone and
mortality risk.
The report, "Estimating Mortality Risk Reduction and Economic Benefits
from Controlling Ozone Air Pollution," is available from the National
Academies Press at: http://www.nap.edu
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