Rare Species Guide

 Calcarius ornatus    (Townsend, 1837)

Chestnut-collared Longspur 


MN Status:
endangered
Federal Status:
none
CITES:
none
USFS:
none

Group:
bird
Class:
Aves
Order:
Passeriformes
Family:
Calcariidae
Habitats:

(Mouse over a habitat for definition)

Minnesota range map
Map Interpretation
North American range map
Map Interpretation

  Basis for Listing

The Chestnut-collared Longspur (Calcarius ornatus) breeds across the northern Great Plains and the southern Prairie Provinces of Canada, southward to northern Colorado. Within this range, the species tends to be localized in abundance or semi colonial. Chestnut-collared Longspur populations in Minnesota and Nebraska have been greatly reduced, and the species no longer breeds in Kansas where it was once considered abundant. In North Dakota, the Chestnut-collared Longspur population declined by about 33% from 1967 to 1993 (Igl and Johnson 1997). During the nineteenth century, the Chestnut-collared Longspur occurred throughout the dry upland prairie of western Minnesota from Jackson County north to the Canadian border. It was most abundant in the southwestern counties where more suitable dry prairie habitat was available. As settlement progressed, however, the Chestnut-collared Longspur rapidly disappeared from that quarter of the state, and by 1930 it was found in only a few isolated colonies on the Glacial Lake Agassiz beach ridges of the Red River Valley (Roberts 1932).

Since the 1960s, Minnesota's Chestnut-collared Longspurs had been found almost exclusively at Felton Prairie in Clay County (Red River Prairie Subsection). There have been occasional, isolated summer reports of Chestnut-collared Longspurs, primarily males, from widespread locations around western Minnesota. One of the most notable reports was from Traverse County where a colony of over 30 individuals was observed in 1984 (Wyckoff 1986b) and persisted for several years before disappearing. In 1995, eight singing males and at least two female Chestnut-collared Longspurs were documented in Polk County. A few birds were still present at this site in 2004, but none were observed in 2013. Another small colony of 5-6 male longspurs was found in Pipestone County in 2006, and at least two males were present again in 2007, but no birds have been seen since then. The Chestnut-collared Longspur was designated a state endangered species in Minnesota in 1984.

  Description

Chestnut-collared Longspurs are named for the long slender claw on their hind toe and the rusty color on the nape of their neck. In male Chestnut-collared Longspurs, the black crown and underparts contrast sharply with the buffy face and chestnut collar. The female's plumage is dull brownish with some dark mottling on the breast and belly and only a trace of chestnut on the nape. Both sexes have a distinctive largely white tail with a central dark triangle. The male's song is similar to that of the Western Meadowlark (Sturnella neglecta), though not as loud or musical. The flight call, a two-syllable “kittle”, is also diagnostic.

  Habitat

The Chestnut-collared Longspur prefers native upland prairie, establishing breeding territories in well-drained sites away from trees and shrubs. In Minnesota, it occurs mostly in relatively dry, moderately grazed prairie (northern dry prairie), though may be found in moderately-grazed northern mesic prairie. Elsewhere in its breeding range, the species is typically found on grazed, hayed, or mowed mixed-grass prairies or other areas with short sparse vegetation and little or no litter accumulation. Although Chestnut-collared Longspurs are not known to nest on agricultural lands, these areas serve as important foraging sites, particularly when planted with wheat or sunflowers (Wyckoff 1986a).

  Biology / Life History

Chestnut-collared Longspurs overwinter on grasslands in the southern U.S. and northern Mexico and usually begin returning to Minnesota in mid-April. Males exhibit a high degree of site fidelity and tend to return to the same nesting site in consecutive years. They defend circular territories of less than 1.0 ha (2.5 acres), though territory size may increase if habitat is marginal. Nests are constructed in a depression on the ground, usually under a clump of grass, and lined with soft grasses and animal hair. An average of 4 eggs are laid, which females incubate for around 10 days. The chicks leave the nest about 10 days after hatching and begin to fly several days later. The parents continue to feed the young for up to 2 weeks after they have left the nest. If the female begins another brood immediately after the first has fledged, as is often the case, the male assumes all care of the fledglings (Harris 1944). Chestnut-collared Longspurs feed by walking along the ground and gleaning insects, spiders, and grass seeds from the vegetation (Bleho et al. 2020).

  Conservation / Management

In Minnesota, the only annually occupied breeding colony of Chestnut-collared Longspurs had been in the Felton Prairie area of Clay County. However, there have been no breeding season reports at Felton Prairie, or anywhere else in the state, since 2019.  Even though this population seems to be extirpated, the site should be checked annually in case Chestnut-collared Longspurs return. Moderate grazing, haying, and/or prescribed burning of the native prairie should be employed to maintain Felton Prairie's suitability as potential Chestnut-collared Longspur breeding habitat. However, extreme or long-term grazing pressure can change the composition of plant species from forbs to graminoids (Wyckoff 1986a), and some areas near breeding colonies at Felton Prairie are beginning to exhibit these characteristics. Spring burning is not recommended when managing for this species, as it reduces both nesting cover and the insects and seeds that longspurs feed upon (Wyckoff 1986a). Gravel mining in the Felton Prairie area has reduced native prairie and continues to be a threat to the Chestnut-collared Longspur population. Wind farm development on the beach ridges also has the potential to impact this population and should be carefully designed with all towers placed outside of the species' native prairie habitat.

  Conservation Efforts in Minnesota

Observers reported 50-60 male Chestnut-collared Longspurs in the Felton Prairie area in the early 1980s, and in 1985 an intensive survey revealed a minimum of 132 males on the site (Wykoff 1986a). Chestnut-collared Longspurs continued to be present annually at Felton Prairie through 2019, though the population had been in decline since the 1980s. There were only 3 records during the 2009-2013 Minnesota Breeding Bird Atlas, with maximum counts of 4-5 birds (Pfannmuller et al. 2017). Despite management efforts, the population continued to decline, and there have been no breeding season reports of Chestnut-collared Longspurs at Felton Prairie from 2020-2025. There was a report of one individual in April 2022, prior to the breeding season, but there have been no reports since then.  Much of the remaining potential range for this species in the state was surveyed by the Minnesota Biological Survey (MBS), and few additional breeding locations were documented. However, none of these small populations persisted for more than a few years.

  Authors/Revisions

Steven P. Stucker (MNDNR), 2025

(Note: all content ©MNDNR)

  References and Additional Information

Harris, R. D. 1944. The Chestnut-collared Longspur in Manitoba. The Wilson Bulletin 56(2):105-115.

Hill, D. P., and L. K. Gould. 1997. Chestnut-collared Longspur (Calcarius ornatus). Number 288 in A. Poole and F. Gills, editors. The birds of North America. The Birds of North America, Inc., Philadelphia, Pennsylvania.

Igl, L. D., and D. H. Johnson. 1997. Changes in breeding bird populations in North Dakota: 1967 to 1992-93. The Auk 114:74-92.

Roberts, T. S. 1932. The birds of Minnesota. Volume 2. University of Minnesota Press, Minneapolis, Minnesota. 821 pp.

Wyckoff, A. M. 1986a. A relict population of Chestnut-collared Longspurs in Western Minnesota. The Loon 58(1):3-11.

Wyckoff, A. M. 1986b. Longspurs breed in Traverse County. The Loon 58(1):51.


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