Ammodramus savannarum

(Gmelin, 1789)

Grasshopper Sparrow

G5Secure Found in 47 roadless areas NatureServe Explorer →
G5SecureGlobal Rank
Least concernIUCN
PSESA Status
Grasshopper Sparrow (Ammodramus savannarum). © Trevor Ambrico; Cornell Lab of Ornithology | Macaulay Library.
© Trevor Ambrico; Cornell Lab of Ornithology | Macaulay Library
Grasshopper Sparrow (Ammodramus savannarum). © Ryan Sanderson; Cornell Lab of Ornithology | Macaulay Library.
© Ryan Sanderson; Cornell Lab of Ornithology | Macaulay Library
Grasshopper Sparrow (Ammodramus savannarum). © Brad Imhoff; Cornell Lab of Ornithology | Macaulay Library.
© Brad Imhoff; Cornell Lab of Ornithology | Macaulay Library
Grasshopper Sparrow (Ammodramus savannarum). © Luke Seitz; Cornell Lab of Ornithology | Macaulay Library.
© Luke Seitz; Cornell Lab of Ornithology | Macaulay Library
Grasshopper Sparrow (Ammodramus savannarum). © Matt Mason; Cornell Lab of Ornithology | Macaulay Library.
© Matt Mason; Cornell Lab of Ornithology | Macaulay Library
Grasshopper Sparrow (Ammodramus savannarum). © Dorian Anderson; Cornell Lab of Ornithology | Macaulay Library.
© Dorian Anderson; Cornell Lab of Ornithology | Macaulay Library
Identity
Unique IDELEMENT_GLOBAL.2.100347
Element CodeABPBXA0020
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVertebrate Animal
IUCNLeast concern
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomAnimalia
PhylumCraniata
ClassAves
OrderPasseriformes
FamilyPasserellidae
GenusAmmodramus
USESAPS
COSEWICPS:SC
Other Common Names
Bruant sauterelle (FR) Gorrión Chapulín (ES) grasshopper sparrow (EN)
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
See Zink and Avise (1990) for relationships within genus Ammodramus (based on analysis of mtDNA and allozymes); Ammodramus (sensu AOU 1983) possibly is not monophyletic; previous generic limits (AOU 1957) seem better to reflect phylogeny than current taxonomy.
Conservation Status
Rank MethodExpertise without calculation
Review Date2016-04-06
Change Date1996-12-04
Edition Date1996-02-21
Range Extent>2,500,000 square km (greater than 1,000,000 square miles)
Rank Reasons
Large range, extending from southern Canada to northern South America; significant population declines in North America and probably elsewhere, due to loss, degradation, and incompatible management of grassland habitat.
Range Extent Comments
BREEDING: eastern Washington, southern British Columbia, southern Alberta, southern Saskatchewan, southern Manitoba, southern Ontario, southwestern Quebec, northern Vermont, New Hampshire, and southern Maine south to southern California, central Nevada, northern Utah, eastern Colorado, eastern new Mexico, northern Texas, Arkansas, northern Mississippi, Alabama, Georgia, North Carolina, and southeastern Virginia; from southeastern Arizona, southwestern New Mexico, and southern Texas south to northern Sonora and northern Chihuahua; and in central Florida (Vickery 1996, AOU 1998). The main population is in the Great Plains, from North Dakota south to northern Texas, and east to Illinois (Johnson et al. 1998). NON-BREEDING: central California, southern Arizona, southern New Mexico, Texas, central Missouri, Tennessee, and North Carolina south through Mexico and Central America to northern Costa Rica and in the Bahamas and Cuba (Vickery 1996, AOU 1998). RESIDENT: Veracruz, Chiapas, Guatemala, Belize, Honduras, northwestern Costa Rica, and Panama; Jamaica, Hispaniola, and Puerto Rico; and in western Colombia, western Ecuador, and the Netherlands Antilles (Vickery 1996, AOU 1998).
Threat Impact Comments
Decline in several areas in the eastern U.S. and southeastern Canada evidently is due to loss of habitat to cultivation, urban sprawl, and reforestation, compounded by losses incurred as a result of mowing of habitat and subsequent increased predation (Ehrlich et al. 1992). In Arizona, grazing decreased populations by removing bunchgrass, whereas in West Virginia, Florida, North Dakota, and Missouri moderate grazing did not cause a decline and (usually) increased grasshopper sparrow density (created areas of favorable short vegetation) (see Smith and Smith 1992). Endangered Florida population (subspecies FLORIDANUS) has declined due to conversion of prairie to pasture. South American populations may be threatened by overgrazing and conversion of natural grasslands in limited range (Ridgely and Tudor 1989). Levels of brood parasitism by Brown-headed Cowbird (MOLOTHRUS ATER) generally low (Vickery 1996). In Michigan, no cases of brood parasitism were found (George 1952).
Ecology & Habitat

Description

A chunky sparrow with a short narrow tail, flat head, buffy breast and sides (adults usually without obvious streaking), dark crown with a pale central stripe, narrow white eye ring, and (in most adults) a yellow-orange spot in front of the eye; juveniles have pale buff breast and sides, streaked with brown; average length 13 cm (NGS 1983).

Diagnostic Characteristics

Differs from many other sparrows in having both an unstreaked buffy breast (adults) and a short tail. Differs from Le Conte's sparrow (AMMODRAMUS LECONTEII) in lacking a buffy-orange eyebrow and blue-gray ear patch. Adult differs from juvenile Henslow's sparrow (AMMODRAMUS HENSLOWII) in lacking a yellowish-olive central stripe on the crown. Juvenile lacks the olive and russet tones of the otherwise similar adult Henslow's sparrow.

Habitat

BREEDING: Prefer grasslands of intermediate height and are often associated with clumped vegetation interspersed with patches of bare ground (Bent 1968, Blankespoor 1980, Vickery 1996). Other habitat requirements include moderately deep litter and sparse coverage of woody vegetation (Smith 1963, Bent 1968, Wiens 1969, Kahl et al. 1985, Arnold and Higgins 1986). Breed in both native and tame grassland vegetation (Kendeigh 1941, Birkenholz 1973, Whitmore 1979, Sample 1989, Wilson and Belcher 1989, Madden 1996), including native prairie, Conservation Reserve Program fields, pasture, hayland, airports, and reclaimed surface mines (Wiens 1973, Ducey and Miller 1980, Whitmore 1980, Kantrud 1981, Renken 1983, Renken and Dinsmore 1987, Bollinger 1988, Frawley and Best 1991, Johnson and Schwartz 1993, Berthelsen and Smith 1995, Hull et al. 1996, Patterson and Best 1996, Delisle and Savidge 1997, Prescott 1997). Occasionally inhabit cropland, such as corn and oats, but at a fraction of the densities found in grassland habitats (Smith 1963, Smith 1968, Ducey and Miller 1980, Basore et al. 1986, Faanes and Lingle 1995, Best et al. 1997).

In South Dakota, preferred large patches of appropriate grassland habitat; in landscapes not dominated by grassland, occupancy rate of patches greater than 50 hectares was 67%, whereas occupancy rate of smaller patches was only 12%. The preference still existed in landscapes dominated by grasslands, although the difference was not as dramatic: 50% in large patches, 40% in small patches (Bakker et al. 2002).

NON-BREEDING: Grass-dominated fields, native prairie (Florida), and grazed pastures (Mexico and Belize) (Vickery 1996).

Ecology

Average territory size is small (< 2 ha) (George 1952, Wiens 1969, Ducey and Miller 1980).

Reproduction

Arrive on the breeding grounds in mid-April and depart for the wintering grounds in mid-September (George 1952, Bent 1968, Smith 1968, Stewart 1975, Vickery 1996). In Saskatchewan and Manitoba, they arrive later (mid-May) and leave earlier (August) (Knapton 1979). Throughout most of their range, are able to produce two broods, one in late May and a second in early July (George 1952, Smith 1968, Vickery 1996). However, in the northern part of its range, one brood is probably most common; in Maine, no territories showed evidence of successfully fledging two broods and double-broodedness in Wisconsin is uncommon (Vickery et al. 1992, Wiens 1969). Frequently renest after nest failure, and if unsuccessful in previous attempts, may renest 3-4 times during the breeding season (Vickery 1996).
Terrestrial Habitats
SavannaGrassland/herbaceousOld field
Other Nations (2)
CanadaN4B
ProvinceRankNative
SaskatchewanS4BYes
ManitobaS2BYes
British ColumbiaS1BYes
OntarioS4BYes
AlbertaS4BYes
QuebecSNAYes
United StatesN5B,N5N
ProvinceRankNative
NebraskaS4Yes
DelawareS4BYes
New HampshireS2BYes
MarylandS4BYes
MaineS1BYes
IllinoisS5Yes
WyomingS4Yes
New MexicoS3B,S3NYes
MontanaS4BYes
LouisianaS1B,S3NYes
UtahS2BYes
MissouriS3Yes
PennsylvaniaS3B,S3MYes
IdahoS3BYes
TennesseeS4Yes
KentuckyS4BYes
MichiganS4Yes
New JerseyS2B,S3NYes
CaliforniaS3Yes
WashingtonS3BYes
MassachusettsS3BYes
ConnecticutS1BYes
OklahomaSNRBYes
District of ColumbiaS3NYes
FloridaSNRNYes
OregonS2BYes
South CarolinaS3Yes
ColoradoS3BYes
MinnesotaSNRBYes
West VirginiaS3BYes
AlabamaS3Yes
OhioS5Yes
KansasS5BYes
Navajo NationSNAYes
TexasS3BYes
MississippiS3B,S3NYes
VirginiaS4Yes
ArkansasS3BYes
New YorkS3BYes
North CarolinaS3B,S1NYes
South DakotaS4BYes
WisconsinS2BYes
IndianaS4BYes
Rhode IslandS1B,S1NYes
IowaS4B,S4NYes
VermontS1BYes
ArizonaS3Yes
North DakotaSNRBYes
NevadaSUYes
GeorgiaS3Yes
Roadless Areas (47)
Arkansas (1)
AreaForestAcres
East ForkOzark-St. Francis National Forest13,037
Florida (1)
AreaForestAcres
SavannahApalachicola National Forest1,927
Illinois (4)
AreaForestAcres
Burke BranchShawnee National Forest6,231
Clear SpringsShawnee National Forest11
Eagle CreekShawnee National Forest38
Ripple HollowShawnee National Forest3,788
Missouri (1)
AreaForestAcres
Big Creek Rare II Study AreaMark Twain National Forest9,277
Montana (5)
AreaForestAcres
Freezeout MountainBeaverhead-Deerlodge National Forest97,305
King MountainCuster National Forest12,134
Mt. Gmt Area HCuster National Forest1,335
North AbsarokaCuster National Forest21,063
Tongue River BreaksCuster National Forest17,481
New Mexico (1)
AreaForestAcres
Peloncillo (NM)Coronado National Forest43,339
North Dakota (16)
AreaForestAcres
BlacktailDakota Prairie Grasslands8,620
Bullion ButteDakota Prairie Grasslands19,877
Collar / Bennett - CottonwoodDakota Prairie Grasslands19,697
DelamereDakota Prairie Grasslands5,087
DurlerDakota Prairie Grasslands12,464
Easy HillDakota Prairie Grasslands7,344
Kinley PlateauDakota Prairie Grasslands16,900
Lone ButteDakota Prairie Grasslands11,465
Ponderosa PineDakota Prairie Grasslands7,471
Scairt WomanDakota Prairie Grasslands6,099
SheyenneDakota Prairie Grasslands14,537
Tracy MountainDakota Prairie Grasslands9,756
Twin ButtesDakota Prairie Grasslands13,492
VenloDakota Prairie Grasslands5,317
WannaganDakota Prairie Grasslands6,026
WannaganDakota Prairie Grasslands6,026
South Carolina (1)
AreaForestAcres
Wambaw ExtFrancis Marion National Forest527
South Dakota (5)
AreaForestAcres
Beaver ParkBlack Hills National Forest5,010
First Black CanyonBuffalo Gap National Grassland4,965
Jim Wilson CanyonBuffalo Gap National Grassland6,024
South ForkDakota Prairie Grasslands7,653
Twin Butte CreekDakota Prairie Grasslands6,700
Utah (2)
AreaForestAcres
Clarkston Mtn.Caribou National Forest7,099
Stansbury MountainsWasatch-Cache National Forest39,696
Virginia (1)
AreaForestAcres
Bear CreekJefferson National Forest18,274
West Virginia (2)
AreaForestAcres
Little MountainMonongahela National Forest8,172
Seneca CreekMonongahela National Forest22,287
Wyoming (7)
AreaForestAcres
Duck CreekThunder Basin National Grassland12,343
Pacific Creek - Blackrock CreekBridger-Teton National Forest24,658
Phillips RidgeBridger-Teton National Forest10,108
Rock CreekBighorn National Forest48,657
Sand CreekBlack Hills National Forest7,950
Spread Creek - Gros Ventre RiverBridger-Teton National Forest166,097
Walker PrairieBighorn National Forest62,434
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