Species: Chlidonias niger

Black Tern
Species

    EGGS: ovate with a tendency toward ovate pyriform (Bent 1921). Ground color varies from dark olive to light buff with markings of dark brown and gray. Markings vary from small dots and scrawls to very large blotches and are often particularly heavy around the larger end of the egg (Goodwin 1960). The average dimensions for 122 eggs in the U.S. National Museum were 34 x 24 mm (Bent 1921).

    Kingdom
    Animalia
    Phylum
    Craniata
    Class

    Aves

    Order

    Charadriiformes

    Family

    Laridae

    Genus

    Chlidonias

    Classification
    Other Global Common Names
    Charrán Negro, Gaviotín Negro - Trinta-Réis-Negro - guifette noire
    Informal Taxonomy
    Animals, Vertebrates - Birds - Other Birds
    Formal Taxonomy
    Animalia - Craniata - Aves - Charadriiformes - Laridae - Chlidonias - of Eurasia.

    EGGS: ovate with a tendency toward ovate pyriform (Bent 1921). Ground color varies from dark olive to light buff with markings of dark brown and gray. Markings vary from small dots and scrawls to very large blotches and are often particularly heavy around the larger end of the egg (Goodwin 1960). The average dimensions for 122 eggs in the U.S. National Museum were 34 x 24 mm (Bent 1921).

    Short General Description
    Black tern, Laridae.
    Migration
    false - false - true - Most arrive in breeding areas in northeastern North America during the first half of May.
    Non-migrant
    false
    Locally Migrant
    false
    Food Comments
    On the breeding grounds the black tern is primarily insectivorous, although small crustaceans, spiders and small fishes are also regular food items (McAtee and Beal 1912, Bent 1921). The diet may vary depending on habitat and food availability. Fishes may be an especially important food item at some sites in the northeast. <br><br>In wetlands, food is captured in the air, at or just below the water surface, and from the surface of emergent vegetation (Goodwin 1960). In the prairies, much of the food is obtained from plowed land and fields of grain (Pittman 1927). Foraging over agricultural land near marshes has also been observed in New York (Morrison pers. comm.). In a sample of 376 feedings of young in different nests at North Pond in New York, Goodwin (1960) found that 41% of the items brought by parents were minnows and 59% were insects, including 45% damselflies. Insects comprised 93.6% of 602 feedings to chicks in Michigan while fishes accounted for just 4.9% (Cuthbert 1954). Although many of the insects could not be identified, damselflies, dragonflies, and mayflies were important food items. In Ontario, Dunn (1979) was unable to identify the majority of 56 food items brought to young, but 13% were minnows and 6% were dragonflies.
    Reproduction Comments
    Most terns in the northeastern United States and Canada return to breeding areas during the first two weeks of May, although birds may arrive in western New York as early as the last week of April (Laughlin and Kibbe 1985, Firstencel 1987, Gerson 1987). Conspicuous aerial courtship displays characterize the courtship period, which begins soon after arrival at the breeding site. In the "high-flight", a group of 2-20 terns ascend together to a great height then split into smaller groups of two or three and descend in rapid glides (Baggerman et al. 1956). During the "fish-flight", a male tern carries a small fish or large insect in its bill and is closely followed by a female as the two fly about the marsh. At the close of this aerial display the male follows the female to a perch and feeds her (Baggerman et al. 1956). <br><br>In the northeastern United States egg laying begins in late May, but may be initiated as late as the middle of July. Nests with eggs were observed at one site in western New York from 24 May to 12 July (Firstencel 1987). During a 1989 survey of colony sites throughout New York, nests with eggs were observed as early as 25 May and as late as 18 July (Novak 1990). Not known to be double brooded and late nests probably represent renesting attempts. At Rush Lake in Wisconsin, Bailey (1977) observed a trend toward three nesting peaks, one in late May, one in early to mid June, and one in late July. This pattern was attributed to two initial nesting periods characterized by a high degree of synchrony, followed by a period of renesting (Bailey 1977). Baggerman et al. (1956) also reported highly synchronous nesting activity. <br><br>One to five eggs may be laid, although the normal clutch is usually two or three (Bent 1921). Clutches with four eggs have been reported in only two recent studies (Bergman et al. 1970, Mossman 1980) and are apparently quite rare. Other than Bent (1921), there are no published reports of five egg clutches. Single egg clutches may often be replacement nests or nests where one or more eggs have already been lost (Bent 1921, Cuthbert 1954, Firstencel 1987). In a recent study in Wisconsin, the average clutch size for 41 closely monitored nests was 2.9 (Bailey 1977). Four nests had clutches of two, but no nests contained less than two or more than three eggs. Average clutch sizes reported in other recent studies where nests may not have been monitored as carefully, range from 2.25 to 2.75 (Cuthbert 1954, Goodwin 1960, Bergman et al. 1970, Mossman 1981, Firstencel 1987, Novak 1990). Incubation begins with the laying of the first egg, and eggs require 20-24 days to hatch (Goodwin 1960, Bergman et al. 1970, Bailey 1977). Both sexes incubate (Goodwin 1960). <br><br>Young are tended by both parents. Chicks are able to swim, walk and run by the time they are two days old (Goodwin 1960). The chicks grow rapidly, doubling their weight in less than three days and quadrupling their weight in less than six days (Bailey 1977). The rate of weight gain slows after the eighth day. In some cases, chicks may be relocated from the nest site to "auxiliary" nests within a few days after hatching (Cuthbert 1954, Firstencel 1987). If disturbance at the nest is minimal, young may remain at the original nest site for as long as 14-25 days, although they hide in the vegetation at the sign of danger and may be found swimming as far as 40 ft from the nest (Cuthbert 1954, Goodwin 1960). The age at fledging is difficult to determine. Bailey (1977) reported fledging at 18 and 19 days for two chicks of known age and suggested that the majority of chicks are flying at 21 days of age with a mean fledging age possibly less than 20 days. Baggerman et al. (1956) and Goodwin (1960) reported fledging at 21 days. Young are fully fledged at about four weeks. <br><br>Estimates of nest success (expressed as a percentage of nests where at least one egg was hatched successfully) from four nest studies are as follows: 27% (15 of 55 nests) in Ontario, 29% (56 of 192 nests) in Iowa, 34% (13 of 38 nests) in Wisconsin, and 50% (12 of 24 nests) in New York (Dunn 1979, Bergman et al. 1970, Bailey 1977, Firstencel 1987, respectively). There was no obvious correlation between nest success, height of eggs above water, and number of nests per substrate in the Iowa study (Bergman et al. 1970). <br><br>Survival of young to fledging is difficult to measure because of the mobility of chicks. Bailey (1977) attempted to measure chick survival by placing fencing around nests to prevent young from moving away from the nest site. Just three of 26 (12%) chicks monitored fledged successfully. Sixteen chicks were lost to predation and several chicks died in the pen netting. Fledging success at unfenced nests (perhaps a better representation of fledging success) was estimated at 15-20% (Bailey 1977). Recent surveys have presented estimates of reproductive success based on the number of fledglings produced per egg laid in the colony (Rabenold 1987, Novak 1990). Estimates for three small (less than 10 pairs) colonies in Indiana were 0%, 53%, and 67%, for an overall average of 30% (Rabenold 1987). Estimates also varied widely for 19 sites in New York, from 4% to 38%, with an overall average of 20% (Novak 1990). Mossman (1980) reported a 25% reproductive success based on the ratio of young: adults observed at one study area in Wisconsin. <br><br>The similarity between reproductive or fledging success rates and nest success (hatching success) supports the observation by Dunn (1979) that most losses occur during the egg stage. Wind and wave action, and storms were responsible for most nest losses in several studies (Bergman et al. 1970, Bailey 1977, Dunn 1979, Faber and Nosek 1985, Chapman-Mosher 1987). Nest losses have also been attributed to egg inviability, predation, muskrat activity, and intraspecific interactions (Bergman et al. 1970, Bailey 1977, Dunn 1979, Firstencel 1987). <br><br>Has been described as a semi-colonial nesting species (Cuthbert 1954, Bergman et al. 1970). Nests may be clumped closely in favorable habitat or more widely scattered in other, perhaps less favorable areas. As is typical of colonial nesting gulls and terns, terns will join together to defend the nesting area from intruders (Cuthbert 1954).
    Ecology Comments
    Gregarious throughout the year. Has been described as a semi-colonial nesting species (Cuthbert 1954, Bergman et al. 1970). Nests may be clumped closely in favorable habitat or more widely scattered in other, perhaps less favorable areas. As is typical of colonial nesting gulls and terns, terns will join together to defend the nesting area from intruders (Cuthbert 1954). <br><br>Ectoparasites include feather mites and lice (Peters 1936, Perez and Atyeo 1984). A trematode, APORCHIS LARUS, was recorded in Russia (Mirzoeva 1980). The effects of these parasites have not been studied. <br><br>Black terns are susceptible to avian botulism. A few dead birds have been found in Nevada and Manitoba (Alcorn 1942, Manuwal 1967), but no major die-offs from this disease have been reported. <br><br>Commonly returns to previous nesting area but also commonly changes sites if conditions become unfavorable. Return rates may vary considerably among specific sites. Stern et al. (1985) found that 67% of recaptured terns nested within the same primary wetlands, while Bailey (1977) and Dunn (1979) reported return rates of 40% and 27% for sites in Wisconsin and Ontario, respectively. These return rates, which are low in comparison with other gulls and terns, may be the result of the relative instability of preferred habitat (McNicholl 1975).
    Length
    25
    Weight
    65
    NatureServe Global Status Rank
    G4
    Global Status Last Reviewed
    1996-11-27
    Global Status Last Changed
    1996-11-27
    Conservation Status Map
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    Global Range
    H - >2,500,000 square km (greater than 1,000,000 square miles) - H - BREEDING: British Columbia and Mackenzie east through northern Saskatchewan to Nova Scotia, south locally to southern California, Colorado, Nebraska, southern Illinois, Ohio, Pennsylvania, northern New England (formerly to Missouri and Kentucky); there is a single breeding record for coastal New Jersey. In Old World from northern Europe, Russia, and Siberia south to Mediterranean, Asia Minor, Turkestan, and Caspian and Aral Seas. Nonbreeders occur in summer south on Pacific coast to Panama, and in eastern North America to Gulf Coast (AOU 1983). Sparse and uncommon in northeast and on southern edge of range (Dunn and Agro 1995). See Gerson (1987) for details on distribution and abundance in Canada. NON-BREEDING: in the Americas along both coasts from Panama south to Peru, Surinam, and French Guiana; rare in Brazil, Uruguay, and Argentina (AOU 1983, Dunn and Agro 1995). In the Old World in tropical Africa south to Angola and Tanzania (AOU 1983). Casual in Hawaii.
    Global Range Code
    H
    Global Range Description
    >2,500,000 square km (greater than 1,000,000 square miles)
    ELEMENT_GLOBAL.2.105682