|

Search
SREL
Herp site
| |
The Rainbow Bay Long-term Study

David Scott,
Tracey Tuberville,
Brian Metts, and
Brian Crawford
 |
Many years have passed since schoolchildren first discovered hundreds of
malformed frogs in a Minnesota farm pond. Almost 20 years have elapsed since
scientists initiated earnest discussions concerning "global amphibian
decline." Still, many questions addressing the decline and disappearance of
frogs, toads, and salamanders remain unanswered. Which species? How many
individuals? Where? And why? |
|
All these questions are the focus of global, ongoing research efforts.
Researchers are investigating the myriad possible causes of decline: wetland
and terrestrial habitat loss, chytrid fungus, climate change, ozone
depletion, aquatic contaminants, endocrine disruption, introduced predators,
parasites, acid rain, and more. Regardless of the research topic, in
virtually every scientific discussion of the amphibian crisis, one research
project is mentioned as a model for acquiring the long-term baseline data
needed to understand amphibian population fluctuations. That study is the
31-year Rainbow Bay Monitoring Project at the Savannah River Site (SRS). |
|
Rainbow Bay is a
2.4-acre isolated seasonal wetland in the center of the SRS. Sampling of the
amphibian and reptile communities that use the wetland, as well as the
surrounding 85-acre terrestrial habitat, began in September 1978. Animal
populations have been censused daily since initiation of the
study, making this project the longest running community study of its kind
in the world. More than 60 scientific articles on the fauna of this wetland
have been published, making it one of the best-studied habitats of its type.
Although this study was initiated by the Department of Energy to assess
potential ecological impacts of construction of a high-level waste
vitrification facility (the Defense Waste Processing Facility), it has
achieved that monitoring goal and much more. Daily records of the amphibians
and reptiles of Rainbow Bay have provided an extensive database regarding
seasonal and annual variation in amphibian numbers at a site that remains
relatively unimpacted by human activities. SREL's data have become
critically important to the scientific and conservation communities in light
of concerns about declining amphibian populations worldwide. The fact that
amphibian breeding populations have not declined at Rainbow Bay suggests
that the role of the SRS as a center for biological diversity in the
southeastern United States is significant, much to the credit of DOE.
Continued research at Rainbow Bay will allow SREL scientists to make better
predictions regarding the ecological impacts of future Savannah River Site
operations and forest management activities. |
| |
 |
|
The long-term
data from Rainbow Bay allow analyses that cannot be conducted on short-term
data – these analyses include population trends, environmental determinants
of changes in community structure, determinants of survivorship, and
potential consequences of climate change, to name a few. |
 |
| |
|
|
Rainbow Bay
currently serves as a reference site for several studies concerned with
potential effects of contaminants on amphibians. Funding for the project is
provided by The National Nuclear Security Administration (NNSA) of DOE, and
the Area Completion Projects group of the Savannah River Nuclear Solutions (SRNS)
company.
|


 |
|
Select reprints:
- Semlitsch, R. D., D. E. Scott, and J. H. K. Pechmann. 1988. Time and size
at metamorphosis related to adult fitness in Ambystoma talpoideum. Ecology
69:184-192. PDF
reprint
- Pechmann, J. H. K., D. E. Scott, R. D. Semlitsch, and J. W. Gibbons.
1989. Influence of wetland hydroperiod on diversity and abundance of metamorphosing
juvenile amphibians. Wetlands Ecology and Management 1:1-9.
-
Pechmann, J.H.K., D.
E. Scott, R. D. Semlitsch, J. P. Caldwell, L. J. Vitt, and J. W. Gibbons.
1991. Declining amphibian populations: the problem of separating human
impacts from natural fluctuations. Science 253:892-895.
PDF
reprint
- Semlitsch, R. D., D. E. Scott, J. H. K. Pechmann, and J. W. Gibbons.
1993. Phenotypic variation in the arrival time of breeding salamanders: individual
repeatability and environmental influences. Journal of Animal Ecology 62:334-340.
PDF
reprint
- Semlitsch, R. D., D. E. Scott, J. H. K. Pechmann, and J. W. Gibbons.
1996. Structure and dynamics of an amphibian community: evidence from a 16-yr study of a
natural pond. Pages 217-248 In "Long-term Studies of Vertebrate Communities." M.
L. Cody and J. D. Smallwood (eds.). Academic Press, New York.
PDF reprint
-
Daszak, P., D. E. Scott, A. M. Kilpatrick, C. Faggioni, J. W. Gibbons, and D.
Porter. 2005. Amphibian population declines at the Savannah River Site are
linked to hydroperiod, not chytridiomycosis. Ecology 86:3232-3237.
-
Taylor, B. E., D.
E. Scott, and J. W. Gibbons. 2006. Catastrophic reproductive failure,
terrestrial survival, and persistence of the marbled salamander. Conservation
Biology 20:792-801.
-
Scott, D. E., E. D. Casey,
M. F. Donovan, and T. K. Lynch. 2007. Amphibian lipid levels at metamorphosis
correlate to post-metamorphic terrestrial survival. Oecologia 153:521-532.
-
Scott, D. E. 2008. Marbled
salamander, Ambystoma opacum. Pages 139-141 in: Jensen, John,
Carlos Camp, Whit Gibbons, and Matt Elliott (eds.), Amphibians and Reptiles of
Georgia. University of Georgia Press, Athens, GA.
|
Rainbow Bay Photos
Herp Lab Projects | "A
Breeding Congress" | Home
|