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Atrazine in agricultural runoff and its impacts on two anuran species in central
Illinois
Lee M. Gross, Karen F. Gaines, and Stephen J. Mullin
Department of Biological Sciences, Eastern
Illinois University
Introduction
Habitat fragmentation has been speculated as one of the main anthropogenic
causes for the decline in amphibians (1). The destruction of wetlands has been
dramatic in Illinois, where almost 90% of native wetlands have been destroyed
for agriculture and urban development (2). Agricultural land use can not only
increase habitat fragmentation of wetland and forest habitats, but can also
increase amphibian exposure to chemicals from agricultural runoff (3). The
herbicide atrazine has been reported to produce adverse effects in amphibians.
Atrazine is the second most commonly used herbicide in the United States.
Research questions
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Is atrazine present in water, sediment, and tissue samples taken from Warbler
Woods Nature Preserve (WWNP)?
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Does atrazine exposure at WWNP cause deformities in naive wood frog larvae?
Methods
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WWNP (81.5 ha) contains secondary oak-hickory forest, old agricultural fields
with tree seedlings, and four ponds (1 ephemeral and 3 permanent ponds, labeled
A,B,C, and D, respectively; Figure 1).
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Pond A (experimental pond) is <35 m to active agricultural fields. Pond C
(control pond) is buffered by early successional fields and is >200 m from
agricultural fields.
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One 80 µm and one 50 µm Nitex® bolting cloth enclosure were put into ponds A and
C. Wood frog larvae (n=125), at Gosner stage, were put into each enclosure (Figure
2). Tadpoles were allowed to complete metamorphosis and frozen for further
tissue analysis.
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Water and sediment samples were taken weekly from March-June, then monthly from
July-October in ponds A and C. Samples were frozen until tested for atrazine
concentration using a test kit from AMBRAXIS, that uses an ELISA.
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Bullfrogs (Rana catesbeiana) were collected from the site to determine if
atrazine is bioaccumulating within amphibian tissues.
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Paired t-tests were used to detect differences between atrazine concentrations
in pond A and pond C samples.
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Figure 1: Map of Warbler Woods Nature
Preserve |
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Figure 2: Enclosures in Pond A |
Results
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No limb deformities were observed from the metamorphs collected from pond A.
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All tadpoles in pond C died or were lost.
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Atrazine was detectable in water from April through September (Figure. 3). There
was no difference in atrazine concentration between pond A and pond C (t=.407,
P=0.688, df=19).
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Figure 3: Atrazine concentration in water
samples from ponds A and C during the 2006 activity season. |
Discussion
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As little as 0.1 ppb of atrazine can be an endocrine disruptor that can produce
feminization in male amphibians, resulting in hermaphrodites, gonadal
deformities, and castration (4).
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Although the atrazine concentrations in WWNP water samples were over 0.1 ppb
most of the year, they were highest during the the time period when wood frogs
were metamorphosing (Figure 4).
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A previous study showed limb deformities were more common in wood frogs (R. sylvatica) that lived in areas that were exposed to agricultural runoff (5).
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No physical deformities were observed in R. sylvatica juveniles.
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Protected areas are still subjected to chemical pollution from agricultural
runoff, making it increasingly difficult for managers to maintain amphibian
populations.
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Figure 4: Atrazine concentration in water
samples from ponds A and C during wood frog larval period of 2006. |
Future Directions
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Sediment, Bullfrog tissues, and wood frog tissues will be analyzed for atrazine.
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Parasite species composition will be assessed from collected bullfrogs.
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Smallmouth salamanders (Ambystoma texanum) have accounted for all but one limb
deformity seen at WWNP (Figures 5 & 6). Therefore, we will repeat this experiment
in 2007, using smallmouth salamander larvae.
References
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Semlitsch, 2000, Journal of Wildlife Management 64:615- 631.
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Suloway & Hubbell, 1994, Illinois Natural History Survey, Champaign.
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Boone & Semlitsch, 2001, Conservation Biology. 15:228-238.
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Hayes, 2004, Bioscience 54:1138-1149.
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Kiesecker, 2002, PNAS 99:9900-9904.
Acknowledgements
We thank the Illinois Department of Natural Resources for funding various
portions of this project. Special thanks goes to B. Bostrom, T. Buhnerkempe, M.
Diana, M. Fincel, A. Fornell, M. Olds, C. Powell, J. Towey, C. Foster, and L.
Walston for all their assistance in the field. L.B. Hunt graciously granted
access to the WWNP site.
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