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Determining
Significant Endpoints for Ecological Risk Analysis

T. G. Hinton, J.
D. Congdon, C. Rowe, David
Scott
(Savannah River
Ecology Laboratory)
and J. Bedford, F. W. Whicker
(Colorado State University)
Background
The Department of Energy (DOE) is faced with
complex decisions regarding the clean-up of contaminated sites.
Ecological risk analyses can contribute greatly to the
decision-making process. The science of quantifying risk to
humans from exposure to radiation is well developed and
internationally accepted. In contrast, the methods, endpoints and
interpretation of ecological risk analyses are still being
developed and lack standardization (see Table 1). Our goal is to
provide DOE with a scientifically defensible protocol for
measuring ecological risks. A sound protocol is possible only
when sub-lethal cellular damage (i.e., from exposure to chronic,
low-level radiation or chemical contaminants) is related to the
performance of individuals and the persistence of populations.
Table 1. Fundamental
Differences In Human and Ecological Risk Analyses
| Type of Risk |
Unit of Observation |
Endpoint |
Dose-Response |
| Human risk |
Individual |
Lifetime cancer |
Relationships established |
| Ecological risk |
Varies |
Varies |
Not established |
Research Objectives
We plan to establish protocols for assessing ecological risks
by coupling measured molecular damage to effects observed at the
individual and population levels of biological organization. Our
working hypothesis is that molecular damage leads to changes in
metabolic rate due to the increased cost of maintenance and
repair. Changes in energy allocation potentially will affect:
growth rates, age at maturity, fecundity, age-specific
survivorship, and longevity.
At present this research focuses primarily on:
1) developing a molecular probe to quantify cellular damage due to
exposure to low-level radiation;
2) quantifying individual- and population-level responses of
organisms exposed to contaminants; and
3) constructing an experimental facility (Guarded Experimental
Tank Facility for Understanding Contaminant Transfer) to examine
effects of chronic low-level radiation and heavy metal exposure
on aquatic organisms in mesocosms.
Metabolic Rate as an
Indicator of Stress from Contaminant Exposure
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Metabolic
rate measures an animal's cost of maintenance or activity. Changes in
metabolic rates have implications for processes such as energy storage,
growth and reproduction. The metabolic rate of exposed organisms may be
an excellent physiological measure of sub-lethal stress because it reflects
multiple processes occurring within an organism. Metabolic rate may therefore
be used to determine whether cellular effects from contaminant exposure
are of significance at higher levels of biological organization. We have documented increased metabolic rates in numerous
species of animals exposed to non-radioactive contaminants from a
coal ash basin (D-Area basin on the SRS). To see representative
results, click on the link below: |
Representative
Results
Currently we are testing:
whether metabolic
rates increase in animals exposed to chronic, low-level
radiation;
how changes in
metabolic rates differ when organisms are exposed to both
radioactive and non-radioactive contaminants; and
how previous
exposures to contaminants affect the metabolic response from
subsequent exposures.
(For more information on this aspect of our work, contact:
Dr. Justin Congdon; 803 -725-2472; congdon@srel.edu)
The Irradiation-Mesocosm
Facility
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We
plan to rear animals in 50 outdoor mesocosms designed to test effects
of chronic, low-level irradiation, alone and in conjunction with metal
contaminants. Replicate treatments and powerful statistical methods are
possible. Each "radiation" mesocosm will have a sealed 137-Cs
source located above it. Radiation exposures to animals will be varied
by varying the strength of the source, and quantified by using thermoluminescent
dosimeters. |
For more images relating to the mesocosm, click
here.
By using a variety of organisms we can determine:
the frequency of
chromosome damage at various radiation exposures and metal
contaminant concentrations;
the relationship
between cellular damage and metabolic rate; and
treatment effects
on an individual's energy allocation pattern, growth and
survival.
Benefits to the DOE are:
reduce
uncertainties associated with ecological risk analyses;
provide defensible
scientific evidence on which cleanup decisions can be based; and
broad application
across DOE sites reduce DOE's need to take an ultra-conservative
approach to cleanup, resulting in substantial cost savings.
(Funded by an EMSP grant from the DOE)
For more information contact : Dr. Tom Hinton, 803 -557 -7454; thinton@srel.edu
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