Over 95% of New York's Roseate Terns breed at a single location, Great Gull Island, on Long Island. It is also a globally significant breeding colony because of its size.
There is only one sizeable colony in New York. Roseate Terns are threatend by loss of breeding habitat from coastal development, rising sea-levels, human disturbance, predation, and increased flooding from storms due to climate change. Buckley and Buckley (1981) suggested that North Atlantic populations may be relict, citing that the species core distribution is tropical. Roseate Terns are listed as endangered in the state by the NY Department of Environmental Conservation and the northeatern U.S. population is federally listed as endangered.
The distribution of Roseate Terns in New York has decreased over the past few decades. They were found in 19 blocks during the first Breeding Bird Atlas from 1980 to 1985 and in 12 blocks in the second atlas from 2000 to 2005, a decline of 37% (McGowan and Corwin 2008). The majority of the population in New York nests on Great Gull Island with only a few nesting attempts documented elsewhere. Numbers on Great Gull Island appear to have increased from the 1980s (range 700-1200 pairs) and have remained relatively stable with high year-to-year variation. The number of breeding pairs ranged from 1150-1950 in the 1990s, 1195-1762 in the 2000s, and 1303-2962 pairs in the 2010s.
Historical trends are not entirely known but numbers likely declined significantly along with other tern species in the late 1800's and early 1900's due to hunting and the millinery trade. Eaton (1910) reported only a few known nesting locations (McGowan and Corwin 2008). The passage of the Migratory Bird Treaty Act in 1918 enabled recovery to begin and numbers increased during the mid-1900's (Bull 1974). From 1974 to 1977 the species suffered significant declines simultaneously in New York and Massachusetts (Buckley and Buckley 1981). By 1978 Roseate Tern numbers had declined by 66% on Long Island (Buckley and Buckley 1981). As a result of this decline, the remaining birds were concentrated in a few large colonies (Buckley and Buckley 1981, Nisbet 1980, Hays 1998).
Roseate Tern numbers were reduced by egging and the millinery trade before the passage of the Migratory Bird Treat Act in 1918. Today, Roseate Terns are threatened by habitat loss and degradation, human disturbance, hunting and egg collecting, increased predation, rising sea-levels, and increased flooding from storms due to global climate change. The concentration of large numbers of Roseate Terns at a few breeding locations is in itself a threat. Environmental factors like storms and flooding and biological factors such as a low nest success due to predation can result in years of low productivity. If these occur in just a few colonies, it could affect the viability of the species in the entire northeastern U.S.
The establishment of additional large, protected, and successful colonies would benefit this species. Colony restoration by first removing gulls is controversial but has been successful at restoring colonies at two locations in Maine and one in Massachusetts (Gochfeld et al. 1998). Restoration of offshore sites that have greater protection from predators is essential to ensure long-term success (USFWS 1998). Predator control may be necessary at some sites where predation is high. Maintaining and protecting habitat at a number of suitable nesting locations is ideal even if some sites are temporarily unoccupied to allow colonies to relocate when disturbance occurs (McGowan and Corwin 2008).
Annual productivity estimates on Great Gull Island seem to indicate good breeding success in that colony (Cormons, pers. comm.). Continued productivity monitoring, in addition to the population index counts that are conducted annually, are needed to monitor the population. If breeding success is low, possible causes should be identified and management actions taken, if possible. In order to ensure adult survival during the nonbreeding season, research on threats to the species on its wintering grounds should continue. Research is currently underway in Brazil (Hays et al. 1997, 1999). In addition, Brazilians from Aquasis in cooperation with the Great Gull Island Project are working to protect the species on the coast of Ceara in Northern Brazil (Hays 2009/2010). Until recently, little was known of the behavior, feeding, and timing and locations of movements on the wintering grounds. However, initial studies currently are underway (Hays in prep.). Research is also needed to determine migratory routes and stopover locations and the relation of these movements to fish availability (Gochfeld et al. 1998). Puerto Rico was recently identified as a stopover location when Gabriel Lugo photographed banded Roseate Terns during migration (Hays et al. 2010).
Roseate Terns nest almost exclusively on islands where predation pressure may be lower than on mainland sites. The largest colony occupies a rocky island with smaller colonies occuring on barrier beach islands and saltmarsh islands. Colonies are often located close to shallow-water locations for fishing (Gochfeld et al. 1998). Nest sites occur most often in dense grass or under boulders and occasionally in more open sites (Jones 1906, Bull 1964, Hays and Pessino 1970, Gochfeld et al. 1998). They can nest on a variety of substrates including sand, shell, rock, and vegetation.
The Roseate Tern's breeding distribution is highly localized throughout its range. Breeding in New York is confined to Great Gull Island and a few scattered locations on Long Island annually. It occurs inland only accidentally. Great Gull Island is recognized as a globally significant colony because of the large number of birds that breed there. Cartwright Island was the next largest colony in New York but it exisits on a sandbar that has been underwater in recent years.
The distribution of the Roseate Tern is widespread and includes the Atlantic, Indian, and southwestern Pacific oceans. BREEDING: Their breeding range in the Americas extends locally along the Atlantic coast of North America, mainly from Quebec to New York; also Dry Tortugas, Florida Keys, Bahamas (Sprunt 1984), and other islands of West Indies, islands off Venezuela, and islands off the northern coast of Honduras and Belize (Spendelow and Patton 1988). In northeastern North America, over 90% of the breeding population is concentrated in three colonies: Great Gull Island in NY, and Bird and Ram Islands in MA. NON-BREEDING: Roseate Terns overwinter in the Americas, primarily along the Brazilian coast (Hays et al. 1997, 1999).
Roseate Terns are a slender, medium-sized tern with bright orange-red legs, a light gray back, and a deeply forked tail. The bill is entirely black when they arrive in May and shows increasing amounts of red at the base as the breeding season progresses (Donaldson 1968, Cormons 1976).
Roseate Terns are slender, medium-sized birds, measuring 33-41 cm (13.0-16.1 in.) in total length and weighing 95-130 g (3.4-4.6 oz.). Breeding adults have a black cap and nape. They have pale gray upperparts and white underparts with a slight pinkish appearance that is not very evident during the summer but is sometimes visible in good light. The bill is entirely black when they arrive in the spring and gradually becomes red at the base during the breeding season. The tail is white, deeply forked, and extends well beyond the wings when a bird is standing with its wings folded. The legs and feet are bright red-orange. Hybrid Common X Roseate Terns have been found with intermediate characteristics (Hays 1975). Non-breeding adults have a black mask that extends from the eye to the nape and do not have a black cap. Non-breeding adults also have a white forehead and pale streaks on the rear part of the head just above the nape (hindcrown), white underparts, and a shorter tail (Gochfeld et al. 1998). Nonbreeding adults often also show the rosy blush, which is sometimes more noticeable than on breeding birds (Hays et al. 2006). Juveniles have a brownish cap that extends over the forehead, mid-back, and folded wings that looks coarsely scaled. They have a lower back that is barred with black. First-summer birds have a white forehead. Some second-year birds have a small amount of white above the base of the bill with black speckling (Donaldson 1969). Birds attain full adult plumage by their second winter (National Geographic Society 1983). Roseate Terns are very vocal in breeding colonies and feeding flocks. At these times, they make loud "pink" and "ki-rik" notes that are sharp and high-pitched. When mobbing an intruder near a nest, they will make a harsh, raspy, single-pitch "aaach" or "kraak" call that sounds like tearing cloth. When attacking terrestrial predators, they will often make a staccato "kekekekekekekeke" sound, sometimes while swooping towards the intruder, ending in a harsh "aaach" when they are nearest. In temperate zones, clutch sizes usually range from one to four eggs. Eggs are various shades of brown, with blackish brown streaks and speckles. It is often difficult to distinguish the eggs of Common Terns and Roseate Terns. However, Roseate Tern eggs are usually more uniformly marked, have more small spots and fewer blotches, and have a darker background color that is less likely to be greenish (Gochfeld et al. 1998).
The combination of characters that distinguish this species from other adult terns during the breeding season are: orange-red legs and feet, pale gray back, deeply forked tail, and a black bill with red at the base. The rosy tint on the breast is generally not a useful character during the summer because it is subtle.
Adults in breeding plumage are easiest to identify but juveniles and birds in their winter plumage can also be distinguished from other tern species.
Roseate Tern pairs are monogamous for the breeding season. They breed in large colonies, frequently with Common Terns (Sterna hirundo) (Bent 1921, Cramp 1985). They have various breeding displays in the air and on the ground (described in detail by Cullen 1960, Cullen 1962, Cramp 1985). Both parents take turns incubating eggs and brooding and feeding chicks. Chicks are semi-precocial at hatching, meaning they aren't fully capable of thermoregulating and feeding themselves. They are already covered in down when they hatch, and they open their eyes and walk as soon as they are dry (Cormons pers. comm.). Adults exhibit a strong fast, flight with shallow wing beats. To capture fish they use an aerial plunge dive and submerge briefly (Gochfeld et al. 1998), remaining underwater for up to 2.5 seconds (Nisbet 1981, Duffy 1986). Roseate Terns have an impressive array of aerial defenses. When a predator or suspected threat enters their territory, they may circle above them, swoop at them, and/or dive-bomb them while giving an attack call (Gochfeld et al. 1998).
Roseate Terns primarily eat small marine fish. They show a strong preference for sand eels (Ammodytes americanus) and their diet is not very diverse. Occasionally, they will also eat insects, squid, or small crustaceans (Gochfeld et al. 1998).
Roseate Terns arrive at their breeding grounds in northeastern North America from late April through May with subadults and juveniles sometimes arriving into mid-July (Gochfeld et al. 1998, Nisbet 1989). Staging for fall migration occurs in August through September (Nisbet 1984, Shealer and Kress 1994). Roseate Terns are most often present in New York from early-May through September.
The time of year you would expect to find Roseate Tern active and reproducing in New York.
Sterna dougallii Montagu, 1813
Nisbet, I. C. T., M. Gochfeld, and J. Burger. 2014. Roseate Tern (Sterna dougallii), version 2.0. In The Birds of North America (A. F. Poole, Editor). Cornell Lab of Ornithology, Ithaca, NY, USA. Available at https://doi.org/10.2173/bna.370 (Accessed June 26, 2019).
Andrews, R. et al. 1988. Draft recoveryplan for roseate tern STERNA DOUGALLII northeastern population. Region 5, U.S. Fish and Wildlife Service.
Andrle, Robert F. and Janet R. Carroll, editors. 1988. The atlas of breeding birds in New York State. Cornell University Press. 551 pp.
Bent, A.C. 1921. Life histories of North American gulls and terns. U.S. Natl. Mus. Bull. 113. Washington, D.C.
Buckley P.A. and F.G. Buckley. 1981. The endangered status of North American Roseate Terns. Colonial Waterbirds 4:166-173.
Buckley, P. A., and F. G. Buckley. 1984. Seabirds of the north and middle Atlantic coast of the United States: their status and conservation. Pages 101-133 in Croxall et al., eds. Status and conservation of the world's seabirds. ICBP Tech. Pub. No. 2.
Bull, John. 1974. Birds of New York State. Doubleday, Garden City, New York. 655 pp.
Burger, J., and M. Gochfeld. 1991. Reproductive vulnerability: parental attendance around hatching in roseate (STERNA DOUGALLII) and common (S. HIRUNDO) terns. Condor 93:125-129.
Clapp, R. B., and P. A. Buckley. 1984. Status and conservation of seabirds in the southeastern United States. Pages 135-155 in Croxall et al., eds. Status and conservation of the world's seabirds. ICBP Tech. Pub. No. 2.
Cooper,D., H.Hays, and C. Pessino. 1970. Breeding of the Common and Roseate Tern on Great Gull Island. Proc. Linnaean Soc., New York 71: 83-104.
Cormons, G. D. 1976. Roseate Tern bill color change in relation to nesting status and food supply. Wilson Bulletin 88 (3): 377-389.
Cramp, S. 1985. Handbook of the birds of Europe, the Middle East and North Africa, Vol. IV. Terns to woodpeckers. Oxford Univ. Press, New York.
Donaldson, G., and H. Hays. 1969. Roseate Tern in unusual plumage. Bird-Banding 40 (3): 255.
Donaldson,G. 1968. Bill color change in adult Roseate Terns. Auk 85 (4): 662-668.
Duffy, D. C. 1986. Foraging at patches: interactions between Common and Roseate Terns. Ornis. Scand. 17:47-52.
Eaton, E.H. 1910. Birds of New York State, part 1. State University of New York, Albany.
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.
Garnett, M. C. 1984. Conservation of seabirds in the South Pacific region: a review. Pages 547-558 in Croxall et al., eds. Status and conservation of the world's seabirds. ICBP Tech. Pub. No. 2.
Gochfeld, M. 1983. The roseate tern: world distribution and status of a threatened species. Biological Conservation 25(2):103-125.
Gochfeld, M., J. Burger, and I.C.T. Nisbet. 1998. Roseate Tern (STERNA DOUGALLII). In A. Poole and F. Gill, editors, The Birds of North America, No. 370. The Birds of North America, Inc., Philadelphia, PA. 32 pp.
Harrison, C. 1978. A Field Guide to the Nests, Eggs and Nestlings of North American Birds. Collins, Cleveland, Ohio.
Hays, H. 1975 Probable Common X Roseate Tern hybrids. Auk 92(2):219-234.
Hays, H. 1998. Bull's birds of New York State. Comstock Publishing Associates, Ithaca, NY.
Hays, H. 2009/2010. Rosy Return. Natural History. vol.118, iss.10; p.48.
Hays, H., P. Lima, L. Monteiro, J. DiCostanzo, G. Cormons, I. C. T. Nisbet, J. E. Saliva, J. A. Spendelow, J. Burger, J. Pierce, and M. Gochfeld. 1999. A nonbreeding concentration of Roseate and Common Terns in Bahia, Brazil. Journal Field Ornithology 70(4):455-464.
Hays, H.,J.Hudon, G.Cormons, J.DiCostanzo, and P.Lima.2006. The Pink Feather Blush of the Roseate Tern. Waterbirds 29 (3): 296-301.
Hays,H., G. Lugo, G.Cormons. 2010. Puerto Rico-Stopover for Migrating Roseate Terns. North American Bird Bander. 35 (3): 127-131.
Hays,H., J. DiCostanzo, G.Cormons, P. de Tarso Zuquim Antas, J.L.Xavier do Nascimento, I. de Lima Serrano do Nascimento, and R. E. Bremer. 1997. Recoveries of Common and Roseate Terns in South America. Journal of Field Ornithology 68 (1): 79-90.
Jones, L. 1906. A contribution to the life history of the Common (Sterna hirundo) and Roseate (S dougalli) Terns. Wilson Bull. 18:36-47.
Levine, E. 1998. Bull's birds of New York State. Comstock Publishing Associates, Ithaca, NY.
Matthews, J.R. and C.J. Moseley (eds.). 1990. The Official World Wildlife Fund Guide to Endangered Species of North America. Volume 1. Plants, Mammals. xxiii + pp 1-560 + 33 pp. appendix + 6 pp. glossary + 16 pp. index. Volume 2. Birds, Reptiles, Amphibians, Fishes, Mussels, Crustaceans, Snails, Insects, and Arachnids. xiii + pp. 561-1180. Beacham Publications, Inc., Washington, D.C.
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.
National Geographic Society (NGS). 1983. Field guide to the birds of North America. National Geographic Society, Washington, DC.
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.
New York State Department of Environmental Conservation. Checklist of the amphibians, reptiles, birds, and mammals of New York State, including their protective status. Nongame Unit, Wildlife Resources Center, Delmar, NY.
Nisbet, I. C. T. 1980. Status and trends of the Roseate Tern (Sterna dougallii) in North America and the Caribbean. Report 50181-084-9. U.S. Fish and Wildlife Service, Newton Corner, MA.
Nisbet, I. C. T. 1981. Biological characteristics of the Roseate Tern (Sterna dougallii). Report 50181-084-9. U.S. Fish Wildlife Service, Newton Corner, MA.
Nisbet, I. C. T. 1984. Migration and winter quarters of North American Roseate Terns as shown by banding recoveries. J. Field. Ornithol. 55:1-17.
Nisbet, I. C. T. 1989. Status and biology of the northeastern population of the Roseate Tern (Sterna dougallii): a literature survey and update: 1981-1989. Contract Report 50181-88-8105. U.S. Fish Wildlife Service, Newton Corner, MA.
Safina, C. 1990a. Foraging habitat partitioning in roseate and common terns. Auk 107:351-358.
Safina, C. 1990b. Bluefish mediation of foraging competition between roseate and common terns. Ecology 71:1804-1809.
Safina, C., et al. 1988. Evidence for prey limitation of common and roseate tern reproduction. Condor 90:852-859.
Shealer, D. A. and S. W. Kress. 1994. Post-breeding movements and prey selection of Roseate Terns at Stratton Island, Maine. J. Field Ornithol. 65:349-362.
Sommers, Laura and Michelle L. Alfieri. 1998. 1997 Long Island Colonial waterbird and piping plover survey. New York State Department of Environmental Conservation, Nongame and Habitat Unit. Delmar, NY and Region 1, Stony Brook, NY.
Spendelow, J. A. and S. R. Patton. 1988. National Atlas of Coastal Waterbird Colonies in the Contiguous United States: 1976-1982. U.S. Fish and Wildlife Service, Biological Report 88(5). x + 326 pp.
Spendelow, J. A., and J. D. Nichols. 1989. Annual survival rates of breeding adult roseate terns. Auk 106:367-374.
Sprunt, A., IV. 1984. The status and conservation of seabirds of the Bahama Islands. Pages 157-168 in Croxall et al., eds. Status and conservation of the world's seabirds. ICBP Tech. Pub. No. 2.
Trull, P. 1988. The roseate tern in Massachusetts. Massachusetts Wildlife 38(3):22-31.
U.S. Fish and Wildlife Service (USFWS). 1990. Endangered and threatened species recovery program: report to Congress. 406 pp.
U.S. Fish and Wildlife Service (USFWS). 2 November 1987. Determination of endangered and threatened status for two populations of roseate tern. Federal Register 52:42064-42068.
U.S. Fish and Wildlife Service. 1998. Roseate Tern Recovery Plan: Northeastern population. First Update. U.S. Fish and Wildlife Service, Hadley, MA.
This guide was authored by: Kelly A. Perkins
Information for this guide was last updated on: June 28, 2019
Please cite this page as:
New York Natural Heritage Program. 2019. Online Conservation Guide for Sterna dougallii. Available from: https://guides.nynhp.org/roseate-tern/. Accessed November 22, 2019.