Calamospiza melanocorys

Stejneger, 1885

Lark Bunting

G5Secure Found in 57 roadless areas NatureServe Explorer →
G5SecureGlobal Rank
Least concernIUCN
Lark Bunting (Calamospiza melanocorys). © Matthew Grube; Cornell Lab of Ornithology | Macaulay Library.
© Matthew Grube; Cornell Lab of Ornithology | Macaulay Library
Lark Bunting (Calamospiza melanocorys). © MI YU; Cornell Lab of Ornithology | Macaulay Library.
© MI YU; Cornell Lab of Ornithology | Macaulay Library
Lark Bunting (Calamospiza melanocorys). © Alex Eberts; Cornell Lab of Ornithology | Macaulay Library.
© Alex Eberts; Cornell Lab of Ornithology | Macaulay Library
Lark Bunting (Calamospiza melanocorys). © Jacob Bliss; Cornell Lab of Ornithology | Macaulay Library.
© Jacob Bliss; Cornell Lab of Ornithology | Macaulay Library
Lark Bunting (Calamospiza melanocorys). © Ryan Sanderson; Cornell Lab of Ornithology | Macaulay Library.
© Ryan Sanderson; Cornell Lab of Ornithology | Macaulay Library
Lark Bunting (Calamospiza melanocorys). © Nick Park; Cornell Lab of Ornithology | Macaulay Library.
© Nick Park; Cornell Lab of Ornithology | Macaulay Library
Lark Bunting (Calamospiza melanocorys). 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.2.104443
Element CodeABPBX98010
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVertebrate Animal
IUCNLeast concern
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomAnimalia
PhylumCraniata
ClassAves
OrderPasseriformes
FamilyPasserellidae
GenusCalamospiza
Other Common Names
Bruant noir et blanc (FR) Gorrión Ala Blanca (ES)
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/.
Conservation Status
Rank MethodExpertise without calculation
Review Date2016-04-06
Change Date1996-12-04
Rank Reasons
Widespread and apparently secure on Great Plains. Some regional declines have been recorded.
Range Extent Comments
BREEDING: southern Alberta, southern Saskatchewan, and southeastern North Dakota south, east of Rockies, to eastern New Mexico, northern Texas, western Oklahoma, eastern Kansas, and northwestern Missouri (AOU 1998). NON-BREEDING: central California, southern Nevada, central Arizona, southern New Mexico, central Texas, southwestern Kansas, and western Oklahoma south to southern Baja California, Jalisco, Guanajuato, Hidalgo, Tamaulipas, and southern Texas (AOU 1998).
Threat Impact Comments
Probably threatened by intensive agricultural operations that alter or disturb nesting habitat. Does not nest in conventionally tilled cropland in North Dakota (Lokemoen and Beiser 1997); only occasionally nests in cropland in Kansas (Faanes and Lingle 1995). Faanes and Lingle (1995) also noted that although the highest nesting densities in cropland were in wheat stubble, nests there may be destroyed by frequent disturbance. In shortgrass prairie in Wyoming, diazinon applications for grasshopper control resulted in declines and mortality of Lark Buntings (McEwen et al. 1972). Nests are parasitized infrequently by Brown-headed Cowbirds (MOLOTHRUS ATER); however, they may be common hosts in local situations (Friedmann 1963). In Kansas, they were unimportant hosts because of loss of nests to farming operations, ejection of cowbird eggs, and desertion of parasitized nests by parents (Hill 1976). Furthermore, in Kansas (Wilson 1976) and Manitoba (Davis 1994, Davis and Sealy in press), Brown-headed Cowbirds did not fledge from parasitized nests. However, in Saskatchewan, 6 cowbirds fledged from 5 nests of 12 that were parasitized naturally (Sealy 1999). Allen (1874) noted that five of 18 nests found in western North Dakota and eastern Montana were parasitized. No studies have investigated a relationship between patch size and nest success or patch size and rates of brood parasitism.
Ecology & Habitat

Habitat

BREEDING: Plains, prairies, meadows and sagebrush (AOU 1998). Use grasslands of low to moderate height with high vegetative cover and 10-15% bare ground (Wiens 1970, Creighton 1974), often with a superstory component such as shrubs (Baldwin et al. 1969, With and Webb 1993). Shrubs are especially important in savanna and sagebrush (ARTEMISIA) habitats (Woolfolk 1945). Shortgrass prairie, mixed-grass prairie, and shrubsteppe habitats support populations, as do weedy fallow croplands, minimum-tillage croplands, planted cover (e.g., Conservation Reserve Program [CRP] fields and Permanent Cover Program [PCP] fields), legume haylands, and pastures planted to either native or tame grasses (Cameron 1908; Shane 1972, in prep.; Wiens 1973; Creighton 1974; Maher 1974; Porter and Ryder 1974; Stewart 1975; Johnsgard 1980; Pleszczynska and Hansell 1980; Johnson 1981; Kantrud 1981; Kantrud and Kologiski 1983; Dunn 1986; Johnson and Schwartz 1993a,b; Lokemoen and Beiser 1997; McMaster and Davis 1998; Duncan and Davis in press). Rotenberry and Wiens (1980) found that abundance in parts of Colorado, Kansas, Montana, Nebraska, Oklahoma, South Dakota, Texas, and Wyoming was correlated positively with litter depth. BBS data indicated that Lark Buntings preferred areas dominated by wheatgrass (AGROPYRON SPP.), blue grama (BOUTELOUA GRACILIS), needle-and-thread (STIPA COMATA), and big sagebrush (ARTEMISIA TRIDENTATA) (Shane in prep.).

Nests on ground, in grass, under or near clump of vegetation or shrub. Nest usually in a depression. In portions of Colorado, Kansas, Minnesota, Nebraska, North Dakota, Oklahoma, South Dakota, and Texas, nested in mixed-grass and shortgrass areas and areas dominated by sagebrush (ARTEMISIA); they also used taller grass areas with scattered shrubs, weedy edges, retired cropland, and alfalfa (MEDICAGO SATIVA) or clover (TRIFOLIUM) fields (Johnsgard 1979). Often build nests under protective vegetation, including forbs, tall grasses, low shrubs, plains prickly pear cactus (OPUNTIA POLYACANTHA), and yucca (YUCCA GLAUCA) (Whittle 1922; Woolfolk 1945; Baumgarten 1968; Baldwin et al. 1969; Creighton 1971; Shane 1972, in prep.; Stewart 1975; Wilson 1976; Pleszczynska 1977; Johnsgard 1979). Vegetative cover may provide protection from inclement weather and from depredation (Woolfolk 1945, Baumgarten 1968, Baldwin et al. 1969, Strong 1971, Creighton 1974, Pleszczynka 1977, With and Webb 1993), as well as provide open views in one or more directions (Baldwin et al. 1969, Shane 1972, Wilson 1976).

The presence of protective cover may be a major factor in reproductive success (Strong 1971, Pleszczynska 1977). In Kansas, oriented nests adjacent to protective vegetation that allowed access to morning sunlight, adequate ventilation, and afternoon shade (Shane 1974). In Colorado shortgrass pasture, the majority of nests were placed on the northern side of vegetation (With and Webb 1993). In other studies, nests were placed on the east or southeast side of protective vegetation (Baldwin et al. 1969, Creighton 1971, Pleszczynska 1977).

Time of season may influence selection of nesting habitat. In Kansas, used stubble fields for nesting during the early part of the breeding season, and later nested in native grassland on hillsides with sparser vegetation (Wilson 1976).

Mean height of vegetation around ground nests in Colorado (Baldwin et al. 1969), Kansas (Shane 1972), and Utah (Johnson 1981) ranged from 15 to 28 centimeters. In sand-sagebrush (ARTEMISIA FILIFOLIA) grasslands in Kansas, areas in which nests were found had fewer and shorter sand sagebrush plants and had higher percent forb cover (mean of 48.2%) than areas where nests were not present (Shane 1972). Successful nests (those with young present 6 days after hatching) were adjacent to tall (mean of 30.6 centimeters) overall vegetation and tall (mean of 41.9 centimeters) forbs.

NON-BREEDING: in migration and winter also in cultivated lands, brushy areas and desert (AOU 1998).

Ecology

Territory size in northcentral Colorado was 0.5-1.1 hectares (Wiens 1970, 1971; Finch et al. 1987). In South Dakota, territory size averaged about 0.2 hectares in idle mixed-grass and alfalfa fields (Pleszczynska 1977). However, territory size may be difficult to measure because unmated males will display within other males' territories (Finch et al. 1987).

Reproduction

Breeding begins mid- to late May (Harrison 1978). Clutch size is 3-7 (usually 4-5). Incubation lasts 12 days (Terres 1980). Nestlings are altricial and downy; young are tended by both adults. Gregarious; may nest only 30 meters apart (Terres 1980).
Terrestrial Habitats
Shrubland/chaparralGrassland/herbaceousDesertCropland/hedgerow
Other Nations (2)
United StatesN5B,N5N
ProvinceRankNative
CaliforniaSNRNYes
MontanaS4BYes
WashingtonSNAYes
MinnesotaSHB,SNRMYes
OklahomaS1Yes
TexasS4BYes
ArizonaS1B,S5NYes
New MexicoS3B,S5NYes
IdahoS1BYes
North DakotaSNRBYes
NebraskaS4Yes
New YorkSNRNYes
South DakotaS5BYes
WyomingS4BYes
ColoradoS4Yes
KansasS5BYes
UtahS2BYes
CanadaN2B
ProvinceRankNative
SaskatchewanS2BYes
OntarioSNAYes
ManitobaS1BYes
AlbertaS2BYes
Roadless Areas (57)
Arizona (4)
AreaForestAcres
ChiricahuaCoronado National Forest76,876
Lime CreekTonto National Forest42,568
PinalenoCoronado National Forest130,920
WhetstoneCoronado National Forest20,728
California (1)
AreaForestAcres
Fox MountainLos Padres National Forest52,072
Colorado (1)
AreaForestAcres
Dome PeakRoutt NF35,716
Montana (6)
AreaForestAcres
King MountainCuster National Forest12,134
King MountainCuster National Forest12,134
Mt. Gmt Area HCuster National Forest1,335
Mt. Gmt Area HCuster National Forest1,335
Tongue River BreaksCuster National Forest17,481
Tongue River BreaksCuster National Forest17,481
New Mexico (3)
AreaForestAcres
Candian RiverCibola National Forest7,149
Little Dog And Pup CanyonsLincoln National Forest25,412
Peloncillo (NM)Coronado National Forest43,339
North Dakota (26)
AreaForestAcres
BlacktailDakota Prairie Grasslands8,620
BlacktailDakota Prairie Grasslands8,620
Bullion ButteDakota Prairie Grasslands19,877
Bullion ButteDakota Prairie Grasslands19,877
Collar / Bennett - CottonwoodDakota Prairie Grasslands19,697
Collar / Bennett - CottonwoodDakota Prairie Grasslands19,697
Dawsons WaterholeDakota Prairie Grasslands6,087
Easy HillDakota Prairie Grasslands7,344
Easy HillDakota Prairie Grasslands7,344
Kinley PlateauDakota Prairie Grasslands16,900
Kinley PlateauDakota Prairie Grasslands16,900
Lone ButteDakota Prairie Grasslands11,465
Lone ButteDakota Prairie Grasslands11,465
Ponderosa PineDakota Prairie Grasslands7,471
Ponderosa PineDakota Prairie Grasslands7,471
Scairt WomanDakota Prairie Grasslands6,099
Scairt WomanDakota Prairie Grasslands6,099
Strom - HansonDakota Prairie Grasslands18,957
Strom - HansonDakota Prairie Grasslands18,957
Tracy MountainDakota Prairie Grasslands9,756
Tracy MountainDakota Prairie Grasslands9,756
Twin ButtesDakota Prairie Grasslands13,492
Twin ButtesDakota Prairie Grasslands13,492
WannaganDakota Prairie Grasslands6,026
WannaganDakota Prairie Grasslands6,026
WannaganDakota Prairie Grasslands6,026
South Dakota (6)
AreaForestAcres
First Black CanyonBuffalo Gap National Grassland4,965
First Black CanyonBuffalo Gap National Grassland4,965
Jim Wilson CanyonBuffalo Gap National Grassland6,024
Jim Wilson CanyonBuffalo Gap National Grassland6,024
South ForkDakota Prairie Grasslands7,653
South ForkDakota Prairie Grasslands7,653
Utah (2)
AreaForestAcres
Clarkston Mtn.Caribou National Forest7,099
WellsvilleWasatch-Cache National Forest1,717
Wyoming (8)
AreaForestAcres
Duck CreekThunder Basin National Grassland12,343
Duck CreekThunder Basin National Grassland12,343
Little BighornBighorn National Forest133,949
Little BighornBighorn National Forest133,949
Sand CreekBlack Hills National Forest7,950
Sand CreekBlack Hills National Forest7,950
Walker PrairieBighorn National Forest62,434
Walker PrairieBighorn National Forest62,434
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