Chestnut-sided Warbler Habitat Model
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Gulf of Maine Watershed Habitat Analysis
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Draft Date:
March, 2001
Species:
Chestnut-sided warbler, Dendroica pensylvanica
Use of Study Area Resources:
Reproduction throughout study area. The breeding range of Chestnut-sided
warblers is eastern North America, from southern Canada southward through
the Appalachian Mountains to upper elevations in northern Georgia (Richardson
and Brauning 1995). Chestnut-sided warblers winter in Central America
(DeGraaf and Rudis 1986).
Habitat Requirements:
Cover. Chestnut-sided warblers breed in open, early successional deciduous
and mixed forest, or shrublands where there is a dense understory of shrubs
or thick herbaceous vegetation, using either wetlands and uplands (Richardson
and Brauning 1995). Typical habitats include regenerating clear-cuts, scrubby
second-growth forests, woodland edges, powerline corridors, abandoned orchards,
neglected pastures or cropland, brushy brooksides, and thickets of mountain
laurel or American chestnut (Bent 1963, Chapman 1968, DeGraaf and Rappole
1995, Richardson and Brauning 1995, Mahoney et al.1997). Abundance
is related inversely to total basal area of trees, number of standing dead
trees, and directly to percent cover by forest within 2 km of site (Robbins
et al. 1989). Chestnut-sided warblers do not occur in built-up areas or active
agriculture (Richardson and Brauning 1995). They may be common on islands
(Palmer 1949).
Feeding. Chestnut-sided warblers are predominantly insectivorous, gleaning the twigs and the undersides of leaves for flies and caterpillars; they also take spiders and some fruit and seeds (Richardson and Brauning 1995).
Mortality data associated with studies at communications towers and tall smokestacks show that chestnut-sided warblers seem more likely than other species to have fatal collisions (Weir 1989, Graber et al. 1983, and Johnston and Haines 1957 in Richardson and Brauning 1995).
Model:
Habitat was mapped by selecting upland shrub, wetland deciduous shrub, powerline
corridors, and oldfield cover types. Upland and wetland deciduous and
upland mixed forest cover within 30 m of these shrub/oldfield types also
were included. We then deleted portions of the habitat within 90 m
of development or agriculture.
NWI Designations
(wetlands only) |
Cover Types | Cover Suitability (0 - 1 scale) |
Upland deciduous forest | 1.0* | |
Upland coniferous forest | ||
Upland mixed forest | 1.0* | |
Grassland | ||
Upland scrub/shrub | 1.0 | |
Cultivated | ||
Developed | ||
Bare ground | ||
PEM, L2EM | Lake/pond, emergent vegetation | |
PFOcon | Palustrine forest, conifer | |
PFOdec | Palustrine forest, deciduous | 1.0* |
PSSdec | Palustrine scrub shrub, deciduous | 1.0 |
PSScon | Palustrine scrub shrub, conifer | |
PAB, L2AB | Lake/pond, aquatic vegetation | |
L1UB, PUB | Lake/pond, unconsolidated bottom | |
L2US | Lake, unconsolidated shore | |
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 | Estuarine intertidal unconsolidated shore | |
M1AB | Marine subtidal vegetated | |
M1UB | Marine subtidal unconsolidated bottom | |
M2AB | Marine intertidal algae | |
M2RS | Marine intertidal rocky shore | |
M2US | Marine intertidal unconsolidated shore | |
Old fields and powerline corridors | 1.0 |
|
NOTES | * Score if within 30 m of shrub/oldfield cover |
Model testing: The chestnut-sided warbler occurrences from the Breeding Bird Survey (1997, 1998 data) were used to test the habitat map. We compared the presence of habitat near a random set of 797 upland points to that at which sparrows actually were observed. Of the 369 sites with birds, 342 had mapped habitat, while 644 sites out of the 797 randomly distributed sites had habitat. The Chi-square was highly significant, indicating that the overall model does indicate localities useful to chestnut-sided warblers.
Sources:
Bent, A.C. 1963. Life Histories of North American Wood Warblers.
Dover Publications, New York, NY. Pp.367-379.
Chapman, F.M. 1968. The Warblers of North America. Dover Publications, Inc. NY.
DeGraaf, R.M. and J.H. Rappole. 1995. Neotropical Migratory Birds: Natural History, Distribution and Population Change. Comstock Publishing Associates, Ithaca, NY. 676 pp.
Mahony, N., E. Nol and T. Hutchinson. 1997. Food-chain chemistry, reproductive success, and foraging behaviour of songbirds in acidified maple forests of central Ontario. Can J. Zool. 75(4):509-517.
Palmer, R. 1949. Maine Birds. Bull. Of Comparative Zoology. Harvard College, Cambridge, MA. Pp. 471-473.
Robbins, C.R., D.K. Dawson and B.A. Dowell. 1989. Habitat area requirements of breeding forest birds of the middle Atlantic states. Wildl. Monogr. 103:1-34.
Richardson, M. and D.W. Brauning. 1995. Chestnut-sided Warbler, Dendroica pensylvanica. In A. Poole and F. Gill, (eds.) The Birds of North America, No. 190. The Academy of Natural Sciences, Philadelphia, and The American Ornithologists' Union, Washington, D.C.