The Seaside Sparrow is a habitat specialist occupying a narrow band of coastal salt marsh habitat.
This species is restricted to coastal salt and brackish marshes (Post and Greenlaw 1994). Habitat alteration is historically reason for decline and currently a potential threat. Coastal development practices, such as ditching and filling of salt marshes, negatively impact this species since ditched wetlands provide lower quality habitat and are used infrequently (Post and Greenlaw 1994). The New York Breeding Bird Atlas documented a decline in the number of probable and confirmed atlas blocks from 46 in the first atlas (1980-1985) to 30 in the second (2000-2005) (McGowan and Corwin 2008).
The Seaside Sparrow is locally common along the barrier islands off the south shore of Long Island. It had been extirpated from Staten Island and the lower Hudson River in Westchester County by the 1940's, but was rediscovered in both of these locations in the 1990's. Recently, numbers have shown a decline in New York. (Levine 1998)
There were 46 probable or confirmed blocks during the first New York Breeding Bird Atlas (1980-1985) and 30 blocks during the second (2000-2005) (McGowan and Corwin 2008). The Breeding Bird Survey also detected a decline in eastern Seaside Sparrow populations from 1985 to 2005, however, it was only over a small number of routes (Sauer et al. 2005).
A historical account by Giraud in 1844 described Seaside Sparrows as common to abundant in south shore bays and on north shore necks of land on Long Island. Although numbers have likely declined, there has been little change to the known historical range except for gaps in distribution largely due to human devlopment along the coast (Post and Greenlaw 1994). The range has slighlty expanded in the northeast from Massachusetts into New Hampshire (Post and Greenlaw 1994).
The major threat is ditching and filling of wetlands in conjunction with costal development. Drying of wetlands from mosquito ditching and wetland impoundment has also been a threat. Natural succession over time of low marsh habitat into high marsh is a potential threat because high marsh generally provides lower quality habitat. Since this species occupies a narrow coastal range, populations may be displaced or impacted by major storms, fires, and oil spills. Flooding can destroy nests and young, diminishing productivity for a season as well as displacing individuals. Climatic change is a potential threat for this species especially in the southern part of the range where salt mash habitat may be lost to invasive mangroves as the climate warms. (Post and Greenlaw 1994)
The major management concern is protection of estuarine wetlands from development, ditching, and from invasive plants.
The Seaside Sparrow has been well-studied in New York and the northeast (Merriam 1979, Post and Greenlaw 1994). This species is monogamous for the breeding season, however, since it often feeds outside the nesting territory research into potential extra-pair copulations, or breeding events with other patners is needed.
The seaside sparrow is a habitat specialist that occupies coastal tidal marshes throughout most of its limited range. Birds in the northeastern portion of the range, including New York, use both high and low marsh. High marsh may provide marginal habitat; areas are dominated by salt meadow grass (Spartina patens), black grass (Juncus gerardi), glasswort (Salicornia spp.) and marsh elder (Iva frutescens). Low marsh is dominated by smooth cordgrass (Spartina alterniflora) and birds select nesting locations near grass tufts (Greenlaw 1983). Birds avoid areas of uniform salt meadow grass in high marsh and nest along edges with marsh elder. Drier, more upland sites consisting of salt panne are used infrequently and brackish marshes historically were used in New York (Levine 1998). Higher quality habitat generally consists of elevated sites removed from flooding with muddy open areas for feeding (Levine 1998).
In New York, the Seaside Sparrow is almost entirely restricted to salt marsh areas on the south shore of Long Island where it occurs from Southampton west to Jamaica Bay. Within this region the center of abundance is in the bays of Nassau and western Suffolk Counties. Outlying colonies occur on Gardiner's and Fisher's islands and two small marshes on the north shore of Nassau County. Seaside Sparrows occur at a single site in Westchester County on the Long Island Sound and formerly occurred at a single brackish marsh at the southern end of the Hudson River (Greenlaw 1992, Andrle and Carroll 1988). There are a small number of birds reported annually in winter counts on Long Island (Levine 1998). It is unknown where birds breeding in New York spend the winter (Levine 1998).
The Seaside Sparrow breeds from Massachusetts south along the Atlantic Coast to the St. Johns River in northcentral Florida, and from Tampa Bay on the Gulf Coast of Florida to Corpus Christi, Texas (AOU 1983). Breeding birds have been noted in recent years in New Hampshire, but it is unlikely that populations can become established much further north since the physiography of tidal marshes changes and they become unsuitable in southern Maine (Greenlaw 1992). Throughout its range, Seaside Sparrow populations are separated into demes by areas of unsuitable habitat. A number of subspecies have been described and at least two of these are now extinct. Human habitat alterations have caused many additional gaps in the breeding distribution of this species. The winter range is similar to the breeding range although most northeastern (New Hampshire to New Jersey) breeding birds are migratory and probably winter primarily in the southeastern United States. In addition, wintering birds occur in coastal Florida and the southeast coast of Texas, to the south of current breeding populations (Post and Greenlaw 1994).
The Seaside Sparrow is a grayish-olive sparrow with dullish breast streaking, yellow spot behind the eye, and long (for a sparrow) spike-like bill.
Both sexes look alike and subspecies in the gulf coast and Florida differ in color from populations in the northeast. Characteristics of northeastern birds are a yellow wrist, overall grayish-olive color, yellow supraloral spot (between eye and bill), no wing bars, dark moustache stripe (extends down from bill), buffy malar stripe (extends down from bill near throat), white throat, and stripped breast, sides and flanks (Post and Greenlaw 1994). The primary song resembles a Red-winged Blackbird but is more buzzy and includes a series of trills and a terminal buzz (National Geographic 1999, Post and Greenlaw 1994). Nests are described as a "simple open cup of grass stems and blades lined with finer grasses" (Post and Greenlaw 1994).
Look for the distinct yellow supraloral spot between the eye and the bill and also the dark moustache stripe that extends down from the bill and the buffy malar stripe under it. Also useful are the overall greyish-olive color, breast streaking, as well as the bill shape.
Seaside Sparrows are monogamous for the breeding season although information on extra-pair copulation is unknown. Both sexes feed the young (Post and Greenlaw 1994). They have been described as a semi-colonial species with uneven distribution of breeding pairs occuring over homogeneous habitat; although this scattered distribution may also indicate heterogenous habitat (Post and Greenlaw 1994). Males defend nesting territories but both males and females may travel long distances away from the defended territory to feed due to the separation of habitats in tidal zones (Post and Greenlaw 1994).
Feeding tends to occur in open areas with a mud substrate, also in ground litter, and at the bases of rooted grasses (Greenlaw 1983). Food is obtained by either climbing through vegetation or walking along the ground while gleaning and probing the mud with the bill (Post et al. 1983). They may also feed along the edges of pools and ditches. Seaside Sparrows eat mostly insects and spiders during the breeding season including insect larva and spider egg cases. Dipterans or flies were documented as an imporant food source in New York as well as some moth species (Merriam 1979). In the fall birds consume a much higher component of seeds in their diet (Post and Greenlaw 1994).
Look for this species in coastal salt marshes in the spring and summer. The first spring arrivals in New York are April 21-26 and fall migration occurs from the end of August through October. There are regular but small numbers of winter birds reported. (Levine 1998, Post and Greenlaw 1994)
The time of year you would expect to find Seaside Sparrow active and reproducing in New York.
Ammodramus maritimus (Wilson, 1811)
American Ornithologists' Union (AOU). 1983. Check-list of North American Birds, 6th edition. Allen Press, Inc., Lawrence, Kansas. 877 pp.
Andrle, Robert F. and Janet R. Carroll, editors. 1988. The atlas of breeding birds in New York State. Cornell University Press. 551 pp.
Bull, John. 1974. Birds of New York State. Doubleday, Garden City, New York. 655 pp.
Bull, John. 1976. supplement to birds of New York State. Special publ. of Federation of New York State Bird Clubs. 52 pp.
Ehrlich, P. R., D. S. Dobkin, and D. Wheye. 1992. Birds in Jeopardy: the Imperiled and Extinct Birds of the United States and Canada, Including Hawaii and Puerto Rico. Stanford University Press, Stanford, California. 259 pp.
Giraud, J.P., Jr. 1844. Birds of Long Island. Wiley and Putnam, New York.
Greenlaw, J. S. 1992. Seaside sparrow, AMMODRAMUS MARITIMUS. Pages 211-232 in K. J. Schneider and D. M. Pence, editors. Migratory nongame birds of management concern in the Northeast. U.S. Fish and Wildlife Service, Newton Corner, Massachusetts. 400 pp.
Greenlaw, J.S. 1983. Microgeographic distribution of breeding seaside sparrows on New York salt marshes. pp 99-114. In: The seaside sparrow, its biology and management.
Harrison, C. 1978. A Field Guide to the Nests, Eggs and Nestlings of North American Birds. Collins, Cleveland, Ohio.
Levine, E. 1998. Bull's birds of New York State. Comstock Publishing Associates, Ithaca, NY.
Marshall, R. M., and S. E. Reinert. 1990. Breeding ecology of seaside sparrows in a Massachusetts salt marsh. Wilson Bull. 102:501-513.
McGowan, K.J. and K. Corwin, eds. 2008. The Second Atlas of Breeding Birds in New York State: 2000-2005. Cornell University Press, Ithaca, NY. 688 pp.
Merriam, T.L. 1979. Feeding ecology and food overlap of two sympatric marsh-inhabiting sparrows. Master's thesis, Long Island University, Brookville, NY.
National Geographic Society (NGS). 1999. Field guide to the birds of North America. Third edition. National Geographic Society, Washington, DC. 480 pp.
New York Natural Heritage Program. 2019. New York Natural Heritage Program Databases. Albany, NY.
New York State Breeding Bird Atlas. 1985. Final breeding bird distribution maps, 1980-1985. New York State Department of Environmental Conservation, Wildlife Resources Center. Delmar, NY.
Post, W., J.S. Greenlaw, T.L. Merriam and L.A. Wood. 1983. Comparative ecology of northern and southern populations of the seaside sparrow. pp 123-136. In: The seaside sparrow, its biology and management.
Post, W., and J. S. Greenlaw. 1994. Seaside sparrow (AMMODRAMUS MARITIMUS). In the Birds of North America, No. 127 (A. Poole and F. Gill, eds.). Philadelphia: The Academy of Natural Sciences. 28 pp.
Sauer, J.R., J.E. Hines, and J. Fallon. 2007. The North American breeding bird survey, results and analysis 1966-2006. Version 10.13.2007. US Geological Survey, Patuxent Wildlife Research Center, Laurel, MD.
Stoll, M. J., and F. C. Golet. 1983. Status of the seaside sparrow in Rhode Island. Aud. Soc. Rhode Island Rep. 17:57-61.
Terres, J. K. 1980. The Audubon Society encyclopedia of North American birds. Alfred A. Knopf, New York.
Zink, R. M., and J. C. Avise. 1990. Patterns of mitochondrial DNA and allozyme evolution in the avian genus AMMODRAMUS. Syst. Zool. 39:148-161.
Information for this guide was last updated on: December 10, 2008
Please cite this page as:
New York Natural Heritage Program. 2019. Online Conservation Guide for Ammodramus maritimus. Available from: https://guides.nynhp.org/seaside-sparrow/. Accessed May 20, 2019.