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In trying to downplay the
significance of the latest tests, EPA has gone too far by suggesting the
off-site areas are not a threat. The most recent chemical testing data for
the creek area surrounding the Brunswick Wood Preserving Superfund Site
shows moderately high levels of toxic chemicals. An Environmental Protection
Agency (EPA) health effects study using exposure models indicates that
although the levels of arsenic, petroleum chemicals, and dioxins are
significant, the levels are not high enough to be acutely toxic. In other
words, it would require long exposure before injury occurs. Unfortunately,
the study model has several flaws that render the conclusions incomplete.
The biggest problem is that the model only used exposure to Burnett Creek
chemicals; it did not consider that children might also receive exposure in
other areas around the site. Secondly, it does not consider whether levels
are increasing or decreasing. These factors are important since the current
model will change depending on the future levels. The data indicate a
significant amount of off-site contamination exists in areas where children
can play, and only a cleanup can make the area free from risk.
Received for review with
reference to the Brunswick Wood Preserving Site are: Review of Off-site Soil
and Sediment Data dated November 3, 2000, an October 30, 2000 Health
Consultation performed by the Agency for Toxic Substances and Disease
Registry (ATSDR) based on the Soil and Sediment Data, portions of the still
incomplete Soil, Sediment and Groundwater Studies, and a Georgia Times Union
article quoting Brian Farrier, the EPA Site Remedial Project Manager (RPM)
regarding the data.
The overall direction of the
Site review and the remarks by Mr. Farrier imply that Burnett Creek and
surrounding areas are not potentially hazardous to children, wildlife or
from subsistence fishing activities.
An Overview of Testing and
Interpretation
The purpose of environmental
testing is to determine the extent of contamination. When contamination is
found, a health-effects modeling study is used to determine if the
contamination is toxic to people or the environment. Health effects are
divided into two categories: cancer and non-cancer risks. Environmental
cancer risk modeling is based on a probability model, in some ways not
unlike “lotto” or other games of chance. Susceptibility to cancer is
determined by environmental and lifestyle effects, but still requires
exposure to certain cancer-causing (carcinogenic) chemicals, viruses, or
energies. Each carcinogen also has a certain potency, or ability, to start
cancer cells growing. That potency is different for different animal species
and in all known cases is “dose-responsive.” Dose-response simply means that
with more carcinogen exposure, the more likely it may cause cancer. Everyone
uses the phrase “more likely” or just “likely” while not really realizing it
is a mathematical probability term. In cancer modeling, a dose-response
effect means that a high carcinogen dose is more likely (higher probability)
to result in more cases of cancer. “Dose” is further broken down into two
different effects: the concentration of the chemical and the length of
exposure to the chemical.
The interaction of all of these
different factors is rolled into a probability model where all of the other
factors (genetics, lifestyle, potency, exposure) are on one side of an
equation and the chemical concentration is on the other side of the
equation. This allows researchers to easily express the relative dangers of
different chemicals in a convenient graph.
In the lotto-type games, if
someone had all 23 million possible tickets (based on a 6 ball, 53-number
game) then they have a 100 hundred percent likelihood of winning. There are
some human carcinogens, ionizing radiation for example, where above a
certain dose the person’s likelihood of getting cancer approaches 100% as
well. However, most environmental toxins contribute to the lifetime risk of
cancer, rather than acting as direct risks. Again, for carcinogens those
risks are expressed in terms of the “chance of getting a cancer.” For
environmental clean-ups, the law places a “one-in-one-million chance” of a
new cancer as acceptable, but allows up to a “one-in-ten-thousand chance.”
This minimum cleanup standard can be viewed as 100 times riskier than the
one-in-one-million chance, and as a policy, it is very controversial. For
chemicals that are known mutagens (anything that causes mutations in DNA,
usually the starting point in cancer development), or where the mechanism of
action is poorly known, a one-in-ten-thousand chance may not be a safe dose.
There is also considerable doubt if the one-in-ten-thousand risk level is
truly safe for children, certainly for some chemicals that level is too
risky.
Toxicity is considered by a
different model. For nearly all-environmental chemicals, there is very good
animal toxicity data. Generally, toxic effects in animals, such as liver or
kidney failure, can be “extrapolated” to humans. Extrapolation means that
the dose for a toxic injury in animals and humans can be compared based on
body-weights. This is in contrast to cancer, where there is no easy
comparison of animal cancers with human cancers. For toxicity, a “Hazard
Quotient” (HQ, or hazard index, HI) is developed again using the chemical
concentration as the benchmark. Chemicals are usually considered hazardous
of the HQ exceeds a value of 1.
If the cancer risk is high, say
one-in-one-thousand, and/or the hazard quotient is high, say over 3, the
response from EPA may be to order an immediate cleanup of the area. These
levels are indicative of acute toxicity or short-term cancer risk.
Unfortunately, the decision system is bureaucratic and inefficient. EPA
collects or orders samples collected. The analysis is performed and the data
sent to the ATSDR (Agency for Toxic Substances and Disease Registry). ATSDR
has no say in how the study is conducted; they only respond to the data sent
to them. Their remarks are then sent back to the EPA for comments on their
comments. At the Brunswick Wood Preserving site several studies have been
done with the on-site areas, different studies done with some off-site
areas, and now this study only looks at the creek areas. In fact, one person
could be exposed in several areas to varying concentrations of the same
chemical, but these studies would not consider that total effect.
In contrast to Region 4 EPA’s
conclusion that the off-site contamination poses no risk to neighborhood
children, the facts plainly tell a different story:
_ Given the long
latency period for cancer development, children exposed to sediments
containing carcinogenic polycyclic aromatic hydrocarbons are enduring too
much risk.
_ The data shows
arsenic levels up to 3.8 parts-per-million. At nearly 8 times the Cancer
Risk Evaluation Guide, this is sufficiently high to justify a fast track
cleanup up the affected areas.
_ The ATSDR Health
Consultation actually found that a significant number of sediment samples
from residential areas exceed chronic guidelines for dioxin. This should be
a cause of concern at the EPA and in the community. Unfortunately, ATSDR and
Region 4 EPA dismissed the importance of these studies by saying “safety
margins” built into the guidelines will protect children. This is
unscientific reasoning.
_ EPA should have
requested a comprehensive assessment by ATSDR rather than the limited
assessment as was done. Region 4 is well aware that bias can result from a
limited assessment.
_ The most striking
fact about the data is that only 10 samples were taken but nearly all
contained toxins from the Brunswick Wood Preserving Site. These sediments
are heavily affected and the potential for toxic injury exists. Certainly a
more comprehensive testing and analysis is needed in this area.
Probability is a complex
science, but look at it this way: if you never buy a lotto ticket, you never
have a chance of losing; likewise, if you are never exposed to a certain
carcinogen, you can never get cancer from it. Region 4 EPA clearly does not
understand this very basic law of probability and is assigning “safe” levels
without a scientific understanding of probability laws.
Worse yet, EPA is
second-guessing the scientific advisory panels which set the safe levels by
saying that there are “safety margins” that Region 4 can exceed at will.
This is similar to a pilot ignoring National Transportation Safety Board
rules on safe aircraft operation by assuming the NTSB set the values
arbitrarily high. Clearly, EPA has exceeded their mandate of authority in
producing conclusions such as stated in these documents.
The result of considering each
small study independent of the whole is that Region 4 EPA does not properly
consider all of the potential exposure. They have subsequently justified
long delays in cleanups by stating that no immediate risk occurs, when the
facts speak differently. The real reason for the long delays in finding the
pollutants and rendering them harmless is not known. Perhaps Region 4 does
not want to spend “their” money cleaning up the Brunswick Wood Preserving
Site. Regardless of the reason, once someone is exposed to a mutagen or
carcinogen that exposure cannot be undone. The earlier in life that exposure
occurs the more likely that harm will accrue. EPA’s assessment of the
potential harm at Brunswick Wood Preserving Site is threatening to area
children.
Written by R. Kevin Pegg,
Ph.D.; edited by Dr. Mary S. Saunders. Copies of the newsletter are
available from the GEC, at the Glynn County library, or at
www.NucleicAssays.com/tags on the Internet.
"This project has been
funded wholly or partly by the U.S. Environmental Protection Agency under
Assistance Agreement Number 1984482-98-0 to The Glynn Environmental
Coalition, Inc. The contents of this document do not necessarily reflect the
views and policies of the U.S. Environmental Protection agency, nor does
mention of trade names or commercial products constitute endorsement or
recommendation for use."
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