Numenius tahitiensis

(Gmelin, 1789)

Bristle-thighed Curlew

G3Vulnerable Found in 5 roadless areas NatureServe Explorer →
G3VulnerableGlobal Rank
Near threatenedIUCN
High - mediumThreat Impact
Identity
Unique IDELEMENT_GLOBAL.2.104761
Element CodeABNNF07030
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVertebrate Animal
IUCNNear threatened
EndemicOccurs (regularly, as a native taxon) in multiple nations, but breeds in a single state or province
KingdomAnimalia
PhylumCraniata
ClassAves
OrderCharadriiformes
FamilyScolopacidae
GenusNumenius
Other Common Names
Courlis d'Alaska (FR)
Concept Reference
American Ornithologists' Union (AOU). 1998. Check-list of North American birds. Seventh edition. American Ornithologists' Union, Washington, D.C. [as modified by subsequent supplements and corrections published in The Auk]. Also available online: http://www.aou.org/.
Taxonomic Comments
Whimbrel (Numenius phaeopus) is generally accepted as the closest relative of N. tahitiensis (Marks et al. 2002).
Conservation Status
Rank Method Rank calculation - Biotics v2
Review Date2022-09-30
Change Date2022-09-30
Edition Date2022-09-30
Edition AuthorsCannings, S., updating earlier work by J. Palis, T. A. Gotthardt, E. W. West, M. Koenen, G. Hammerson, and D. W. Mehlman. Rev. by R. E. Gill.
Threat ImpactHigh - medium
Range Extent20,000-200,000 square km (about 8000-80,000 square miles)
Number of Occurrences6 - 80
Rank Reasons
Breeding population consists of only 3,200 pairs in two remote areas in Alaska; however the trend appears to be close to stable. Climate change is a potential threat on both breeding and wintering grounds. Wintering populations on Pacific islands may be threatened by habitat loss, predation, and disturbance.
Range Extent Comments
The breeding range encompasses remote mountainous regions of western Alaska in the Andreafsky Wilderness Area north of the Yukon River mouth and on the central Seward Peninsula (McCaffery and Peltola 1986, Kessel 1989, Gill et al. 1990, Marks et al. 2002, Marks et al. 2022). Small population may breed north of Kotzebue, Alaska (BirdLife International 2020). Nonbreeding individuals occur in summer on coastal tundra from Kotzebue Sound south to Hooper Bay and occasionally in the Hawaiian Islands (AOU 1998). Range extent estimate of 150,000 km2 based on breeding range map in BirdLife International (2020).

Critical migration staging areas in Alaska include the coastal portions of the central and southern Yukon-Kuskokwim River Delta. The only currently known critical stopover site south of Alaska is the Northwestern Hawaiian Islands. Other possible migration stopover areas include the southern Line Islands, and the Phoenix, or Marshall island groups (Palmisano 1993).

During the non-breeding season, the Bristle-thighed Curlew occurs on Pacific Ocean islands and atolls from the Hawaiian (most commonly from Midway east to French Frigate Shoals) and Marshall islands south to the Fiji, Tonga, Samoa, Marquesas, and Tuamotu islands; also reaching the Solomon Islands, Norfolk Island, Kermadec Islands, Pitcairn Islands (notably Oeno) and Easter Island (Gill and Redmond 1992, Vilina et al. 1992, Brooke 1995, AOU 1998, Marks et al. 2002, BirdLife International 2020). Bristle-thighed Curlew is unique among migratory shorebirds in wintering on remote islands (Marks et al. 1990). Subadults may remain in the Pacific until they are nearly 3 years old (Collar et al. 1992).
Occurrences Comments
Two known and one suspected breeding areas exist in Alaska, but the number of distinct occurrences has not been determined using standardized criteria. Four key staging areas are known on the Yukon-Kuskokwim Delta (Gill and Tibbitts 1990). The number of wintering ground occurrences is uncertain due to the wide dispersion of the birds on South Pacific Islands (Gill and Redmond 1992).
Threat Impact Comments
Nonbreeding: Potential threats include predation by a variety of introduced species, especially feral dogs but also feral pigs and cats (BirdLife International 2020). Nonbreeding birds are most susceptible to predation during molt and are readily captured at this time by subsistence hunters (Marks et al. 1990, Marks and Redmond 1994a). However, the degree of predation and its impact on the population are not known. Subsistence harvest is believed to be much lower now than in the past (see Marks et al. 2002) and is localized (BirdLife International 2020). The presence of curlews on atolls in the Tuamotu Archipelago suggests they are resilient to the occurrence of Pacific rats and to the alteration of native habitats. However, lack of data on their historic numbers at these sites makes it difficult to assess the full affect of altered conditions (Tibbitts et al. 2003). Habitat is being lost to development of tourist facilities (Marks and Redmond 1994a), and through clearing for coconut plantations (BirdLife International 2020). Global climate change is threatening many coastal feeding areas with rising sea levels (Pearce-Higgins et al. 2017).

Breeding: There are no immediate anthropogenic threats exist in breeding habitat (Gill and Handel 1987, Marks et al. 2002). Climate change is causing habitat change (e.g. shrubification) and geographic shifting on the breeding grounds, and is expected to alter the phenology of invertebrate prey (Pearce-Higgins et al. 2017). Gold mining on Alaska's Seward Peninsula is a potential future threat to habitat (BirdLife International 2020). Travel across the tundra in heavy machinery can lead to localized habitat damage (Lanctot 1990). Open dumps in villages near the Yukon-Kuskokwim Delta have resulted in an unnaturally high populations of Common Ravens, known predators of curlew eggs and chicks (BirdLife International 2020).

Staging: Subsistence hunting may pose a threat to birds on the Yukon-Kuskokwim Delta. Hunter surveys indicate a substantial increase in the take of large shorebirds by Native Americans. Because hunter survey forms do not distinguish between curlews, Whimbrels, and Bar-tailed Godwits, the extent of curlew harvest is unknown, but estimated from 2002 reports to be between 90 and 100 birds (fide B. McCaffery in R. Gill, pers. comm. 2004).
Ecology & Habitat

Description

A large brownish shorebird with a moderately long decurved bill, striped head, and tawny unbarred rump. The stiff feathers on the thighs and flanks are not easily seen in the field (NGS 1983).

Diagnostic Characteristics

Differs from the Whimbrel (Numenius phaeopus) in being tawnier and by having a tawny unbarred rump, less streaking on the breast, and a paler bill. Bill is much shorter than that of Long-billed (Numenius americanus) and Far Eastern curlews (Numenius madagascariensis); longer, thicker, and more curved than in Eskimo Curlew (Numenius borealis); which averages 7 cm shorter).

Habitat

Breeding: Breeding occurs in the low, mountainous regions northeast of the lower Yukon River (Nulato Hills) and uplands of the Seward Peninsula, Alaska (Handel and Dau 1988, Marks et al. 2002). Physiography differs markedly between Seward Peninsula and Nulato Hills; the latter is characterized by lower relief, gentler slopes, more complex drainage patterns, and smaller areas of specific habitats (Marks et al. 2002). Breeding areas encompass a mosaic of subarctic and arctic tundra habitats including: low shrub/tussock tundra (Betula nana, Empetrum nigrum, Ledum palustre, Vaccinium spp., Salix spp.), mixed shrub thicket/tundra (Salix spp., Betula nana, and Alnus crispa over tussocks), tall shrubs (Salix alexensis, typically along water courses), and shrub meadow/tundra (species similar to low shrub/tussock tundra but lower and with more bare ground). Sedge (Carex aquatilis, C. bigelowii), cottongrass (Eriophorum spp.) and lichen meadows, though a small fraction of the overall land area, are also important habitats.

Habitat use changes during the breeding season. During pre-nesting, curlews tend to be found primarily in shrub meadow/tundra (33%) and low shrub/tussock (47%); during nesting the birds shift their activities mostly to shrub meadow/tundra; and during brood rearing, adults attending young increase their use of sedge meadows. Younger broods tend to use habitats with a moderate level of tussocks and shrub cover; after fledging they prefer sedge and lichen meadows (Gill et al. 1990).

Foraging microhabitat: Foraging occurs primarily in dwarf-shrub meadow tundra on slopes and ridges, also in wetlands and medium-shrub (0.5-1.0 meters tall) habitats including marshy streambeds, stream shorelines, shallow lakes, moss or grass/sedge understory along margins (rarely interiors) of willow thickets, and lingonberry and Labrador tea (Ledum spp.) understory around dwarf birch thickets. On staging grounds, foraging birds are most common in tundra/meadow mosaic (Marks et al. 2002).

Staging: Staging prior to primary migration occurs on the coastal fringe of the Yukon-Kuskokwim Delta and coastal lowlands of the Seward Peninsula, Alaska. Staging habitats include sedge and graminoid meadows and upland tundra (Handel and Dau 1988). Annual variation in standing crop of fruits of black crowberry and ericaceous shrubs appears to be a major determinant of habitat use. Southward migrants on the central Yukon Delta roost at night in shallow brackish pond edges surrounded by large wet-sedge meadows (Marks et al. 2002).

Nonbreeding: Winter habitats are primarily throughout Polynesia in the Central and South Pacific. This species is unique among migratory shorebirds in that the entire population is confined to islands during the nonbreeding season (Marks et al. 1990). Subadults may remain in the Pacific until they are nearly three years old (Collar et al. 1992). Habitats include ocean terraces or reef flats, ocean beaches, inter-islet channels, lagoon sand beaches, lagoon coral reefs, mudflats, saltpans, coconut groves, and vegetated clearings (Pratt et al. 1987, Gill and Redmond 1992).Gill and Redmond (1992) found that wintering birds were associated principally with saltpans (36%) and inter-islet channels (27%). During molt, flightless birds take shelter during the day in dense stands of bunchgrass (Eragrostis variabilis) (Marks et al. 1990). In the Tuamotu Archipelago, curlews were found on all atolls surveyed, regardless of rat presence or absence. Most birds were detected in coastal habitats either on the ocean (44%) or lagoon shores (41%; Tibbitts et al. 2003).

Ecology

Breeding territories encompass approximately 0.5-1.5 square kilometers (Gill et al. 1990) and average densities range from 0.45 birds per square kilometer in early July to 0.04 birds per square kilometer in late July (Gill and Handel 1987). Territory size varies with topography, particularly configuration of drainages, and is smaller for southern population (40-100 ha in Nulato Hills) than for northern population (150-275 ha at Neva Creek). During incubation, adults at Neva Creek regularly travel from nesting territories to communal feeding and roosting areas up to 7 km away. Adults with broods move away from nesting sites, traveling on average 0.3-1.0 km in first week, 0.5-1.6 km (up to 4.4 km) in second and third weeks, and 0.6-1.0 km (up to 2.6 km) in fourth and fifth weeks (Lanctot et al.1995).

On staging grounds, gathers in communal nocturnal roosts (in shallow water ponds) of up to approximately 120 individuals (Tibbitts 1990). The average diurnal flock size on the staging grounds is 3.1 birds (range 1-33; Handel and Dau 1988). Flock size in nonbreeding habitat ranges from a few to more than 100 individuals (Pratt et al. 1987). While on the Pacific islands, many birds lose so many primaries and secondaries during molt that they become flightless for about two weeks; during molt, birds are extremely secretive by day, hiding in dense vegetation (Marks 1993). Adults molt from July through December and juveniles throughout the year (Marks et al. 1990, Marks 1993). Estimated annual survivorship for wintering birds is 80-90% (Marks 1992). The oldest known individual was one killed on Laysan Island that had been banded 23 years, 10 months earlier (Marks 1992).

Potential predators on the breeding grounds include Golden Eagles (Aquila chrysaetos), Rough-legged Hawks (Buteo lagopus), Northern Harriers (Circus cyaneus), Merlins (Falco columbarius), Short-eared Owls (Asio flammeus), Long-tailed Jaegers, Short-tailed Weasels (Mustela erminea), red foxes, and brown bears (Ursus arctos; McCaffery 1990, Lanctot et al. 1995). On breeding grounds, known predators of adults include Gyrfalcon (Falco rusticolus); of eggs, Parasitic Jaeger (Stercorarius parasiticus) and Common Raven (Corvus corax); and of chicks, red fox (Vulpes vulpes), Northern Harrier (Circus cyaneus), Gyrfalcon (Falco rusticolis), Sandhill Crane (Grus canadensis), and Long-tailed Jaeger (McCaffery 1990, Lanctot et al. 1995, Marks et al. 2002)

Forms temporary associations with American and Pacific Golden-Plover (Pluvialis dominica and P. fulva), Whimbrel, Bar-tailed Godwit, Western Sandpiper and Long-tailed Skua (Stercorarius longicaudus). Curlews and other larger-bodied species commonly attack-mobbed predators together, whereas smaller-bodied species generally give alarm calls and circle predators (Lanctot et al.1995).

Reproduction

Spring migrants usually arrive singly or in groups of two, occasionally in flocks. Males often precede mates by 1-6 days. Females rarely observed before mates in same year. Nest building begins within 1-3 days of arrival. At Nulato Hills (1987-1991), most nests initiated during last two weeks of May with successful nests hatching from 15-30 June. At Neva Creek, median clutch initiation was 24-31 May, about two weeks after arrival of females. Late clutches (initiated 9-18 June) attributed to late arriving females rather than renesting attempts. Median hatching dates 22-28 June with only a few nests hatching in July. Between 95-100% of pairs hatched nests within 8-10 days in two early years and 21-22 days in one late year at Neva Creek. Second brood per season not known to occur (Marks et al. 2002).

Clutch size is typically four eggs (Kyllingstad 1948, McCaffery and Peltola 1986) which are incubated by both sexes for 24-25 days (McCaffery and Gill 1992). In the Nulato Hills of the Yukon Delta National Wildlife Refuge, 80 percent of nests beneath tundra willows hatched, whereas only about 33 percent of nests in the open were successful. Curlew nests constructed near nest sites of aggressively defensive Long-tailed Jaegers (Stercorarius longicaudus) were more successful than those in more isolated areas (McCaffery and Gill 1992). Seven of 9 nests examined by McCaffery and Peltola (1987) in the Nulato Hills were lost to predation.

Chicks are precocial and leave the nest within 12 hours of hatching. Young can fly when 21-24 days old (Lanctot et al. 1995). When 1-4 weeks old, juveniles congregate in brood aggregations (Lanctot et al. 1995). These groups typically remain intact until juveniles depart for staging areas in early August. Brood aggregations generally consist of fewer than 20 juveniles, but can contain up to 30 (McCaffery and Gill 1992, Lanctot et al. 1995). Brood groups studied by Gill et al. (1990) contained an average of 6.5 young (range = 1-12) from a minimum of 1-3 different broods. However, aggregations can include young from as many as 10 broods (Lanctot et al. 1995). Brood aggregations are tended by up to 14 parent birds, sometimes even if the aggregation does not contain any of their own young (Gill et al. 1990, McCaffery and Gill 1992, Lanctot et al. 1995). Brood aggregations move up to two kilometers per day (McCaffery and Gill 1992). Males attend aggregations 10-14 days longer than females (Gill et al. 1990). Brood aggregations often include young of other birds such as Bar-tailed Godwit (Limosa lapponica), American Golden-Plover (Pluvialis dominica), Pacific Golden-Plover (Pluvialis fulva), Whimbrel, Long-tailed Jaeger, and Western Sandpiper (Calidris mauri) (Lanctot et al. 1995). Curlews become reproductively mature in their third year (Marks 1993).
Terrestrial Habitats
Grassland/herbaceousAlpineTundraSand/dune
Other Nations (1)
United StatesN2B,NNRN
ProvinceRankNative
HawaiiS1NYes
AlaskaS2BYes
Threat Assessments
ThreatScopeSeverityTiming
3 - Energy production & miningLarge - smallModerate or 11-30% pop. declineModerate (short-term)
3.2 - Mining & quarryingLarge - smallModerate or 11-30% pop. declineModerate (short-term)
5 - Biological resource useLarge - smallModerate or 11-30% pop. declineHigh (continuing)
5.1 - Hunting & collecting terrestrial animalsLarge - smallModerate or 11-30% pop. declineHigh (continuing)
8 - Invasive & other problematic species, genes & diseasesPervasive - largeModerate or 11-30% pop. declineHigh (continuing)
8.1 - Invasive non-native/alien species/diseasesPervasive - largeModerate or 11-30% pop. declineHigh (continuing)
9 - PollutionLarge - smallUnknownHigh (continuing)
9.2 - Industrial & military effluentsLarge - smallUnknownHigh (continuing)
11 - Climate change & severe weatherPervasive (71-100%)UnknownModerate (short-term)
11.1 - Habitat shifting & alterationPervasive (71-100%)UnknownModerate (short-term)

Roadless Areas (5)
Alaska (5)
AreaForestAcres
Chugach-13Chugach National Forest13,337
Copper River WetlandsChugach National Forest85,972
Kenai LakeChugach National Forest213,172
Roaded DonutChugach National Forest968
Sheridan GlacierChugach National Forest224,683
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