Editorial Type:
Article Category: Other
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Online Publication Date: 01 Sept 2013

Fish Influences on Amphibian Presence and Abundance in Prairie and Parkland Landscapes of Minnesota, USA

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Page Range: 489 – 497
DOI: 10.1670/11-283
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Abstract

Many amphibian populations are declining, and increased understanding of the drivers of amphibian presence and abundance will help in their conservation. In 2005 and 2006 we estimated relative abundance of larvae of two common amphibian taxa, Tiger Salamanders (Ambystoma tigrinum) and ranid tadpoles (Northern Leopard Frog Lithobates pipiens and Wood Frog Lithobates sylvaticus), in 75 shallow lakes in prairie and parkland areas in Minnesota. We used a two-step procedure in which we first modeled presence-absence with data from all lakes and then modeled abundance only in lakes where the amphibian taxa were present. For the two amphibian taxa, a generalized linear mixed effects model was used to examine the effects of dynamic factors like fish abundance and static (timeframe of study) variables like fish community type, depth, and adjacent land cover. Fish variables had the greatest influence but differed for the presence and abundance models. Salamander and tadpole presence was inversely correlated to the abundance of benthivorous fish, while salamander abundance was best explained by total fish abundance and tadpole abundance by fish community type. We did not detect influences of land cover types on the amphibian taxa we surveyed. Our findings are important because they complement previous studies documenting that negative correlations with fish extend beyond piscivores to include both planktivores and benthivores. Hydrological changes in our study landscape (e.g., installation of drainage networks, wetland consolidation) associated with agriculture and other land uses have likely increased the distribution and abundance of fish populations, thus dampening amphibian breeding success.

Copyright: 2013
<sc>Fig</sc>
. 1.
Fig . 1.

Map showing the locations of our study areas relative to Minnesota's major ecoregions.


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. 2.
Fig . 2.

Relationship between: (A) log10 benthivorous fish CPUE and probability of larval Tiger Salamander presence in prairie and parkland shallow lakes in 2005 and 2006; (B) log10 overall fish CPUE and larval Tiger Salamander abundance; and (C) log10 benthivorous fish CPUE and probability of ranid tadpole presence.


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. 3.
Fig . 3.

Mean count ± 1 SE of (A) larval Tiger Salamanders and (B) ranid tadpoles in prairie and parkland sites in 2005 (white bars) and 2006 (gray bars). Mean values for tadpole counts in parentheses.


Contributor Notes

Corresponding Author. E-mail: brian.herwig@state.mn.us
Accepted: 28 Jun 2012
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