Astur cooperii

(Bonaparte, 1828)

Cooper's Hawk

G5Secure Found in 298 roadless areas NatureServe Explorer →
G5SecureGlobal Rank
Least concernIUCN
Identity
Unique IDELEMENT_GLOBAL.2.100417
Element CodeABNKC12040
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVertebrate Animal
IUCNLeast concern
CITESAppendix II
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomAnimalia
PhylumCraniata
ClassAves
OrderAccipitriformes
FamilyAccipitridae
GenusAstur
Synonyms
Accipiter cooperii(Bonaparte, 1828)
Other Common Names
Cooper's hawk (EN) Épervier de Cooper (FR) Gavilán de Cooper (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/.
Taxonomic Comments
Formerly (AOU 1983, 1998) included in Accipiter, but genetic data (Catanach et al. 2024) show that Accipiter sensu lato did not form a monophyletic group, and that the species now placed in Astur are not closely related to true Accipiter (AOS 2025).

Constitutes a superspecies with A. gundlachi and A. bicolor (AOU 1998). See Whaley and White (1994) for information on geographic variation.
Conservation Status
Rank MethodExpertise without calculation
Review Date2016-04-06
Change Date1996-11-26
Edition Date1995-05-04
Edition AuthorsSoule, J., C. Sahley, and G. Hammerson; revised by S. Cannings
Range Extent>2,500,000 square km (greater than 1,000,000 square miles)
Number of Occurrences81 to >300
Rank Reasons
Large breeding range throughout the forested portions of the contiguous U.S., southern Canada, and northern Mexico; populations have stabilized or are increasing in some parts of range, but the species has not fully recovered from the drastic decline of the period 1940-1970+ throughout much of the eastern part of the range; reasons for this lack of recovery are unknown; potentially threatened by the use of organochlorine biocides in Central America and locally by habitat loss.
Range Extent Comments
BREEDING: southern British Columbia across southern Canada to central Saskatchewan, southern Quebec, and the Maritime Provinces, south to Baja California, northern Mexico (Chihuahua, Nuevo Leon), and southeastern U.S., though basically absent from the western Great Plains (AOU 1983, Rosenfield and Bielefeldt 1993). NON-BREEDING: Washington, Rocky Mountain states, southern Minnesota, southern Ontario, and New England south to Middle America (commonly to Honduras, rarely but regularly to Costa Rica, casually to Colombia) (AOU 1983, Stiles and Skutch 1989, Johnsgard 1990, Rosenfield and Bielefeldt 1993).
Occurrences Comments
Numerous occurrences but precise number is unknown.
Threat Impact Comments
Major threats are pesticide use (especially chlorinated hydrocarbons used in Central America) and loss of habitat. Sometimes shot by hunters and farmers, or nests are robbed by falconers. PESTICIDES: The principal cause for the population crash since the 1950s has been nesting failure due to DDT poisoning. A severe decline in the eastern portion of the range was first noted in counts of migrating populations during the 1960s (Peterson 1964, Spofford 1969, Nagy 1977). More direct evidence for the role of pesticide poisoning includes observations of drastically reduced fledging success rates (Schriver 1969), reductions in egg-shell thickness (Anderson and Hickey 1972), and a strong correlation between egg-shell thinning and residues of DDT and its metabolites found in egg tissues (Snyder et al. 1973). Fledging success rates dropped from 3.53 young per successful nest prior to 1946 to 2.67 during 1946-1967 (Pattee et al. 1985). Despite the ban on DDT that has been in effect in the U.S. since the 1970s, numbers have failed to rebound to former levels in the eastern U.S. (Robbins et al. 1986). This failure to regain their former abundance may be due to the continued use of the pesticide in Central America, where at least part of the species spends the winter. An adult was found dying of acute DDT poisoning as late as 1980 (Prouty et al. 1982). Many prey species consumed are neotropical migrants, and probably continue to be contaminated by DDT during their winters south of the United States. Illegal use of DDT in this country has also been proposed as a possible cause. It is, however, still unclear to what extent DDT or other organochloride pesticides are contributing to the slow rebound of this species. In a study of contaminants in eggs from Connecticut, Maryland, Michigan, Pennsylvania, and Wisconsin, only one egg from Connecticut contained levels of DDE, a break-down product of DDT, above the level hypothesized to cause reproductive failure. The data suggested that egg shell thinning was not a significant problem in these states in 1980, although at least two individual birds had thin-shelled eggs containing high residues. Other contaminants, including other pesticides, PCB, lead and mercury, also showed up at levels below hypothesized impact levels (Pattee et al. 1985). In addition to the hazards of long-lived, bioconcentrating organochlorine pesticides such as DDT, the more widely used and acutely toxic organophosphate pesticides may pose a threat. Two reports of poisoning were made in the 1980s (Rosenfield et al. 1991). So little effort has been put into monitoring this type of poisoning in dead raptors, that it is impossible to assess the magnitude of this threat. HABITAT LOSS: Deforestation has also been cited as a current threat and may become increasingly important. Required habitat (dense forest isolated from human activities or narrow riverine forest corridors) is under pressure for forest product harvest and development (Snyder 1978, Herron 1985, Weir 1987). Habitat loss was cited as the primary threat to raptor populations in a recent survey of U.S. state agencies by the National Wildlife Federation (Rosenfield et al. 1991). Rosenfield et al. (1991), however, concluded that breeding habitat does not appear to be limiting for this species in Wisconsin. They found that hawks often utilized pine plantations for nesting, and in fact may achieve their highest nesting densities in such habitat. Similarly, Wiggers and Kritz (1991) found hawks nesting in rather small stands (an average of 4.1 hectares) of young pines. If this habitat use is common in Wisconsin, it is probably also the case for neighboring Minnesota and Michigan, and suggests that habitat may not be limiting in the Great Lakes region. Also, reports that this species has been moving in to urban/suburban areas also raise questions about the importance of habitat loss (A. Stewart, pers. comm.). Other threats include continued persecution by hunters or irate farmers, and the collection of live birds by falconers. Although bounty hunting was once a major mortality factor for this species, that threat has been curtailed by the legal protection now given all birds of prey. Apart from humans, the greatest enemies are probably other raptors. Great horned owls (BUBO VIRGINIANUS) are known predators (Terres 1980). Goshawks (ACCIPITER GENTILIS) are competitors (Reynolds et al. 1982). Nestlings and eggs are also preyed upon by raccoons (PROCYON LOTOR), crows (CORVUS spp.), and possibly snakes (Schriver 1969, Campbell et al 1990).
Ecology & Habitat

Description

A medium-size diurnal raptor with rounded wings, a long brown/black banded tail (often rounded at the end), and a hooked bill; adult is mainly gray/brown above, barred rusty brown below, with strong contrast between dark crown and paler nape and back; immature is paler, with brown upperparts, dark-streaked whitish or buffy underparts, and white undertail coverts. Average length 36-51 centimeters, wingspan 74-94 centimeters; females average larger than males (NGS 1983).

Diagnostic Characteristics

Differs from sharp-shinned hawk (Accipiter striatus) by longer, more rounded tail that has a wider white terminal band; larger head; and (in adult) stronger contrast between the dark crown and paler nape and back. Differs from goshawk (Accipiter gentilis) in smaller size (average length 36-51 centimeters vs. 53-66 centimeters), lack of conspicuous pale eyebrow, less conspicuous white undertail coverts, broader white tip on tail, and proportionately longer tail and shorter wings (NGS 1983).

Habitat

BREEDING: Primarily mature forest, either broadleaf or coniferous, mostly the former; also open woodland and forest edge (AOU 1983, Rosenfield and Bielefeldt 1993). Nests in both pine and hardwood groves, and riparian cottonwoods and sycamores in the West; Douglas-fir in northeastern Oregon. Usually builds new nest on horizontal limb near trunk or in crotch, 6-18 meters above ground; may modify old one or squirrel or crow nest. Campbell et al. (1990) reported one instance of a nest being reused for six consecutive years in British Columbia. Rosenfield and Bielefeldt (1992) found that nesting areas were irregularly reused by the same or different adults in subsequent years.

In Nevada, Cooper's Hawks were frequently sighted in montane forests and pinyon-juniper woodlands, but riparian habitat was recorded as well (Floyd et al. 2007). In California, this species is seldom found in areas without dense tree stands, or patchy woodland habitat. It nests in deciduous trees in crotches 3-23 m (10-80 ft), but usually 6-15 m (20-50 ft), above the ground. It also nests in conifers on horizontal branches, in the main crotch, often just below the lowest live limbs. They usually nest in second-growth conifer stands, or in deciduous riparian areas, usually near streams. They frequent landscapes where wooded areas occur in patches and groves (Beebe 1974) and often use patchy woodlands and edges with snags for perching (CDFG 2011). Cooper's Hawks tend to use older, taller, and less dense woodlots than Sharp-shinned Hawks in California (Rosenfield and Bielefeldt 1993). In southern California, Cooper's Hawk generally favors extensive riparian bottomlands (Garrett and Dunn 1981). In Oregon, nests were in stands of conifers that included older and taller trees, a deeper crown, and a more open understory than a typical single-story Sharp-shinned Hawk nest stand (Reynolds et al. 1982). See also Grindrod and Walton Cooper's Hawk account at http://www.blm.gov/ca/pdfs/cdd_pdfs/coha.pdf.

Generally is an inhabitant of deep woods, utilizing thick cover both for nesting and hunting. Openings, especially where hedgerows or windbreaks offer shelter for prey species, may also be used when foraging. Johnsgard (1990) states that Cooper's are less fussy about the forest type than sharp-shins, and are more often "associated with deciduous and mixed forests and open woodland habitats such as woodlots, riparian woodlands, semiarid woodlands of the southwest, and other areas where the woodlands tend to occur in patches and groves or as spaced trees."

In the Northwest and Northeast, conifers are used for nesting (Bent 1937, Reynolds et al. 1982), but elsewhere the preference is for hardwoods (Brown and Amadon 1968). In the Northwest a preference may exist also for the cooler microclimates offered by north and east facing slopes (Reynolds et al. 1982). In that area, the Cooper's hawk is typically found in middle-aged stands, 50 - 60 years in age, whereas the sharp-shin prefers younger stands and the goshawk older ones (Reynolds et al. 1982). That difference might express competitive displacement, because in the East, where the goshawk rarely nests, the Cooper's hawk prefers mature stands (Brown and Amadon 1968).

In some areas the species seems to require large tracts of forests and to avoid human contact, in others they may use small forest tracts, (e.g., British Columbia and Nevada), woodlots (e.g., Ohio) or urban/suburban areas where they seem tolerant of human activities (e.g., British Columbia, Utah, Wisconsin, Indiana) (Hennessy 1978, Herron et al. 1985, Campbell et al 1990, Peterjohn and Rice 1991, Rosenfield et al. 1991).

In New Jersey-New York, nested mostly in mixed deciduous-coniferous forest with eastern hemlock the dominant coniferous species at many sites. Tended to nest in areas with relatively large basal area and more canopy cover. Nests located in live overstory trees (43% conifers), typically within the canopy, and always in dense forest but commonly near wetland openings or source of water, on level ground or lower slopes, typically several hundred meters from paved roads (but sometimes within 100 meters or less). Avoided southern exposures (Reynolds et al. 1982, Bosakowski et al. 1992).

A recent study in Missouri documented numerous Cooper's Hawks nesting in young pine plantations in essentially the same habitat as sharp-shins. Also found that trees with deformed crowns were preferred (Wiggers and Kritz 1991). Rosenfield et al. (1991) report that pine plantations are important habitat for breeding Cooper's hawks throughout the Midwest, and particularly in Wisconsin. See Kennedy (1988) for details on nesting habitat in New Mexico.

NON-BREEDING: Migrates mostly along ridges and coastlines (NGS 1983). Winter habitat is much the same as in the nesting season, although open woodlands and fields may be utilized to a greater extent.

Ecology

Few data on population densities exist. Craighead and Craighead (1956) found 1554 hectares per pair in 1947-1948 in Michigan. In Maryland a density estimate of 200 hectares per pair was calculated by Stewart and Robbins (1958). Rosenfield et al. (1991) compiled nesting densities from various studies. These densities ranged from a low of 5000 hectares per pair in North Dakota in 1987, to a high of 331 hectares per pair in a pine plantation in southeastern Wisconsin in 1986.

Strongly territorial. Males vigorously defend an area 30 meters in diameter around the nest site although they may forage up to 3.2 kilometers away (Brown and Amadon 1968). Johnsgard (1990) reported home range sizes that ranged from 105 to 784 hectares (the latter was seasonal home range; daily home range was 231 hectares). Nests are typically spaced 2.4 - 5.6 kilometers apart (Brown and Amadon 1968, Reynolds and Wight 1978, Kennedy 1980, Campbell et al 1990) and not usually less than one kilometer apart (Palmer 1988). The smaller sharp-shinned hawk also appears to keep similar distances from Cooper's hawk nests (Brown and Amadon 1968, Reynolds and Wight 1978), indicating interspecific aggression probably related to competition for food. Winter range is larger. Michigan birds ranged over areas of 2.4 - 3.2 kilometers in diameter.

Dispersal range is limited. In Wisconsin, six males dispersed 4 - 35 kilometers (mean 12 kilometers) from natal site to nesting site; one female dispersed 14 kilometers (Rosenfield and Bielefeldt 1992). Hunt by a combination of still-hunting and searching flights along woodland edges and natural routes (Johnsgard 1990).

Birds following inland migration routes apparently migrate over longer distances than those following coastal routes, and tend to have longer wings and tails, creating lower "flight-surface loading." This is thought to be an adaptation to the longer flight distances, more open country, and stronger thermal updrafts encountered along the inland routes (Smith et al. 1990).

Mortality appears to be quite high during the birds' first winter, approaching 78% as opposed to only 34% per year for the adults 2 to 8 years old (Henny and Wight 1972). The maximum recorded lifespan is 8 years (Henny and Wight 1972). Life history traits place it intermediate for population turnover rate between the larger goshawk and smaller sharp-shinned hawk. This may partially explain the slower recovery of Cooper's from a population crash in the 1950s-1960s compared to sharp-shinned hawks (Bednarz et al. 1990).

Reproduction

The breeding season usually begins in early April and extends through May and June (Bent 1937, Brown and Amadon 1968). The annual molt begins in late June but can occur as late as October (Bent 1937). Southward migration commences in the northern states in late August, with September being the peak month; it is essentially over by November. Northward migration occurs from late February to early April (Brown and Amadon 1968).

The male does most of the nest building and occasionally some of the incubation; most of the incubation is done by the female, which seldom leaves the nest before the young have fledged (Brown and Amadon 1968). During the pre-fledging period the male provides both the female and the young with food, while both parents feed the young for up to four weeks after they leave the nest (Brown and Amadon 1968).

Only one brood is raised each year. The normal clutch is four-five eggs, with clutches of three and six being rarely observed (Bent 1937). A national average has been calculated at 3.5 eggs (Bednarz et al. 1990). Replacement clutches are laid if the first set is lost, and laying can be delayed under conditions of low food availability (Bent 1937, Snyder and Wiley 1976).

Hatching success data are limited, but in areas unaffected by DDT contamination the average hatching rate ranges from about 70% to 83% (Craighead and Craighead 1956, Johnsgard 1990), with some further reduction in the brood occurring after hatching. Normal fledging success rates range from 2.1 to 3.5 for pairs with successful nests (Craighead and Craighead 1956, Schriver 1969, Henny and Wight 1972, Reynolds and Wight 1978, Herron et al. 1985); roughly 80% of nests produce at least one fledgling (Henny and Wight 1972). In areas affected by DDT poisoning these figures were reported to be dramatically reduced.

The young fledge one month after hatching, the males leaving the nest three-four days earlier than the larger females. They remain dependent on their parents until they are eight weeks of age and have learned to forage on their own (Brown and Amadon 1968). Only about 19% of the birds breed in their first year. Most nest by the second year and continue breeding throughout the rest of their lives.
Terrestrial Habitats
Forest - HardwoodForest - ConiferForest - MixedWoodland - HardwoodWoodland - ConiferWoodland - MixedSuburban/orchard
Palustrine Habitats
Riparian
Other Nations (2)
CanadaN5B,N5N
ProvinceRankNative
ManitobaS4BYes
OntarioS4Yes
AlbertaS4B,SUNYes
New BrunswickS1BYes
QuebecS4BYes
SaskatchewanS4B,S2N,S2MYes
British ColumbiaS5Yes
Nova ScotiaS1B,SUN,SUMYes
United StatesN5B,N5N
ProvinceRankNative
WisconsinS4B,S4NYes
OhioS3Yes
LouisianaS4Yes
IowaS3BYes
VermontS3B,S3NYes
West VirginiaS3B,S4NYes
Rhode IslandS1B,S3NYes
TexasS4B,S3NYes
ConnecticutS5BYes
AlabamaS3B,S4NYes
IdahoS4Yes
MontanaS4BYes
New JerseyS4B,S4NYes
MississippiS2BYes
FloridaS3Yes
MassachusettsS4B,S5NYes
IndianaS3BYes
TennesseeS3BYes
South DakotaS3BYes
MarylandS4B,S4NYes
MissouriS3Yes
WashingtonS4B,S4NYes
District of ColumbiaS3N,SHBYes
ArkansasS1B,S3NYes
Navajo NationS4Yes
MaineS3B,S3NYes
NebraskaS5Yes
VirginiaS3B,S3NYes
CaliforniaS4Yes
OregonS4Yes
ColoradoS3B,S4NYes
DelawareS1BYes
NevadaS5Yes
New HampshireS2BYes
MinnesotaSNRB,SNRNYes
ArizonaS4Yes
KansasS3B,S4NYes
North DakotaSUYes
New YorkS4Yes
IllinoisS3Yes
New MexicoS4B,S4NYes
MichiganS4Yes
KentuckyS4B,S4NYes
North CarolinaS3B,S4NYes
OklahomaS2Yes
South CarolinaS3Yes
UtahS4B,S3NYes
PennsylvaniaS5BYes
WyomingS4Yes
GeorgiaS3Yes
Roadless Areas (298)
Arizona (22)
AreaForestAcres
Barbershop CanyonCoconino National Forest1,311
Black CanyonPrescott National Forest10,683
BoulderTonto National Forest40,359
Butterfly Roadless AreaCoronado National Forest42,296
Catalina St. Pk. Roadless AreaCoronado National Forest951
Cdo WsaCoronado National Forest1,955
ChiricahuaCoronado National Forest76,876
East Clear CreekCoconino National Forest1,613
GaliuroCoronado National Forest28,333
GoldfieldTonto National Forest15,257
Hell HoleApache-Sitgreaves National Forests15,512
Lime CreekTonto National Forest42,568
MazatzalTonto National Forest16,942
Middle Dragoon RoadlessCoronado National Forest10,543
Middle Romero WSRCoronado National Forest60
Oracle RoadlessCoronado National Forest22,365
PinalenoCoronado National Forest130,920
Santa TeresaCoronado National Forest8,929
Sierra Ancha Wilderness ContiguousTonto National Forest7,787
TumacacoriCoronado National Forest44,594
Upper Romero WsrCoronado National Forest150
WhetstoneCoronado National Forest20,728
California (101)
AreaForestAcres
AntimonyLos Padres National Forest40,911
Arroyo SecoAngeles National Forest4,703
Barker ValleyCleveland National Forest11,940
Bell MeadowStanislaus National Forest7,968
Benton RangeInyo National Forest9,637
Birch CreekInyo National Forest28,816
Black ButteMendocino National Forest15,461
Black CanyonInyo National Forest32,421
Cactus Springs BSan Bernardino National Forest3,106
CalienteCleveland National Forest5,953
CamuesaLos Padres National Forest8,209
Castle Crags AShasta-Trinity National Forest113
Castle Crags BShasta-Trinity National Forest1,619
Castle PeakTahoe National Forest14,974
ChannellSequoia National Forest45,429
ChicoSequoia National Forest39,836
City CreekSan Bernardino National Forest9,997
ColdwaterCleveland National Forest8,402
Crystal CreekSan Bernardino National Forest6,783
Cucamonga AAngeles National Forest1,249
Cucamonga BSan Bernardino National Forest11,933
Cucamonga CSan Bernardino National Forest4,106
Cutca ValleyCleveland National Forest14,530
CuyamaLos Padres National Forest19,631
DardanellesEldorado National Forest8,110
Deep CreekSan Bernardino National Forest23,869
Dexter CanyonInyo National Forest17,053
Dry LakesLos Padres National Forest17,043
Eagle PeakCleveland National Forest6,481
East YubaTahoe National Forest17,968
EbbettsHumboldt-Toiyabe National Forest255
Excelsior (CA)Inyo National Forest45,607
Fish CanyonAngeles National Forest29,886
Fox MountainLos Padres National Forest52,072
Glass MountainInyo National Forest52,867
Granite ChiefTahoe National Forest6,546
Granite PeakSan Bernardino National Forest450
Greenhorn CreekSequoia National Forest28,226
Grizzly PeakPlumas National Forest6,222
Hall Natural AreaInyo National Forest5,236
Heart LakeLassen National Forest9,349
Heartbreak RidgeSan Bernardino National Forest4,455
Hixon FlatSan Bernardino National Forest8,095
Hoover - Emma LakeHumboldt-Toiyabe National Forest1,007
Hoover - Mt.olsenHumboldt-Toiyabe National Forest624
Hoover - NorthHumboldt-Toiyabe National Forest1,574
Hoover - Virginia LksHumboldt-Toiyabe National Forest5,050
Horse Creek RidgeSan Bernardino National Forest8,969
Horse Mdw.Inyo National Forest5,687
HortonInyo National Forest5,717
Jennie LakeSequoia National Forest2,388
LaddCleveland National Forest5,300
LavasModoc National Forest25,864
Log Cabin SaddlebagInyo National Forest15,165
Lpoor CanyonLos Padres National Forest13,762
Magic MountainAngeles National Forest15,542
Malduce BuckhornLos Padres National Forest14,177
MatilijaLos Padres National Forest5,218
Middle ForkPlumas National Forest29,278
Middle YubaTahoe National Forest7,379
Mill CreekSequoia National Forest27,643
Mill PeakSan Bernardino National Forest7,884
MonoLos Padres National Forest28,141
Mt. JacksonHumboldt-Toiyabe National Forest20,721
Mt. EddyShasta-Trinity National Forest7,232
Mt. RebaStanislaus National Forest3,869
No NameCleveland National Forest4,897
NordhoffLos Padres National Forest12,031
PaiuteInyo National Forest58,712
Pine CreekCleveland National Forest503
Pleasant ViewAngeles National Forest26,395
PyramidEldorado National Forest24,347
Pyramid Peak BSan Bernardino National Forest7,194
QuatalLos Padres National Forest7,253
Raymond PeakStanislaus National Forest3,646
Raywood Flat BSan Bernardino National Forest11,373
Red MountainAngeles National Forest8,034
Rouse HillSan Bernardino National Forest13,745
San DimasAngeles National Forest7,160
San SevaineSan Bernardino National Forest6,866
Santa CruzLos Padres National Forest21,182
Sawmill - BadlandsLos Padres National Forest51,362
Sespe - FrazierLos Padres National Forest106,910
Sheep MountainAngeles National Forest21,098
SherwinInyo National Forest3,140
Sill HillCleveland National Forest5,294
South SierraSequoia National Forest8,008
South SierraInyo National Forest41,853
Strawberry PeakAngeles National Forest7,245
SugarloafSan Bernardino National Forest8,206
TequepisLos Padres National Forest9,080
TinemahaInyo National Forest27,060
Tioga LakeInyo National Forest829
TrabucoCleveland National Forest23,341
Tragedy - Elephants BackEldorado National Forest20,866
UnderwoodSix Rivers National Forest6,591
Wheeler RidgeInyo National Forest15,744
White LedgeLos Padres National Forest18,632
WildhorseCleveland National Forest1,483
Wonoga Pk.Inyo National Forest11,272
WoolstaffSequoia National Forest41,445
Colorado (5)
AreaForestAcres
Comanche Peak Adjacent AreaArapaho & Roosevelt NFs44,158
Dome PeakRoutt NF35,716
HermosaSan Juan NF148,103
Long ParkRoutt NF42,100
Pole Mountain / Finger MesaRio Grande NF43,863
Idaho (6)
AreaForestAcres
Bear CreekCaribou-Targhee National Forest118,582
Borah PeakSalmon-Challis National Forest130,463
HoodooNez Perce-Clearwater National Forest153,868
PalisadesCaribou-Targhee National Forest122,002
Pioneer MountainsSawtooth National Forest119,563
Pioneer MountainsSalmon-Challis National Forest172,460
Montana (17)
AreaForestAcres
Big Horn MountainBeaverhead-Deerlodge National Forest50,846
Bmss Ra 1485Flathead National Forest334,275
Cube Iron - SilcoxLolo National Forest36,998
Freezeout MountainBeaverhead-Deerlodge National Forest97,305
Gallatin FringeGallatin National Forest51,571
Hyalite - Porcupine - Buffalo Horn Wilderness Study AreaGallatin National Forest143,991
Jerico MountainHelena National Forest8,445
Lazyman GulchHelena National Forest11,614
Line Creek PlateauCuster National Forest24,825
MadisonGallatin National Forest127,859
Mt. Hefty Ra 1481Flathead National Forest12,938
QuiggLolo National Forest67,267
Red Lodge Creek HellroaringCuster National Forest17,210
Reservation DivideLolo National Forest16,908
Silver KingBeaverhead-Deerlodge National Forest64,289
Thompson Seton RA 1483Flathead National Forest52,235
Tuchuck Ra 1482Flathead National Forest17,730
Nevada (21)
AreaForestAcres
Angel Peak NorthHumboldt-Toiyabe National Forest12,577
Bald Mtn.Humboldt-Toiyabe National Forest41,598
Currant - East SlopeHumboldt-Toiyabe National Forest10,101
Humboldt - SouthHumboldt-Toiyabe National Forest11,152
Jobs Peak (NV)Humboldt-Toiyabe National Forest1,342
Lobdell SummitHumboldt-Toiyabe National Forest7,791
Lovell Summit SouthHumboldt-Toiyabe National Forest28,455
MckinneyHumboldt-Toiyabe National Forest5,790
Mt. EtnaHumboldt-Toiyabe National Forest20,527
Mystic (NV)Humboldt-Toiyabe National Forest5,644
Rose - Alum CreekHumboldt-Toiyabe National Forest853
Rose - Davis Mdw.Humboldt-Toiyabe National Forest2,361
Rose - EvansHumboldt-Toiyabe National Forest4,782
Rose - GalenaHumboldt-Toiyabe National Forest3,711
Rose - Whites CanyonHumboldt-Toiyabe National Forest2,568
Snake - Big WashHumboldt-Toiyabe National Forest4,146
Snake - HatcheryHumboldt-Toiyabe National Forest4,627
Snake - Peacock CynHumboldt-Toiyabe National Forest1,069
South SchellHumboldt-Toiyabe National Forest125,614
Toiyabe RangeHumboldt-Toiyabe National Forest99,225
WilhoitesHumboldt-Toiyabe National Forest11,297
New Hampshire (2)
AreaForestAcres
Great Gulf Ext.White Mountain National Forest15,110
KearsargeWhite Mountain National Forest4,554
New Mexico (23)
AreaForestAcres
Bearhead PeakSanta Fe National Forest8,277
Canada Bonito RNASanta Fe National Forest487
Contiguous To Black & Aldo Leopold WildernessGila National Forest111,883
Contiguous To Gila Wilderness & Primitive AreaGila National Forest79,049
Cruces BasinCarson National Forest5,244
El InviernoSanta Fe National Forest29,927
Hell HoleGila National Forest19,553
Jacks CreekSanta Fe National Forest740
Juan de Gabaldon GrantSanta Fe National Forest8,023
Latir PeakCarson National Forest3,573
LemitasSanta Fe National Forest8,129
Meadow CreekGila National Forest34,167
Nichols ReservoirSanta Fe National Forest1,518
Ortega PeakLincoln National Forest11,545
Pacheco CanyonSanta Fe National Forest1,012
Pecos WS RiverSanta Fe National Forest5,396
Peralta RidgeSanta Fe National Forest4,027
RendijaSanta Fe National Forest2,176
Ryan HillCibola National Forest34,201
Sierra Negra Rare II Study AreaCarson National Forest9,470
Thompson PeakSanta Fe National Forest33,001
Virgin CanyonSanta Fe National Forest6,068
West Face Sacramento MountainsLincoln National Forest41,176
North Carolina (1)
AreaForestAcres
Cheoah BaldNantahala National Forest7,795
North Dakota (1)
AreaForestAcres
Long X DivideDakota Prairie Grasslands10,099
Oregon (17)
AreaForestAcres
Bend WatershedDeschutes National Forest14,829
Dixie ButteMalheur National Forest12,208
Green MountainOchoco National Forest6,613
Hebo 1aSiuslaw National Forest13,930
HellholeUmatilla National Forest65,679
HomesteadWallowa-Whitman National Forest5,817
Hurricane CreekWallowa-Whitman National Forest1,606
Little SheepWallowa-Whitman National Forest5,238
Mt. JeffersonDeschutes National Forest2,282
Mt. Hood AdditionsMt. Hood National Forest13,061
North PaulinaDeschutes National Forest19,670
South PaulinaDeschutes National Forest9,074
Twin MountainWallowa-Whitman National Forest58,533
Utley ButteMalheur National Forest9,700
W - T ThreeUmatilla National Forest1,705
Walla Walla RiverUmatilla National Forest34,416
West - South BachelorDeschutes National Forest25,994
South Dakota (1)
AreaForestAcres
Indian CreekBuffalo Gap National Grassland24,666
Tennessee (1)
AreaForestAcres
Slide HollowCherokee National Forest4,057
Texas (1)
AreaForestAcres
Big CreekNational Forests in Texas1,447
Utah (41)
AreaForestAcres
0401001Ashley National Forest11,705
0401005Ashley National Forest38,930
0401024Ashley National Forest12,882
0419020Ashley National Forest355,684
418009Uinta National Forest18,064
418012Uinta National Forest25,758
418013Uinta National Forest14,643
418014Uinta National Forest9,683
418016Uinta National Forest35,240
418024Uinta National Forest51,699
418025Uinta National Forest32,698
418026Uinta National Forest14,038
418027Uinta National Forest13,884
418028Uinta National Forest34,002
418029Uinta National Forest15,673
418040Uinta National Forest1,702
Boulder MountainWasatch-Cache National Forest8,852
Burch CreekWasatch-Cache National Forest6,938
Capital ReefDixie National Forest763
Clarkston Mtn.Caribou National Forest7,099
CottonwoodDixie National Forest6,754
FishhookDixie National Forest12,959
Lava BedsDixie National Forest14,944
Lewis PeakWasatch-Cache National Forest11,616
Lone Peak ContiguousWasatch-Cache National Forest874
Long Neck Mesa / Steep Creek / Oak Creek - Steep Creek / OakDixie National Forest55,489
Mahogany RangeWasatch-Cache National Forest11,409
Middle FrancisWasatch-Cache National Forest3,296
Mt. AireWasatch-Cache National Forest9,681
Mt. Logan NorthWasatch-Cache National Forest18,930
Mt. NaomiWasatch-Cache National Forest41,922
Mt. OlympusWasatch-Cache National Forest9,982
North FrancisWasatch-Cache National Forest8,148
Pine Valley MountainsDixie National Forest57,673
Signal PeakFishlake National Forest30,889
South FrancisWasatch-Cache National Forest3,374
Stansbury MountainsWasatch-Cache National Forest39,696
Swan Creek MountainWasatch-Cache National Forest9,390
Temple PeakWasatch-Cache National Forest24,081
Twin PeaksWasatch-Cache National Forest6,157
WellsvilleWasatch-Cache National Forest1,717
Virginia (7)
AreaForestAcres
Broad RunJefferson National Forest10,971
Brush MountainJefferson National Forest6,002
Oak KnobGeorge Washington National Forest10,882
Peters Mountain Addition A (VA)Jefferson National Forest1,268
Peters Mountain Addition BJefferson National Forest2,909
Raccoon BranchJefferson National Forest4,388
Seng MountainJefferson National Forest6,428
Washington (18)
AreaForestAcres
Black CanyonOkanogan National Forest9,681
ChelanWenatchee National Forest74,650
Devils GulchWenatchee National Forest24,419
Granite MountainOkanogan National Forest27,428
Grassy TopColville National Forest10,302
Grassy TopIdaho Panhandle National Forests13,485
Long SwampOkanogan National Forest66,344
Meadow CreekUmatilla National Forest4,882
Mt. Baker MaMt Baker-Snoqualmie National Forest24,847
Slide RidgeWenatchee National Forest11,430
SpanglerUmatilla National Forest5,936
Stormy Mtn.Wenatchee National Forest32,612
TaneumWenatchee National Forest26,140
TeanawayWenatchee National Forest72,849
Thorp Mtn.Wenatchee National Forest22,717
TiffanyOkanogan National Forest22,045
White PassGifford Pinchot National Forest1,145
Willow SpringsUmatilla National Forest10,414
West Virginia (2)
AreaForestAcres
Mcgowan MountainMonongahela National Forest10,504
Peters Mountain Addition A (WV)Jefferson National Forest343
Wyoming (11)
AreaForestAcres
0401036Ashley National Forest6,309
Canyon CreekShoshone National Forest7,530
Grayback RidgeBridger-Teton National Forest295,113
Middle ForkShoshone National Forest51,772
Munger MountainBridger-Teton National Forest12,827
PalisadesTarghee National Forest1,121
Phillips RidgeBridger-Teton National Forest10,108
Sulphur CreekShoshone National Forest30,221
West Slope TetonsTarghee National Forest47,448
West Slope WindsBridger-Teton National Forest143,252
Wilderness Study AreaTarghee National Forest51,961
References (95)
  1. American Ornithological Society (AOS). Chesser, R. T., S. M. Billerman, K. J. Burns, C. Cicero, J. L. Dunn, B. E. Hernández-Baños, R. A. Jiménez, O. Johnson, N. A. Mason, and P. C. Rasmussen. 2025. Sixty-sixth Supplement to the American Ornithological Society’s Check-list of North American Birds. Ornithology 142:1-19.
  2. American Ornithologists' Union (AOU). 1983. Check-list of North American Birds, 6th edition. Allen Press, Inc., Lawrence, Kansas. 877 pp.
  3. 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 <i>The Auk</i>]. Also available online: http://www.aou.org/.
  4. Anderson, D. W. and J. J. Hickey. 1972. Eggshell changes in certain North American birds. Pp. 514-40 in Proceedings of the XVth Ornith. Congress.
  5. Arbib, R. 1972. The Blue List for 1973. American Birds 26(6):932-3.
  6. Bednarz, J. C., D. Klem Jr., L. J. Goodrich, and S. E. Senner. 1990. Migration counts of raptors at Hawk Mountain, Pennsylvania, as indicators of population trends, 1934-1986. The Auk 107:96-109.
  7. Beebe, F.L. 1974. Field studies of the Falconiformes of British Columbia. Vultures, eagles, hawks, and falcons. Occasional Papers of the British Columbia Provincial Museum No. 17. Dept. Recreation and Conservation, Victoria, BC, Canada. 163 pp.
  8. Bent, A.C. 1937. Life histories of North American birds of prey. Part 1. Bull. U.S. Natl. Mus. 137. 409 pp.
  9. Bielefeldt, J., R. N. Rosenfield, and J. M. Papp. 1992. Unfounded assumptions about diet of the Cooper's hawk. Condor 94:427-436.
  10. BirdLife International. 2004b. Threatened birds of the world 2004. CD ROM. BirdLife International, Cambridge, UK.
  11. Bosakowski, T., D. G. Smith, and R. Speiser. 1992. Nest sites and habitat selected by Cooper's hawks, ACCIPITER COOPERII, in northern New Jersey and southeastern New York. Can. Field-Nat. 106:474-479.
  12. Brown, L. and D. Amadon. 1968. Eagles, Hawks, and Falcons of the World. McGraw-Hill, NY.
  13. California Department of Fish and Game (CDFG). California Wildlife Habitats Relationship System (CWHR). CWHR Life History Accounts and Range Maps. Accessed November 2011. Online: http://www.dfg.ca.gov/biogeodata/cwhr/cawildlife.aspx.
  14. Campbell, R. W., N. K. Dawe, I. McTaggart-Cowan, J. M. Cooper, G. W. Kaiser, and M. C. McNall. 1990b. The birds of British Columbia. Volume 2. Nonpasserines: diurnal birds of prey through woodpeckers. University of British Columbia Press, Vancouver, B.C. 636 pp.
  15. Castrale, J. 1992. Division of Fish and Wildlife, Indiana Dept. Natural Resources, Mitchell, IN. Pers. comm.
  16. Clarkson, K. E. and L. P. Laniawe. 2000. Hawaiian Hawk, <i>Buteo solitarius</i>. In A. Poole and F. Gill, editors. The Birds of North America. No. 523. The Birds of North America, Inc., Philadelphia, PA. 16 pp.
  17. Craighead, J. J., and F. C. Craighead, Jr. 1956. Hawks, Owls and Wildlife. The Stackpole Company, Harrisburg, Pennsylvania, and the Wildlife Management Institute, Washington, D.C.
  18. Crocker-Bedford, D. C. 1990. Goshawk reproduction and forest management. Wildl. Soc. Bull. 18:262-269.
  19. Crocker-Bedford, D. C., and B. Chaney. 1988. Characteristics of goshawk nesting stands. Pages 210-7 in Glinski et al., editors. Proc. Southwest raptor management symposium and workshop. Nat. Wildl. Fed. Sci. and Tech. Ser. No. 11.
  20. Ehrlich, P. R., D. S. Dobkin, and D. Wheye. 1992. Birds in Jeopardy: the Imperiled and Extinct Birds of the United States and Canada, Including Hawaii and Puerto Rico. Stanford University Press, Stanford, California. 259 pp.
  21. England, A. S., M. J. Bechard, and C. S. Houston. 1997. Swainson's Hawk (<i>Buteo swainsoni</i>). No. 265 IN A. Poole and F. Gill, editors, The birds of North America. The Academy of Natural Sciences, Philadelphia, PA, and The American Ornithologists' Union, Washington, DC. 28pp.
  22. Evans, D. L. 1982. Status reports on twelve raptors. U.S. Department of the Interior, Fish and Wildlife Service, Special Scientific Report No. 238. 68 pp.
  23. Fisher, A.K. 1893. The hawks and owls of the United States in their relation to agriculture. Washington U.S. Dept. of Agriculture Bull. no. 6. 210 pp.
  24. Floyd, T., C. S. Elphick, G. Chisholm, K. Mack, R. G. Elston, E. M. Ammon, and J. D. Boone. 2007. Atlas of the breeding birds of Nevada. University of Nevada Press, Reno and Las Vegas, Nevada. 581 pp.
  25. Fuller, M. R., and J. A. Mosher. 1987. Raptor survey techniques. Pages 37-65 in B. A. Giron Pendleton, et al., eds. Raptor management techniques manual. National Wildlife Federation, Washington, D.C.
  26. Fyfe, R. W., and R. R. Olendorff. 1976. Minimizing the dangers of nesting studies to raptors and other sensitive species. Canadian Wildl. Serv. Occas. Pap. 23. 17 pp.
  27. Garrett, K. and J. Dunn. 1981. Birds of Southern California: Status and Distribution. Los Angeles Audubon Society, Los Angeles, CA.
  28. Grindrod, P., and B. J. Walton. No Date. Cooper's Hawk,<i> Accipiter Cooperi</i>. Bureau of Land Management (BLM), California. Species accounts - West Mojave Plan. Online. Available: http://www.blm.gov/ca/pdfs/cdd_pdfs/coha.pdf.
  29. Harrison, C. 1978. A Field Guide to the Nests, Eggs and Nestlings of North American Birds. Collins, Cleveland, Ohio.
  30. Harrison, H. H. 1979. A field guide to western birds' nests. Houghton Mifflin Company, Boston. 279 pp.
  31. Hawbecker, A. C. 1942. A life history study of the white-tailed kite. Condor 44:267-276.
  32. Hector, D. P. 1988b. Aplomado Falcon (<i>Falco femoralis</i>). Pages 315-322 in R. S. Palmer, editor, Handbook of North American birds. Vol. 5: Family Accipitridae, Family Falconidae. Yale University Press, New Haven, Connecticut.
  33. Hennessy, S.P. 1978. Ecological relationships of accipiters in northern Utah - with special emphasis on the effect of human disturbance. M.S. thesis. Utah State University, Logan, UT.
  34. Henny, C. J. and D. L. Meeker. 1981. An evaluation of blood plasma for monitoring DDE in birds of prey. Env. Pollution. 25A:291-304.
  35. Henny, C. J. and H. M. Wight. 1972. Population ecology and environmental pollution: red-tailed and Cooper's Hawks. Pp. 229-50 in Population Ecology of Migratory Birds: A Symposium. U.S.D.A. Wildlife Res. Rep. 2 pp.
  36. Herron, G. B., C. A. Mortimore, and M. S. Rawlings. 1985. Nevada raptors: their biology and management. Nevada Dept. of Wildlife. Biological Bulletin No. 8.
  37. Houston, C. S., and J. K. Schmutz. 1995. Swainson's Hawk banding in North America to 1992. North American Bird Bander 20:120-127.
  38. Howell, S. N. G., and S. Webb. 1995. A guide to the birds of Mexico and northern Central America. Oxford University Press, Oxford, UK.
  39. Iverson, G. C., and M. R. Fuller. 1991. Area-occupied survey technique for nesting woodland raptors. Pages 118-124 in Proceedings of Midwest Raptor Management Symposium and Workshop 27 Feb - 1 Mar 1989, Chicago, Illinois. National Wildlife Federation Scientific and Technical Series No. 15.
  40. Johnsgard, P. A. 1990. Hawks, eagles, and falcons of North America. Smithsonian Inst. Press, Washington, D.C. xvi + 403 pp.
  41. Johnson, R. R., R. L. Glinski, and S. W. Matteson. 2000. Zone-tailed Hawk (<i>Buteo albonotatus</i>). No. 529 IN A. Poole and F. Gill, editors, The birds of North America. The Birds of North America, Inc., Philadelphia, PA. 20pp.
  42. Kennedy, P. L. 1980. Prey size selection patterns of nesting male and female Cooper's hawks. University of Idaho, Idaho. M.S. Thesis.
  43. Kennedy, P. L. 1988. Habitat characteristics of Cooper's hawks and northern goshawks nesting in New Mexico. Pages 216-227 in Glinski et al., eds. Proc. Southwest raptor management symposium and workshop. Nat. Wildl. Fed. Sci. and Tech. Ser. No. 11.
  44. Kingsley, N.P., and T.H. Nicholls. 1991. Raptor habitat in the midwest. Pages 185-194 in Proc. midwest raptor management symposium and workshop. National Wildlife Federation, Washington, DC.
  45. Kirk, D. A., D. Hussell, and E. Dunn. 1995. Raptor population status and trends in Canada. Bird Trends (Canadian Wildlife Service) 4:2-9.
  46. Kochert, M. N. 1986. Raptors. pages 313-349 IN: A. Y. Cooperrider, R. J. Boyd, and H. R. Stuart, editors. Inventory and monitoring of wildlife habitat. Denver, CO: U.S. Department of the Interior, Bureau of Land Management, Denver Service Center.
  47. Leary, A. W., R. Mazaika, and M. J. Bechard. 1998. Factors affecting the size of Ferruginous Hawk home ranges. Wilson Bulletin 110:198-205.
  48. Lefranc, M. N., Jr., and R. L. Glinski. 1988. Southwest raptor management issues and recommendations. Pages 375-392 in Glinski et al., eds. Proc. Southwest raptor management symposium and workshop. National Wildlife Federation Science and Tech. Ser. No. 11.
  49. Matteson, S. W., and J. O. Riley. 1981. Distribution and nesting success of Zone-tailed Hawks in west Texas. Wilson Bulletin 107:719-723.
  50. Montoya, A.B., P.J. Zwank, and M. Cardenas. 1997. Breeding biology of Aplomado Falcons in desert grasslands of Chihuahua, Mexico. Journal of Field Ornithology 68(1):135-143.
  51. Mosher, J. A. 1989. Accipiters. Pp. 47-52 in Pendleton, B. G. (ed.). Proceedings of the northeast raptor management symposium and workshop held 16-18 May 1988, Syracuse, NY. Institute for Wildlife Research, Nathional Wildlife Federation, Scientific and Technical Series No. 13.
  52. Mosher, J. A., M. R. Fuller, and M. Kopeny. 1990. Surveying woodland raptors by broadcast of conspecific vocalizations. J. Field Ornithol. 61:453-461.
  53. Nagy, A. C. 1977. Population trends indices based on 40 years of autumn counts at Hawk Mountain. Pages 243-53 in 1975 Proceedings of the ICBB World Conference on Birds of Prey, Vienna.
  54. National Geographic Society (NGS). 1983. Field guide to the birds of North America. National Geographic Society, Washington, DC.
  55. Olendorff, R. R. 1993. Status, biology, and management of Ferruginous Hawks: a review. Raptor Res. and Tech. Asst. Cen., Special Report. U.S. Dept. Interior, Bureau of Land Management, Boise, Idaho. 84 pp.
  56. Palmer, R. S., editor. 1988a. Handbook of North American birds. Vol. 4. [Diurnal raptors, part 1]. Yale University Press, New Haven, CT. vii + 433 pp.
  57. Parker III, T. A., D. F. Stotz, and J. W. Fitzpatrick. 1996. Ecological and distributional databases for neotropical birds. The University of Chicago Press, Chicago.
  58. Pattee, O. H., M. R. Fuller, and T. E. Kaiser. 1985. Environmental contaminants in eastern Cooper's hawk eggs. Journal of Wildlife Management 49:1040-1044.
  59. Penak, B.L. 1983. Status report on the Cooper's Hawk ACCIPITER COOPERII. Committee on the Status of Endangered Wildlife in Canada (COSEWIC). 69 pp.
  60. Pendleton, B. A. G., B. A. Millsap, K. W. Cline, and D. M. Bird. 1987. Raptor management techniques manual. National Wildlife Federation, Sci. and Tech. Ser. No. 10. 420 pp.
  61. Peterjohn, B.G., and D.L. Rice. 1991. Ohio breeding bird atlas. Ohio Department of Natural Resources, Division of Natural Areas and Preserves, Columbus, Ohio. 416 pp.
  62. Petersen, L. 1979. Ecology of Great Horned Owls and Red-tailed Hawks in southeastern Wisconsin. Wisconsin Department of Natural Resources Technical Bulletin no. 111.
  63. Peterson, R. T. 1964. Introduction. In Bird Studies at old Cape May. Dover Pub., New York, New York.
  64. Poole, A. F. and F. B. Gill. 1992. The birds of North America. The American Ornithologists' Union, Washington, D.C. and The Academy of Natural Sciences, Philadelphia, PA.
  65. Prouty, R.M., O.H. Pattee, and S.K. Schmeling. 1982. DDT Poisoning in a Cooper's Hawk collected in 1980. Bull. Environ. Contam. Toxicol. 28:319-321.
  66. Reynolds, R. T. and H. M. Wight. 1978. Distribution, density, and productivity of accipiter hawks breeding in Oregon. Wils. Bull. 90:182-96.
  67. Reynolds, R. T., E. C. Meslow, and H. M. Wight. 1982. Nesting habits of coexisting Accipiter in Oregon. Journal of Wildlife Management 46:124-31.
  68. Ridgely, R. S. 2002. Distribution maps of South American birds. Unpublished.
  69. Robbins, C. S., D. Bystrak, and P. H. Geissler. 1986. The Breeding Bird Survey: its first fifteen years. U.S. Fish and Wildlife Serv. Resource Publ. 157. iii + 196 pp.
  70. Rosenfield, R. N., and J. Bielefeldt. 1992. Natal dispersal and inbreeding in the Cooper's hawk. Wilson Bull. 104:182-184.
  71. Rosenfield, R. N., and J. Bielefeldt. 1993. Cooper's Hawk (<i>Accipiter cooperii</i>). In A. Poole and F. Gill, editors, The Birds of North America, No. 75. Academy of Natural Sciences, Philadelphia, and American Ornithologists' Union, Washington, DC. 24 pp.
  72. Rosenfield, R. N., et al. 1985. Taped calls as an aid in locating Cooper's Hawk nests. Wildl. Soc. Bull. 13:62-3.
  73. Rosenfield, R. N., J. Bielefeldt, and R. K. Anderson. 1988. Effectiveness of broadcast calls for detecting breeding Cooper's hawks. Wildl. Soc. Bull. 16:210-212.
  74. Rosenfield, R.N., J. Bielefeldt, R.K. Anderson, and J.M. Papp. 1991. Status reports: Accipters. Pages 42-49 in Proc. midwest raptor management symposium and workshop. National Wildlife Federation, Washington, DC.
  75. Schriver, E. C. Jr. 1969. The status of Cooper's hawks in western Pennsylvania. Pages 356-9 in J. J. Hickey (editor). Peregrine Falcon Populations: Their Biology and Decline. University of Wisconsin Press, Madison, Wisconsin.
  76. Smith, D. G., and J. R. Murphy. 1973. Breeding ecology of raptors in the eastern Great Basin of Utah. Brigham Young University Science Bulletin, Biol. Ser. 13:1-76.
  77. Smith, J. P., S. W. Hoffman, J. A. Gessaman. 1990. Regional size differences among fall-migrant accipiters in North America. J. Field Ornithol. 61:192-200.
  78. Snyder, H. A. 1978. Cooper's hawk. Pages 85-6 in H. W. Kale (editor). Rare and Endangered Biota of Florida. Vol. 2. Birds. University of Florida Press, Gainesville, Florida.
  79. Snyder, N. C. N. and J. W. Wiley. 1976. Sexual size dimorphism in hawks and owls of North America. Ornith. Monographs. 20:1-96.
  80. Snyder, N. C. N., H. A. Snyder, J. L. Lincer, and R. T. Reynolds. 1973. Organochlorines, heavy metals, and the biology of North American accipters. Bioscience. 23:300-305.
  81. Spofford, W. R. 1969. Hawk Mountain counts as population indices in northeastern North America. In J. J. Hickey (editor). Peregrine Falcon Populations: Their Biology and Decline. University of Wisconsin Press, Madison, Wisconsin.
  82. Steenhof, K. 1998. Prairie Falcon (<i>Falco mexicanus</i>). In A. Poole and F. Gill, editors, The Birds of North America, No. 346. The Birds of North America, Inc., Philadelphia, PA. 28 pp.
  83. Stewart, R. E., and C. S. Robbins. 1958. Birds of Maryland and the District of Columbia. North American Fauna No. 62. U.S. Govt. Printing Office, Washington, D.C.
  84. Stiles, F. G. and A. F. Skutch. 1989. A guide to the birds of Costa Rica. Cornell University Press, Ithaca, New York, USA. 511 pp.
  85. Tate, J. 1981. The Blue List for 1981: the first decade. American Birds 35:3-10.
  86. Tate, J., and D. J. Tate. 1982. The blue list for 1982. Am. Birds 36:126-135.
  87. Tate, J., Jr. 1986. The Blue List for 1986. American Birds 40:227-236.
  88. Terres, J. K. 1980. The Audubon Society encyclopedia of North American birds. Alfred A. Knopf, New York.
  89. Thomas, J.W., et al. 1993. Viability Assessments and Management Considerations for Species Associated with Late-Successional and Old-Growth Forests of the Pacific Northwest. USDA, National Forest System, Forest Service Research, Portland, OR.
  90. Titus, K., and M. R. Fuller. 1990. Recent trends in counts of migrant hawks from northeastern North America. Journal of Wildlife Management 54:463-470.
  91. Weir, R. D. 1987. Red-shouldered hawk. Pages 120-121 in Federation of Ontario Naturalists and the Long Point Bird Observatory, M. D. Cadman, P. F. J. Eagles, and F.M. Helleiner, compilers. Atlas of breeding birds of Ontario. Univ. Waterloo Press, Waterloo, Ontario.
  92. Whaley, W. H., and C. M. White. 1994. Trends in geographic variation of Cooper's hawk and northern goshawk in North America. Proc. Western Foundation Vertebrate Zoology 5(3):161-209.
  93. Wiggers, E.P., and K.J. Kritz. 1991. Comparison of nesting habitat of coexisting sharp-shinned and Cooper's hawks in Missouri. Wilson Bulletin 103:568-577.
  94. Woodbridge, B., K. K. Finley, and P. H. Bloom. 1995. Reproductive performance, age structure, and natal dispersal of Swainson's Hawks in the Butte Valley, California. Journal of Raptor Research 29:187-192.
  95. Zook, J. L. 2002. Distribution maps of the birds of Nicaragua, Costa Rica, and Panama. Unpublished.