Rhynchophanes mccownii

(Lawrence, 1851)

Thick-billed Longspur

G4Apparently Secure Found in 12 roadless areas NatureServe Explorer →
G4Apparently SecureGlobal Rank
Least concernIUCN
Thick-billed Longspur (Rhynchophanes mccownii). Photo by U.S. Fish & Wildlife Service, Public Domain (U.S. Government Work), via ECOS.
U.S. Fish & Wildlife Service, https://www.usa.gov/government-works
Identity
Unique IDELEMENT_GLOBAL.2.101543
Element CodeABPBXA6010
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVertebrate Animal
IUCNLeast concern
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomAnimalia
PhylumCraniata
ClassAves
OrderPasseriformes
FamilyCalcariidae
GenusRhynchophanes
Synonyms
Calcarius mccownii(Lawrence, 1851)
Other Common Names
Escribano Piquigrueso (ES) McCown's longspur (EN) Plectrophane à ventre gris (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
Previously in the genus Calcarius, transferred to Rhynchophanes by AOU (2010). The common name has been updated to Thick-billed Longspur (AOS 2021).
Conservation Status
Rank MethodExpertise without calculation
Review Date2016-04-09
Change Date2003-09-03
Edition Date1999-10-30
Edition AuthorsJENNINGS, R., and J.D. REICHEL; Revisions by M. KOENEN and D.W. MEHLMAN
Range Extent>2,500,000 square km (greater than 1,000,000 square miles)
Number of Occurrences81 to >300
Rank Reasons
Still apparently secure overall, but dramatic declines have occurred in the northern part of the range.
Range Extent Comments
BREEDING: southeastern Alberta, southern Saskatchewan, northern North Dakota and (previously) southwestern Minnesota, south through Montana to southeastern Wyoming, northeastern Colorado, Oklahoma, northwestern Nebraska, and Manitoba (With 1994a, AOU 1998). NON-BREEDING: primarily from western Oklahoma, western Kansas, southeastern Arizona, and central New Mexico south through Sonora and Chihuahua to northern Durango (With 1994a, AOU 1998). Rarely in Idaho, Utah, Nevada, and ne and coastal California (With 1994a).
Occurrences Comments
No exact figures.
Threat Impact Comments
HABITAT LOSS AND FRAGMENTATION: Habitat destruction due to agricultural conversion and development of native prairie habitat. Restriction of fire also reduced available shortgrass prairie. Population may also be limited by availability of microclimatic features. Initial territories have southern exposure; birds may be sensitive to ground temperature or moisture. No studies have investigated a relationship between patch size and nest success or patch size and rates of brood parasitism by Brown-headed Cowbirds (MOLOTHRUS ATER). Cowbird parasitism, however, appears rare (With 1994a).

PREDATION: Nest predation believed to limit productivity. In Saskatchewan, Wyoming, and Colorado, about half of all nests were lost to predators, such as the thirteen-lined ground squirrel (CITELLUS TRIDECEMLINEATUS; see With 1994a). Nests in heavily grazed pasture suffered higher predation rates (up to 75 percent) compared to nests in moderately grazed pasture (up to 60 percent; With 1994a). Both eggs and nestling were depredated.

PESTICIDES: Application of insecticide toxaphene resulted in direct poisoning of nestlings (McEwen and Ells 1975 cited in With 1994a).

DISTURBANCE: May have a relatively high incidence of nest desertion due to human interference. In Saskatchewan, 10.8 percent of nests and 7.5 percent of nestlings may have been abandoned due to human interference (Felske 1971, cited in With 1994a). Individuals, however, vary in response to human disturbance; some allowed approach to within 5 - 10 meters of nest, others flushed within 25 meters (With 1994a).
Ecology & Habitat

Habitat

Sparse short-grass plains, plowed and stubble fields, and areas of bare or nearly bare ground (AOU 1983). Use grasslands with little litter (Felske 1971) and low vegetation cover (DuBois 1935, Creighton 1974), such as that provided by shortgrass or heavily grazed mixed-grass prairie (Saunders 1914; Finzel 1964; Wiens 1970; Maher 1973, 1974; Creighton 1974; Oberholser 1974; Porter and Ryder 1974; Stewart 1975; With 1994a; Prescott and Wagner 1996). Cultivated lands also may be utilized, including small-grain stubble fields, minimum- and conventional-tilled land, and summer fallow fields (Felske 1971, Stewart 1975, Martin in prep.), although, historically, agricultural lands were avoided (DuBois 1935, Mickey 1943). Early-season abundance of nesting birds in cropland fields in southcentral Alberta showed a positive correlation with percent bare ground, and productivity appeared to be negatively correlated with the vertical density of forbs (Martin in prep.). Often breed on high, barren hillsides with southern exposures (Giezentanner 1970a,b; Felske 1971; Creighton 1974). Blue grama (BOUTELOUA GRACILIS) and buffalo grass (BUCHLOE DACTYLOIDES) are dominant plants in nesting areas (DuBois 1935, Cassel 1952, Creighton 1974).

Nests usually in a scrape on the ground at the base of a bush or clump of grass, or beside cattle dung. Nests beside shrubs may be subject to heavy predation by ground squirrels (With 1994a). Nests tend to be oriented to the north (With and Webb 1993), and about one-third to one-half of nests are placed near clumps of grass, shrubs, plains prickly pear (OPUNTIA POLYACANTHA), or cowpies (DuBois 1935, Mickey 1943, With 1994b). However, shrubs and prickly pear near the nest may facilitate depredation by providing protective cover to predators. In northcentral Colorado, for example, 75-80 percent of nests placed near shrubs or prickly pear were depredated (With 1994b). Nests depredated during incubation had six times more shrub cover within 1 meter of the nest than did successful nests.

In northcentral Colorado, nests were exposed completely to solar radiation at midday and had 45 percent total exposure per day (With and Webb 1993). High exposure to solar radiation may ameliorate cold stresses associated with an early breeding season. Nests constructed later in the season were more likely to be constructed near vegetative cover than those constructed earlier in the season (With and Webb 1993). In southeastern Wyoming, percent vegetation coverage within 5 centimeters of the ground was higher in occupied territories than in unoccupied territories (Greer and Anderson 1989). Occupied territories also had fewer cowpies, less lichen, and lower forb coverage than unoccupied areas.

Ecology

Area requirements vary by region. Reported territory sizes were 0.6 hectares in southeastern Wyoming (Greer and Anderson 1989), 0.5-1.0 hectares in Saskatchewan (Felske 1971), and 1-1.5 hectares in central Colorado (Wiens 1970, 1971; With 1994a). Pairs often nest near each other (Mickey 1943, Felske 1971). In winter may be seen with flocks of horned larks.

Reproduction

The breeding season extends approximately from mid-March through mid-October (Mickey 1943, Giezentanner and Ryder 1969, Felske 1971, Creighton 1974, Salt and Salt 1976, With 1994a), but may remain on the breeding grounds as late as mid-November in some locations (Johnsgard 1980). The female incubates three to four, sometimes up to six, eggs for 12 days. In northeastern Colorado, usual clutch size was three (With 1994a). Nestlings are altricial. Young are tended by both adults, leave nest in 10 days, and fly 12 days after hatching (Terres 1980). Second broods were reported in northcentral Colorado and in Montana (DuBois 1935, Strong 1971). Second broods may be initiated as soon as three weeks after fledging of the initial brood, but may be limited by female energy reserves (Felske 1971, With 1994a).
Terrestrial Habitats
Grassland/herbaceousCropland/hedgerow
Other Nations (2)
United StatesN4B,N4N
ProvinceRankNative
ArizonaS2NYes
South DakotaSHBYes
ColoradoS2BYes
KansasS3NYes
OklahomaS2NYes
North DakotaS2Yes
CaliforniaSNRNYes
New MexicoS3NYes
MontanaS3BYes
NebraskaS3Yes
MinnesotaSXB,SNRMYes
TexasS4Yes
WyomingS3BYes
CanadaN3B
ProvinceRankNative
AlbertaS3BYes
SaskatchewanS3BYes
Roadless Areas (12)
Montana (8)
AreaForestAcres
Bear - Marshall - Scapegoat - SwanLewis and Clark National Forest344,022
Bear - Marshall - Scapegoat - SwanLewis and Clark National Forest344,022
Bear - Marshall - Scapegoat - SwanLewis and Clark National Forest344,022
Big Horn MountainBeaverhead-Deerlodge National Forest50,846
Big Horn MountainBeaverhead-Deerlodge National Forest50,846
Big Snowy Mountains WsaLewis and Clark National Forest88,003
North AbsarokaGallatin National Forest159,075
North AbsarokaGallatin National Forest159,075
New Mexico (2)
AreaForestAcres
Capitan MountainsLincoln National Forest14,069
Capitan MountainsLincoln National Forest14,069
Wyoming (2)
AreaForestAcres
Walker PrairieBighorn National Forest62,434
Walker PrairieBighorn National Forest62,434
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