FORAGING TRADE-OFFS ALONG A PREDATOR–PERMANENCE GRADIENT IN SUBALPINE WETLANDS

Authors

  • Scott A. Wissinger,

    1. Biology Department, Allegheny College, Meadville, Pennsylvania 16335 USA
    2. Rocky Mountain Biological Laboratory, P.O. Box 519, Crested Butte, Colorado 81224 USA
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  • Howard H. Whiteman,

    1. Department of Biological Sciences, Murray State University, Murray, Kentucky 42071 USA
    2. Rocky Mountain Biological Laboratory, P.O. Box 519, Crested Butte, Colorado 81224 USA
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  • Grace B. Sparks,

    1. Environmental Science Department, Allegheny College, Meadville, Pennsylvania 16335 USA
    2. Rocky Mountain Biological Laboratory, P.O. Box 519, Crested Butte, Colorado 81224 USA
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    • Present address: College of Forest Resources, University of Washington, Seattle, Washington 98195 USA.

  • Gretchen L. Rouse,

    1. Environmental Science Department, Allegheny College, Meadville, Pennsylvania 16335 USA
    2. Rocky Mountain Biological Laboratory, P.O. Box 519, Crested Butte, Colorado 81224 USA
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    • Present address: U.S. Geological Survey, National Water Quality Assessment Program, 425 Jordan Road, Troy, New York 12180 USA.

  • Wendy S. Brown

    1. Rocky Mountain Biological Laboratory, P.O. Box 519, Crested Butte, Colorado 81224 USA
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Abstract

We conducted a series of field and laboratory experiments to determine the direct and indirect effects of a top predator, the tiger salamander (Ambystoma tigrinum nebulosum), on larvae of two species of limnephilid caddisflies (Limnephilus externus and Asynarchus nigriculus) in subalpine wetlands in central Colorado. Asynarchus larvae predominate in temporary wetlands and are aggressive intraguild predators on Limnephilus larvae, which only predominate in permanent basins with salamanders. We first conducted a field experiment in mesocosms (cattle tanks) to quantify the predatory effects of different life stages of salamanders on the two caddisfly species. Two life stages of the salamanders (larvae and paedomorphs) preferentially preyed on Asynarchus relative to Limnephilus. Subsequent laboratory experiments revealed that high Asynarchus activity rates and relatively ineffective antipredatory behaviors led to higher salamander detection and attack rates compared to Limnephilus. In a second field experiment (full factorial for presence and absence of each of the three species), we found that salamander predation on Asynarchus had an indirect positive effect on Limnephilus: survival was higher in the presence of salamanders + Asynarchus than with just Asynarchus. In the laboratory we compared the predatory effects of salamanders with and without their mouths sewn shut and found the observed indirect positive effect on Limnephilus survival to be mainly the result of reduced numbers of Asynarchus rather than salamander-induced changes in Asynarchus behavior. We argue that indirect effects of predator–predator interactions on shared prey will be mainly density-mediated and not trait-mediated when one of the predators (in this case, Asynarchus) is under strong selection for rapid growth and therefore does not modify foraging behaviors in response to the other predator. The reciprocal dominance of Limnephilus and Asynarchus in habitats with and without salamanders probably reflects a trade-off between competitive superiority and vulnerability to predation. The high activity levels and aggressiveness that enable Asynarchus to complete development in temporary habitats result in strong asymmetric competition (via intraguild predation) with Limnephilus. In permanent habitats these same behaviors increase Asynarchus vulnerability to salamander predation, which indirectly benefits Limnephilus. This and previous work implicate salamanders as keystone predators that exert a major influence on the composition of benthic and planktonic assemblages in subalpine wetlands.

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