Solitary Sandpiper Habitat
Model
go to:
USFWS
Gulf of Maine Watershed Habitat Analysis
go to:
Species
Table
Draft Date:
November 2002
Species:
Solitary sandpiper, Tringa solitaria
Use of Study Area Resources:
Migration. Solitary sandpipers breed in the boreal forests of Alaska and
Canada, as far east as Quebec and Labrador (Moskoff 1995). They winter in
the Caribbean, Central and South America.
Habitat Requirements:
Solitary sandpipers do not migrate in large flocks as do most sandpipers
(Moskoff 1995). They migrate inland, along the coasts and offshore, flying
mostly at night (Moskoff 1995). Stop-over sites are wet or muddy, often stagnant
areas typically associated with lakes, ponds, swamps, sewage ponds and drainage
ditches (Veit and Petersen 1993). Hayman et al. (1986) and Moskoff
(1995) regard them as "uniquely a shorebird of forested ponds, often at high
elevations.... Rarely seen in coastal saltmarshes or other intertidal habitats."
However, Johnsgard (1981) states they occasionally use the upper ends of
estuaries. In fact, a Maine Department of Inland Fisheries and Wildlife (MDIFW)
shorebird database and the Manomet Bird Observatory's International Shorebird
Survey (ISS) database for Maine, Massachusetts and New Hampshire documented
a total of 48 tidal riverine and estuarine occurrence sites used by this
species.
Solitary sandpipers feed on insect (adults and larvae), small crustaceans, worms, molluscs, small fishes and frogs (Moskoff 1995), frequently on mats of floating vegetation.
Model:
Sites with known solitary sandpiper occurrences were scored higher than areas
having appropriate cover types but without observation data. We used
abundance/occurrence information from the MDIFW shorebird coverage, the ISS
database, and Pierson et al. (1996) for additional inland sites used by solitary
sandpiper in Maine. This occurrence information was used to select the general
localities (polygons or buffers around observation points) used by the species.
Environmental data sets (bathymetry and wetland cover type) were used to
identify areas within those localities likely to have been used. The ISS
data specified the observation locations only to the nearest geographic minute,
and Pierson's observations also were somewhat general. Therefore, all suitable
cover types (see table, below) within the MDIFW polygons or within a 1 km
radius of the point data were regarded as having the respective levels of
use for that observation.
| NWI Designations
(wetlands only) |
Cover Types | Cover Suitability (0 - 1 scale) |
| Upland deciduous forest | 0.5* | |
| Upland coniferous forest | 0.5* | |
| Upland mixed forest | 0.5* | |
| Grassland | ||
| Upland scrub/shrub | ||
| Cultivated | ||
| Developed | ||
| Bare ground | ||
| PEM, L2EM | Lake/pond, emergent vegetation | 0.5* |
| PFOcon | Palustrine forest, conifer | 0.5* |
| PFOdec | Palustrine forest, deciduous | 0.5* |
| PSSdec | Palustrine scrub shrub, deciduous | |
| PSScon | Palustrine scrub shrub, conifer | |
| PAB, L2AB | Lake/pond, aquatic vegetation | 1.0 |
| 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 | |
| E2RS, R1RS | Estuarine, tidal river rocky shore | |
| E2SS | Estuarine intertidal shrub | |
| E2US, R1US | Estuarine, riverine intertidal unconsolidated shore | 0.5 |
| M1AB | Marine subtidal vegetated | |
| M1UB | Marine subtidal unconsolidated bottom | |
| M2AB | Marine intertidal algae | |
| M2RS | Marine intertidal rocky shore | |
| M2US | Marine intertidal unconsolidated shore | |
| NOTES | * where forest borders pond or marsh |
Habitat Suitability Scoring: Sites with solitary sandpiper occurrences and having any of the suitable landcover types (see table) first were scored according to level of use. If a site had 5 or more birds observed at any time, the landcover scores were applicable as presented; otherwise, if any birds were present, the landcover values were half the nominal score.
Suitable cover types outside of the observation/occurrence polygons were scored 0.2 for inland features and 0.1 for unconsolidated coastal substrates.
Sources:
Hayman, P., J. Marchant and T. Prater. 1986. Shorebirds, an Identification Guide. Houghton Mifflin Co., Boston, MA. 412 p.
Johnsgard, P.A. 1981. The Plovers, Sandpipers and Snipes of the World. University of Nebraska Press. Lincoln. 493 pp.
Moskoff, W. 1995. Solitary sandpiper (Tringa solitaria). In A. Poole and F. Gill (eds.) The Birds of North America, No. 156. The Birds of North America, Inc. Philadelphia, PA.
Pierson, E.C., J E. Pierson and P.D. Vickery. 1996. A Birders Guide to Maine. Down East Books, Camden, ME.
Veit, R.R. and W.R. Petersen. 1993. Birds of Massachusetts. Massachusetts Audubon Society. 514 p.