Species names in all available languages
Language | Common name |
---|---|
Albanian | Shqiponja e maleve |
Arabic | عقاب ذهبية |
Armenian | Քարարծիվ |
Asturian | Águila real |
Azerbaijani | Berqut qartalı |
Basque | Arrano beltza |
Bulgarian | Скален орел |
Catalan | Àguila daurada |
Chinese | 金鵰 |
Chinese (SIM) | 金雕 |
Croatian | suri orao |
Czech | orel skalní |
Danish | Kongeørn |
Dutch | Steenarend |
English | Golden Eagle |
English (United States) | Golden Eagle |
Finnish | maakotka |
French | Aigle royal |
French (French Guiana) | Aigle royal |
Galician | Aguia real |
German | Steinadler |
Greek | Χρυσαετός |
Hebrew | עיט זהוב |
Hungarian | Szirti sas |
Icelandic | Gullörn |
Italian | Aquila reale |
Japanese | イヌワシ |
Korean | 검독수리 |
Latvian | Klinšu ērglis |
Lithuanian | Kilnusis erelis |
Mongolian | Цармын бүргэд |
Norwegian | kongeørn |
Persian | عقاب طلایی |
Polish | orzeł przedni |
Portuguese (Portugal) | Águia-real |
Romanian | Acvilă de munte |
Russian | Беркут |
Serbian | Suri orao |
Slovak | orol skalný |
Slovenian | Planinski orel |
Spanish | Águila Real |
Spanish (Mexico) | Águila Real |
Spanish (Spain) | Águila real |
Swedish | kungsörn |
Turkish | Kaya Kartalı |
Ukrainian | Беркут |
Aquila chrysaetos (Linnaeus, 1758)
Definitions
- AQUILA
- aquila
- chrysaeta / chrysaetos
The Key to Scientific Names
Legend Overview
Golden Eagle Aquila chrysaetos Scientific name definitions
Version: 2.0 — Published September 17, 2020
Account navigation Account navigation
Tables and Appendices
Table 1
Morphological measurements of North American Golden Eagles.
All measurements are from live eagles except those reported by Edwards and Kochert (Edwards and Kochert 1986), which were from necropsied birds, and Bortolotti (Bortolotti 1984a) and Friedman (Friedmann 1950), which were from museum skins. Region represents the area of capture but may include both migrants and residents. Mass measurements in particular are expected to be season and condition-dependent. In particular, aside from the Edwards and Kochert (Edwards and Kochert 1986) measurements that were collected at necropsy, the USGS unpublished data were collected in all times of the year, Lish et al. (Lish et al. 2016) was a study of migratory individuals, TAM, Lanzone & Cooper data were from migratory and wintering birds and EHC, T. Craig data were from wintering eagles of unknown residency status. A = Adult, SA = Subadult, J = Juvenile.
Males |
Females |
||||||||
Measurement |
Age |
Region |
n |
Mean |
Range |
n |
Mean |
Range |
Source |
Wing chorda (mm) |
All |
Range wide |
190 |
593 |
(545-636) |
107 |
631 |
(586-666) |
|
|
A/SA |
Range wide |
23 |
595 |
(569-619) |
27 |
640.4 |
(601-674) |
|
A |
Range wide |
12 |
580.5 |
(555-610) |
17 |
633.2 |
(620-666) |
||
A |
MT, WY |
15 |
587 |
(565-612) |
6 |
632 |
(619-659) |
||
A |
East NA |
12 |
583.8 |
(557-605) |
20 |
622.1 |
(585 – 660) |
TAM, M. Lanzone, J. Cooper, unpublished data |
|
SA |
East NA |
20 |
575.1 |
(549–592) |
6 |
607.3 |
(580-635) |
TAM, M. Lanzone, J. Cooper, unpublished data |
|
|
J |
Range wide |
26 |
585.9 |
(559-636) |
31 |
632.2 |
(601-665) |
|
J |
MT, WY |
5 |
583 |
(562-597) |
7 |
630 |
(610-659) |
||
J |
East NA |
11 |
597.3 |
(555-654) |
6 |
610 |
(551–625) |
TAM, M. Lanzone, J. Cooper, unpublished data |
|
Tail length (mm) |
All |
Range wide |
183 |
326 |
(289 – 371) |
108 |
346 |
(298-375) |
|
|
A/SA |
Range wide |
22 |
286.5 |
(267-310) |
24 |
307.2 |
(290-330) |
|
|
A |
Range wide |
12 |
337.4 |
(320-360) |
17 |
366.2 |
(350-390) |
|
A |
East NA |
11 |
306.2 |
(270-320) |
20 |
331.2 |
(280-350) |
TAM, M. Lanzone, J. Cooper, unpublished data |
|
SA |
East NA |
17 |
305 |
(275-323) |
6 |
321.3 |
(270-353) |
TAM, M. Lanzone, J. Cooper, unpublished data |
|
|
J |
Range wide |
23 |
297.7 |
(269-341) |
30 |
322 |
(285-375) |
|
J |
East NA |
11 |
326.1 |
(300-365) |
6 |
331.7 |
(325-344) |
TAM, M. Lanzone, J. Cooper, unpublished data |
|
Exposed culmen lengthb (mm) |
All |
Range-wide |
181 |
41 |
(37-50) |
107 |
44 |
(41-48) |
|
A/SA |
Range wide |
23 |
40.6 |
(36.9-43.5) |
27 |
44.2 |
(41.7-47.5) |
||
A |
Range wide |
12 |
39.5 |
(37-41) |
17 |
44 |
(41-47) |
||
J |
Range wide |
26 |
39.4 |
(36.2-42.6) |
31 |
43.3 |
(39.9-50.0) |
||
Middle toec (mm) |
A |
Range wide |
12 |
60.5 |
(57-66) |
17 |
67.5 |
(62-73) |
|
Foot pad (mm) |
A |
ID |
31 |
131.6 |
(120-137) |
18 |
145.4 |
(139-153) |
|
Hallux claw (mm) |
All |
Range wide |
184 |
48 |
(39-54) |
108 |
54 |
(49-60) |
|
A/SA |
Range wide |
23 |
49.4 |
(45.9-52.9) |
26 |
55.7 |
(49.8-63.4) |
||
J |
Range wide |
24 |
47.8 |
(44.9-51.3) |
30 |
54 |
(49.7-58.2) |
||
Tarsus width (mm) |
All |
East NA |
24 |
16.08 |
(14.09 – 17.80) |
21 |
19.65 |
(16.70 – 24.00) |
TAM, M. Lanzone, unpublished data |
All |
WY |
21 |
12.38 |
(11.63 – 13.45) |
10 |
14.59 |
(13.72 – 16.87) |
M. Lockhart, unpublished data |
|
All |
ID |
10 |
15.2 |
(14.0 – 16.2) |
8 |
16.8 |
(15.9–18.1) |
EHC, T. Craig, unpublished data |
|
Tarsus Length (mm) |
A |
Range wide |
12 |
111.6 |
(101-122) |
17 |
114.9 |
(103-123) |
|
Body Mass (g) |
All |
ID |
31 |
3,477 |
(2,495 - 4,281) |
18 |
4,913 |
(3,374-6,124) |
|
All |
SW ID |
34 |
3,900 |
(3,000-4,475) |
14 |
4,627 |
(4,075-5,280) |
USGS, unpublished data |
|
|
All |
Range wide |
140 |
3,348 |
(2,387–4,361) |
80 |
4,778 |
(3,048–6,442) |
|
A |
MT & WY |
15 |
3,553 |
(3250-4180) |
6 |
5,097 |
(4,600-6,000) |
||
A |
East NA |
12 |
4,055 |
(3,540-4,430) |
20 |
5,226 |
(4,200-6,460) |
TAM, M. Lanzone, J. Cooper, unpublished data |
|
SA |
East NA |
22 |
3,928 |
(3,370-4,500) |
7 |
4,923 |
(4,250-6,020) |
TAM, M. Lanzone, J. Cooper, unpublished data |
|
|
J |
MT & WY |
5 |
3,730 |
(3,250-4400) |
7 |
4,257 |
(3,600-5,300) |
|
J |
East NA |
10 |
3,647 |
(2,690-4,300) |
7 |
4,644 |
(4,300-5,120) |
TAM, M. Lanzone, J. Cooper, unpublished data |
a Unflattened wing chord
b Measured from cere
c Without claw
Table 2
Prey of primary, secondary, and tertiary importance in nesting season diets of Golden Eagles in the western United States, Alaska, and northern Canada summarized by CEC Level II Ecoregiona. Number of prey items are the minimum number of individuals identified.
Ecoregion Level IIb |
Years (areas) |
# Prey Items |
Primary Prey |
Secondary Prey |
Tertiary Prey |
Southern Arctic, Canadac |
4 (1) |
44 |
Sciurids (U. parryii g) |
Waterfowl (Branta canadensis, Somateria spp.) |
Leporids (Lepus arcticus) |
Alaska Tundrad |
2 (1) |
727 |
Sciurids (S. parryii g) |
Birds (Lagopus spp.) |
Waterfowl (F. Anatidae) |
Boreal Cordillera e |
13 (1) |
2,569 |
Sciurids (S. parryii g) |
Leporids (Lepus americanus) |
Birds (Lagopus lagopus) |
Western Cordillera f |
45 (1) |
3,859 |
Sciurids (O. variegatusi) |
Sciurids (Marmota spp.) |
Leporids (Lepus spp.) |
West Central Semi-Arid Prairies f |
7 (3) |
2052 |
Leporids (Lepus spp., Sylvilagus spp.) |
Birds |
Sciurids (Cynomys spp.k, Marmota spp.) |
South Central Semi-Arid Prairies f |
1 (1) |
200 |
Leporids (Lepus spp., Sylvilagus spp.) |
Sciurids (Cynomys spp.k) |
Other mammals |
Cold Deserts f |
129 (22) |
36,641 |
Leporids (Lepus spp., Sylvilagus spp.) |
Sciurids (Otospermophilus/ Urocitellus/Marmota/Cynomys spp.k) |
Birds |
Warm Deserts f |
10 (6) |
1,790 |
Leporids (Lepus spp., Sylvilagus spp.) |
Sciurids (O. variegatusi) |
Other mammals |
Mediterranean California f |
8 (3) |
904 |
Sciurids (O. beecheyij) |
Other mammals |
Leporids (Lepus spp.) |
Upper Gila Mountains f |
1 (1) |
336 |
Leporids (Lepus spp., Sylvilagus spp.) |
Other mammals |
Sciurids (O. variegatusi, Cynomys spp.k) |
a From Table 2 in Bedrosian et al. (Bedrosian et al. 2017), except for the Southern Arctic, Boreal Cordillera, and Alaska Tundra ecoregions.
b (CEC 2016)
c Poole and Bromley (Poole and Bromley 1988a), North-central Nunavut, Canada (68° N)
d Herzog et al. (Herzog et al. 2019), Seward Peninsula, Alaska (65° N)
e Carol L. McIntyre (unpublished data), Denali National Park, Alaska (64° N)
f See Bedrosian et al. (Bedrosian et al. 2017) for specific data sources, years of study, and study locations.
g Urocitellus parryii, Arctic ground squirrel
i Otospermophilus variegatus, Rock squirrel
j Otospermophilus beecheyi, California ground squirrel
k Cynomys spp., prairie dogs
Table 3
Laying and hatching dates by geographic region of western North America.
Dates are shown as a mean, with a range and a sample size in parentheses.
Location |
Laying |
Hatching |
Source |
Northeastern Alaska |
16 April (28 March–14 May, 25) |
28 May (9 May–25 June, 25) |
|
Northeastern Alaska |
(13 April–14 May, 8) |
(25 May–25 June, 8) |
|
Nunavut Territory |
24 April (13 April–4 May, 19) |
5 Jun (25 May–15 June, 19) |
|
Seward Peninsula Alaska |
19 April (16 March – 10 May, 175) |
3 June (30 April-24 June, 175) |
ADFGa, unpublished data |
Central Alaska |
13 April (23 Mar–7 May, 902) |
26 May (4 May–18 June, 902) |
CLM |
East-central Alaska |
(4 - 28 April, 17) |
(16 May - 9 June, 17) |
|
Northeastern Wyoming |
14 March (27 February–13 April, 86) |
25 April (10 April–25 May, 86) |
|
Southeastern Wyoming |
(20 March–4 April, 7) |
(2 May–31 May, 7) |
|
Northwestern Wyoming |
8 March-26 March |
19 April-7 May |
|
Northeastern Colorado |
(10 March–1 April, 11) |
(21 April–13 May, 11) |
|
Washington |
(15 February-17 April, 83) |
(29 March-29 May, 83) |
|
Southeastern Oregon |
5 March (16 February–26 March 22) |
16 April (30 March–7 May, 22) |
|
Southwestern Idaho |
25 February (28 January–24 Mar, 60) |
8 April (10 March–5 May, 60) |
|
Southwestern Idaho |
1 March (3 February–17 April, 1,489) |
12 Aprilb (17 March–29 May, 1,489) |
USGS, unpublished data |
Central Utah (desert) |
1 March (16 January – 21 April, 913) |
12 April (27 February–2 June, 913) |
K. Keller, unpublished data |
North-central Utah |
(25 February–11 Aprilb, 9) |
(12 April–16 April, 9) |
|
North-central Utah |
7 March (21 February–2 April, 14) |
18 April (3 April–14 May, 14) |
|
Four Cornersc |
2 March (2 February-1 April) |
13 April (16 March-13 May) |
|
West-central California |
27 February (5 February–15 March, 51) |
9 April (19 March–26 April, 51) |
|
Central Mexico |
10 February (21 January-2 March) |
25 March (13 March-14 April) |
Cruz-Romo et al.,d unpublished data |
Baja California, Mexicoe |
11 February (9-12 February) |
25 March (24–27 March) |
a Alaska Department of Fish and Game
b Includes renesting.
c Southeastern Utah, southwestern Colorado, northeastern New Mexico, northwestern Arizona
d Cruz-Romo, J. L., J. J Vargas-Velasco, I.Cruz-Molina, M. D. Valdés-Alarcón, L. F. Lozano-Román, M.Sánchez-Vilchis
Table 4
Brood size of Golden Eagles from studies across North America. The data used in this summary were only from study areas where data: a) were collected for at least three years, and b) brood size was documented when nestlings were at least 49 days of age.
Study area location |
Lat/long, center study area |
Study years |
Years of study |
N broods |
3-brood yearsa |
Pr. by brood size |
Data source |
||
1 |
2 |
3 |
|||||||
Zacatecas, MX |
22.9 N, 102.5W |
2015 - 2017 |
3 |
10 |
0 |
0.75 |
0.25 |
0.00 |
L. Valdes-Alarcón, unpublished data |
Baja California, MX |
31.3 N, 115.3 W |
2013 - 2015 |
3 |
22 |
0 |
0.65 |
0.35 |
0.00 |
|
AZ |
34.4 N, 111.8 W |
2015 - 2018 |
4 |
125 |
1 |
0.63 |
0.36 |
0.01 |
McCarty et al. 2015, McCarty et al. 2016, McCarty et al. 2017, McCarty et al. 2018 |
Northeastern NM |
36.0 N, 104.2 W |
2006 - 2009 |
4 |
86 |
0 |
0.67 |
0.33 |
0.00 |
Stahlecker, D. and B. Howe, unpublished data |
Navajo Nation, U.S. |
36.1 N, 109.2 W |
1996-2005, 2010, -12, 2015 -16 |
14 |
408 |
4 |
0.72 |
0.27 |
0.01 |
Navajo Nation, unpublished data; Stahlecker et al. 2017; |
Jicarilla Nation, NM |
36.5 N, 107.1 W |
2002 - 2018 |
17 |
192 |
3 |
0.66 |
0.32 |
0.02 |
Jicarilla Nation, unpublished data |
Diablo Range, CA |
37.5 N, 121.7 W |
1994 - 2000 |
7 |
184 |
3 |
0.53 |
0.45 |
0.02 |
|
Butte Valley, Siskiyou Country, CA |
41.9 N, 122.0 W |
1985- 97, 2014-16 |
16 |
180 |
1 |
0.19 |
0.80 |
0.01 |
Woodbridge, B., unpublished data |
NE Panhandle, WW, northeast CO |
42.6 N, 105.0 W |
2014 - 2016 |
3 |
20 |
1 |
0.70 |
0.25 |
0.05 |
USFWS R6, D. Stahlecker, B. Smith, unpublished data; |
Southwestern, ID |
43.1 N, 115.9 W |
1966 - 2012 |
47 |
1140 |
25 |
0.43 |
0.52 |
0.05 |
USGS, unpublished data |
OR |
43.9 N, 120.9 W |
2011 - 2018 |
8 |
1187 |
6 |
0.62 |
0.36 |
0.02 |
Frank B. Isaacs, personal communication |
Campbell & Converse Counties, WY |
44.0 N, 105.7 W |
1981 - 1985 |
5 |
331 |
3 |
0.54 |
0.44 |
0.02 |
|
Yellowstone NP, WY |
44.7 N, 110.3 W |
2011 - 2018 |
8 |
40 |
0 |
0.85 |
0.15 |
0.00 |
USNPS, unpublished data |
Southeastern MT, northern WY |
44.9 N, 106.9 W |
1975 - 1985 |
11 |
127 |
1 |
0.54 |
0.44 |
0.02 |
|
Livingston, Montana |
45.7 N, 110.6 W |
2010 - 2018 |
9 |
181 |
1 |
0.65 |
0.34 |
0.01 |
R. Crandall, unpublished data; Crandall 2013); Crandall et al. 2015; Crandall et al. 2016 |
Sainte-Marguerite 3, QC, Canada |
51.1 N, 66.7 W |
1994, 97-98, 2000, -02, -04, -07 |
7 |
22 |
0 |
0.82 |
0.18 |
0.00 |
|
Kisaralik River, Yukon Delta NWR, AK |
60.4 N, 159.9 W |
1991-2004, 2012-14 |
16 |
99 |
5 |
0.55 |
0.38 |
0.07 |
B. J. McCaffery, USFWS, unpublished data |
Sustina Watana Hydro Project, AK |
62.8 N, 148.4 W |
2012 - 2014 |
3 |
15 |
0 |
0.73 |
0.27 |
0.00 |
ABR, Inc. 2015 |
Denali NP, AK |
63.6 N, 149.6 W |
1988 - 2018 |
31 |
852 |
16 |
0.59 |
0.37 |
0.04 |
C.L. McIntyre, NPS, unpublished data |
Kugluktuk, Nunavut, Canada |
67.7 N, 115.6 W |
2015 - 2018 |
4 |
25 |
0 |
0.63 |
0.37 |
0.00 |
Lamont et al. 2015b; 2017c; unpublished data; Hawkshaw et al. 2018d |
Brooks Range, ANWR, AK |
69.5 N, 144.0 W |
1988 - 1990 |
3 |
20 |
0 |
0.78 |
0.22 |
0.00 |
|
Total/mean |
|
|
223 |
5,2660 |
70 |
0.63 |
0.35 |
0.02 |
|
a Number of years observed in which broods of n = 3 nestlings.
b Lamont, M., L. M. Leclerc, and A. Franke (2015). Western Kitikmeot Raptor Survey, July 2015. 35pp. Unpublished report.
c Lamont, M., C. Britt, A. Franke, and G. Roemer (2017). Western Nunavut GOEA Survey Summary Report 15pp. Unpublished report.
d Hawkshaw, K. A., E. M. Hedlin, M. Lamont, G. Roemer, L. M. Leclerc, B. Millsap, and A. Franke (2018). Bluenose East Caribou Calf Predation by Golden Eagles: 2018 Annual Report to the Government of Nunavut. 46pp. Unpublished report
Table 5
Home range sizes of Golden Eagles, by age class and averaged across both sexes, from different studies across the world.
Data collection frequencies vary dramatically, from one location every 15 minutes to a set of locations collected every 3-4/days per month. Estimators and data collection approaches vary from study to study, several studies report multiple estimators, we provide here only one per study. Abbreviations for home range estimators are, in order of appearance in the table, kernel density estimator (KDE), adaptive localized convex hull (aLoCoH), minimum concave polygon (MCcP), and minimum convex polygon (MCvP). Dashed lines indicate that the home range estimator is not clearly described.
Age |
Region |
Estimator |
Season |
Mean (km2) |
Range (km2) |
Source |
Adult |
Alaska |
KDE |
Breeding |
1,409 |
7 – 29,267 |
Booms et al, unpublished |
|
Mojave Desert, California |
aLoCoH |
Monthly |
308 |
4.5 – 3,547 |
|
|
Tehachapi, California |
aLoCoH |
Monthly |
104 |
3 - 650 |
|
|
Eastern North America |
aLoCoH |
Breeding |
2,758 |
37 – 14,625 |
|
|
|
|
Non-breeding |
1,499 |
44 – 9,341 |
|
|
SW Idaho |
MCcP |
Breeding |
23 |
2 – 83 |
|
|
|
|
Non-breeding |
305 |
14 – 1,700 |
|
|
|
-- |
Breeding |
29 |
5 – 49 |
|
|
|
|
Non-breeding |
9 |
3 – 17 |
|
|
|
-- |
Breeding |
44 |
-- |
Schueck unpublished |
|
|
|
Non-breeding |
248 |
-- |
Schueck unpublished |
|
Columbia Basin |
BBMM |
Breeding |
42 |
-- |
|
|
|
|
Non-breeding |
87 |
-- |
|
|
Wyoming |
-- |
Breeding |
24 |
-- |
|
|
|
|
Non-breeding |
14 |
-- |
|
|
Western North America |
MCvP |
Non-breeding |
12,693 |
814 – 46,648 |
|
|
Sweden |
KDE |
Breeding |
245 |
70 – 580 |
|
|
Finland |
MCvP |
Breeding |
297 |
154 – 783 |
|
|
Ethiopia |
Spot mapping |
Breeding |
4 |
2 – 9 |
|
|
Scotland |
MCvP |
Breeding |
74 |
39.7 – 128 |
|
|
Scotland |
Spot mapping |
Breeding |
30 |
16 – 47 |
|
Subadult |
Alaska |
KDE |
Breeding |
4,184 |
22 – 16,473 |
Booms et al, unpublished |
|
Tehachapi, California |
aLoCoH |
Monthly |
408 |
6 – 1,501 |
|
|
Eastern North America |
aLoCoH |
Breeding |
9,361 |
68 – 110,446 |
|
|
|
|
Non-breeding |
2,874 |
51 – 27,429 |
|
Juvenile |
Eastern North America |
aLoCoH |
Breeding |
4,483 |
126 – 16,910 |
|
|
|
|
Non-breeding |
3,750 |
97 – 27,970 |
|
|
Tehachapi, California |
aLoCoH |
Monthly |
45 |
3 - 86 |
|
|
Southwestern North America |
MCvP |
Nov-April |
2,304 |
-- |
|
|
Western North America |
KDE |
Non-breeding |
25,257 |
4,429 – 69,478 |
|
|
Sweden |
MCvP |
Post-fledging |
41 |
3 - 96 |