Mercury and Cremation Issues Revisited
By Paul Rahill
Paul Rahill is President of the Matthews International
Cremation Division (MCD) headquartered in Orlando, Florida.
Matthews Cremation designs and manufactures cremation
equipment systems, caskets and urns as well as providing
service and repairs for cremation equipment, and crematory
supplies for the Cremation Industry.
Paul's involvement with the cremation industry began
in 1973. He has worked in various capacities in the
design, manufacturing and service of cremation equipment,
as well as research, development, environmental and
regulatory issues. Paul also develops and implements
seminars, training and certification programs for the
cremation industry.
Questions and concerns regarding mercury emissions from
crematories in the United States and Canada continue
to arise from time to time. Minimizing emissions of
all types are certainly a priority to crematory owners,
operators and cremator manufacturers who have developed
training programs to minimize many types of emissions
common to crematories. These training programs which
include special sections on cremator design, the environment
and proper operations have been presented to thousands
of operators over the last 20 years.
North American cremator designs have typically performed
better environmentally due to designs that included
large afterchambers for the reburning and scanning of
the exhaust prior to discharge into the atmosphere.
These types of designs are important as the locations
where crematories have often been built in North America
are light commercial and adjoining residential properties.
The most extensive cremation equipment emissions research
ever undertaken confirmed that the design and operation
of typical North American crematories provided significantly
better emissions than regulations required, and even
exceeded expectations with older operating systems.
However, issues will continue to come up and it is important
to address them by revisiting the information that is
available to us, updating both the facts and accuracy
at each opportunity. It is important to acknowledge
that often those raising these issues and questions,
though well-meaning, base their concerns on inadequate
information or un-answered questions. In this article,
I would like to specifically review how the cremation
process correlates to mercury emissions into the atmosphere,
the effect on the surrounding environment and the trends
for the future that will impact mercury emissions.
The United States Environmental Protection Agency (EPA)
describes mercury as a "naturally occurring
element that can be found throughout the environment".
Although naturally occurring, different activities by
humans can increase the amount of mercury that is moving
between the atmosphere, bodies of water, soils and within
themselves.
Some of these human activities that recycle mercury
in the environment are: municipal incinerators, breaking
of fluorescent lamps, dental facilities operations,
production and disposal of batteries, household waste
disposal and the operation of crematories as well as
other sources.
As this naturally occurring element cycles through our
environment, particularly in water, it is ingested by
small organisms as they feed. These organisms become
part of nature's food chain. The accumulation of mercury
we are most familiar with tends to center on fish. Different
types of fish have differing levels of mercury.
The lower a fish is in the food chain the lower it's
likely level of mercury accumulation. The higher the
fish is in the food chain the higher the potential mercury
concentration may be. Shark, swordfish and kingfish
are often cited as those having some of the highest
concentrations of mercury. Of course, human consumption
of these fish could increase one's exposure to mercury
depending on the actual levels found in the fish.
So, we can see that although mercury is a naturally
occurring element, over-exposure to it is not a good
thing for humans.
The most notable way that mercury enters the cremation
cycle, and therefore crematory emissions, is through
silver amalgam dental fillings found in many dead human
bodies.
Silver amalgam fillings contain mercury alloys that
when introduced through dead humans into the cremation
process of intense heat, often exceeding 180°F,
results in the volatilization of mercury and its emissions
into the atmosphere.
Silver amalgam tooth fillings containing mercury have
been common for many years, but their use appears to
be in significant decline. It is estimated that at one
time silver amalgam represented the greatest majority
of filling materials used, possibly as high as 90%.
Within the last 10 years, the percentage of fillings
containing mercury has already declined by 30%, a significant
decrease.
Although concern for the environment has always been
a priority for the dental industry, the primary driver
of this trend is actually found in the mirror, appearance.
Composite resins blend better with the color and appearance
of natural teeth. Other materials, such as gold, porcelain
and non-precious alloys are also used to restore teeth,
but none of these contain mercury. All these changes
in dental practices and consumer preferences have resulted
in significantly less mercury entering the cremation
stream and thereby reducing mercury emissions by reducing
mercury input.
Mercury emissions from crematories today are in significant
decline due primarily to changes in dental practices,
but how bad were they actually before this recent trend?
One of the most detailed studies of mercury emissions
impact was conducted in the United Kingdom where over
70% of dead humans are cremated. The study focused on
a crematorium that had been in operation for over 40
years, processing more than 112,000 cremations at the
time of the study.
The direction of the prevailing winds of the crematory
exhaust was determined to identify the land surrounding
the crematory where the highest concentrations of mercury
could be found. Five soil samples were taken along this
windward axis; three samples were taken on the downwind
axis and two additional samples were taken on the upwind
axis. All the samples were then analyzed.
As anticipated, the downwind samples contained a higher,
though not significant, level of mercury. "Trigger
concentrations" had been determined to evaluate
level of soil contamination. These "trigger levels"
ranged from low levels of 1mg/kg for human food producing
soils to 20mg/kg levels that are deemed acceptable for
children's playgrounds. The concentration of mercury
found in the crematory soil samples averaged less than
.15 mg/kg, almost 7 times lower than that allowed for
food production and more than 100 times lower than that
allowed for children's playgrounds. The soils were deemed
uncontaminated even after 112,000 cremations and 40
years of operation.
Consider that typical North American crematories operate
at only 20% of these production levels used in the analysis,
and it becomes readily apparent the anticipated impact
of mercury emissions from those crematories are even
further diminished.
As an industry, we must be receptive to discussing environmental
and performance issues whenever they come up. Proper
training of crematory operators and managers must be
continually encouraged and older cremation systems should
be properly maintained and updated to keep them in prime
operating condition.
Mercury use in the dental profession is significantly
in decline. However we should always scrutinize the
input of other materials into our crematories while
looking for and encouraging alternative materials to
be used in all areas of the death care profession, whenever
possible.
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