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Suitability of Coastal Marshes as Whooping Crane (Grus americana) Foraging Habitat in Southwest Louisiana, USA
Suitability of Coastal Marshes as Whooping Crane (Grus americana) Foraging Habitat in Southwest Louisiana, USA
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Suitability of Coastal Marshes as Whooping Crane (Grus americana) Foraging Habitat in Southwest Louisiana, USA
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Suitability of Coastal Marshes as Whooping Crane (Grus americana) Foraging Habitat in Southwest Louisiana, USA
Suitability of Coastal Marshes as Whooping Crane (Grus americana) Foraging Habitat in Southwest Louisiana, USA

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Suitability of Coastal Marshes as Whooping Crane (Grus americana) Foraging Habitat in Southwest Louisiana, USA
Suitability of Coastal Marshes as Whooping Crane (Grus americana) Foraging Habitat in Southwest Louisiana, USA
Journal Article

Suitability of Coastal Marshes as Whooping Crane (Grus americana) Foraging Habitat in Southwest Louisiana, USA

2014
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Overview
Foraging habitat conditions (i.e., water depth, prey biomass, digestible energy density) can be a significant predictor of foraging habitat selection by wading birds. Potential foraging habitats of Whooping Cranes (Grus americana) using marshes include ponds and emergent marsh, but the potential prey and energy availability in these habitat types have rarely been studied. In this study, we estimated daily digestible energy density for Whooping Cranes in different marsh and microhabitat types (i.e., pond, flooded emergent marsh). Also, indicator metrics of foraging habitat suitability for Whooping Cranes were developed based on seasonal water depth, prey biomass, and digestible energy density. Seasonal water depth (cm), prey biomass (g wet weight m-2), and digestible energy density (kcal g-1m-2) ranged from 0.0 to 50.2 ± 2.8, 0.0 to 44.8 ± 22.3, and 0.0 to 31.0 ± 15.3, respectively. With the exception of freshwater emergent marsh in summer, all available habitats were capable of supporting one Whooping Crane per 0.1 ha per day. All habitat types in the marshes had relatively higher suitability in spring and summer than in fall and winter. Our study indicates that based on general energy availability, freshwater marshes in the region can support Whooping Cranes in a relatively small area, particularly in spring and summer. In actuality, the spatial density of ponds, the flood depth of the emergent marsh, and the habitat conditions (e.g., vegetation density) between adjacent suitable habitats will constrain suitable habitat and Whooping Crane numbers.