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Trends in Dioxin Emissions and Exposure
in the United States
Introduction
| Dioxins are byproducts of many
types of combustion, both natural and anthropogenic, including
industrial, municipal and medical incineration; domestic
fireplace and wood stove use; backyard barrel burning;
and forest and brush fires. |
There are several encouraging developments regarding the
issue of dioxin1 emissions and
exposure in the United States. U.S. Environmental Protection
Agency (EPA) data (2006) show recent dramatic declines in
dioxin emissions to the environment from quantified sources.
In addition to an overall decline in dioxin emissions, the
pattern of emitted dioxin chemical forms, or congeners, which
have toxicities varying over several orders of magnitude,
has changed. On average, current dioxin emissions are composed
of a greater percentage of lower toxicity congeners than in
the past.
| The 3-T Rule: Combustion temperature,
time and turbulence conditions are adjusted to minimize
dioxin formation. |
Total environmental releases of dioxins from all quantified
sources decreased by 90% between 1987 and 2000 (see Figure
1). This significant decrease in dioxin emissions can be attributed
to successful US government regulation as well as to the voluntary
application of control technologies by industry. Emissions
from the major historic source of dioxin for the past 30 years,
incineration (especially of municipal solid waste and medical
waste), have been continually declining since at least 1987.
According to EPA data, backyard burning of rubbish2,
currently a largely unregulated source, is the largest identifiable
source of dioxin emissions. ("Regulated sources" refers to
those sources which have controlled emissions of dioxins,
either by virtue of regulations designed specifically for
that purpose or by virtue of regulations targeting other pollutants,
which have also reduced dioxin emissions.)
US Environmental Protection Agency Dioxin Emission
Data Show Declining Levels and a Changing Pattern of Sources
Declining emissions levels of dioxin to the environment are
characterized by a changing pattern of emission sources over
time. EPA data demonstrate that industry and regulatory controls
on incineration have resulted in significantly diminishing
contributions of dioxin from this source since 1987 (see the
blue portions of the stack graphs in Figure 1). The "3-T Rule"
is an industry "rule of thumb" stating that combustion temperature,
time and turbulence conditions may be optimized to minimize
dioxin formation. Application of this rule has proven that
technology works to reduce dioxin emissions. As emissions
from industry have declined, largely unregulated sources such
as backyard barrel burning of rubbish and residential wood
burning have risen in significance as contributors to overall
emissions.

*Includes incineration of municipal solid waste, sewage sludge,
and hazardous waste.
**Other category includes: leaded and unleaded gasoline,
land applied 2,4-D, iron ore sintering, oil-fired utilities,
EDC/vinyl chloride, lightweight aggregate kilns that combust
hazardous waste, petroleum refinery, catalyst regeneration,
cigarette smoke, boilers/industrial furnaces, crematoria and
drum reclamation.
1 "Dioxin" here is defined as the totality of
7 dioxins and 10 furans. "TEQ" denotes "toxic equivalent,"
a quantitative measure of the combined toxicity of a mixture
of dioxin-like chemicals.
2 U.S. EPA (Environmental Protection Agency). 2006.
An inventory of sources and environmental releases of dioxin-like
compounds in the United States for the years 1987, 1995, and
2000. National Center for Environmental Assessment, Washington,
DC; EPA/600/P-03/002F. (http://cfpub.epa.gov/ncea/cfm/recordisplay.cfm?deid=159286)
Backyard Barrel Burning is Estimated to be a Major
Source of Dioxin Emissions to the Environment
Dioxin emissions have decreased dramatically as a result
of regulations and voluntarily implemented controls. Today,
unregulated sources such as backyard barrel burning of rubbish
constitute the major sources of dioxin emissions to the environment.
It is important to note that estimates of dioxin emissions
from private rubbish burning are subject to great uncertainty.
Quantities and types of dioxin congeners formed during backyard
burning depend upon the amount of rubbish burning that occurs
over a region, the composition of the rubbish burned and the
physical conditions of burning.

*"Dioxin" here is defined as the totality of 7
dioxins and 10 furans. "TEQ" denotes "toxic equivalent," a
quantitative measure of the combined toxicity of a mixture
of dioxin-like chemicals.
Source: U.S. EPA (Environmental Protection Agency). 2006.
An inventory of sources and environmental releases of dioxin-like
compounds in the United States for the years 1987, 1995, and
2000. National Center for Environmental Assessment, Washington,
DC; EPA/600/P-03/002F. (http://cfpub.epa.gov/ncea/cfm/recordisplay.cfm?deid=159286)
EPA dioxin emissions data, divided into categories of industrial/municipal/transportation
and non- industrial/municipal/transportation sources, are
depicted in Figure 2, above. (Non- industrial/municipal/transportation
sources are backyard barrel burning of rubbish, residential
wood burning and cigarette smoke.) Dioxin emissions from industrial,
municipal and transportation sources have been greatly reduced
by regulations targeting (a) dioxin specifically and (b) other
pollutants, the regulation of which, coincidentally, has reduced
dioxin emissions. Figure 2 demonstrates that, overall, industrial,
municipal and transportation dioxin emissions have declined
dramatically as a result of regulation, whereas emissions
from backyard barrel burning of rubbish and residential wood
burning have remained essentially constant since 1987, and
as of 2000 have overtaken industrial/municipal/transportation
sources as more significant emitters of dioxin.
Based on the EPA's inventory of dioxin sources, more stringent
restrictions on the regulated community will not significantly
reduce dioxin emissions. Instead, the mostly unregulated practice
of backyard barrel burning of rubbish is a likely candidate
for effecting further emissions reductions. In fact, Maine,
New Hampshire, California, and other states have recently
enacted legislation to control dioxin emissions from burn
barrels.
A Changing Pattern of Congener Emissions Results in
Changing Exposure
Overall environmental levels of dioxin have fallen over the
past 30 years. In addition, the relative proportions of dioxin
congeners emitted to the environment have changed such that
greater proportions of dioxin congeners of lower toxicity
are emitted. This pattern of decline has resulted in significant
reductions in average human exposure to 2,3,7,8-TCDD, the
dioxin congener of greatest toxicity and concern, and current
exposures to dioxin are typically composed of smaller amounts
of lower toxicity congeners.
Hays and Aylward (2001) examined mean serum lipid levels
of 2,3,7,8-TCDD in 1,419 US Air Force Vietnam era veterans
not occupationally exposed to Agent Orange. These researchers
back-calculated the amount of 2,3,7,8-TCDD the veterans would
have had to be exposed to in order to produce the measured
serum lipid levels of this compound. Their model predicts
that 2,3,7,8-TCDD intake must have declined to very low levels
by 1992 in order to produce the mean measured serum lipid
2,3,7,8-TCDD decrease seen over the decade 1986-1996.
Thus, not only are overall environmental levels of dioxin
declining through decreased emissions, but also, the total
toxicity of the congeners to which humans are exposed are
decreasing. As environmental levels of 2,3,7,8-TCDD have dropped,
average body levels of this chemical also have decreased substantially.
Indeed, Petreas et al. (2001) in a study of persistent
halogenated contaminants, recently documented a decrease in
Californians' dioxin body burdens which demonstrated statistically
significant decreases in all but one major congener (2,3,4,7,8-PeCDF).
The authors claim the decline is ".consistent with decreases
observed worldwide and probably reflects successful measures
of pollution control" (p. 878).

Summary
In conclusion, the application of control technologies, especially
to incineration processes in the US, has led to significant
decreases in dioxin emissions to the environment. Furthermore,
remaining emissions are characterized by a less toxic array
of dioxin congeners. Given the documented substantial declines
in serum 2,3,7,8-TCDD for the decade preceding 1996, and the
application of control technologies by industry, it is likely
that 2,3,7,8-TCDD body levels have continued to decrease,
reflecting further declines in exposure to this chemical.
Unregulated domestic burning has supplanted incineration
as a major source of dioxins and may become increasingly regulated.
Although natural combustion processes, such as forest fires,
ensure the enduring presence of a baseline of dioxins in the
environment which can never be eliminated, the use of technology
to minimize anthropogenic dioxin emissions is a documented
success story.
References
Hays, S.M. and Aylward, L.L. (2001). Temporal trends in body-burden
suggest that dioxin exposure in the general population have
declined significantly. Organohalogen Compounds, 52, 214.
Petreas, M., She, J., Visita, P., Winkler, J., McKinney,
M., Brown, F.R., Dhaliwal, J., Denison, G., and Mok, M. (2201).
Trends in persistent contaminants in California biota, Symposia
Papers Presented Before the Division of Environmental Chemistry,
American Chemical Society, Sand Diego, CA, April 1-5, 2001.
U.S. EPA (Environmental Protection Agency). 2006. An inventory
of sources and environmental releases of dioxin-like compounds
in the United States for the years 1987, 1995, and 2000. National
Center for Environmental Assessment, Washington, DC; EPA/600/P-03/002F.
(http://cfpub.epa.gov/ncea/cfm/recordisplay.cfm?deid=159286)
U.S. EPA (September, 2000 Draft). Exposure and Human Health
Reassessment of 2.3.7,8-Tetrachlorodibenzo-p-Dioxin (TCDD)
and Related Compounds. Part III: Integrated Summary and Risk
Characterization for 2.3.7,8-Tetrachlorodibenzo-p-dioxin (TCDD)
and Related Compounds.
World Health Organization, (June, 1999). "Dioxins and their
effects on human health". [On-Line]. Available: http://www.who.int/inf-fs/en/fact225.html.
World Health Organization (1998). Executive Summary. Assessment
of the health risk of dioxins: re-evaluation of the tolerable
daily intake (TDI). Available: http://www.who.int/pcs/pubs/dioxin-exec-sum/exe-sum-final.html.
Notes
1"Dioxin" here is defined as the
totality of 7 dioxins and 10 furans (of a much larger family
of similar but less toxic compounds) of environmental concern.
2"Backyard barrel burning of rubbish"
is the mostly rural practice of burning domestic household
and garden refuse in open air, often in steel barrels.
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