DEVELOPMENT OF EXPECTATIONS OF LARVAL AMPHIBIAN ASSEMBLAGE STRUCTURE IN SOUTHEASTERN DEPRESSION WETLANDS

By J. Snodgrass, A. Bryan, J. Burger. 2000

93 citations recorded by the source corpus.

Subfields: Ecological Modeling, Global and Planetary Change, Nature and Landscape Conservation

View Paper: https://www.semanticscholar.org/paper/d0c02fb4b08d7defbabc81c8b6457a08456ba550

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In Ecological Modeling

In Global and Planetary Change

In Nature and Landscape Conservation

Citations in the corpus

AGRICULTURAL PONDS SUPPORT AMPHIBIAN POPULATIONS (2004, result): “Our finding that species richness was negatively associated with pond area concurs with the idea that many amphibian populations depend upon temporary water bodies (Skelly 1996, Snodgrass et al. 2000).”
Macroinvertebrate community structure across a wetland hydroperiod gradient in southern New Hampshire, USA (2005, background): “Several researchers have recently pointed out the limited practical use of using wetland size as a basis for wetland protection (Semlitsch and Bodie 1998; Snodgrass et al. 2000a, b; Paton and Crouch, 2002; Babbitt et al. 2003).”
Habitat partitioning in European and North American pond‐breeding frogs and toads (2003, background): “…on the gradient varies more strongly among years than that in ephemeral or permanent ponds, because predators accumulate during wet periods and are largely eliminated by drying events (Harris et al., 1988; Jefferies, 1994; Schneider, 1997; Van Buskirk & Relyea, 1998; Snodgrass et al., 2000).”
Disturbance heterogeneity determines freshwater metacommunity structure (2004, background): “However, because pond size need not be associated with permanence (Snodgrass et al. 2000) and because increased aquatic macrophyte structure and decreased tree canopy cover can both result from hydroperiodinduced tree mortality (Relyea 2002), habitat permanence is likely the main factor explaining…”
Comparative water snake ecology: conservation of mobile animals that use temporally dynamic resources (2004, background): “Anuran prey are often more abundant in ephemeral wetlands than in permanent wetlands because wetlands that dry often lack fish predators, or only support low numbers of fish (Werner and McPeek, 1994; Snodgrass et al., 2000).”
Climate change and amphibians (2005, background): “Predators and competition from other amphibians restricts the ability of these species to switch to more permanent water (Wellborn et al., 1996; Snodgrass et al., 2000).”
Functional equivalence of non‐lethal effects: generalized fish avoidance determines distribution of gray treefrog, Hyla chrysoscelis, larvae (2003, background): “…of preda- Accepted 6 March 2003 Copyright © OIKOS 2003 ISSN 0030-1299 OIKOS 102:3 (2003) 623 tory fish is a particularly well-documented field pattern; certain species do not occur or occur at reduced densities where fish are present (Hecnar 1997, Babbitt and Tanner 2000, Snodgrass et al. 2000).”