Editorial Type:
Article Category: Research Article
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Online Publication Date: 10 Sept 2008

Growth and Developmental Effects of Coal Combustion Residues on Southern Leopard Frog (Rana sphenocephala) Tadpoles Exposed throughout Metamorphosis

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Page Range: 499 – 503
DOI: 10.1643/CG-07-047
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Abstract

The effects of aquatic deposition of coal combustion residues (CCRs) on amphibian life histories have been the focus of many recent studies. In summer 2005, we raised larval Southern Leopard Frogs, Rana sphenocephala, on either sand or CCR substrate (approximately 1 cm deep within plastic bins) and documented effects of sediment type on oral disc condition, as well as time to, mass at, and total body length at key developmental stages, including metamorphosis (Gosner stages [GS] 37, 42, and 46). We found no significant difference in mortality between the two treatments and mortality was relatively low (eight of 48 in the control group and four of 48 in the CCR group). Ninety percent of exposed tadpoles displayed oral disc abnormalities, while no control individuals displayed abnormalities. Tadpoles raised on CCR-contaminated sediment had decreased developmental rates and weighed significantly less at all developmental stages, on average, when compared to controls. The CCR treatment group was also significantly shorter in length than controls at the completion of metamorphosis (GS 46). Collectively, these findings are the most severe sub-lethal effects noted for any amphibian exposed to CCRs to date. More research is needed to understand how these long term effects may contribute to the dynamics of local amphibian populations.

Copyright: 2008 by the American Society of Ichthyologists and Herpetologists
Figure 1
Figure 1

Mean masses ±1 standard error of Rana sphenocephala tadpoles exposed to control (n  =  10) or CCR-contaminated (n  =  6) substrate at 50 days post exposure (DPE), early hind limb toe differentiation (GS 37), forelimb emergence (GS 42), and completion of metamorphosis (GS 46). Treatments are significantly different (repeated measures ANOVA; P  =  0.007, F  =  10.063).


Figure 2
Figure 2

Mean total body lengths ±1 standard error of Rana sphenocephala tadpoles exposed to control (n  =  10) or CCR-contaminated (n  =  6) substrate at the completion of metamorphosis (GS 46). Treatments are significantly different (ANOVA; P  =  0.003, F  =  12.864).


Figure 3
Figure 3

Mean times ±1 standard error to early hind limb toe differentiation (GS 37), forelimb emergence (GS 42), and completion of metamorphosis (GS 46) post exposure to control (n  =  10) or CCR-contaminated (n  =  6) substrate for larval Rana sphenocephala. Treatments are significantly different (repeated measures ANOVA; P  =  0.024, F  =  6.451).


Contributor Notes

Associate Editor: J. F. Webb.

Department of Biological Sciences, Auburn University, 331 Funchess Hall, Auburn, Alabama 36849; E-mail: (JDP) peterj1@auburn.edu. Send reprint requests to JDP.
Received: 12 Feb 2007
Accepted: 01 Nov 2007
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