Short-billed Dowitcher Habitat
Model
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Gulf of Maine Watershed Habitat Analysis
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Species
Table
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Draft Date:
March, 2001
Species:
Short-billed Dowitcher, Limnodromus griseus
Use of Study Area Resources:
Migration. Short-billed dowitchers use coastal flats while migrating through
the study area. They breed in southeast Alaska and across subarctic Canada,
and winter in coastal areas of southern California, Mexico, Central America,
the Carribean and northern coasts of South America (Johnsgard 1981, Hayman
et al. 1986).
Habitat Requirements:
Short-billed dowitchers are one of several species of shorebirds which use
primarily coastal areas as intermediate stopover points for feeding and resting
during long distance migration (McNeil and Cadieux 1972, Fefer and Schettig
1980). Dowitchers feed on mud and sand flats in sheltered bays and estuaries,
on borders of shallow pools in salt marshes, on sandy beaches and may even
use flooded fields (Hayman et al. 1986, Degraaf and Rappole 1995). In Maine
they also feed on muddy flats of lakes during draw-down events (Pierson et
al. 1996). They forage almost entirely by tactile probing of wet substrates,
and take primarily polychaete worms, and amphipod crustaceans, and also small
bivalve and gastropod molluscs (McCollough 1981) and eggs of horseshoe crabs
(Sperry 1940 in Terres 1995).
Model:
The model relied on abundance/occurrence information from a Maine Department
of Inland Fisheries and Wildlife (MDIFW) shorebird coverage, the Manomet
Bird Observatory's International Shorebird Survey (ISS) database for
Massachusetts and New Hampshire, and inland sites used by least sandpipers
in Maine (Pierson et al. 1996). The occurrence information was used to select
the general localities used by the species. Environmental data sets (bathymetry
and wetland cover type) were used to select areas within those localities
likely to have been used. The ISS data specified the observation locations
only to the nearest minute, and Pierson et al.'s (1996) observations also
were somewhat general, so all suitable cover types (see table, below) within
a 1 km radius of those points were regarded as having the level of use indicated
at the observation point.
| NWI Designations (wetlands only) |
Cover Types | Cover Suitability (0 - 1 scale) |
| Upland deciduous forest | ||
| Upland coniferous forest | ||
| Upland mixed forest | ||
| Grassland | ||
| Upland scrub/shrub | ||
| Cultivated | ||
| Developed | ||
| Bare ground | ||
| PEM, L2EM | Lake/pond, emergent vegetation | 0.5* |
| PFOcon | Palustrine forest, conifer | |
| PFOdec | Palustrine forest, deciduous | |
| PSSdec | Palustrine scrub shrub, deciduous | |
| PSScon | Palustrine scrub shrub, conifer | |
| PAB, L2AB | Lake/pond, aquatic vegetation | |
| L1UB, PUB | Lake/pond, unconsolidated bottom | 0.5* |
| L2US | Lake, unconsolidated shore | 1.0 |
| L2RS | Lake, rocky shore | |
| R1UB | Riverine subtidal unconsolidated | |
| Rper | Riverine perennial | |
| E1AB | Estuarine subtidal vegetated | |
| E1UB | Estuarine subtidal unconsolidated bottom | |
| E2AB | Estuarine intertidal algae | |
| E2EM | Estuarine intertidal emergent | 0.5 |
| E2RS, R1RS | Estuarine, tidal river rocky shore | |
| E2SS | Estuarine intertidal shrub | |
| E2US | Estuarine intertidal unconsolidated shore | 1.0 |
| M1AB | Marine subtidal vegetated | |
| M1UB | Marine subtidal unconsolidated bottom | |
| M2AB | Marine intertidal algae | |
| M2RS | Marine intertidal rocky shore | |
| M2US | Marine intertidal unconsolidated shore | 1.0 |
| NOTES | *included only if within 1 km of known site with regular draw-downs |
Habitat Suitability Scoring: Sites with short-billed dowitcher occurrences and having any of the suitable landcover types (see table, above) first were scored according to level of use. If a site had 5 or more birds observed at any time, the suitability index = 1.0; else, if any birds were present, or use was expressed as a narrative (Pierson et al. 1996), the suitability index = 0.5. This value then was multiplied by the landcover score.
Suitable cover types outside of the observation/occurrence polygons were scored as potential foraging habitats; unconsolidated sediment cover types were rescored 0.2 and marsh 0.1.
Sources:
DeGraaf, R.M. and J.H. Rappole. 1995. Neotropical Migratory Birds: Natural
History, Distribution and Population Change. Comstock Publishing Associates,
Ithaca, NY. 676 pp.
Fefer, S.I. and P.A. Schettig. 1980. An Ecological Characterization of Coastal Maine. U.S. Fish and Wildlife Service, Northeast Region, Newton Corner, MA.
Hayman, P., J. Marchant and T. Prater. 1986. Shorebirds: an Identification Guide to the Waders of the World. Houghton Mifflin Co., Boston, MA. 412 pp.
Johnsgard, P.A. 1981. The Plovers, Sandpipers and Snipes of the World. Univ. of Nebraska Press. Lincoln, NE. 493 pp.
McCollough, M.A. 1981. The feeding ecology of migratory semipalmated sandpipers, short-billed dowitchers, semipalmated plovers, and black-bellied plovers on staging areas in eastern Maine. M.S. thesis. Univ. of Maine at Orono. December 1981.
McNeil, R. and F. Cadieux. 1972. Fat content and flight range capabilities of some adult spring and fall migrant North American shorebirds in relation to migration routes on the Atlantic coast. Le Naturalist Canadien 99:589-606.
Pierson, E.C., J E. Pierson, and P.D. Vickery. 1996. A Birders Guide to Maine. Down East Books, Camden, ME.
Terres, J.K. 1995. The Audubon Society Encyclopedia of North American Birds. Wings Books, NY. 1109 pp.