|At Raftsund, Lofoten/Norway|
|Range of H. albicilla Nesting range Wintering range Year-round range|
Falco albicilla Linnaeus, 1758
The white-tailed eagle (Haliaeetus albicilla) is a very large eagle widely distributed across Eurasia. As are all eagles, it is a member of the family Accipitridae (or accipitrids) which includes other diurnal raptors such as hawks, kites, and harriers. One of up to eleven members in the genus Haliaeetus, which are commonly called sea eagles, it is not infrequently also referred to as the white-tailed sea-eagle. It is also sometimes known as the ern or erne (depending on spelling by sources), gray sea eagle and Eurasian sea eagle
While found across a very wide range, today breeding as far west as Greenland and Iceland across to as far east in Hokkaido, Japan, they are often scarce and very spottily distributed as a nesting species, mainly due to human activities. These have included habitat alterations and destruction of wetlands, about a hundred years of systematic persecution by humans (from the early 1800s to around World War II) followed by inadvertent poisonings and epidemics of nesting failures due to various manmade chemical pesticides and organic compounds, which have threatened eagles since roughly the 1950s and continue to be a potential concern. Due to this, the white-tailed eagle was considered endangered or extinct in several countries. However, some populations have recovered well due to some governmental protections and dedicated conservationists and naturalists protecting habitats and nesting sites and partially regulating poaching and pesticide usage, as well as careful reintroductions into parts of their former range.
White-tailed eagles usually live most of the year near large bodies of open water, including both coastal saltwater areas and inland freshwater, and require an abundant food supply and old-growth trees or ample sea cliffs for nesting. They are considered a close cousin of the bald eagle (Haliaeetus leucocephalus), which occupies a similar niche in North America.
- 1 Taxonomy
- 2 Systematics
- 3 Description
- 4 Distribution and habitat
- 5 Behaviour
- 6 Dietary biology
- 7 Breeding
- 8 Relationship with humans
- 9 Heraldry
- 10 Prehistory
- 11 Folklore
- 12 References
- 13 Further reading
- 14 External links
The first formal description of the white-tailed eagle was by the Swedish naturalist Carl Linnaeus in 1758 in the tenth edition of his Systema Naturae under the binomial name Falco albicilla. The genus Haliaeetus was introduced in 1809 by the French naturalist Marie Jules César Savigny in the Description de l'Égypte. The name Haliaeetus is New Latin for "sea-eagle", from Ancient Greek hali-, "sea-" and aetos, "eagle". The specific albicilla, "white-tailed", is from New Latin albi-, "white" and cilla, "tail". The Anglo-Saxon name erne means “soarer”. It has many Gaelic names, including iolar sùil na grèine or 'eagle of the sun's eye.'
The white-tailed eagle is a member of the genus Haliaeetus, a monotypical group comprised by 11 living species, including the closely related Ichthyophaga fish eagles which may or may not be part of a separate genus. The latter group, comprised by the lesser (Haliaeetus humilis) and the grey-headed fish eagle (Haliaeetus ichthyaetus), differ mostly in life history, being more fully devoted to fish eating and habituating wooded areas, especially in mountainous areas. In appearance the two Ichthyaetus are slenderer, longer tailed and more uniform and grey in colour than typical sea eagles. This species pair may not be genetically distinct enough to warrant division into separate genera. Other than these Ichthyophaga-type species found farther north in Asia, Sanford's sea eagle (Haliaeetus sanfordi) of the Solomon Islands is the most atypical Haliaeetus, retaining rufous-brown plumage into adulthood (this particularly resembling the white-bellied sea eagle juvenile, likely a closely related species) more typical of juveniles in other species and it also dwells more so in dense, coastal forests where it feeds mostly on birds and mammals rather than fish and water birds. Outside of the genus Haliaeetus, among other extant forms, they appear to be most closely related to milvine kites and Old World vultures, based on modern forms from these subfamilies that broadly share morphological and life history traits with sea eagles: the Brahminy kite (Haliastur indus) (historically sometimes referred to as the “red-backed sea eagle”) and the palm-nut vulture (Gypohierax angolensis) (which was once widely referred to as the “vulturine fish eagle”). The relation of these species to the sea eagles is partially borne out by their genetic sequencing. Other groups, beyond milvine kites and Old World vulture, of modern accipitrid that are seemingly in some way related, albeit very distantly, to the sea eagles include Accipiters, harriers, chanting-goshawks and buteonines. Notably excluded from their relations are most other species referred to as “eagles”, including booted eagles and snake and serpent eagles.
The white-tailed eagle itself forms a species pair with the bald eagle. These diverged from other sea eagles at the beginning of the early Miocene (c. 10 mya) at the latest, possibly (if the most ancient fossil record is correctly assigned to this genus) as early as the early or middle Oligocene, about 28 mya. A recent genetic study of mitochondrial DNA is consistent with this idea. Greenlandic white-tailed eagles (proposed as H. a. groenlandicus) form, on evolutionary time scales, a relatively recently founded population that has not yet accumulated many unique genetic characteristics and may not strictly fulfill the distinction of a subspecies. However, the population appears to be demographically isolated and deserves special protection. At one time an eastern subspecies (H. a. brooksi) was proposed as well but there is little evidence supporting this as more than a case of clinal variation in coloring and size. As in other sea-eagle species pairs, this one consists of a white-headed (the bald eagle) and a tan-headed species. They probably diverged in the North Pacific, spreading westwards into Eurasia and eastwards into North America. Like the third large northern species, Steller's sea eagle (Haliaeetus pelagicus), adults have yellow feet, beaks and eyes. Another species, likely intermediate between the white-tailed, bald and Steller's sea eagles and the Ichthyophaga type fish eagles, is the Pallas's fish eagle, which in life history seems to range farther from water and to higher elevations than the three northern species normally do. Due to the similar dietary and nesting habits of sea eagles, they are mostly allopatric in distribution as competition can be considerable between these eagles.
Currently, eagles only occur in the Hawaiian Islands as vagrants, but Quaternary bones of Haliaeetus have been found on three of the major islands. An ancient DNA study published in 2015 characterized the rapidly evolving mitochondrial control region of one of these specimens. DNA from a ∼3500-year-old sea eagle skeleton found in a lava cave on Maui was sequenced. Phylogenetic analyses suggested that the Hawaiian eagle represents a distinct (>3% divergent) mtDNA lineage that is most closely related to extant white-tailed eagles. Based on fossil calibration, the Hawaiian mtDNA lineage probably diverged around the Middle Pleistocene. Thus, although not clearly differentiated in morphology from its relatives, the Hawaiian eagle likely represented an isolated, resident population in the Hawaiian archipelago for more than 100,000 years, where it was the largest terrestrial predator. The reasons for its extinction are unknown.
The white-tailed eagle is a very large bird and one of the largest living birds of prey. It is the largest of the dozen species called eagle to be found in Europe and is the largest eagle across its distribution, excluding the Russian Far East and during winter in Hokkaido where it co-exists with its larger cousin, Steller's sea eagle. The white-tailed eagle is sometimes considered the fourth largest eagle in the world  and is on average the fourth heaviest eagle in the world. The only extant eagle eagle species known to be more massive in mean bulk are Steller's sea eagle, the harpy eagle (Harpia harpyja) and the Philippine eagle (Pithecophaga jefferyi). The white-tailed eagle measures anywhere from 66 to 94 cm (26 to 37 in) in total length with a typical wingspan of 1.78 to 2.45 m (5 ft 10 in to 8 ft 0 in). This species may have the largest wingspan of any living eagle. The Steller's sea eagle, which is larger in weight, total length and non-wing standard measurements, may be the closest rival for median wingspan amongst living eagles. Average wingspans are not known for the Steller's species, however white-tailed eagles do appear to outsize the average wingspan of the wedge-tailed eagle (Aquila audax), which is sometimes also titled the largest winged extant eagle. In one sample from Norway, 5 male white-tailed eagle were found to average 2.26 m (7 ft 5 in) and 8 females were found to average 2.37 m (7 ft 9 in). In another sample of wild birds of unspecified origin, 5 males were found to average 2.1 m (6 ft 11 in) and 7 females averaged 2.3 m (7 ft 7 in). Record wingspans have included a specimen from Greenland which measured 2.53 m (8 ft 4 in) while another specimen apparently spanned 2.6 m (8 ft 6 in). The bald eagle broadly overlaps in size with the white-tailed eagle. In direct comparison, the white-tailed eagle averages somewhat larger in body mass than the bald eagle and may be marginally larger in bill and talon size although these linear aspect can be quite similar between the two species. However, the white-tailed has a significantly larger wing chord and average wingspan. On the other hand, the bald eagle usually possesses a longer tail length on average, which imparts a somewhat longer total length that the white-tailed eagle, and a longer mean tarsal length.
Size variation is generally a clinal trend, these figures usually being measured in standard measurement such as wing, tail and tarsal length, or body mass rather than wingspan or total length. As expected for many widely distributed animals of varied lineages, the white-tailed eagle conforms to Bergmann's rule in that more northerly birds tend to outsize those found relatively closer to the Equator. Somewhat less predictably, size seems to decrease from west to the east as well. The largest white-tailed eagles appear to be found in Greenland, which are just slightly larger than those from Scotland and Scandinavia and notably larger than eagles from central Europe, especially in proportions of the wing area. Meanwhile, those from the southerly portions of their breeding range, such as Asia Minor (principally Turkey), southern Kazakhstan and Korea Bay appear to be the smallest-bodied population, but this is complicated by the fact that there's nearly been no comprehensive measurements or published weights known for these extremely sporadic and rare Asian populations of eagle. Furthermore, weights of fully grown eagles from Greenland are not known. Unlike many accipitrids, in white-tailed eagle (and seemingly other sea eagles as well) juveniles are often of similar weight to adult eagles, whereas in most the juveniles will usually weigh somewhat less. However, more typically, juvenile eagles have somewhat larger average wing and tail lengths than adults. In the white-tailed eagle, body mass can typically range from 4 to 6.9 kg (8.8 to 15.2 lb) in females. The slightly smaller male may typically weigh from 3.1 to 5.4 kg (6.8 to 11.9 lb). Average weights in European white-tailed eagles can range from 4.02 kg (8.9 lb) in 5 males and 5.11 kg (11.3 lb) in 9 females to (from the reintroduced birds of Scotland of Norwegian stock) 4.98 kg (11.0 lb) in 39 males and 6.06 kg (13.4 lb) in 43 females. In comparison, the weight ranges for white-tailed eagles from northeast China were claimed as only 2.8 to 3.78 kg (6.2 to 8.3 lb) in males and 3.75 to 4.6 kg (8.3 to 10.1 lb) in females. The heaviest female white-tailed eagles can apparently scale up to 7.5–8 kg (17–18 lb) and even males can sometimes weigh up to 6.5 kg (14 lb), which would make the largest males perhaps the heaviest recorded modern male eagle as male harpy and Philippine eagles (being more sexual dimorphic in favor of the female) are not known to exceed 5 kg (11 lb) (the highest weights for male Steller's sea eagle are not known). The global mean body mass of white-tailed eagles is estimated at approximately 5 kg (11 lb). The average female Steller's sea eagle may weigh just under 25% more than the average female white-tailed eagle (the average weight of male Steller's is not known) while the average European golden eagle weigh about 11-12% less than the average European white-tailed eagle and the bald eagle species as a whole about 10% less than the white-tailed eagle species.
Standard measurements and sexual dimorphism
The most reliable method to sex birds is by tarsus width and depth and bill depth but these are infrequently measured.  In some cases females are as much as 25% heavier and 15% greater in linear dimensions, though the sexes are rarely this discrepant in standard measurements. Among standard measurements, the wing chord is 552 to 695 mm (21.7 to 27.4 in) in males, averaging 606 and 645 mm (23.9 and 25.4 in) in European adults and juveniles, respectively, and 646.5 mm (25.45 in) in Greenland males. In females, the wing chord may measure 605 to 740 mm (23.8 to 29.1 in), averaging 668 and 685 mm (26.3 and 27.0 in) in European adults and juveniles, respectively, and 691.3 mm (27.22 in) in Greenland females. Adult tail length is 250 to 331 mm (9.8 to 13.0 in) in males, averaging 280 mm (11 in), and 276 to 330 mm (10.9 to 13.0 in) in females, averaging 305 mm (12.0 in). Juvenile tail lengths can reach roughly 380 mm (15 in) in both sexes, however. The tarsus is 90 to 101 mm (3.5 to 4.0 in), averaging 95.5 mm (3.76 in). In terms of their killing apparatuses, their hallux claw, the largest talon on all accipitrids, is 37 to 46 mm (1.5 to 1.8 in) in length, averaging 40.9 mm (1.61 in). The hallux claw averages about a centimeter less than that of a golden eagle and is more sharply curved, an adaptation to prevent escape of slippery prey such as fish, while that of a bald eagle is similarly about 40.4 mm (1.59 in) and of similar curvature. The exposed culmen is typically large as in all Haliaeetus, ranging from 45 to 65 mm (1.8 to 2.6 in), with an average of 56.1 mm (2.21 in). The average culmen length of the bald eagle is 54.3 mm (2.14 in), thus averaging slightly smaller. However, the average culmen length in the large bald eagles of Alaska is considerably larger than other bald eagles as well as most white-tailed eagles at up to 75 mm (3.0 in) and can even rival the length (but perhaps not the girth) of the truly massive bill of the Steller's sea eagle.
Coloring and field appearance
The adult white-tailed eagle is a greyish mid-brown color overall. The plumage is fairly uniform over most of the body and the wing but the upper wing coverts are typically somewhat paler. Contrasting with the rest of the plumage in the adult are a clearly paler looking head, neck and upper breast which is most often a buffy hue. In worn or bleached plumages these light areas can be even paler at times, ranging to nearly whitish, which can render a resemblance in such eagles to a washed-out bald eagle. Some of the palest birds are also washed out looking even on the body which can appear anywhere from cream-tawny to light grayish. It is thought that in some populations perhaps paleness increases with age, although it is possible that there is an historic genetic factor to such pale variations. On the contrary, some adults can also be a richer, more deeply dark brown (or somewhat rufescent) than average with perhaps a mild increase in average darkness of hue to the east of the species’ range. When many of the feathers are freshly molted, they can take on a slight purplish gloss. The brownish hue of the adult overall makes the somewhat wedge-shaped white tail stand out in contrast. All the bare parts of their body on adults are yellow in color, including the bill, cere, feet and eyes. Juvenile and immature are a much darker brown than the adult white-tailed eagle and are more unevenly marked, with whitish feather edgings variably showing, mostly manifesting in some small areas of the underside and under-wing, with a narrow white axillary strip usually apparent.
Their upperside is usually similarly darkish brown but variable based on extent of blackish-brown tip to otherwise buff-brown feathers of the mantle, back and upper wing. The head of juveniles is normally a blackish-brown hue, somewhat darker and always more uniform than most other feathers. The juvenile white-tailed eagle's tail tends to be a washed out greyish-cream color with messy blackish color on the feather edges and on the tips. Some individual juveniles may evidence some faint barring on the tail while others may appear largely dirty whitish on the tail. The bill of juveniles is usually nearly half dark brown from the tip and half dirty, dull yellowish or gray to the base, while the feet are usually a dirty yellow and the eyes are a darkish brown. Juvenile males may average a slightly darker brown plumage with less speckling on their upper body than like-age females, their head and neck plumes may also appear shorter, which can accentuate the slighter, more angular skull possessed by males. In disposition, the male juveniles are said to be more highly strung and higher voiced than their female counterparts. The head gradually grows paler over several years. The whitish mottling may increase on the upperparts, belly and especially on the underwing area later into their 3rd year (considered the first subadult plumage) and subadult birds can appear fairly blotched with white but much individual variation in coloring is known at this age. However, this white mottling then fades late into the 4th year and the plumage becomes less contrasting. Although sexual maturity is considered to be attained at 5 to 6 years of age, usually the fully white tail and the uniform pale head and neck are not obtained until the 8th year. Juveniles first molt in May/June until October/November at just over a year of age. Their 2nd molt is the following year in March or April, with two more subsequent molts usually beginning around this time for the next couple years. Like other large raptors, feathers are molted at slow intervals in order to not inhibit food capture. Only relatively small portions of the flight feathers are molted each year. Molts occur more or less continuously, although it may pause in winter if food is in short supply.
White-tailed eagles are of all ages typically perch in quite upright positions on exposed branch, rock or other vantage point, but tend to sit more horizontally on the ground or other level surfaces. They have an ample bill with a relatively high culmen, helping impart a relatively narrow and high crowned facial look, especially compared to Aquila eagles. Their neck is at times unexceptedly long-looking, more so than the bald eagle, which can give the upper body a vulturine appearance. The tail is relatively short, in some adults it can appear almost strangely so in relation to the massive body, and slightly wedge-shaped. All ages have a well-feathered tibia but bare tarsi. In flight, the white-tailed eagle's wings are extremely broad and deeply fingered (usually at least 6 fingers tend to be visible), creating a "flying door" effect. Juvenile are longer tailed, which is usually more evident in flying than perched birds, with sometimes a slightly bulging section of feathers manifesting on the wing secondaries. The species tends to fly with shallow wing beats, at times their beats can be fairly fast for bird of this size interspersed at times with glides or not gliding at all. At a great distance, they may suggest a huge brown heron due to this flight style. The wings are held flat or slightly upraised at tip in flight and the species is well known to soar extensively. The white-tailed eagles can be surprisingly maneuverable on the wing, usually during aerial displays or dogfights with other birds. The eagles may too maneuver by half-closing both wings or closing one wing.
The white-tailed eagle is considered a very vocal bird of prey during the breeding season, although some authors consider their voice "not loud or impressive for the size of the bird". The male call is oft transcribed as gri-gri-gri or krick-krick-krick, while the female is a deeper gra-gra-gra-gra or krau-krau-krau-krau. These will increase in tempo & pitch, with about 15-30 calls in a sequence. Often pairs will duet during early spring, in flight or from a perch. When perched, the male calls kyi-kyi-kyi-kli-kliek-yak with the head thrown back and upwards in the last call ended with a lower ko-ko-ko, the perched call of females is similar but deeper, a krau-krau-krau-uik-ik. Typically, the perched version of their calls tend to be shriller and higher than those issued in flight. In courtship display, male calls krau-krau-krau-uik-ik-ik answered by females with a lower ra-rack-rack-rack-rack. Young in nest call a shrilly piieh-piieh, while the female when receiving food from male calls out with tschie-tschie or vueee-vueee. Single or repeated krlee or similar component of calls used in other circumstances, but this can be very variable. Alarm calls tend to be 3-4 short, loud klee or klek notes. Sometimes a different call of alarm or anger, a deep gah-gah-gah or jok-jok-jok, similar to alarm calls of a large gull, is also uttered when a nest is approached (usually recorded while directed towards humans). The young let out a monotonous veee-veee when hungry (or "bored") which intensifies if the eaglets are not fed or brooded immediately.
Given reasonable view, adult white-tailed eagles are difficult to mistake for any other bird. There are no other eagles with fully white tails in their range except for in the easternmost limits of their range, their cousins the bald and Steller's sea eagles, which in adults are obviously very different in all other respects of plumage. Even in poor light, the bald species shows a sharp demarcation from white to dark brown whereas the color contrast is far subtler in white-tailed eagles between their brown body (of a paler hue than that of a bald eagle) and buff-colored head. At a great distance, the adult may be potentially confusable with the Griffon vulture (Gys fulvus), as the coloring of the two species is vaguely similar and they can overlap somewhat in size although the vulture can average rather heavier and longer winged. However even at long range, the relatively tiny head, distinctly curved trailing wing-edges and more raised wings make the vulture distinctive from the white-tailed eagle. Juveniles may be harder to distinguish, mainly from other sea eagles in few areas of overlap. In northern Mongolia (perhaps spilling over into southern Siberia), the northern part of the Caspian Sea and some central and southern parts of Kazakhstan, the white-tailed eagle may (or may not) live alongside the rarer, relatively poorly-known Pallas's fish eagle. The Pallas's juveniles are more distinctively whitish marked on the underwing. In flight or perched, the Pallas's fish eagle are usually markedly smaller and slighter than white-tailed eagles with a longer and differently marked tail. At all ages, the white-tailed eagle averages a duller, slightly darker and browner colour overall than the Pallas's fish eagle. Pallas's fish eagles are mid-brown on the body in juvenile plumage with no paler feather edging as seen in juveniles and especially subadults of the larger species. Adult Pallas's fish eagles are immediately distinctive rufous hue with a more restricted but more sharply demarked paler buffy head. Bald eagle juveniles may be found together with white-tailed eagles in the Aleutian islands (where the white-tailed eagle formerly bred until about 30 years ago) and when vagrants of white-tails occur in Alaska. Juveniles of bald and white-tailed eagles often strongly resemble each other but the bald eagles have a shorter neck, a relatively longer and squarer tail, and somewhat less broad wings. In the coloring, the bald juvenile is similarly as dark or even darker brown above as white-tailed eagle juveniles but on the underside often has more extensive whitish mottling, especially on the underwing. Steller's sea eagles are usually distinctly larger and longer tailed, with a taller, bulkier look in eagles standing on the ground or perched. Steller's juveniles have a different wing shape (roughly paddle-shaped) and a considerably more massive and paler bill, which is yellow even in juveniles unlike in bald and white-tailed eagles. Juvenile Steller's sea eagles are a distinctly darker soot colour than juvenile white-tailed eagles with even less whitish showing on the body than the latter species but, on the other hand, the underwing often as white marked as juvenile bald eagles (dissimilarly from juvenile white-tailed eagles), albeit in different pattern. In all three large northern sea eagles, the tail color is similar at the various stages of development but the shape is more distinctive, especially the bolder wedge shape of the Steller's. The cinereous vulture (Aegypius monachus) may too be considered superficially similar to the juvenile white-tailed eagle, but it is considerably larger and longer-winged and possesses a more uniform and darker hue with conspicuous paler legs and a relatively smaller head. Young white-tailed eagles are also potentially confusable with any Aquila, but should be obvious even as a silhouette in its huge wings, relatively truncated and slightly wedge-shaped tail and obvious projection of the neck and head. All Aquila lack pale the axillary band often visible on juvenile and subadult white-tailed eagles. Some greater spotted eagles (Clanga clanga) can suggest the wing shape of a white-tailed eagle but are far smaller and shorter winged and never with a protruding head. The golden eagle usually appears smaller than the white-tailed eagle and tends to be more dashing in flight, which is usually done with a distinct dihedral. When perched, the golden eagle looks more sleek and compact than the white-tailed eagle and tends to be a darker, richer hue of brown. Golden eagles have a much shorter neck, with a smaller head and bill and a longer, squarer tail. White wing patches of juveniles are also differently distributed in golden than juvenile white-tailed eagles.
Distribution and habitat
This eagle breeds in northern Europe and northern Asia. Their European range extends to as far west as southeastern Greenland, northern and eastern Iceland, and the reintroduced populations in some areas of Ireland and Scotland, particularly conserved coastal spots. In mainland Europe, often isolated outposts remain in coastal and western Norway (broadly), northern and southwestern Finland, eastern Sweden, southern Denmark (and some spots in the north), islands of the Baltic Sea, western Austria, northeastern Germany, northern and eastern Poland, the Czech Republic, much of the east Baltic countries, the non-montane areas of the Ukraine, eastern Slovenia, central and southern Hungary (and adjacent northeastern Croatia), very sporadically in Greece, the Danube sections of Romania and Bulgaria to the Black Sea and western and eastern Moldova. In Asia Minor, it only remains as a breeder in very sparse and small pockets of Turkey and Georgia, taken as a region there is likely to be fewer than 30 breeding pairs in this region. In the Middle East, the white-tailed eagle may still be found breeding only along the southern coast of the Caspian Sea in northern Iran and southwestern Turkmenistan. Discontinuously, they are found as residents in Kazakhstan where they live in a long strip of the southern part of the country starting at the Aral Sea and the northwestern portion (but not, as far as is known, breeding in the Kazakh part of the Caspian Sea coast). The only country in which the white-tailed eagle is found over a continuous and extremely large area is Russia. The species is found very broadly everywhere in Russia from European Russia in the west to the Bering Sea in the east, only being fully absent as a nester as far as is known from the high Arctic regions and a section bordering westernmost Kazakhstan, although it breeds to south of this in the Russian coastal part of the Caspian Sea. Their northern limits occur in Russia to the Ob river to 70 degrees north at the mouth of the Yenisei River and on the Gydan and Yamal Peninsulas, to the Kolyma, Indigirka and Lena rivers to above 72 degrees north, even to 75 degrees north on the Taymyr Peninsula. They are said to be common around the White Sea, reportedly even the most abundant bird of prey locally and found both on coasts and inland lakes, although breeding rates are low due to the frigid weather. From Russia, breeding populations spill somewhat into northernmost Mongolia, extreme northwestern China and northern North Korea. The white-tailed eagle also breeds on Sakhalin Island, the Kuril Islands and Hokkaido, the northernmost island of Japan.
The wintering range is less well understood for the white-tailed eagle given the extreme reductions and fluctuations of northern breeding populations over the last few centuries, so that the delineation of regular wintering areas versus areas of mere vagrancy is difficult to ascertain. It is known that a small number winter on Etang de Lindre of Lorraine, France as well as an area on the border of France to Germany around Strasbourg, with vagrants to elsewhere in France, as well as to Spain, Portugal and Malta. A well-defined wintering population may occur in much of the Netherlands, even with infrequent modern breeding in the northern coastal areas. A non-breeding population is known in western Germany from North Rhine-Westphalia to Bonn, as well as far northern Germany into southwestern Denmark. Other established wintering areas are known in Europe in west-central Italy, northern Austria, fairly broadly in southern Slovakia and northern Hungary and a few protected pockets of Southeast Europe apart from the portions in the north and east where they still breed. Intermittent forms of vagrancy and migration (most from eagles that breed in or disperse from Russia) are known to occur in several areas of Turkey, the Levant countries, Azerbaijan and Iran down to even the Persian Gulf, albeit seldom is the species to be found commonly or reliably anywhere in these regions. Further east, rare wintering areas are known in a few small, scarce pockets of Turkmenistan, Afghanistan, Uzbekistan, Tajikistan and Pakistan. It is a very rare winter visitor to India, namely the extreme northwest and along the border of Nepal to Bhutan and extreme northern Bangladesh. Scattered pockets of wintering birds are known to occur too in central and southern China, into northeastern Mynamar, and more broadly and regularly in much of northeastern China. Good numbers winter too in much of South Korea and Japan down to as far as Honshu. White-tailed eagles dispersing from their breeding grounds or natal sites in the Russian Far East are known to occasionally disperse across the Bering Sea to North America in several parts of the Aleutian Islands, the Pribilof Islands and some of mainland coastal Alaska down to Kodiak Island. Some white-tailed eagles even bred in Alaska on Attu Island in the late 1970s to the early 1980s (until 1984 when the last attempts were recorded) but it was not clear whether young were ever successfully fledged.
White-tailed eagles may be found in varied habitat but usually are closely associated with water and generally occurs in lowland areas. Although mainly a lowland species, the species is known to live at elevations of 1,500 to 2,300 m (4,900 to 7,500 ft) so long as there is water access in some parts of Central Asia and Siberia. In coastal areas, the species may range from high sea cliffs down to low-lying islands and archipelagos. Especially in winter, many white-tailed eagles often frequent low coastal spots, estuaries and coastal marshes. Several studies have supported that coastal areas are preferred when available during winter. In many areas, white-tailed eagles can seem to switch freely between usually cliff habitat and wooded spots for nesting sites and the center of their home range habitat. In some areas, such as Japan, this species may occur in regions with intensive human fishing activity and they may become unusually partially habituated to this human presence. Inland, white-tailed eagles usually require secluded woods, forested areas or groups of trees with tall mature trees and access to freshwater wetlands such as lakes, river systems, marshes or extensive, low-disturbance farmland. In the alluvial wetlands of Croatia, 95% of nests were found within 4 km (2.5 mi) of deep freshwater. In some areas, white-tailed eagles readily visit commercial fish farms, carp ponds and similar areas with easily accessible food but they will usually avoid areas where human disturbances (especially noisy varieties such as construction, water sporting and heavy boating activities and hunting) commonly occur. However, forestry activity and resulting lessened numbers of tall mature trees and large tree stands in Estonia was found to affect breeding white-tailed eagles less so than it seemed to affect breeding black storks (Ciconia nigra). On the other hand, from studying wintering white-tailed eagles in partially or heavily disturbed wetlands in parts of the Netherlands shows that such areas cannot support the eagles for any long-term period and may only be visited for a day or two by individual eagles.
White-tailed eagles spend much of their day perched on trees or crags, and may often not move for hours. Perhaps up to 90% of a day may spend perched, especially if weather is poor. Also, they will alternate periods of soaring with perching, especially flying over water or well-watered areas, but do considerably less soaring on average than do golden eagles. Pairs regularly roost together, often near to their nest, either on a crag or tree or crevices, overhung ledges or small isolated trees on a crag.
Migration and dispersal
The white-tailed eagle may be considered a rather inconsistent and partial migrant. The species seldom migrates in the western part of its range, with eagles even breeding as far north as Greenland, Iceland and coastal Norway not moving at all for winter, but for some southward juvenile movements following dispersal. Juveniles overall are more migratory and dispersive and leave natal areas sooner, which is by August–September in northwestern Europe and return later, by March/April, than adults do. Few Norwegian juveniles, per banding studies, were recorded to travel any considerable distance. Extreme cases include one that was found 720 km (450 mi) south of its nest near Karlstad, Sweden, another set of 4 color marked 1st year juveniles were also recorded to turn up in southern Sweden but one was found down to the Wadden Sea in the Netherlands and it is likely that trickling down numbers of Norwegian post-dispersal juveniles have gone onto form much of the known Dutch white-tailed eagle population. In contrast, young from Finland and Sweden tend to distribute to the southwesterly direction to the shores of the Baltic sea. One from Finland was recovered 520 km (320 mi) west in northern Norway and another was found as far south as Bulgaria. In more southerly areas, winter movements are drawn-out and irregular, with most mature pairs probably never leaving their nesting haunts year-around. Those that breed on inland waterways may migrate to sea coast. German juveniles usually do not travel far, with most recorded to travel less than 50 km (31 mi) from their nests and a majority staying near the Baltic coast. However, some eagles that hatched from nests in Germany have been found as far south as in Italy, 1,030 km (640 mi) away to the southeast, or to Gironde, France, 1,520 km (940 mi) to the southwest. In several parts of Russia, quite unlike many European populations, the white-tailed eagle seems to be largely migratory. In the far east, the species appear to take different migratory routes in fall and spring, traveling from north-central Kamchatka thru the Kurile islands to Hokkaido in fall, while in spring these eagles travel north through Sakhalin and the Okhotsk Coast. In the White Sea area, southward moments begin in September with most white-tailed eagles being gone by November but in mild winters some adults may remain behind. Some white-tailed eagles from the White Sea were found well over 2,000 km (1,200 mi) away to the west, in countries such as Hungary and Italy. Return spring migration to the White Sea is by February–March. During winter, whether long-distance migrants or short-distance dispersers, white-tailed eagles tend to become gregarious, especially younger juvenile birds. Many such groups can contain up to 10 and, in areas near large breeding populations such as in Norway, at least 30-40 individuals. Wintering congregations at the Baltic coast and on the River Elbe from 37 winters show that arrivals begin in November, with numbers peaking in January and then declining during March and early April. Although juveniles usually return to their natal area some apparently overshoot these areas, such as those returning to Romania or on the Black Sea which have been recorded 330 km (210 mi) north of their natal site and 510 km (320 mi) northeast of their natal site.
Territory size in white-tailed eagles may vary from 52 to 415 km2 (20 to 160 sq mi), usually less than 130 km2 (50 sq mi), per one estimate. However, home ranges in northeastern Germany were much smaller than this, at 2.25 to 19.16 km2 (0.87 to 7.40 sq mi). While territorial behavior is known in well more than half of all modern birds, essentially all predatory birds of different lineages are particularly strongly territorial because the live prey necessary to feed a family, including the female of the pair (which must remain near the young for them to survive) and the young themselves, tends to be sparser. Furthermore, appropriate habitat is needed in which to execute this hunting and also, of course, to build a nest with some security. While a relatively gregarious raptor, especially among wintering birds and juveniles and immature birds, they are territorial and intrusion by a male in adult plumage often provokes vigorously fighting, in which either combatant can even die. In some cases, these viscous fights can even cause damage to the nest as the two fighting eagles plummet down trying to slash at each other.
The white-tailed eagle's diet is varied, opportunistic and seasonal. Prey specimens can often include fish, birds and, mostly in a secondary capacity, mammals. White-tailed eagles are powerful predators and capable of attacking large prey of considerable sizes but, like most predators, prefer prey that is vulnerable and easy for them to capture. Especially during the winter (and opportunistically in all seasons), many birds of the species live largely as scavengers, usually by coming across available carrion or watching for the activity of corvids, vultures or other raptors. White-tailed eagles in northeastern Germany were shown to hunt mostly from perches, in a “sit-and-wait” style, usually from a prominent tree perch. Like other sea eagles, they can only capture fish normally in the littoral zone, seldom hunting fish when they exceed a water depth of 1.5 to 2 m (4.9 to 6.6 ft). In addition to trees, they may also use crags, hillocks or high grassy tussocks as hunting perches so long as the perch provides a good overall view of the environment. Fish tend to be grabbed in a shallow dive after a short distance flight from a perch, usually with the eagles only getting their feet wet. Occasionally, though, white-tailed eagles have been recorded plunging right into water, usually while hunting on the wing at a height of at least 200 m (660 ft). In Norway, plunge-diving is considered rare. At times they will also fish by wading into shallows, often from shores or gravel islands. The species will at times variously follow fishing boats, readily exploits commercial fisheries, stocked lakes, carp ponds and the like, and scavenges dead fish or fish-offal in a wide range of situations. When it comes to non-fish prey, it has been said that white-tailed eagles often hunt by flying low over sea coast or lake shore and attempt to surprise victims. However, the hunting success rates on healthy birds can be low as revealed in studying wintering eagles in Sweden attempting to hunt mallards (Anas platyrhynchos). White-tailed eagles also regularly pirate food from otters and other birds including cormorants, gulls, ospreys, corvids and various other raptors. Carrion is often the primary food source during lean winter months, with fish and ungulates preferred but everything from cetaceans to livestock to even humans being eaten after death. From studies of captive white-tailed eagles, daily food requirements were estimated at 500 to 600 g (1.1 to 1.3 lb), which is equivalent to about 10% of the birds' body weight, with crop contents commonly of 190–560 g (0.42–1.23 lb). Some semi-captive juveniles on the isle of Rùm, Scotland could eat up to 1.4 kg (3.1 lb) in one sitting. However, in Norway, it was estimated that a family of wild white-tailed eagles including each adult and 3 fledglings were consuming on average up to 625 g (1.378 lb) per bird each day. Furthermore, one male consumed an estimated 2 kg (4.4 lb) in a single meal upon capturing a large fish. The crop can bulge to the size of a small grapefruit after they've consumed a large meal.
Many studies have reflected that the primary foods of white-tailed eagles are fish and water birds. These are the primary food as well for other sea eagle species. However, unlike most Haliaeetus, including the bald eagle and Steller's sea eagle, the water birds tend to take the primary position in the diet. From 26 accumulated food studies for this species, prey remains and pellets show that about 48.5% of the diet is made up of birds, 39.95% by fish, 9.95% by mammals and 1.6% by other foods. In total, more than 300 prey species are known throughout the bird's range. However, based on studies of prey remains and pellets in laboratories from Greenland white-tailed eagles, birds were shown to be biased in both kinds of remains (pellets and prey remains) whereas in situ study and direct nest observation favor fish. Going on pellet/remains alone here in Greenland from 557 items in the 1979 study, 68% of the diet would’ve been represented by birds and only 20% by fish but comprehensive observation shifted it to show fish were the primary food at 58% and birds were secondary at 30%. This study claimed this is often because the bones of fish are dissolved by the large digestive tract of the eagles upon consumption and may thus leave almost nothing in remains and to some extent in pellets. Subsequent studies here showed a much stronger preference for fish in Greenland by 1983, as fish comprised an extreme 91.8% of 660 items. However, this kind of direct continuous observation of food deliveries to nests is not always possible. Furthermore, despite similar bias for prey that is large and leaves conspicuous remains (including any larger fish, bird or mammal), in the bald eagle it was found that fish were usually detectable and dominant in remains and pellets. Most modern biologists may need to leave some fish unidentified but will account for different methodologies of prey study to get the most complete picture attainable. During winter, mammal prey can become more important in foods locally, as indicated in Scotland and shown in Norway and eastern Germany. As much as 41% of the diet can be made up of mammals, as was the case on the Kola Peninsula. There is evidence of strong seasonal shifts in food habits in several parts of the range, usually the largest portions of fish are caught during warmer months while birds and mammals are more important in the colder months, especially in coastal areas such as Norway when preferred fish prey often move to deeper water during winter. Among both fish and bird prey, it is thought that a majority that are caught weigh between 0.5 and 3 kg (1.1 and 6.6 lb). At times it has been said that “most” prey of white-tailed eagles will weigh only 0.5 to 1 kg (1.1 to 2.2 lb). However, the mean prey sizes caught can show greater variability. Three studies showed that mean prey size varied from 578 g (1.274 lb) in the Wigry National Park, Poland,1,062.1 g (2.342 lb) in the Rybinsk Reservoir, Russia and 1.72 kg (3.8 lb) in the Volga-Kama Nature Reserve, Russia. Thus, the mean prey size falls just slightly short of the mean prey mass of the golden eagle, which globally averages about 1.35 to 1.63 kg (3.0 to 3.6 lb).
Overall, nearly 70 species of fish are known to be taken from throughout the white-tailed eagle's range. White-tailed eagles can hunt fish in fresh or saltwater as well as those that prefer brackish water areas. However, they are basically restricted to taking fish in extremely shallow water, often by preference in water less than 1 m (3.3 ft) deep. Ideal fishing areas can be found in areas such as the Baltic sea, where low coasts and archipelagos often have relatively shallow water. While healthy, large fish are often taken as well, white-tailed eagles often take out sickly, injured or already dead fish. In some cases, the fish prey will float to the surface when infected by fish tapeworm, as is often the case with some fish families such as carp. Fish are also caught after being battered, injured and killed at power plants, from large-scale fishing nets or are taken directly from human fishermen. Benthic fish tend to cling to rocks or sandy soil in shallows may be more vulnerable since they tend to look downward rather upward and are less competent at escaping predators coming from above the water's surface. Therefore, lurking benthic fish such as lumpsuckers are more vulnerable than many. Besides vulnerability, habitat and prey behaviour, fish body size may be a driver in the piscivorian dietary preferences. Studies have indicated that fish less than 20 cm (7.9 in) are taken infrequently, since they have a lower yield, fish of up to 30 cm (12 in) are taken secondarily and fish between 30 and 60 cm (0.98 and 1.97 ft) are preferred since they have the highest nutritional benefit. Fish taken can exceed 0.9 to 1 m (3.0 to 3.3 ft) but since they can start to considerably exceed the weight of the eagle itself, they may be prove too difficult to overpower. One large Atlantic halibut (Hippoglossus hippoglossus) was found with the disembodied feet of a white-tailed eagle still imbedded in its back, presumed the eagle drowned after being overpowered and drug under only to rot off, leaving only feet. Since they do not have the waterproofing oils on the plumage of the more accomplished raptorial diver, the osprey (Pandion haliaetus), white-tailed eagles prefer not to get their feathers wet as it can take a long time for them to dry. This may also make them vulnerable to losing their catch to other white-tailed eagles since their flight may be impaired until the wings are dried. Therefore, when hunting fish, they will almost always take flight as soon as possible to a feeding perch or nest. The largest fish lifted in flight and flown off with have been claimed anecdotely to reach weights of as much as 15 kg (33 lb) in the case of a Atlantic halibut in Norway. However, this is likely reported in error as no living eagle would likely be able to take flight with this heavy a load as they are more or less constrained to carrying in flight a load more or less equal to their own body weight, and even then only laboriously and in favorable wind conditions. The same Norwegian study coincided that another eagle when trying to fly with an Atlantic cod (Gadus morhua) weighing about 8 kg (18 lb), the fish was quickly drop as it was apparently deemed too heavy. The widely reported case of a white-tailed eagle carrying off a 3.5-year-old girl in Norway flight by the back of her dress only to drop her mostly unharmed below the eagle's eyrie, which was included in the Guinness Book of World Records, is considered most likely to be apocryphal since she weighed approximately 18 kg (40 lb), far too heavy for any living eagle to lift in flight. Another option when taking particularly large fish is for the eagle to stay in water and row, swimming using their wings, across the water to the nearest bank or shore. While this would leave them waterlogged, of course, the food yield from such a catch is obviously attractive. White-tailed eagles have been photographed doing this with a large fish successfully in Greenland and 35 such cases were reported in Norway alone.
The most frequently recorded prey species in 18 food studies from across the range is the northern pike (Esox lucius), present in at least 16 of those studies. Pike were found to be the main prey species in both the Baltic Sea and Lapland in Sweden, at three breeding locations in Finland, in two studies from Germany and in Belarus. The maximum representation of pike known was in Lapland, Sweden where they comprised 38.2% of 809 food items. Considered a top predator in many freshwater ecosystems (and thus with less significant anti-predator camouflage), the pike may be more conspicuous than many fish to hunting eagles due to the fish's boldly speckled flanks. While an average mature weight for a pike is around 1.4 kg (3.1 lb), white-tailed eagles often attack larger sized pike, with an estimated average weight range of 2 to 5 kg (4.4 to 11.0 lb). Some pike taken by white-tailed eagles were even estimated to weigh around 12 kg (26 lb), however the eagle would be unable to fly with such a large catch and would need to row it the nearest shore. The next most widely reported fish prey species is the common bream (Abramis brama). This bream was reported in 10 of 18 dietary studies and was the main prey in the Polesie State Radioecological Reserve, Belarus, in the Ural mountains region of Russia, and in the Kostomuksha Nature Reserve, Russia. Like the pike, the relatively large size of common bream, which weigh about 1.09 kg (2.4 lb) on average, can prove attractive to hunting eagles. They are also vulnerable to tapeworms so can be easily taken while floating close the water's surface in ill condition.
Many varieties of fish are taken opportunistically and randomly, as opposed to pike and bream, which can locally appear to be selected out of proportion to their regional population. Particularly diverse in the white-tailed eagle's prey spectrum are the family Cyprinidae, of which more than 20 species are known to be predated including the common bream. Others taken with some preference may include salmonids and cod and their allies, both families known to obtain relatively large body sizes and occasional habituate shallow water, as well as lumpsuckers, because they are benthic. In Greenland, the leading prey species is the salmonid, the Arctic char (Salvelinus alpinus), which comprised 27.2% of 660 prey items. The secondary prey in Greenland was recorded as two species of cod. While the Arctic char can average up to 2.53 kg (5.6 lb) and cod can sometimes grow considerably larger than that, the average weight of cod taken here was estimated at only 420 to 640 g (0.93 to 1.41 lb) and the average char at 660 to 740 g (1.46 to 1.63 lb). In Norway, of 524 fish prey items, the common lumpsucker (Cyclopterus lumpus), which averages up to 1.43 kg (3.2 lb) but is usually smaller, made up 24% of fish taken and the 2.13 kg (4.7 lb) Atlantic wolffish (Anarhichas lupus) made up 17% of fish taken. However, fish were secondary to birds overall in Norway. Per two studies from Sweden, fish were usually the main food unlike in Norway and Finland and could comprise from 51-60% of the diet. Fish were also somewhat dominant in the foods from two studies in Belarus, making up 48.1-53.7% of the diet. Fish similarly were important to nesting eagles in Hokkaido, where 54% of 533 prey items were fish, led by the 800 g (1.8 lb) Alaska pollock (Gadus chalcogrammus) at 18.4%. In different studies of the Danube Delta of Romania, from 44.6% to 79% of the diet was comprised by fish, led by the common carp (Cyprinus carpio) and Prussian carp (Carassius gibelio). In the Kostomuksha Nature Reserve of Russia, fish were strongly dominant in food remains, making 80% of the known diet.
White-tailed eagles are known to prey on about 170 species of bird, the most diverse group in their prey spectrum. While hunting birds, this massive, relatively slow-flying eagle requires an element of surprise, with often a tactful use of cover or bright sunlight upon the approach from a nearby perch. For example, grey herons (Ardea cinerea) have been caught after an eagle used a low flight over turbulent water to ambush them. However, even with a stealthy attack, the waterfowl favored in the avian diet tend to be highly wary and will more often than not escape. The white-tailed eagles must then attack birds at times of vulnerability or injury, or will often utilize the prey's escape tactics against them. Diving ducks and other diving water birds will be taken preferentially where they are available. In hunting diving birds, they utilize a technique of forcing the birds to dive repeatedly to avoid attacks, until the victim is exhausted from the efforts and can then be caught. Usually while hunting like this, the white-tailed eagle tends to circle low to stay close to the intended victim, with birds diving in shallower water being preferred. Ducks with conspicuous plumage, such as male common eiders (Somateria mollissima), with their pale plumage, may be easier to see under water and so may be taken somewhat more via this hunting method. Beyond waterfowl, both loons and grebes have been seen to be successfully hunted in this way. Eagles were recorded doing between 7 and 12 attacks on eiders in Russia and were usually successful in procuring prey. Even as many as 65 passes have recorded in less 45 minutes but more than a few attacks also start to exhaust the eagle, as one immature gave up after 15-28 attempts at a little grebe (Tachybaptus ruficollis). While bald eagles may attack diving ducks in the same way, they appear to do so somewhat less regularly and successfully. White-tailed eagles usually have less success hunting dabbling ducks because their normal predator response behavior is to take flight. In one instance, a mallard was caught while flying in mid-air, but usually the much larger eagle is unable to capture ducks in flight. While somewhat less swift in flight, healthy geese can usually outpace a heavier eagle as well and one bean goose (Anser fabalis) was even recorded to have defended itself successfully against an eagle's attack even though this goose was injured. White-tailed eagles often hunt dabbling ducks and geese most successfully when they are molted into their eclipse plumage which renders them temporarily flightless. Swans during winter may find themselves forced to land due to their bulk on a sheet of ice over water if they can find no open water, which can make their feet stuck to the ice. White-tailed eagles have been recorded utilizing this disability to attack and kill swans. They’ve also been seen to attack numerous waterfowl when the birds are injured by buckshot from duck hunters. Due to their status as enemy of other large birds, they are frequently mobbed by them and white-tailed eagles have been recorded utilizing violent mobbings to suddenly turn over in flight and predaceously grab one of the birds mobbing them, including large gulls and even a northern goshawk (Accipiter gentilis). As an opportunistic predator, it often takes young birds freely as well as adult and fledged juvenile birds. In general, due to different nesting situations, white-tailed eagles instead of dabbling or diving water birds usually attack the more conspicuous or open nests of gulls, those of several other types of seabird, large corvids or other accipitrids. In Germany and Scotland, up to 86% of gulls taken were nestlings and juveniles. Cases of white-tailed eagles eating eggs, instead of nestlings or older birds, is considered rare. Nonetheless, they have been recorded eating a few eggs, which they may carry in their beaks rather in their feet, of some seabirds such as kittiwakes, eiders, cormorants and gulls.
The most widely recorded avian prey species and, second most widely recorded prey species behind the pike, is the 1.14 kg (2.5 lb) mallard, due to its circumpolar range and commonality in many wetlands areas. However, as aforementioned, healthy mallards are difficult for white-tailed eagles due to their tendency to fly at first sign of danger. However, exploiting the mallard's flightlessness during eclipse plumage may result in eagles hunting them intensely only in late summer. Due to this mallards are usually a secondary prey species year around. The largest known representation of mallards in the diet were from Müritz National Park, Germany, where mallards were the 3rd best represented prey species at 10.1% of 247 items and from Augustów Primeval Forest, Poland, where mallards were the 2nd most numerous prey and made up 9.84% of 803 items. Taken more preferentially where they occur are common eiders. When hunting eiders, perhaps the largest of diving ducks at a mean weight of 2.06 kg (4.5 lb), white-tailed eagles frequently force the eider to dive repeatedly until it is exhausted and can be captured. When sitting on the nest, the female common eider will try to escape in flight but is a relatively weak and ponderous flier and so too may be often victimized by the eagles. Otherwise the pale plumage of adult male common eiders while they’re diving is reported to make them more vulnerable to eagle attacks. Eiders were the leading prey species in Norway making 18.8% of 1612 prey items, as well as in the Åland Islands, Finland where the eider comprised 18.63% of 5161 prey items (thus nearly a thousand eiders were taken here). Eiders also appeared to be the main prey species in Iceland. There is evidence that a growing white-tailed eagle population is having a net negative effect on eider numbers in some areas, and locally eiders have altered to partial nocturnal foraging apparently to avoid hunting eagles. In inland regions, an avian prey species preferred by white-tailed eagles is the 836 g (1.843 lb) Eurasian coot (Fulica atra). The coot is the second most widely represented bird prey species (and fourth species of any class known overall) in 18 dietary studies. Coots bunch together in marshy spots when approached by a flying eagle and as many as 5 eagles at once have been recorded attacking large flocks on the water. Coots behaviour often endangers them to large raptors: they seldom dive, are weaker and slower fliers than most water birds and are collectively often less wary and more approachable than most waterfowl are. Coot were strongly the dominant food in Wigry National Park, Poland where they made up 44.1% of 299 items, and were also the leading prey in Augustów Primeval Forest, Poland where they made up 11.59% of the foods. Overall at Wigry and Augustów, birds altogether made up 66.2% and 47.83% of the diets, respectively. In the Danube Delta, Romania, birds climbed in importance of the diet from 21% in 1970 to 50% by 2015, thanks largely to increased numbers of coots.
In total, about 38 species of waterfowl are known to be hunted, as well as all available species of loons and grebes, several types of rails, tubenoses as well as herons, storks and other assorted large waders. White-tailed eagles also are known to hunt some 42 species of shorebird, most significantly gulls and alcids. Even shorebirds as small as 21.1 g (0.74 oz) little stint (Calidris minuta), 62.6 g (2.21 oz) wood sandpiper (Tringa glareola) and 64 g (2.3 oz) common ringed plover (Charadrius hiaticula) are known to be preyed upon, albeit quite rarely. More than a dozen gulls are known in the prey spectrum from the smallest to all four largest extant species. In the United Kingdom, northern fulmar (Fulmarus glacialis) are noted as a common prey species and as such may contribute to locally high levels of DDT and PCB chemicals in nesting eagles. However, fulmars defend themselves by regurgitating a smelly, tar-like oily substance that can impair the flight of predators and may even kill some intended predators when it is in large quantity, and young juvenile eagles, being less cautious and experienced, are most prone to being severely “oiled”. Alcids such as murres tend to become especially important in the diet of eagles in coastal Norway during winter, especially near offshore islands, when coastal fish tend to move to deeper waters. At least 8 species of dabbling duck are known in the prey spectrum. Due to the social inclination of dabbling ducks, they perhaps have the most success hunting isolated birds but they’ve also been taken from panic-stricken flocks as well. Despite the difficulty of taking them, dabbling ducks of unidentified species were found to be the main food of white-tailed eagles in Lake Baikal, where they comprised 51.8% of 199 prey items. In Fennoscandia, they are attracted to coastal waters during winter to attack large numbers of diving ducks including eiders, common goldeneye (Bucephala clangula), common (Mergus merganser) and red-breasted mergansers (Mergus serrator), tufted ducks (Aythya fuligula) and scoters. Year around in the Åland Islands, 66.2% of 5161 food items were birds, while in the 3 sites in different parts of Finland birds made up 51.1% of 3152 food items. In Germany, 52.4% of 1637 prey items were birds, mostly coots and unidentified waterfowl. More locally in Germany, in Müritz National Park the percentage of birds in the diet climbs to 65.73% Birds were strongly dominant in food records from Scotland, making up 73.53% of 1930 prey items, and in Kandalaksha Nature Reserve, where they comprised 75% of 523 prey items.
While most of the aforementioned water birds are modest of size and taken largely due to ease (diving water birds, whether healthy or infirm, and usually infirm or molting dabbling water birds), white-tailed eagles routinely attack larger water birds as well. In many areas, large numbers of 3.31 kg (7.3 lb) graylag geese (Anser anser), Europe's largest native wild goose, are taken. For example, they were the main prey, making up 28.2% of 192 prey items, for wintering eagles in Oostvaardersplassen, Netherlands, and the 2nd most often recorded prey species in both Müritz National Park, Germany, where they made up 16.42% of 247 prey items, and in Austria, where they made up 9.5% of 349 items. White-tailed eagles are known to prey on at least 10 species of geese, ranging in size from the 1.23 kg (2.7 lb) red-breasted goose (Branta ruficollis) to the non-native 3.69 kg (8.1 lb) Canada goose (Branta canadensis). They will take many goslings during summer, as greylag goslings alone can comprise up 23% of the seasonal bird prey, and fully-grown geese in other seasons. Large waders are taken when possible, including a half dozen heron species, and, larger still, both the young and adults of 5.5 kg (12 lb) common cranes (Grus grus) and both the 2.93 kg (6.5 lb) black and the 3.44 kg (7.6 lb) white stork (Ciconia ciconia). Black and white storks are primary prey species in the Polesie State Radioecological Reserve, Belarus where they comprised 12.6% (2nd most regular prey species) and 6.3% (4th most regular) of the diet, respectively. Large numbers of black stork were also taken in Augustów Primeval Forest where nearly 50 were found around eagle nests. They are reported to have attacked and eaten the largest seabirds they encounter, such as great cormorants (Phalacrocorax carbo) and in some cases, such as in the Baltic sea, have nearly destroyed whole colonies, from the eggs to the adults which average about 2.57 kg (5.7 lb). In the Estonian island of Hiiumaa, home to at least 25 pairs of sea eagles, as many as 26 individuals have been observed simultaneously culling a single cormorant colony. Similarly large numbers were taken of the 2.82 kg (6.2 lb) Japanese cormorant (Phalacrocorax capillatus), which was the second most numerous prey species, making up 11.63% of 533 prey items in Hokkaido, and opportunistically, when their north Atlantic colonies are accessed, great numbers of 3 kg (6.6 lb) northern gannets (Morus bassanus). Vagrant white-tailed eagles in Hawaii were recorded to prey on several Laysan albatross (Phoebastria immutabilis) and were suspected to prey on black-footed albatross (Phoebastria nigripes), both weighing about 3.17 kg (7.0 lb). Another large water bird taken as adults are 4.98 kg (11.0 lb) common loons (Gavia immer). However, the largest water birds they are known to kill are adult swans, including mute (Cygnus olor), whooper (Cygnus cygnus) and Bewick's swans (Cygnus columbianus bewickii). While cygnets and disabled birds (either by natural conditions such as ice or by human hunters) are at the greatest risk for eagle predation, white-tailed eagles have prey upon even healthy adult swans weighing at least 10 kg (22 lb).
While land birds are a more infrequently part of the diet, at least 60 species have been recorded in the white-tailed eagles prey spectrum. For the most part, land birds are taken so infrequently as to not warrant much mention. However, variable numbers of gamebirds are taken opportunistically, and in Belarus and Russia, especially around the White Sea where ptarmigan are not infrequent prey, they will take a few grouse. White-tailed eagles are known to prey on some numbers of ring-necked pheasant (Phasianus colchicus) in Austria. They will at times attack adult male western capercaillie (Tetrao urogallus), of note for their large size at 4.2 kg (9.3 lb). However, this is dwarfed by the largest avian prey credited to a white-tailed eagle, an adult male great bustard (Otis tarda), which weighed an estimated 15 kg (33 lb) (which, much like exceptionally large fish taken, must have been consumed in the killing spot or subsequently dismantled as too large to fly with). Among the land birds taken, more than 20 passerines are included in the prey spectrum but most are obviously too small and swift to be anything but incidental prey. The smallest avian prey known for white-tailed eagles was a great tit (Parus major), a species which weighs 16.4 g (0.58 oz) on average. On one hand, small bird prey may be under-recorded since they leave few conspicuous remains but, on the other, are unlikely worthy of much pursuit as they have little food value. However, in one case, a white-tailed eagle was seen to fly into a murmuration of Eurasian starlings (Sturnus vulgaris) and come away with a starling in hand. The only passerine family taken in numbers would be the larger corvids, of which 8 species are known in the prey spectrum. In Hokkaido, Japan, two species of corvid were well-represented in the diet, the 519.5 g (1.145 lb) large-billed crow (Corvus macrorhynchos) and the 570 g (1.26 lb) carrion crow (Corvus corone), which together comprised 14.8% of 533 prey items.
Mammals and other prey
Mammals are usually a quite secondary component of the diet. Although usually better represented than other non-fish and bird prey, their regional importance is variable. In known dietary studies, the mammalian contribution can vary from 0.49% to 41% of prey by number. When mammals are most significant to the diet, it usually due to local white-tailed eagles preying on rabbits and hares with some regularity. In some studies from Scotland, the European rabbit (Oryctolagus cuniculus) and mountain hare (Lepus timidus) were found to contribute as much as nearly 25% of the diet. A similar contribution of European hares (Lepus europaeus) was found in the diet from Austria, where hares were the leading prey species making up 24.35% of 349 prey items (with mammals making up 34.67% of the overall diet). In studies from Germany, European hares were taken fairly often but were numerically secondary prey. Given that these rabbits and hares have average mature weights from 1.8 kg (4.0 lb) in rabbits to 3.8 and 4.2 kg (8.4 and 9.3 lb) in European and Arctic hares (Lepus arcticus), they can make a hearty contribution to the prey biomass when available (although certainly juveniles are attacked as much if not more so than adult rabbits and hares). Other large mammalian prey can include foxes, with 3.2 kg (7.1 lb) Arctic foxes (Vulpes lagopus) being the 6th most regular prey species in Greenland and about a dozen 5.77 kg (12.7 lb) red foxes (Vulpes vulpes) recorded as taken or scavenged in Norway (predaceous attacks on adult red foxes have been reportedly witnessed). In both the offshore islands of Norway, where Arctic hare can be important prey, and Greenland, where the Arctic fox are prey, large numbers of both are taken when their pelage remains white but snow melts prematurely. A white-tailed eagle was once observed to kill and feed on a live adult golden jackal (Canis auereus) that was trapped in a furbearer's trap. White-tailed eagles are known to prey on seal pups but most are likely sickly and perhaps both adult and pup seals are most likely to be eaten as carrion. Four Baikal seal (Pusa sibirica) pups were taken in Lake Baikal. They are considered a predator even for live grey seal (Halichoerus grypus) pups that weigh 11.75 kg (25.9 lb) at birth. In one instance, a white-tailed eagle reportedly tried to attack an adult harbor seal (Phoca vitulina) but was immediately dragged into the water and soon surfaced dying with a broken wing. Similarly, in one anecdote, an eagle drowned while apparently attacking an adult harbor porpoise (Phocoena phocoena). At least 7 species of mustelid have been recorded in the white-tailed eagle's diet, from the smallest weasel to, rarely, even adult European otters (Lutra lutra). Another mustelid, the American mink (Neovison vison) was introduced as a furbearer to Finland but then became an invasive pest, as a fast-breeding killer that threatens many native species. In turn, Finnish white-tailed eagles have become the main natural control and may inhibit the mink from breeding via heavy predation. Conversely, the white-tailed eagle have not been known to prey on the critically endangered, native European mink (Mustela lutreola) (perhaps due to its shier habits) which the American mink are known to have been outcompeting in some areas (but the European has mainly declined due to massive overhunting by humans as a furbearer). Kits of larger mammals such as Eurasian (Castor fiber) and North American beavers (Castor canadensis) (introduced) and of European badger (Meles meles) have been found as prey.
The most widely reported mammalian prey known (albeit usually as a supplemental prey species) in the non-native muskrat (Ondatra zibethicus), which averages about 1.1 kg (2.4 lb), and may be taken from “muskrat farms” or feral wetland populations. While largely a supplemental prey item, a respectable number of 137 were recorded in the diet from Finland. Also, a study on the Ili delta in Kazakhstan has shown up to 30-43% of prey remains at eyries to consist of muskrat in spring and fall but only 14% in summer (for unknown reasons). In total, about 20 rodent species are known in the white-tailed eagle's prey spectrum. In some of the coldest climes of Russia, such as in the Ural mountains or the Kola peninsula, white-tailed eagles have been recorded to live on surprisingly high numbers of small rodents, comprising 13.8% and more than 21% of all prey remains, respectively. Even agile red squirrels (Sciurus vulgaris) may be caught from trees in some cases. The smallest rodents known in the prey spectrum are the 27.4 g (0.97 oz) common vole (Microtus arvalis) and the 23.4 g (0.83 oz) wood mouse (Apodemus sylvaticus) but mammalian prey down to the size of 8.1 g (0.29 oz) common shrews (Sorex araneus), indeed the smallest vertebrate known to have been preyed upon, has been recorded. On the other end of the size scale from rodents, more than a dozen ungulate species have been found in the foods of white-tailed eagles, but a very large proportion of this is likely from carrion found already dead. Very large food sources such as horses (Equus ferus caballus), moose (Alces alces), cattle (Bos taurus) and European bison (Bison bosanus) are certainly visited as carrion always. Wild ungulate species known to have their young attacked by white-tailed eagles in variable numbers may include deer such as reindeer (Rangifer tarandus), red deer (Cervus elaphus) and European roe deer (Capreolus capreolus) and wild boar (Sus scrofa). Boar made up 7.1% of the prey remains at Polesski Reserve, Belarus. At least two successful attacks on adult roe deer have been reported, which could potentially weigh around 25.4 kg (56 lb) (their average mature weight), in addition to several cases of predation on young roe deer. A yearling juvenile male eagle scaling 5 kg (11 lb), newly reintroduced into the wild on Rùm killed a healthy, 7 kg (15 lb) red deer calf within a couple days. One of the primary causes of the white-tailed eagles persecution by humans is that white-tailed eagles often feed on domestic sheep (Ovis aries) and goats (Capra aegagrus hircus), especially lambs and kids. However, they very seldomly take any healthy specimens and mostly feed on these after death. Of 36 cases of feeding on lambs and kids by white-tailed eagles in Norway, only 12 could be proven to have been taken alive by the eagles.
Prey of other animal classes is rarely taken by white-tailed eagles. Particularly, the diversity of reptiles known in the prey spectrum, at only 6 species, is quite paltry when compared to the many species known to be hunted by the bald eagle. Further among amphibians only two species of toad are known to be taken. The Ural mountains is the only region where some diversity of reptile and amphibian species have been reported in their diet. In only the white-tailed eagles nesting in Hokkaido, they’ve been known to hunt large cephalopods such as robust clubhook squid (Onykia robusta) and giant Pacific octopus (Enteroctopus dofleini), though likely mainly younger specimens and those collected and perhaps injured by large-scale fishing operations. White-tailed eagle juveniles have been seen rarely foraging for unidentified clams and mussels on the Rhine. However, the miscellaneous shells of marine mussels and snails found in Norway are probably usually consumed secondarily from the stomachs of eiders. An exceptional number of insects, amounting to 24% of food items by number, were found in the foods of white-tailed eagles in Augustów Primeval Forest, Poland, almost entirely Odonata. The source of this food is not clear as the white-tailed eagle is far too large and bulky a raptor to invest much time in pursuit of insects.
Interspecies predatory relationships
As the largest eagle in the majority of its distribution, the white-tailed eagle is assuredly an apex predator in its range. In some areas, it may compete somewhat however with other large raptors, especially golden eagles. Relations between these two species are complex and variable. In Scotland, where both eagles have been reintroduced or re-established, competition is particularly considerable. This is, in part, due to their diets being more similar than elsewhere in their range, with both species preying heavily on rabbits and hares and being reliant on carrion year-around, whereas in most other areas both favor carrion mostly only in winter. As much as 90% of their diets in Scotland can overlap. As in Scotland, golden eagles by preference hunt mainly rabbits, hares and gamebirds (and some ground squirrels) while the white-tailed eagle elsewhere usually prefers fish and water birds. Another factor is the reintroduction of white-tailed eagles occurred after golden eagles had been re-established in Scotland and that some of the golden eagles began to nest, beyond their usually rocky, mountainous habitats, in or near trees in coastal or near lowland wet areas historically occupied by white-tailed eagles. Therefore, increased heated territorial conflicts between the species have been recorded in the last several decades. Given appropriate healthy populations and ample habitat, as in Norway, the golden and white-tailed eagles are considerably segregated in nesting regions and direct competition is much milder. In spite of a size advantage for the white-tailed eagle, the golden eagle is reportedly “strongly dominant” over the white-tailed in food conflicts and, perhaps, in direct nesting competition. This is in part because of the swifter, more agile flight of golden eagles, as well as their greater overall aggression towards other raptors and perhaps due to their somewhat longer toes and larger talons, although there is little evidence that the golden and white-tailed eagles are notably different in strength. In many intraguild diurnal raptor assemblages, a slightly smaller, swifter-flying species often dominate their heavier competitors unless size differences become extreme, to the contrary of owls and several other predators which often adhere fairly strictly to a size-based dominance hierarchy. Golden eagles won all food conflicts over carrion observed by one author over the course of two winters in Norway, with the white-tailed eagles only displacing goldens after the golden eagles had already fed for some time. However, cases of white-tailed eagles winning food conflicts have been reported as well and perhaps more assured mature white-tailed eagles may fare better in such conflicts. Some territorial conflicts in Scotland have escalated, albeit rarely, to both eagle species killing the other. White-tailed eagles are said to be “dominant”, however, in population ecology as they can exist at higher population densities and typically outnumber golden eagles because of their longer gut and more efficient digestive system, being able to live better with less food. Notably, in competition in North America, neither the golden or bald eagle are said to be dominant and either species may win conflicts. Furthermore, bald eagles may succeed in procuring up to 25% of fresh golden eagle kills in winter and golden eagles are reported to decidedly avoid active nesting areas of bald eagles.
Beyond golden eagles, white-tailed eagles may live alongside a wide range of other large raptors, but other eagles are considerably different in dietary and habitat preferences, so there is almost no competitive effect. For example, in Kazakhstan, white-tailed eagles were recorded to nest in proximity to golden eagles, eastern imperial eagles (Aquila heliaca) and steppe eagles (Aquila nipalensis) and all four eagles appear almost entirely indifferent to the presence of the other species, given their considerable partitioning in diet and habitat preferences. More significantly than the Aquila species, the white-tailed eagle seemed to have no issue nesting within a few hundred metres of the other eagles. A more direct effect may be detected on other fish-eating birds, for example recovering numbers of white-tailed eagles in Lithuania was thought to limit local osprey populations. However, in similar habitats, white storks and lesser spotted eagles (Clanga pomarina) appeared to not be competitively effected. Besides competitive effects, white-tailed eagles may adversely effect ospreys by habitually robbing them of their catches. Besides the poorly studied relations between the Pallas's fish eagle and white-tailed eagle in the southern limits of the latter's Asian distribution, the only other Haliaeetus to live broadly alongside white-tailed eagles are Steller's sea eagles. Being larger and heavier, the Steller's is often characterized as a more powerful predator. Nonetheless, studies of the species ecologies show that the Steller's is a more restricted feeder on salmonids and that the Steller's tended to defend a smaller home range area than white-tailed eagles do in the Russian Far East. However, the Steller's appeared to be more flexible in readily switching nest sites between trees and rocky areas, whereas white-tailed eagles of this area exclusively nested in trees. Both species seemed to avoid active territories of the other but little direct conflict during breeding was detected. Although the Steller's sea eagle may be somewhat favored in wintertime food conflicts given its sometimes considerably larger size, both it and the white-tailed eagles have been observed to win conflicts over fish, with golden eagles sometimes entering the fray and sometimes losing or winning conflicts. Given their larger population and farther current range into warmer areas (whereas the modern white-tailed eagle is only common in cold, northern climes), bald eagles (the ecological equivalent of the white-tailed eagle in North America) have a considerably broader prey spectrum than white-tailed eagles that ranges well over 400 species, with more species recorded from nearly all animal taxon. Although about 56% of the bald eagle's diet is comprised by fish, bald eagles often take a higher diversity and numbers of alternate prey such as mammals, reptiles and amphibians than do white-tailed eagles.
Although other birds of prey are seldom caught, given that they are wary, fast and can defend themselves well, the white-tailed eagle can be characterized as an opportunistic predator of such birds. Indicating that they are regarded as a threat to raptors is that they are frequently mobbed by a wide range of raptor species when displaying active flights, to a similar regard that the perhaps more aggressively predatory golden eagle is. Given the difficulty of this prey type, white-tailed eagles are likely to attack other birds of prey when the victims are distracted, whether by migration on windy days, nesting duties or when trying to capture their own prey, are previously injured or they may even capture one while the raptor tries to mob the eagle. Certainly, nestlings and fledglings can certainly comprise a large fraction of the birds of prey caught as well as adult ones. Other accipitrids they are known to have preyed upon, in increasing order of size are the Eurasian sparrowhawk (Accipiter nisus), western marsh harrier (Circus aeruginosus), black kite (Milvus migrans), European honey-buzzard (Pernis apivorus), common buzzard (Buteo buteo), northern goshawk, red kite (Milvus milvus), lesser spotted eagle (Clanga pomarina) and eastern imperial eagle, in addition to osprey. Non-accipitrid raptorial birds, these more likely restricted to fully independent birds due to their less conspicuous nests, known to fall prey to white-tailed eagles include Eurasian pygmy owl (Glaucidium passerinum), boreal owl (Aegolius funereus), Eurasian hobby (Falco subbuteo), long-eared owl (Asio otus), northern hawk owl (Surnia ulula), short-eared owl (Asio flammeus), peregrine falcon (Falco peregrinus), snowy owl (Bubo scandiacus) and Eurasian eagle owl (Bubo bubo). Accipitrid prey size ranges by body mass ranges from 237 g (8.4 oz) for a sparrowhawk to 3.13 kg (6.9 lb) in the imperial eagle and that of non-accipitrid raptors ranges from 58.5 g (2.06 oz) for the pygmy owl to 2.68 kg (5.9 lb) for the eagle owl and apparently both imperial eagles and eagle owls that were caught were adults. As true apex predators, healthy adult white-tailed eagles have no known natural predators.
Courtship and mating
The breeding season is from January to July in the south of the white-tailed eagles range, and from April to September in the northern part of their range. They pair for life, though if one dies replacement can occur quickly. A bond is formed when a permanent home range is chosen. White-tailed eagles frequently engage during early spring variously in soaring, sky-dancing and other aerial displays, all with much loud calling, often performed by pair members together, including spectacular mutual cartwheel downwards where talons touch or interlock. Nuptial displays may occur almost year-around in some parts of the range, increasing after young disperse in autumn, thence at rare intervals until spring when such behavior, of course, peaks. Courtship often begins with a bird, often the male, "sky pointing" or "long calling" by throwing their head back. Soaring by pairs follows, with either partner leading by 1 to 6 m (3.3 to 19.7 ft) or soaring opposite directions. One may swoop upon the other who responds by tilting to one side or may roll over to touch talons momentarily before separating. This may be repeated or gain intensity until they are talon-grappling or "mutual cartwheeling", consisting of the pair locking talons mid-air and whirling earthwards in series of spectacular cartwheels. When doing this, the pair may stop only a few feet above the ground. Talon grappling is usually associated with territorial clashes in most accipitrids, especially between males, but in Haliaeetus such behaviour also seems to be related to courtship and is engaged by pairs as well as males attacking intruding males. When locally common, 2-3 pairs can be seen displaying in the sky quite near each other but each pair in fact are within a border of a well-defined territory. In Greenland, recorded pair densities were 0.3-0.6 occupied territories per 100 km2 (39 sq mi). In eastern Germany, densities were reported as 1.6-2 pairs per 100 km2 (39 sq mi). Norwegian nests appear at no closer than 1–2 km (0.62–1.24 mi); territory size on Norwegian coasts were reported as roughly 6 to 9 km2 (2.3 to 3.5 sq mi). Fischer noted 8-9 pairs on the small Norwegian island of Fugloy due to its huge seabird colonies, with late summer numbers boosting to 75 eagles, all within an area of only 22 km2 (8.5 sq mi). 5 occupied nests were noted on a 80 km (50 mi) stretch of the Russian Yenisei River. Mating chiefly occurs between mid-March and mid-April in most parts of the range. The pair may copulate be about once every 20 minutes for several hours. Prior to mating, a more skilled and graceful flying than usual may be undertaken by the male as the final stage of courtship. After his final display, the female crouches low, almost flat, with her head and neck outstretched, wings half open, and tail held level with the rest of the body. Mating has been recorded in white-tailed eagles to occur almost anywhere including a low perch, on the nest, on the ground or even on frozen lake surfaces, usually close to the nest at least but also at as far away from the nest as 3 km (1.9 mi) in Norway. Sometimes both members of the pair will assume the female's typical mating position simultaneously side-by-side until he jumps on her back. Once the male mounts he often calls loudly and flaps both wings to maintain his balance. After about 12 seconds he dismounts and sits quietly, ultimately will do so about 5 to 6 in 1.5 hours and at nearly any time of the day.
White-tailed eagles most often nest in large trees, with perhaps coniferous trees preferred and nests may be in a high main fork, on the canopy or a large side branch. Access to food is a key consideration in the nest's location in white-tailed eagles. In Germany, 75% of eyries were within 3 km (1.9 mi) of a lake, although one was 11 km (6.8 mi) away from any lake though was somewhat closer to the Baltic Sea. 80% of German nests were described as being in forests but eagles exhibited preferences for wooded islands or promontories and most nests were usually towards edge of open space: a clearing, marshy ground or even agricultural land. Among the few eyries in open land were never more than 150 m (490 ft) away from woods. Only 1 cliff nest was recorded in Germany, on the Baltic island of Rugen. Older records indicated ground nests also recorded in the German Baltic region. Most German nests were at heights from 2 to 10 m (6.6 to 32.8 ft) off ground in the main fork of trees, rarely on ample horizontal tree branches. Tree nest height is partially based on tree species, i.e. in Romania, on black poplars (Populus nigra) and willows nest height would was recorded at 15 to 25 m (49 to 82 ft) of the ground but one was on a broken tree at only 7 m (23 ft) from the ground. There in the lower Danube of Romania beyond the mainly utilized black poplars and willows, one was on "a weak oak sapling", 6 on high, thick oaks, 5 in white poplars (Populus alba), 2 in beeches and one in a wild pear tree. Another quote on eyrie height along the Danube was at 19 to 33 m (62 to 108 ft) above the ground. Trees used for nests in Hokkaido were often the tallest in a stand, averaging 2.8 m (9.2 ft) higher than the average tree height in their stand. Tree species preferred here were Picea glehnii and Alnus japonica. Nest height in Hokkaido was similar to that in Europe at 16.5 to 25 m (54 to 82 ft) above the ground. In eastern Germany, among 177 nests, 65% were in mature pines, 22% in copper beeches (Fagus sylvatica), 8% in oak with the remainder in alder, elm, poplar and birch. The German eyries ranged in height from 8 to 30 m (26 to 98 ft), averaging 20 m (66 ft), usually in tallest trees available. Nests can be on crags, whether or not trees may be available, depending on regional habitat. In 98 Norwegian eyries, only 8 were in trees, the rest were on cliffs. In comparison, against the 86% nests that were on cliffs in Norway, 79% known in Scotland were too, 77% in Iceland and all known Greenlandic nests were in cliffs or other rocky spots. Nest height on cliffs can be over 75 m (246 ft) above the nearest flat ground. Rarely, they may nest on the ground or a low hummock, as well as smaller trees, low bushes, on sand banks or among reed beds. Showing their adaptability, one pair even nested on a buoy on a Norwegian shipping route.
Nests are usually huge, constructed of sticks and branches, averaging roughly 1 m (3.3 ft) across and up to 2 m (6.6 ft) deep, but can be several metres in width & depth, lined variously with moss, greenery, seaweed or wool. The nest must have easy access for the eagles with a clear view of the surrounding environment, shelter from the elements and protection from nest predators. In forest of Finland, it has been estimated that perhaps only 1 in a thousand trees will prove attractive to white-tailed eagles. Cliff nests often include lesser materials, some may be only a scooped shallow depression of soil, or pile of heather or juniper stems with stipes of dried Laminaria, but also sticks up to 1.5 m (4.9 ft) and several cm thick may be incorporated; almost any material available may line the nests such as seaweed, driftwood, even glass or metal floats and, in one to two cases, the dried skeleton a sheep. In tree nests, the average nest diameter is about 1.5 m (4.9 ft), with nests in trees tending to be larger, more rigid and stronger. A relatively new 4 year old nest weighed 240 kg (530 lb) and one about twice that age can exceed 600 kg (1,300 lb) in mass. Some tree nests may range easily up to 2 m (6.6 ft) in diameter and 3 m (9.8 ft) deep after many repairs over years, with extreme sizes of perhaps another metre in diameter and depth, or “twice the height of a man”. Tree nests may be lined with lichen, moss, seaweed, ferns, grass, woodrush, heather or Empetrum; many tree nests may be lined with sheep's wool. The male of the pair more often brings nesting branches, while female takes the primary role in construction. A nest may be added to by the resident pair at as early as December onwards, but usually do so starting in March at high latitudes. A new nest may take several months to construct, but if an old nest is lost in late winter, pairs have been known to build a new nest faster than average in less than a month, however egg laying may be inhibited in such cases. Repair to an existing nest can take about 18 days. White-tailed eagles have also used nests built by other species: black kite, common buzzard, common raven (Corvus corax) and, subsequent to the eagles evicting them, ospreys and red kites. Eastern imperial eagles, saker (Falco cherrug) and peregrine falcons have used old white-tailed eagles nests, in the two swift falcon species they've been recorded in evicting pairs of white-tailed eagles from their eyries with persistent dive-bombing. In one case, after having been displaced by humans from an eyrie that had seen 30 years of white-tailed eagle use, an eagle pair returned to find the nest occupied by peregrine falcons. Despite many dogfights, the eagles constructed a nest higher up in the same tree. Although fighting continued, both species succeeded in raising 1 fledgling each. In Norway, pairs of ravens, peregrines and white-tailed eagles have been known to successfully nest on the same cliff face. Many small species of bird may nest in the immediate area of white-tailed eagle eyries, presumably due to incidental protection: Eurasian tree sparrow (Passer montanus), white wagtail (Motacilla alba), Eurasian treecreepers (Certhia familiaris), common redstarts (Phoenicurus phoenicurus), European crested tits (Lophophanes cristatus), Eurasian starlings and stock doves (Columba oenas). Like in the golden eagle, pairs of white-tailed eagles often build multiple nests on their home range over time and use them randomly over different years (sometimes using one for several consecutive years or changing nests every year over several years). The species may build from 1 to 11 nests, averaging 2.5 in Norway with pairs with up to 5 nests being not uncommon in that country.
Eggs and incubation
Individual white-tailed eagles tend to be remarkably consistent on egg-laying times from year to year, seemingly regardless of surrounding weather conditions. Egg laying does vary of course by latitude. Historic breeders from Israel and Iran (where they still usually breed) were reported to lay eggs in January, while in Greece and the lower Volga river it is during February, in Germany mostly during March and in the subarctic of Lapland and northern Russia, to as late as late April to early May. White-tailed eagles in Scotland seem to have average egg laying about 3 weeks later, late March to early April, than those in coastal Norway. Even near Arctic in Finland, eggs were found as early as March 5 despite ranging often to as late as May. Younger pairs may nest later on average than older ones. In white-tailed eagles, many (perhaps a majority) of clutches consist of 2 eggs, especially in Irish and Scottish nests, with 3 egg clutches being considered uncommon to rare there. 4 egg clutches have been recorded on the Isle of Skye, as well as in at least Poland, Romania and Norway. Clutch size in Scotland averages 1.56, while in Norway it is 2.16. The eggs are a broad oval shape and dull white in colour, sometimes with a glossy sheen and are usually unmarked but for occasional yellowish stain. Fresh egg weigh from 120 to 148 g (4.2 to 5.2 oz), with an average of approximately 135 g (4.8 oz) for the 1st egg and 124 g (4.4 oz) for the 2nd. If replacement clutch is laid, usually a single egg is laid which may weigh as little as 112 g (4.0 oz). Average egg dimension seem to keep in accordance with the female body size, smallest mean size known were from Turkey where the average dimensions were 71.8 mm × 56.2 mm (2.83 in × 2.21 in) to the largest in 3 surveys from Greenland, where they were 78 mm × 59.3 mm (3.07 in × 2.33 in). In 54 eggs from Scotland they ranged from 67.5 to 84.2 mm (2.66 to 3.31 in), averaging 75.8 mm (2.98 in), in height by 53.4 to 64 mm (2.10 to 2.52 in), averaging 58.7 mm (2.31 in), in width. In comparison, 90 eggs from mainland Europe ranged from 66 to 88.2 mm (2.60 to 3.47 in), averaging 73.4 mm (2.89 in), by 54 to 63.5 mm (2.13 to 2.50 in), averaging 57.6 mm (2.27 in). Eggs may be compromised quickly by frost and snow in relatively early clutches. Incubation starts as soon as the 1st egg is laid. In the species, a 2 to 3 day interval between the first and 2nd egg being laid (as well as hatching) is recorded. The female does up to 80-90% of incubation and all known nighttime incubating. However, in Norway, the male of a pair could contribute up to about 27% of incubation to daylight hours. There may be as many as 11 changes of the incubating individual within a day. The longest period recorded the clutch was unguarded was 20 minutes, although 1 pair perched nearby the nest without incubating for 48 minutes. The clutches in Norway left alone only 2-4% of the time. In some cases female may do all the incubation alone, however. When the female is off the nest, she sometimes kills prey and returns with a full crop, but prey capture during incubation is often up to the male. Late into incubation, shift changes decreases and the female will sit tight and will crouch down at the approach of a human rather than leave the nest. Calling and displaying are reduced during incubation, but occasionally both may leave the clutch and display still. The time range for incubation can vary from 34 to 46 days, but usually are between 38 and 42 days. A calculated mean time range for incubation of 38.3 days.
Hatching, development and fledgling
In 1983, it was listed that brood size is one 56.5% of the time and two 40.8% of the time in 8 studies from different parts of the range; only 2.5% of these studies had a brood size of three and only 1 from Norway was a brood size of four recorded. From 14 studies, the mean number of chicks in a brood may range from 1.1 in western Germany to 1.9 in southern Kazakhstan, with average overall brood size of 1.52. However, these datasets may be skewered lower than natural brood size as a majority these are from the mid to late 20th century when pesticide use considerably lowered the mean number of hatchlings in many parts of the range. New hatchlings will weigh about 90 to 100 g (3.2 to 3.5 oz) but in Hokkaido new hatchlings were surprisingly notably heavier at 110 to 115 g (3.9 to 4.1 oz). The sex of nestlings can be identified using field methods, or using DNA. Initially, the hatchlings have a creamy white down which is longest and whitest on the head and often dirty grayish on wings and rump. Before they start walking about the nest, their underside may have several bare patches. The nestlings first become audible at around 2 to3 days and have become active enough to move around the nest and excrete over the nest edge by 10 days old. The initial down is replaced by a thick woolly coat of longer, coarser grayish down, which is usually darker on the crown, underparts and flanks. The legs and cere at this young nestling age can range from pinkish to pale yellow. By about 30 days the first feathers poke through the down. The eaglets can feed themselves starting at 35–40 days. At 6 weeks (40 days) they are more firm on their feet and between this and the following week feathers take over the down, with patches of down remaining but usually gone by week 7. Wing flapping begins only when the wings are partially feathered at 42 days. Around seven weeks of age, the eaglet is more alert and stronger and frequently manipulates sticks and walks more so. At 8 weeks only the long feathers of the wing and tail have yet to develop fully and eaglets tend to start exploring the surrounding branches. The eaglets will attempt their first flight at about 70 days and will usually be flying well by about 90 days of age. Fledgling occurs around mid- to late July in Norway, and about 3–4 weeks later in Russian White Sea.
The female of the white-tailed eagle pair seems to do all the brooding early on and will be especially reluctant to leave the nest as well. Thereafter, at 14 to 28 days, brooding behaviour by the female gradually declines. The male may start to brood occasionally around this time period but will not do so at night. Females may sit on the nest or shelter the fledglings from rain even 28 days after fledging but usually such behavior is much reduced. Chicks may be fed as many as 11 times in 24 hours by the female who usually dismantles prey brought by the male. To 28 days, male continues to do most of the prey capture but thereafter female does much of it and both parents begin to leave kills on the nest for the eaglets to consume. As the chicks grow older, favored food often switches from fish to birds to meet their increasing food requirements as well as prey behavior as waterfowl may be flightless during eclipse. Caches are often depleted quickly late into nestling development. At start of fledgling, 4-5 carcasses may be brought in a week but by the end only 1 to 2 are usually brought, probably to encourage the young to start their own prey captures. After leaving the nest, the young usually stay nearby for another 35–40 days and may still be largely fed by their parents but gradually learn to take their own prey. In continental Europe, the young eagles are gone from the nest as early as early July to about August 10 and fully independent by late August. In this late summer stage, they may learn quickly to feed on stranded fish or to capture ducks flightless in eclipse. Juvenile eagles may remain for a long time on their parents range and apparently are not resented or repelled even to the ages of 1 to 3 years. However, usually by their first winter they will have congregated with other unrelated juveniles. Communal juvenile roosts in Norway can maintain 30-40 white-tailed eagles usually in trees or steep slopes of offshore islands. Sexual maturity is reached at 5 to 6 years of age.
Nesting failures and longevity
Normally white-tailed eagles succeed in raising 1-2 from a clutch of 2 and 2 from a clutch of 3. The average breeding success seems to be about 1.1-1.6 young per annum (i.e. 45-48 young from 40 observed cases, with 16 failures) (1.6 young per pair in 93 recorded Norwegian nests). About 33% of nesting attempts will fail to produce any young, and this is sometimes is as many as 75% (at times of heavy persecution or pesticide use). Beyond manmade threats to white-tailed eagle nestlings, starvation and nest collapse are considerable causes of nestling deaths. Natural threats in the nest may also include siblicide (or “cainism”) wherein the largest nestling behave aggressively and gradually kill their smaller sibling, which is often consumed. Despite claims to contrary, siblicide in white-tailed eagle does occur with some regularity in some parts of the range, from Germany to Hokkaido although is certainly less frequent than in some eagle species, including the golden eagle. Single cases were reported in the White Sea and Iceland, and it may occur situationally as in many birds of prey when prey populations are low or prey capture is inhibited by poor weather. Siblicide can be avoided in white-tailed eagles with manipulative techniques, which may include taking out and hand-rearing the runt, put a chick into a nest with slightly younger brood which it is about the same size as, or taking the first egg out and putting it back in later so it develops evenly with its younger sibling. Surplus chicks are sometimes removed from nests to use in reintroduction programs in areas where the species has died out. If left in the nest, they often die sooner or later, as with most large eagles. In such programs the birds are raised in boxes on platforms in the tree canopy and fed in such a way that they cannot see the human supplying their food, until they are old enough to fly and thus find their own food.
Known natural predators of white-tailed eagle eggs and nestlings include red foxes, martens and bears, especially if nesting in overly accessible rock formations, while wild boars have been recorded eating eggs and nestlings that’ve fallen out of the nest too early. Avian predation, overall a seemingly rare occurrence, of white-tailed eagle eggs and nestlings have been reported as crows, common ravens and western marsh harriers, which are likely to succeed in cases where nest attendance is low or if successful in driving away the parents via fierce mobbing. Furthermore, Eurasian eagle owls have been reported to prey upon "fairly large" nestlings of white-tailed eagle in nighttime ambushes. Many juveniles do not survive their first year post-independence. In the 1970s, an average of 56% banded first-year white-tailed eagles in Norway, Sweden and Greenland were found dead, most often having been shot. In eastern Germany, of 194 white-tailed eagles found dead between 1946 and 1972, of those where cause of death could be determined, 39% had been shot, accidents (especially powerlines) accounted for 6%, territorial disputes 7.5% and conservatively 13% were from poisoning. It is estimated that the survival of those that reach adulthood at 70%. Another estimate of average lifespan for those who reach adulthood is just over 12 years. Widely reported individuals have been found to live for 25 years or more, Another estimate of mean lifespan (presumably without persecution) is 21 years. At one point, the oldest banded white-tailed eagle known in the wild known lived for 27 years. However, a wild eagle of the species was subsequently recorded to life for 33.1 years. White-tailed eagles in captivity have lived for more than 40 years, though their exactly captive longevity record is not known.
Relationship with humans
The white-tailed eagle formerly bred over much wider area, extending west to much of western Europe and perhaps south almost continuously in that region to the Mediterranean. From the 19th century, the species underwent a huge, well-documented decline. Ultimately the white-tailed eagle was almost extinct in Europe, extirpated from all but Scandinavia (mainly remaining in Norway) and some sparse patches of eastern Europe. They were extinct in the entire British Isles by the early 1900s. At one time, the white-tailed eagle bred down to Africa in Egypt, particularly around Lake Manzala with individuals wandering rarely to Algeria and Tunisia. It is likely that habitat degradation and drying conditions caused the extirpation of the species as all but a vagrant in Egypt. Two pairs that nested in the Jordan valley of Israel ceased to breed, apparently due to agricultural chemicals, in the early 1950s. The species also once bred in northern Syria but is not found reliably there even in winter in modern times.
Causes of decline
In Britain, the opinion towards white-tailed eagles became negative in sync with the creation of farmland and commercial fishing, as it was quickly perceived that they were competitors for resources and could deplete the livelihood of flocks for shepherds (despite this being largely untrue) and game animals for gamekeepers. Therefore, laws were passed to facilitate their destruction. Already by the end of the 18th century, down from breeding in all appropriate habitat, the English population was down to only localized breeding, namely in the Isle of Wight, Lundy, Isle of Man and (probably) near Plymouth; within a couple decades the species only remained in the Lake District. Before the advent of firearms, few people in England and Scotland were highly motivated to kill eagles since this could be time-consuming and hazardous process, therefore the British government rose the bounty on eagles to a very high 5 shillings a head by the turn of the 18th century. Unfortunately, eyries in many coastal sites were found to be easily accessible so that destroying or selling eggs was common. Subsequent to systematic persecution, in Greenland 62% of eyries found to be "easily accessible" and only 13% foiled all attempts to reach them. Similar findings were found in sea cliff nests in Iceland, Norway and Scotland. White-tailed eagles are more vulnerable to direct persecution than golden eagles since most nests are highly accessible for white-tailed eagle but not for golden eagles which usually nest in mountainous, precipitously rocky terrain, in contrast to sea cliff nests of which 67-87% were found to be accessible. Before firearms were widely available in Scotland and Norway automatic traps were utilized wherein carrion was laid out to entice an eagle with a person hiding in a near subterranean trap waited until the eagle was distracted, at that point grabbing the eagle by the leg. Petrified by the darkness once drug below, white-tailed eagles apparently offer no resistance once caught. However, habitat had to be favorable and even when conditions were correct, success at capture as such was low. The main driver of declines before firearms and industrialized poisons was habitat alterations. After about the 1840s, firearms became available and declines accelerated considerably, by 1916 the last nesting pair in all of Britain attempted to raise a brood on the isle of Skye. While other ecological factors have been considered in this decline, stringent research has shown the extirpation here was fully correlated to intentional, rapacious predation by man. Many gamekeepers poisoned and shot eagles and destroyed nearly any nest they encountered. A few more enlightened landowners forbade the killing of eagles but there's evidence that the gamekeepers sometimes chose to destroy eagles regardless of the rule of law. On deer forest, eagles were tolerated later than in other British areas, but destructions accelerated there by the late 1800s. Also many white-tailed eagles were poisoned by shepherds who considered it enemy of the flock. Elsewhere in Europe, persecution rates in the 19th and 20th century were just as drastic. In Romania, more than 400 white-tailed eagles were killed in 2 decades by a single hunter. In Norway between 1959 and 1968, an average of 169 eagles were killed annually; with a maximum of 221 in 1961. Around the year 1860, an author estimated that about 400 were being killed annually throughout Germany. Between 1946 and 1972 in eastern Germany, a total of 194 dead white-tailed eagles were found, about half of them shot, after governmental protection of the species had been instituted there.
Top predators, especially those that are aquatic and coastal, are almost immediately vulnerable upon exposure to DDT. Therefore, white-tailed eagles are highly susceptible to this pesticide, as are similar fish eaters, such as otters, and bird eaters, such as peregrine falcons. Distributed by man nearly across the developed world as an insecticide in the 1950s, by the early 1970s, authors found many species of bird experienced reduced egg shell thickness. Thus the incubating parents inadvertently crushed their normally hardy eggs and, in turn, many water birds and raptors had their nesting success dropped precipitously. In fact, the species was found to have the highest concentration of DDT of any European raptor. Egg shell thickness was found down from 0.62 mm (0.024 in) prior to 1935 from 1969 to 1975 down to only 0.52 mm (0.020 in), a 16% reduction. In Sweden, coastal birds were considerably more effected by DDT than the inland birds of Lapland. In eastern Germany, where pesticide use was heavy, only 1 out of 28 nesting attempts were known to succeed in 1976. Overall, about 75% nesting attempts failed in western Germany, Finland and the Swedish Baltic area. Other pollutants carelessly put into the white-tailed eagles natural environments included heavy metal contaminations which affect them through bioaccumulation. These were recorded in white-tailed eagles, to 6600 mg/g, compared to about 2500 mg/g in peregrine falcons & only 100-280 g in grey partridges (Perdix perdix) and ring-necked pheasants. Overall, their mercury levels were reported as the highest in any Swedish animal. Like humans, white-tailed eagles are most often threatened by methylmercury when consuming fish (and water birds) with high levels of mercury. The amount of white-tailed eagles killed by mercury poisoning rose from 6.4% during 1946-1957 to 24.6% in 1958-1965 in Germany. It was estimated that pesticides and metal contaminations reduced the white-tailed eagle population in Hungary from 1957 to 1967 by about 50-60%. Lead poisoning, caused by lead bullets left in carcasses that the white-tailed eagles will eat in winter, is also another issue faced by the species. Fatal and near fatal levels of lead exposure continues to be a major issue in the 21st century in many parts of the range, at least from Poland to Hokkaido. Despite regulations on their usage, lead and mercury poisonings were found to be the cause of death of 61 white-tailed eagles found in Germany from 1993 to 2000.
In order to offset the numerous chemical and metal based poisoning that humans were inadvertently exposing the species to, a widespread operation was undertaken to feed white-tailed eagles uncontaminated foods in Sweden. Here, carcasses from slaughterhouses placed in areas free of human disturbance, usually fields, bogs, marshes or frozen lakes, from October to March, as after these months, the eagles will ignore carrion in favor of capture of live prey. Apparently, breeding success improved from 29% to 44% when program began. In southern Sweden, 5 of 11 breeding pairs included a bird breeding for the first time and 2 previously unoccupied territories were taken over by new pairs, thus winter feeding was seemingly highly beneficial to immature eagles. Similar winter feeding stations set up in Finland from 1972 to 1978. In Sweden, brood size has varied from 1.3 per nest prior to 1950, down to 0.3 in 1965-1985. Now the brood sizes have increased, at somewhat less than 1 brood size on average, but still somewhat less productivity than historical numbers. In several parts of the European range, especially southern Scandinavia and central Europe, protections have allowed white-tailed eagles to recolonized former parts of their range. Since recolonizing Schlewsig-Holstein, Germany in 1947, they’ve increased slowly; from 1975-2008, increases were recorded at 6.7% in population per annum and enjoyed much higher productivity. Perhaps particularly key has been conserving white-tailed eagle habitats. In the 1970s, 75% of the potential and current white-tailed eagle territories became protected in Schleswig-Holstein. In Poland, 78% of forests are state owned and clusters of 10 or more trees are preserved around each white-tailed eagle eyrie. The Swedish Forest Service limits logging activities to within 200 m (660 ft) of a nest tree which expands to within 1,000 m (3,300 ft) during breeding season; however this acts not as a law but only as an advisory where the eyries are located on private land. Limits on recreational activity were established as these can disturb white-tailed eagle nests especially in well-trodden countries such as Germany and Sweden, but even in the remote Russian Kandalaksha. In northern Finland, artificial eyries were constructed for their use. Out of 19, 14 were visited by white-tailed eagle, eggs laid in at least 9 and 2 ultimately fledged young. Regulations have been established on direct use of pesticides that harm white-tailed eagles such as DDT, however because of political variances, despite widespread monitoring, not at all areas are strictly protected. Similarly, regulations on lead usage in hunting has been inconsistent in comparison with the stronger efforts to ban lead bullet fragments in North America. The residuals of mercury from various fungicides (now banned), air particles and pollution run-off water have caused huge concentrations in fish of many different areas, which continues to effect humans as well as entire ecosystems of wildlife. Unfortunately, methylmercury is still difficult to manage in Europe as it is elsewhere.
The first attempts at reintroduction in Scotland were in 1959 in Glen Etive, Argyll abortively and then a better informed but also ultimately unsuccessful attempt on Fair Isle in 1968. The isle of Rùm in the inner Hebrides was chosen for the first Scottish reintroduction because of its large size (10,600 ha (26,000 acres)) with access to the isle of Skye (where last native pair known in Britain last bred in 1916) and it is only 24 km (15 mi) from the mainland. Also Rùm hosts large seabird colonies that make for viable prey, including eider, shag (Phalacrocorax aristotelis), auks and gulls; as well as one of the few in Britain of manx shearwater (Puffinus puffinus). Furthermore, mainly as a source of carrion, were a population of around 1500 red deer and 200 feral goats; otters and gulls were also numerous and available to kleptoparasitize. The birds to be used for reintroduction were gathered as nestlings from western Norway, as this is the nearest native breeding population. The young eagles were either kept in high grade fowl cages or tethered all within reach of an artificial eyrie, cover and feeding stations. Direct human contact, which the naturally wild young eagles tended to shun anyway, is minimal short of veterinary care. Releases were carried by taking bird out tethered, wearing a leather hood to prevent imprinting and then releasing with a radio-monitor. Most of the eagles, despite no direct parenting, turned out to be competent hunters within a couple of weeks or do well at stealing meals, including from other released eagles. Despite some dying before release due to illness and some found dead subsequent to release, most survived. A total of 95 birds were received for the Rùm reintroductions and 82 were successfully released between 1975 and 1987. The white-tailed eagle now breeds throughout the Western Isles and the mainland coast of Wester Ross. However, a low reproductive output of reintroduced Scottish eagles was recorded in 1996, and it was advocated that additional releases were needed. In August 2008, an additional fifteen chicks raised in Norway were released at a secret location in Fife, in expectation of reintroducing the species to the east coast of Scotland as well. Breeding success of reintroduced birds in Scotland (from 1975-1985 & 1993-1998) is moderate compared overall in species, in 1982-1992: productivity was 0.38, with a mean fledgling number 1.61. In comparison, for the years 1993-2000, productivity was 0.61 and fledgling number was 1.48, while in 2000-2007, productivity was 0.7 and mean fledgling number 1.44. Overall in Britain, there are estimated 36 breeding pairs in 2006 and 40 in 2008. Juvenile survival rates are somewhat low overall compared to other areas. Reintroduction efforts succeeded in the Bohemia area of the Czech Republic as well, where the biologists similarly followed the guidelines of guarding of occupied eyries and provision of safe foods.
The white-tailed eagle is also being reintroduced to Ireland, where its Irish name of Iolar Mara (sea eagle) reflects its historic association with the island's long coast. The Irish program was begun in the summer of 2007. Fifteen to twenty young eagles from Norway are being released each spring into the Killarney National Park in the south-west of Ireland. This comprehensive project will last a number of years, with many more eagles being released. The species has a rich history on the island but became extinct in Ireland in the 1900s due to persecution from landowners. The last pair bred on the coast of Mayo in 1912. In 2007, a hundred local sheep farmers gathered at Kerry airport to protest the eagles' arrival. Irish Farming Association Hill Committee chairman Mr O'Leary said he had no doubt the eagles would take lambs. Since their reintroduction seven eagles have been confirmed poisoned in County Kerry, two suspected of having been poisoned, and one shot. A 13th eagle released in Kerry was shot in Northern Ireland. Twenty more eagles were due for release in 2010. However, Dr Allan Mee, in charge of the sea eagle project, stated "the continuing loss of eagles to poisoning had cast a shadow over the future of the ambitious programme." The first white-tailed eagle breeding pair since 1912 nested 100 years later on Lough Derg (Loch Deirgeirt), marking a great success for the Irish reintroduction programme. In early May 2013, the first eaglets were born in Ireland since the re-introduction programme began; one in the Killarney National Park and two in County Clare. In Spring 2015, five nests hatched chicks in 4 counties in Ireland - Clare, Cork, Galway and Kerry.
Densities of white-tailed eagles have greatly increased in some parts of the range due to conservation efforts. Some threats still remain, notably illegal persecution by gamebird shooting and egg thieves in Scotland. In prime habitat in north Europe, distance between breeding pairs can be only 4 km (2.5 mi) (even as little as 1–2 km (0.62–1.24 mi) locally) such as in Norway, density at one Polish forest were even reported at 6-7 in each square kilometer. In the late 1990s, it was estimated that Russia held as many as 5,000-7,000 pairs, with around 175 pairs in Greenland and almost 3,500 pairs in Europe, led by Norway (1,500+ pairs), European Russia (900-1,100), Poland (180-240), Germany (140-150) and Sweden (100-150). The largest population in Europe is found along the coast of Norway. The Norwegian population in 2008 was claimed to have stood at 9,000–11,000 pairs, much larger than prior estimates, and indeed this may refer to the total number of individuals rather than total breeding pairs. Even in the early 1980s, Norway maintained a population greater than all other European white-tailed eagle populations combined. In isolation, Turkey holds merely 10-30 pairs. Over 500 winter in Japan, mainly Hokkaido, but this island may have only 20 pairs breeding. Strong increases were recorded in Croatia, with no less than 135 breeding pairs estimated in Croatia by 2009, up from only 25-30 in 2007.
Beyond the threat of chemical poisonings, a new threat from wind turbines is emerging with significant mortality (considerably in excess of the area's population productivity) occurring at the Smøla Wind Farm in Norway. From 2005 to 2010, 36 birds killed by wind farm on isle of Smøla, including 4 of 45 recent radio-tagged fledglings. Breeding attempts within 500–1,000 m (1,600–3,300 ft) of the wind farm were considerably reduced in success. The white-tailed eagles of the region seem to have no behavioral avoidance capabilities, as in many raptors, since the blades are not visible at close range. In a recovering population in north-east Germany, a trade-off between the distance to neighbouring breeding pairs and to the nearest water body (the birds' favoured foraging habitat) was found. This indicates that pairs may be increasingly selecting suboptimal habitats to reduce competition as the population increases, and has implications in the management of such populations.
White-tailed eagles have apparently re-established themselves as a native breeding species in numerous countries: Austria (now breeding in extreme northwestern portions), Denmark (where broadly re-established as breeders), the Czech Republic and Slovakia (scattered pairs in both now with reintroductions factoring in the Czech Republic), Hungary, and Bulgaria. In Demark, in just 16 years, the breeding population has increased from none to at least 37 pairs by 2011. This is dwarfed by the re-establishment (starting from none in the 1970s) in Hungary, where 114 out of 166 breeding pairs by 2007 were successful producing altogether 182 fledged young. Wintering Hungarian population may now reach about a thousand eagles. In Lithuania, back in 1985 no pairs were known to have bred but established pairs numbered 90 by 2007 and swelled to 120 by 2011. On 22 May 2006, it was announced that a pair of white-tailed eagles breeding in the Oostvaardersplassen nature reserve in the Netherlands had arrived on their own, not as a reintroduction. This was the first time the bird has bred in the Netherlands in living memory. In 2007, 2008 and 2009 the eagles returned to their nest. In 2010, it turned out that the white-tailed eagle was also breeding in the Zwarte Meer nature district and in the Lauwersmeer area. There is also a confirmed case of breeding white-tailed eagles in the Biesbosch. Currently (2017), there are around ten pairs breeding spread over Dutch country.
Studies of microsatellite and mitochondrial DNA in white-tailed eagles from north-central Europe have shown that the recovering European population has retained appreciable amounts of genetic diversity, implying low risk of inbreeding depression (a serious concern in species with low population density). Therefore, recovery of this formerly endangered species is a true success story for nature conservation. The story also shows how local protection of a species can be successful and important for preserving the species' evolutionary potential. In total, as of 2013, the IUCN estimated the world population of white-tailed eagles at 20,000-49,999 individuals.
WTE are prominent in ancient Saxon folkore and artwork with many landmarks named after the species It is believed to be the White eagle shown in the Polish coat of arms and in the Serbian coat of arms. The sea eagle is often blazoned grasping a fish (usually a pike) in its talons, distinguishing it from an ordinary eagle.
On Orkney, Scotland, sea eagle bones have been found in 6000-year-old burial mounds, among them the Tomb of the Eagles, suggesting that the birds were revered by the prehistoric people there, a belief strengthened by the Pictish stone carvings of sea eagles from Orkney. Cut marks have been found in white-tailed eagle talons in Krapina, suggesting Neanderthals' use of jewellery.
In the Shetland Isles, Scotland, fishermen believed that as soon as a sea eagle appeared fish would rise to the surface, belly up; this led to some fishermen using eagle fat, smeared on their bait, to increase their catch.
- BirdLife International (2016). "Haliaeetus albicilla". IUCN Red List of Threatened Species. 2016: e.T22695137A93491570. doi:10.2305/IUCN.UK.2016-3.RLTS.T22695137A93491570.en. Retrieved 2 June 2018.CS1 maint: Uses authors parameter (link)
- Helander, B., & Stjernberg, T. (2003). Action plan for the conservation of white-tailed sea eagle (Haliaeetus albicilla). In Convention on the Conservation of European Wildlife and Natural Habitats, Strasbourg, France.
- Love, J.A. (1983). The return of the Sea Eagle. Cambridge University Press, ISBN 0 521 25513 9.
- Amadon, D. (1963). Comparison of fossil and recent species: some difficulties. The Condor, 65(5), 407-409.
- Ridgway, R., & Friedmann, H. (1919). The birds of North and Middle America: a descriptive catalogue of the higher groups, genera, species, and subspecies of birds known to occur in North America, from the Arctic lands to the Isthmus of Panama, the West Indies and other islands of the Caribbean sea, and the Galapagos Archipelago (Vol. 50, No. 8). Govt. Print. Off.
- King, W. B., & Vincent, J. (1978). Endangered birds of the world, The ICBP Bird red data book (Vol. 2). Smithsonian Inst Press.
- Hailer, F., Gautschi, B., & Helander, B. (2005). Development and multiplex PCR amplification of novel microsatellite markers in the White‐tailed Sea Eagle, Haliaeetus albicilla (Aves: Falconiformes, Accipitridae). Molecular Ecology Resources, 5(4), 938-940.
- Krone, O., Stjernberg, T., Kenntner, N., Tataruch, F., Koivusaari, J., & Nuuja, I. (2006). Mortality factors, helminth burden, and contaminant residues in white-tailed sea eagles (Haliaeetus albicilla) from Finland. AMBIO: A Journal of the Human Environment, 35(3), 98-104.
- Ferguson-Lees, James; Christie, David A. (2001). Raptors of the World. Illustrated by Kim Franklin, David Mead, and Philip Burton. Houghton Mifflin. ISBN 978-0-618-12762-7. Retrieved 2011-05-29.
- Krüger, O., Grünkorn, T., & Struwe-Juhl, B. (2010). The return of the white-tailed eagle (Haliaeetus albicilla) to northern Germany: Modelling the past to predict the future. Biological Conservation, 143(3), 710-721.
- Love, J. A. (1988). The reintroduction of the white-tailed sea eagle to Scotland: 1975-1987. Nature Conservancy Council.
- Wink, Heidrich & Fentzloff 1996.
- Linnaeus, C. (1758). Systema Naturæ per regna tria naturae, secundum classes, ordines, genera, species, cum characteribus, differentiis, synonymis, locis, Volume 1 (in Latin). v.1 (10th ed.). Holmiae:Laurentii Salvii. p. 89.
- Mayr, Ernst; Cottrell, G. William, eds. (1979). Check-list of Birds of the World. Volume 1 (2nd ed.). Cambridge, Massachusetts: Museum of Comparative Zoology. p. 301.
- Savigny, Marie Jules César (1809). Description de l'Égypte: Histoire naturelle Volume 1 (in French). Paris: Imprimerie impériale. pp. 68, 85.
- Jobling, James A. (2010). The Helm Dictionary of Scientific Bird Names. London: Christopher Helm. pp. 38, 185. ISBN 978-1-4081-2501-4.
- The Nature of Scotland, p. 49.
- Seibold, I., & Helbig, A. J. (1996). Phylogenetic relationships of the sea eagles (genus Haliaeetus): reconstructions based on morphology, allozymes and mitochondrial DNA sequences. Journal of Zoological Systematics and Evolutionary Research, 34(2), 103-112.
- Griffiths, C. S., Barrowclough, G. F., Groth, J. G., & Mertz, L. A. (2007). Phylogeny, diversity, and classification of the Accipitridae based on DNA sequences of the RAG‐1 exon. Journal of Avian Biology, 38(5), 587-602.
- Olsen, J. (2016). Notes on Sanford's Sea-Eagle Haliaeetus sanfordi and Other Raptors in the Solomon Islands. Australian Field Ornithology, 17(2).
- Seibold, I., & Helbig, A. J. (1995). Evolutionary history of New and Old World vultures inferred from nucleotide sequences of the mitochondrial cytochrome b gene. Phil. Trans. R. Soc. Lond. B, 350(1332), 163-178.
- Wink, M., & Sauer-Gürth, H. (2004). Phylogenetic relationships in diurnal raptors based on nucleotide sequences of mitochondrial and nuclear marker genes. Raptors worldwide, 483-498.
- Kenward, Robert (2006). The Goshawk. London, UK: T & A D Poyser. p. 274. ISBN 978-0-7136-6565-9.
- Hailer et al. 2007.
- Oberholser, H.C. (1921). Journal of the Washington Academy of Sciences; Abstract: Ornithology. Washington Academy of Sciences.
- Hailer, Frank; James, Helen F.; Olson, Storrs L.; Fleischer, Robert C. (2015). "Distinct and Extinct: Genetic Differentiation of the Hawaiian Eagle" (PDF). Molecular Phylogenetics and Evolution. 83: 40–43. doi:10.1016/j.ympev.2014.11.005. PMID 25463753.
- Fleischer, R. C., Olson, S. L., James, H. F., & Cooper, A. C. (2000). Identification of the extinct Hawaiian eagle (Haliaeetus) by mtDNA sequence analysis. The Auk, 117(4), 1051-1056.
- del Hoyo, J.; Elliott, A.; Sargatal, J., eds. (1994). Handbook of the Birds of the World. 2. Barcelona: Lynx Edicions. ISBN 978-84-87334-15-3.
- National Geographic Field Guide to the Birds of North America (4th ed.). Washington, D.C.: National Geographic. 2002. ISBN 978-0792268772.
- Wood, Gerald (1983). The Guinness Book of Animal Facts and Feats. ISBN 978-0-85112-235-9.
- Willgohs, J. F. (1961). The white-tailed eagle Haliaëtus albicilla albicilla (Linné) in Norway. Norwegian Universities Press.
- Brown, L.H.; Amadon, D. (1968). Eagles, hawks and falcons of the world. Vol. 1. Hamlyn Publishing Group.
- Smárason, Hjörtur (29 March 2011). "World's Largest White-tailed Eagle".
- Krone, O., Kenntner, N., Trinogga, A., Nadjafzadeh, M., Scholz, F., Sulawa, J., Totschek, K., Schuck-Wersig, P. & Zieschank, R. (2009). Lead poisoning in white-tailed sea eagles: causes and approaches to solutions in Germany. Ingestion of Lead from Spent Ammunition: Implications for Wildlife and Humans. The Peregrine Fund, Boise, Idaho, USA. DOI, 10.
- Friedmann, H. (1950). Birds of North and Middle America, Pt. 2. U.S. Nat. Mus. Bull. no. 50.
- Imler, R. H., & Kalmbach, E. R. (1955). The Bald Eagle and its economic status (Vol. 30). US Government Printing Office.
- Zhengjie, Z. (2001). Birds of China, Vol.1 (Non-Sparrow-shaped): Jilin Science and Technology Press: 275-276
- Cramp, S., & Brooks, D. J. (1992). Handbook of the birds of Europe, the Middle East and North Africa. The birds of the western Palearctic. Oxford University Press, Oxford.
- CRC Handbook of Avian Body Masses, 2nd Edition by John B. Dunning Jr. (Editor). CRC Press (2008), ISBN 978-1-4200-6444-5.
- Šebík, J. (2013). Orel mořský. Czech Atlas of Oceanic Life.
- Nadjafzadeh, M., Voigt, C. C., & Krone, O. (2016). Spatial, seasonal and individual variation in the diet of White‐tailed Eagles Haliaeetus albicilla assessed using stable isotope ratios. Ibis, 158(1), 1-15.
- Sutton, A. E. (2015). Leadership and management influences the outcome of wildlife reintroduction programs: findings from the Sea Eagle Recovery Project. PeerJ, 3, e1012.
- Watson, Jeff (2010). The Golden Eagle. A&C Black. ISBN 978-1-4081-1420-9.
- Patterson. D. (1998). Size variation of migrant Bald Eagles at Glacier National Park, Montana. J. Raptor Res 32:120–125.
- Helander, Hailer & Vilà 2007.
- Helander, B. (1981). Nestling measurements and weights from two White-tailed Eagle populations in Sweden. Bird Study, 28(3), 235-241.
- Bortolotti G.R. (1984). "Age and sex size variation in Golden Eagles". Journal of Field Ornithology. 55: 54–66.
- Zylo, M. T. (2012). Bald eagles (Haliaeetus leucocephalus) wintering in northern Arizona select perches based on food availability, visibility and cover (Doctoral dissertation, Northern Arizona University).
- "Haliaeetus albicilla". AVIS-IBIS: Birds of Indian Subcontinent. External link in
- RSPB Handbook of British Birds (2014). UK ISBN 978-1-4729-0647-2.
- Forsman, D. (1999). The raptors of Europe and the Middle East: a handbook of field identification. London: T & AD Poyser.
- Porter, R. F. (1981). Flight identification of European raptors. A&C Black.
- Mecionis, R., & Jusys, V. (1994). The White-Tailed Eagle Haliaeetus albicilla at Kursiu Lagoon. Acta Orn. Lituanica, 9-10.
- BirdLife International (2001). Threatened birds of Asia: the BirdLife International Red Data Book . Cambridge, UK : BirdLife International.
- Gilbert, M., Tingay, R., Losolmaa, J., Sureda, N., Gilbert, C., Batmunkh, D., & Gombobaatar, S. (2014). Distribution and status of the Pallas’s Fish Eagle Haliaeetus leucoryphus in Mongolia: a cause for conservation concern? Bird Conservation International, 24(3), 379-388.
- MacKinnon, J. R., MacKinnon, J., Phillipps, K., & He, F. Q. (2000). A field guide to the birds of China. Oxford University Press.
- Howell, S. N., Lewington, I., & Russell, W. (2014). Rare Birds of North America. Princeton University Press.
- Stjernberg, T. (1981). Projekt havsörn i Finland.–I Stjernberg, T.(red.): Projekt havsörn i Finland och Sverige. Förhandlingar från ett havsörnssymposium 8-9.1. 1979 på Tvärminne Zoologiska station, Finland. Luonnonvarainhoitotoimiston julkaisuja (Helsinki), 3, 31-60.
- Ehmsen, E., Pedersen, L., Meltofte, H., Clausen, T., & Nyegaard, T. (2011). The occurrence and reestablishment of White-tailed Eagle and Golden Eagle as breeding birds in Denmark. Dansk Ornitologisk Forenings Tidsskrift, 105(2), 139.
- Bogucki, Z. (1976). Status of the White-tailed Eagle in Poland. In W: Report of WWF symposium on the White-tailed Eagle (pp. 31-32).
- Vagliano, C. 1977. The status of birds of prey in Greece. Pages 118-125 in RD Chancellor [ED.], World conference on birds of prey, Report of Proceedings, International Council for Bird Preservation.
- Puscariu, V., & Filipascu, A. (1975). The situation of Birds of Prey in Rumania in 1970-1974. In World conf. Birds of Prey. Vienna (pp. 148-152).
- Bijleveld, M. F. (1974). Birds of prey in Europe. Macmillan.
- Firouz, E. (2005). The complete fauna of Iran. IB Tauris.
- Knystautas, A. (1993). Birds of Russia. HarperCollins.
- Flerov, A. I. (1970). The ecology of the White-tailed Eagle of the Kandalaksha Bay. Proceeding of the Kandalaksha State Nature Reserve, No. VII: 215-232.
- Bent, A. C. (1937). Life histories of North American birds of prey. US Government Printing Office.
- Rijn, S. V., Zijlstra, M., & Bijlsma, R. G. (2010). Wintering white-tailed eagles Haliaeetus albicilla in The Netherlands: aspects of habitat scale and quality. Ardea, 98(3), 373-382.
- Rasmussen & Anderton, P.C. & J.C. (2005). Birds of South Asia. The Ripley Guide. Washington, D.C. and Barcelona.: Smithsonian Institution and Lynx Edicions. p. 87.
- Khan, Asif N. (2015-08-01). "Sighting of a Juvenile White-Tailed Eagle at Jor Beed Carcass Dump, Bikaner, Rajasthan, India". Journal of the Bombay Natural History Society. 112 (2): 92–93. doi:10.17087/jbnhs/2015/v112i2/104934. ISSN 0006-6982.
- Mackinnon, J., & Hicks, N. (2017). Birds of China. Bloomsbury Publishing.
- Brazil, M. (2009). Birds of East Asia: China, Taiwan, Korea, Japan, and Russia. A&C Black.
- Murie, O. J. (1959). Fauna of the Aleutian Islands and Alaska peninsula. North American Fauna, 1-364.
- Tobish Jr, T. G., & Balch, L. G. (1987). First North American nesting and occurrence of Haliaeetus albicilla on Attu Island, Alaska. The Condor, 89(2), 433-434.
- Treinys, R., Dementavičius, D., Rumbutis, S., Švažas, S., Butkauskas, D., Sruoga, A., & Dagys, M. (2016). Settlement, habitat preference, reproduction, and genetic diversity in recovering the white-tailed eagle Haliaeetus albicilla population. Journal of Ornithology, 157(1), 311-323.
- Evans, R. J., Pearce‐Higgins, J., Whitfield, D. P., Grant, J. R., MacLennan, A., & Reid, R. (2010). Comparative nest habitat characteristics of sympatric White‐tailed Haliaeetus albicilla and Golden Eagles Aquila chrysaetos in western Scotland. Bird Study, 57(4), 473-482.
- Tingay, R. E., & Katzner, T. E. (Eds.). (2010). The eagle watchers: Observing and conserving raptors around the world. Cornell University Press.
- Radović, A., & Mikuska, T. (2009). Population size, distribution and habitat selection of the white-tailed eagle Haliaeetus albicilla in the alluvial wetlands of Croatia. Biologia, 64(1), 156-164.
- Rosenvald, R., & Lõhmus, A. (2003). Nesting of the black stork (Ciconia nigra) and white-tailed eagle (Haliaeetus albicilla) in relation to forest management. Forest Ecology and Management, 185(3), 217-223.
- Sutherland, W. J. (1998). Evidence for flexibility and constraint in migration systems. Journal of Avian biology, 441-446.
- Hagen,Y. (1976). Havørn og kongeørn i Norge. Viltrapport, 1: 93 pg.
- Helander, B. (1985). Colour-ringing of white-tailed sea eagles in northern Europe. Conservation studies on raptors.–ICBP Technical Publication, (5), 401-407.
- von Blotzheim, U. N. G., Bauer, K., & Bezzel, E. (1993). Handbuch der vögel mitteleuropas. Akademische Verlagsgesellschaft.
- Ueta, M., Sato, F., Lobkov, E. G., & Mita, N. (1998). Migration route of White‐tailed Sea Eagles Haliaeetus albicilla in northeastern Asia. Ibis, 140(4), 684-686.
- Krone, O., Nadjafzadeh, M., & Berger, A. (2013). White-tailed Sea Eagles (Haliaeetus albicilla) defend small home ranges in north-east Germany throughout the year. Journal of Ornithology, 154(3), 827-835.
- Brown, J. L. (1969). Territorial behavior and population regulation in birds: a review and re-evaluation. The Wilson Bulletin, 293-329.
- Valero, S.O.P. (2008). White-tailed Eagle hunting behaviour and food choice in Kvismaren. Sveriges Ornitologiska Förening.
- Nadjafzadeh, M., Hofer, H., & Krone, O. (2016). Sit-and-wait for large prey: foraging strategy and prey choice of White-tailed Eagles. Journal of Ornithology, 157(1), 165-178.
- Rudebeck, G. (1950). The choice of prey and modes of hunting of predatory birds with special reference to their selective effect. Oikos, 2(1), 65-88.
- "White-tailed eagle: Feeding". RSPB. Retrieved 3 February 2012.
- Uttendorfer, O. (1939). Die Ernahrung der deutschen Raubvogel und Eulen. Neudamm. Verlag Neumann, 204-209.
- Mlíkovský, J. (2009). The food of the white-tailed sea eagle (Haliaeetus albicilla) at Lake Baikal, East Siberia. Slovak Raptor Journal, 3, 35-39.
- Vrezec, A. (2016). Prehranska niša orla belorepca (Haliaeetus albicilla) z idejnim predlogom za izvedbo dodatnega krmljenja vrste v širši okolici Reškega jezera pri Kočevski reki. Poročilo v okviru projekta LIFE Kočevsko (LIFE13 NAT/SI/000314), Ljubljana.
- Wille, F., & Kampp, K. (1983). Food of the white‐tailed eagle Haliaeetus albicilla in Greenland. Ecography, 6(1), 81-88.
- Kampp, K. and F. Wille. (1979). Fodevaner hos den Gronlandske Havorn Haliaeetus albicilla groenlandicus Brehm. (Food habits of the Greenland White-tailed Eagle). Dansk Ornithologisk Forenings Tidsskrift, 73:157-64. (In Danish with English summary).
- Mersmann, T. J., Buehler, D. A., Fraser, J. D., & Seegar, J. K. (1992). Assessing bias in studies of bald eagle food habits. The Journal of wildlife management, 73-78.
- Dornbusch, M. (1977). Der Seeadler Haliaeetus albicilla (L. 1758) in der Deutschen Demokratischen Republik. In Report of WWF symposium of the White-tailed Eagle: 17-18.
- Sulkava, S., Tornberg, R., & Koivusaari, J. (1997). Diet of the white-tailed eagle Haliaeetus albicilla in Finland. Ornis Fennica, 74(2), 65-78.
- Zawadzka, D. (1999). Feeding habits of the black kite Milvus migrans, red kite Milvus milvus, white-tailed eagle Haliaeetus albicilla and lesser spotted eagle Aquila pomarina in Wigry National Park (NE Poland). Acta ornithologica, 34(1), 65-75.
- Babushkin, M. V., Kuznetsov, A. V., & Demina, O. A. (2017). White-Tailed Eagle on the Rybinsk reservoir: abundance, ecology, migration and wintering sites. In The collection of Abstracts and Short Notes of the SEA EAGLE 2017 conference (pp. 5-7).
- Ayupov, A.S. (2017). The use of camcorder in nesting biology research of Haliaeetus albicilla (L). In The collection of Abstracts and Short Notes of the SEA EAGLE 2017 conference (pp. 13).
- Bergman, G. (1961). The food of birds of prey and owls in Fenno-Scandia. British Birds, 54(8), 307-320.
- Bolam, G. (1913). Wild life in Wales. F. Palmer.
- Buckley, T. E., & Harvie-Brown, J. A. (1891). A vertebrate fauna of the Orkney Islands (Vol. 4). D. Douglas.
- Huey, L. M. (1962). Comparison of the weight-lifting capacities of a house finch and a golden eagle. The Auk, 79(3), 485-485.
- Palmer, R. S. (Ed.). (1988). Handbook of North American Birds Volume VI: Diurnal Raptors (Part 1). Yale University Press.
- Barth EK. 1979. Did a White-tailed Eagle carry a small child? Var Fuglefaun, 2: 49-50.
- Wille, F. (1979). Choice of Food of the Greenland White-tailed Eagle- method and preliminary results. Dansk ornithogisk Forenings Tidsskrit, 73: 165-170.
- Fischer W. (1982). Die Seeadler . Die Neue Brehm-Bücherei , A. Ziemsen Verlag , WittenbergLutherstadt.
- Ekblad, C. (2004). Havsörnens häckningstida näringsval i olika skärgårdszoner på Åland. Doktorsavhandling. Institutionen för Ekologi och Systematik. Avdelningen för populationsbiologi. Februari.
- Kobler, A., Klefoth, T., Mehner, T., & Arlinghaus, R. (2009). Coexistence of behavioural types in an aquatic top predator: a response to resource limitation? Oecologia, 161(4), 837-847.
- Sternberg, D. (1992). Northern Pike and Muskie: Tackle and Techniques for Catching Trophy Pike and Muskies. Creative Publishing International.
- Adrianova, O. V., & Kashevarov, B. N. (2005). SOME RESULTS OF LONG-TERM RAPTOR MONITORING IN THE KOSTOMUKSHA NATURE RESERVE. Status of Raptor Populations in Eastern Fennoscandia, Proceedings of the Workshop, Kostomuksha, Karelia, Russia.
- Yurko, V.V. (2016). Diet of the White-Tailed Eagle During the Breeding Season in the Polesski State Radiation-Ecological Reserve, Belarus. Raptor Conservation, 32: 21-31.
- Samago, L. (1995). White-tailed eagle - Haliaeetus albicilla L. Propagation of the Urals and adjacent territories to poly-terrestrial sources: 107-122.
- Khristenko, D. S., & Kotovska, G. O. (2017). Length-Weight Relationship and Condition Factors of Freshwater Bream Abramis brama (Linnaeus, 1758) from the Kremenchug Reservoir, Middle Dnieper. Turkish Journal of Fisheries and Aquatic Sciences, 17(1), 71-77.
- Harris, L. N., Tallman, R. F., & Department of Fisheries and Oceans, Ottawa, ON(Canada); Canadian Science Advisory Secretariat, Ottawa, ON(Canada). (2010). Information to support the assessment of Arctic Char, Salvelinus alpinus, from the Isuituq River system, Nunavut. Fisheries and Oceans Canada, Science.
- Collette, B., Fernandes, P. & Heessen, H. 2015. Anarhichas lupus. The IUCN Red List of Threatened Species 2015: e.T18155993A44739312.
- Simpson, M.R., Gauthier, J., Benoît, H.P., MacDonald, D., Hedges, K., Collins, R., Mello, L. & Miri, C. (2016). A pre-COSEWIC assessment of the Common Lumpfish (Cyclopterus lumpus, Linnaeus 1758) in Canadian Atlantic and Arctic waters. Canadian Science Adversary.
- Ivanovsky, V.V. (2010). White-tailed eagle Haliaeetus albicilla in the Byelorussian Poozerie: materials on the biology of the species within the range. Russian Ornithological Journal, 19: 1876-1887.
- Mori, S. (1980). Breeding biology of the White-tailed Eagle Haliaeetus albicilla in Hokkaido, Japan. Japanese Journal of Ornithology, 29(2-3), 47-68.
- Bailey, K. M., Powers, D. M., Quattro, J. M., Villa, G., Nishimura, A., Traynor, J. J., & Walters, G. (1999). Population ecology and structural dynamics of walleye pollock (Theragra chalcogramma). Dynamics of the Bering Sea, 581-614.
- Sandor, A. D., Alexe, V., Marinov, M., Dorosencu, A., Domsa, C., & Kiss, B. J. (2015). Nest-site selection, breeding success, and diet of white-tailed eagles (Haliaeetus albicilla) in the Danube Delta, Romania. Turkish Journal of Zoology, 39(2), 300-307.
- Tuvia, J., & Välia, Ü. (2007). The impact of the White-tailed Eagle Haliaeetus albicilla and the Osprey Pandion haliaetus on Estonian Common Carp Cyprinus carpio production: How large is the economic loss? Estonian Journal of Ecology, 56(3).
- Todd, C. S., Young, L. S., Owen Jr, R. B., & Gramlich, F. J. (1982). Food habits of bald eagles in Maine. The Journal of Wildlife Management, 636-645.
- Buehler, D. A. (2000). Bald Eagle (Haliaeetus leucocephalus) , version 2.0. In The Birds of North America (A. F. Poole and F. B. Gill, Editors). Cornell Lab of Ornithology, Ithaca, NY, USA.
- Fischer, W. (1970). Die Seeadler. A. Ziemsen Verlag.
- Meinertzhagen, R. (1959). Pirates and Predators: The piratical and predatory habits of birds. Oliver and Boyd.
- Wolley, J. (1907). Ootheca Wolleyana: an illustrated catalogue of the collection of birds' eggs. Repressed Publishing LLC.
- Kilpi, M., & Öst, M. (2002). The effect of White-tailed Sea Eagle predation on breeding Eider females off Tvärminne, Western Gulf of Finland. Suomen Riista, 48, 27-33.
- Ingólfsson, A. 1961. The distribution and breeding ecology of the White-tailed Eagle Haliaeetus albicilla (L.) in Iceland. B.Sc. (Hons.) thesis. University of Aberdeen.
- Ravn Merke, F., & Mosbech, A. (2008). Diurnal and nocturnal feeding strategies in common eiders. Waterbirds, 31(4), 580-586.
- Hipfner, M. J., Blight, L. K., Lowe, R. W., Wilhelm, S. I., Robertson, G. J., Barrett, R., Anker-Nilssen, T. & Good, T. P. (2012). Unintended consequences: how the recovery of sea eagle Haliaeetus spp. populations in the northern hemisphere is affecting seabirds. Recovery of Sea Eagles in the northern hemisphere. Marine Ornithology 40: 39–52.
- Ryabtsev, V.V. (1997). The White-tailed Sea Eagle Haliaeetus albicilla in Baikal Lake. Russian Ornithological Journal, 20: 3-12.
- Vasilievich, S.B. (2014). Nesting of the White-tailed Sea Eagle Haliaeetus albicilla in the Black Irtysh. Russian Ornithological Journal, 1007: 1720-1725.
- Broad, R. A. (1974). Contamination of birds with fulmar oil. British Birds, 67, 297-301.
- Mlíkovský, J. (1992). Population status and food of the White-tailed Fish Eagle Haliaeetus albicilla (Aves: Accipitridae) in the Svjatoj Nos wetlands, Lake Baikal. MLÍKOVSKÝ, J. & STÝBLO, P.(Eds.): Ecology of the Svjatoj Nos wetlands, Lake Baikal.-Ninox Press, Praha: 79, 88.
- Probst, R. (2009). Der Seeadler (Haliaeetus albicilla) in Österreich: Das WWF Österreich Seeadlerprojekt. Denisia, 27, 29-50.
- Berezovikov, N.N. (2006). WHITE-TAILED EAGLE HALIAEETUS ALBICILLA AND THE LOCAL CONCENTRATION OF WATER BIRDS ON LAKES OF NORTH KAZAKHSTAN. Russian Ornithological Journal, 335: 1028-1030.
- Ouweneel, O., & van Straalen, D. (2016). Paalzittende Zeearenden Haliaeetus albicilla op de Hellegatsplaten. De takkeling, 24(3), 188-193.
- "Turun Sanomat: Merikotkat oppineet syömään aikuisiakin merimetsoja" (in Finnish). Retrieved 3 February 2012.
- "Kormoraniküttidel läheb hästi" [Cormorant Hunters are doing well]. Hiumaa Life (in Estonian). 13 April 2012. External link in
- Whitfield, D. P., Marquiss, M., Reid, R., Grant, J., Tingay, R., & Evans, R. J. (2013). Breeding season diets of sympatric White-tailed Eagles and Golden Eagles in Scotland: no evidence for competitive effects. Bird study, 60(1), 67-76.
- Zaun, B. J. (2009). First modern record of the White-tailed Eagle in Hawaii. Western Birds, 40, 35-38.
- Brazil, M. (2010). The whooper swan. Bloomsbury Publishing.
- Nolet, B. A., Fuld, V. N., & Van Rijswijk, M. E. (2006). Foraging costs and accessibility as determinants of giving‐up densities in a swan‐pondweed system. Oikos, 112(2), 353-362.
- Müller, H. (2011). Brutbiologische Beobachtungen an einem Seeadler Haliaeetus albicilla-Brutplatz in Bayern. Ornithol. Anz, 49, 193-200.
- Halley, D.J. (1998). "Golden and white-tailed eagles in Scotland and Norway. Coexistence, competition and environmental degradation". British Birds. 91 (5): 171–179. ISSN 0007-0335.
- Watson, J., Leitch, A. F., & Broad, R. A. (1992). The diet of the sea eagle Haliaeetus albicilla and golden eagle Aquila chrysaetos in western Scotland. Ibis, 134(1), 27-31.
- Forrest, H. E. (1907). The vertebrate fauna of North Wales. Witherby.
- MacGillivray, W. (1836). Descriptions of the Rapacious Birds of Great Britain.[With plates.]. Maclachlan & Stewart.
- Angerbjörn, A. (1995). Lepus timidus. Mammalian species, (495), 1-11.
- Wootton, J. T. (1987). The effects of body mass, phylogeny, habitat, and trophic level on mammalian age at first reproduction. Evolution, 41(4), 732-749.
- Chapman, J. A., & Flux, J. E. (Eds.). (1990). Rabbits, hares and pikas: status survey and conservation action plan. IUCN.
- Audet, A. M., Robbins, C. B., & Larivière, S. (2002). Alopex lagopus. Mammalian species, 1-10.
- Larivière, S., & Pasitschniak-Arts, M. (1996). Vulpes vulpes. Mammalian species, (537), 1-11.
- Bannerman, D. A. (1959). The birds of the British Isles (Vol. 8). Oliver and Boyd.
- Bowen, D. (2016). Halichoerus grypus. The IUCN Red List of Threatened Species 2016: e.T9660A45226042.
- Arkadevich, M.V., Yuryevna, P.Y., Vladimirovich, T.A. & Valerevna, M.J. (2014). Nesting of the White-tailed Eagle (Haliaeetus albicilla) and the Long-legged Buzzard (Buteo rufinus) in the Rostovsky Reserve. News of higher educational institutions. North-Caucasian region. Natural Sciences.
- Salo, P., Nordström, M., Thomson, R. L., & Korpimäki, E. (2008). Risk induced by a native top predator reduces alien mink movements. Journal of Animal Ecology, 77(6), 1092-1098.
- Salo, P. (2009). On lethal and nonlethal impacts of native, alien and intraguild predators-evidence of top-down control. Section of Ecology, Department of Biology, University of Turku, Finland.
- Catsadorakis, G., & Källander, H. (Eds.). (2010). The Dadia-Lefkimi-Soufli Forest National Park, Greece: Biodiversity, Management and Conservation. WWF Greece.
- Rosell, F., Bozser, O., Collen, P., & Parker, H. (2005). Ecological impact of beavers Castor fiber and Castor canadensis and their ability to modify ecosystems. Mammal review, 35(3‐4), 248-276.
- Feldhamer, G. A., Thompson, B. C., & Chapman, J. A. (Eds.). (2003). Wild mammals of North America: biology, management, and conservation. JHU Press.
- Berg, B. (1923). De sista örnarna. Norstedt.
- Korpimäki, E., & Norrdahl, K. (1989). Avian and mammalian predators of shrews in Europe: regional differences, between-year and seasonal variation, and mortality due to predation. In Annales Zoologici Fennici (pp. 389-400). Finnish Zoological Publishing Board, formed by the Finnish Academy of Sciences, Societas Scientiarum Fennica, Societas pro Fauna et Flora Fennica and Societas Biologica Fennica Vanamo.
- Selva, N., Jedrzejewska, B., Jedrzejewski, W., & Wajrak, A. (2003). Scavenging on European bison carcasses in Bialowieza primeval forest (eastern Poland). Ecoscience, 10(3), 303-311.
- MacGillivray, W. (1836). Descriptions of the Rapacious Birds of Great Britain. [With plates.]. Maclachlan & Stewart.
- Alexander, T. L., & Buxton, D. (Eds.). (1986). Management and diseases of deer: a handbook for the veterinary surgeon. Veterinary Deer Society.
- Gorbet, G.B. & Harris, S. (1991). The Handbook of British Mammals, Third Edition. Blackwell Science Publications. ISBN 0-632-01691-4.
- Marquiss, M., Madders, M., Irvine, J., & Carss, D. N. (2004). The impact of White-tailed Eagles on sheep farming on Mull. Scottish Executive.
- Marquiss, M., Madders, M., & Carss, D.N. (2003). White-tailed Eagles (Haliaeetus Albicilla) and Lambs (Ovis Aries).
- Sherrod, S. K. (1978). Diets of North American Falconiformes. Raptor Res, 12(3/4), 49-121.
- Uttendörfer, O. (1952). Neue Ergebnisse überdie Ernährung der Greifvögel und Eulen. Stuttgart & Ludwigsburg: Eugen Ulmer.
- Halley, D. J., & Gjershaug, J. O. (1998). Inter‐and intra‐specific dominance relationships and feeding behaviour of Golden Eagles Aquila chrysaetos and Sea Eagles Haliatetus albicilla at carcasses. Ibis, 140(2), 295-301.
- Poole, K. G., & Bromley, R. G. (1988). Interrelationships within a raptor guild in the central Canadian Arctic. Canadian Journal of Zoology, 66(10), 2275-2282.
- Janes, S. W. (1985). INTERSPECIFIC INTERACTIONS AMONG GRASSLAND AND SHRUBSTEPPE RAPTORS: THE SMALLER SPECIES WINS. Behavioral interactions and habitat relations among grassland and shrubsteppe raptors, 7.
- Voous, K.H. 1988. Owls of the Northern Hemisphere. The MIT Press, 0262220350.
- Mikkola, H. (1976). Owls killing and killed by other owls and raptors in Europe. British Birds, 69, 144-154.
- Pettersson J. 1977. White-tailed Eagle, Haliaeetus albicilla, robbing Golden Eagle, Aquila chrysaetos, of its prey. Var Fagelvarld, 36: 54.
- "Golden Eagle surrenders meal to White Tailed Eagle". London: The Telegraph. 2010-12-16. Retrieved 2013-04-30.
- Whitfield, P. (2000). Golden Eagle Aquila chrysaetos ecology and conservation issues. SNH REVIEW, (132).
- Jorde, D.G. (1998). "Kleptoparasitism by Bald Eagles wintering in South-Central Nebraska". Journal of Field Ornithology. 59 (2): 183–188.
- Garcelon, D. K. (1988). The reintroduction of bald eagles on Santa Catalina Island, California (Doctoral dissertation, Humboldt State University).
- Erskine, A. J. (1968). Encounters between Bald Eagles and other birds in winter. The Auk, 85(4), 681-683.
- Katzner, T. E., Bragin, E. A., Knick, S. T., & Smith, A. T. (2003). Coexistence in a multispecies assemblage of eagles in central Asia. The Condor, 105(3), 538-551.
- Treinys, R., Dementavičius, D., Mozgeris, G., Skuja, S., Rumbutis, S., & Stončius, D. (2011). Coexistence of protected avian predators: does a recovering population of White-tailed Eagle threaten to exclude other avian predators? European journal of wildlife research, 57(6), 1165-1174.
- Ladygin, A. (1991). Morpho-ecological adaptations in Stellers sea and White-tailed sea eagles, a comparative analysis. Current Ornithology, 1991. Vol.1. P. 42-56.
- Masterov, V.B. 1992. Ecological energetic and interspecific relations between White-tailed and Steller's Sea eagles (Haliaeetus albicilla L., Haliaeetus pelagicus Pall.) in Lower Amur and Sakhalin. The materials of Ph.D. work, 157 pp., (In Russian).
- Steller's sea eagle photo – Haliaeetus pelagicus – G113853. ARKive. Retrieved on 2012-08-21.
- The Secret Lives of Sea Eagles – National Wildlife Federation. Nwf.org (2011-10-26). Retrieved on 2012-08-21.
- Photo Keywords : steller's sea eagle : White-tailed Eagle and Steller's Sea Eagle. Golden First Light (2012-06-21). Retrieved on 2012-08-21.
- Stalmaster, M.V. (1987). The Bald Eagle. Universe Books, New York.
- Grubb, T. G. (1995). Food habits of bald eagles breeding in the Arizona desert. The Wilson Bulletin, 258-274.
- Bergo, G. (1987). Territorial behaviour of Golden Eagles in western Norway. British Birds, 80, 361-376.
- Cheke, A. S. (1964). SOME NOTES ON BIRDS IN EASTERN HOKKAIDO. Tori, 18 (83): 175-185.
- Dementavičius, D., Rumbutis, S., Vaitkuvienė, D., Dagys, M. & Treinys, R. (2017). Does mesopredator Lesser Spotted Eagle suffers breeding costs in a high-density area of the White-tailed Eagle? The Collection of Abstracts and Short Notes of the Sea Eagle Conference 2017.
- Golovatin, M.G. & Paskhalny, S.P. (2005). Distribution, numbers and ecology of White-tailed Eagle in the north of West Siberia. Berkut, 14 (1): 59-70.
- Kirmse, W. (1998). Morphometric features characterizing flight properties of palearctic eagles. Holarctic Birds of Prey, 339-348.
- Helander, B. (1985). Reproduction of the white‐tailed sea eagle Haliaeetus albicilla in Sweden. Ecography, 8(3), 211-227.
- Simmons, R. E., & Mendelsohn, J. M. (1993). A critical review of cartwheeling flights of raptors. Ostrich, 64(1), 13-24.
- Debus, S. J. S. (2008). Biology and diet of the White-bellied Sea-Eagle Haliaeetus leucogaster breeding in northern inland New South Wales. Australian Field Ornithology, 25(4), 165.
- Hansen, K. (1979). Status over bestanden av Havorn Haliaeetus albicilla groenlandicus Brehm i Grönland i ärene 1972-74. Danskorn. Foren. Tidskr . 73, 107-30.
- Oehme, G. (1961). Die Bestandsentwicklung des Seeadlers, Haliaeetus albicilla (L.). Deutschland mit Untersuchungen zur Wahl der Brutbiotope. In: Schildmacher, H.: Beiträge zur Kenntnis deutscher Vögel. Jena, 1-61.
- Shiraki, S. (1994). Characteristics of white-tailed sea eagle nest sites in Hokkaido, Japan. Condor, 1003-1008.
- Christensen, J. (1979). Den Grönlandske havörns Haliaeetus albicilla groenlandicus Brehm ynglebiotop, redeplacering og rede.(with English Summary: The breeding habitat, nest-site and nest of the Greenland White-tailed Eagle Haliaeetus albicilla groenlandicus Brehm.). Dansk Orn. Foren. Tidsskr, 73, 131-155.
- Ussher, R. J., & Warren, R. (1900). Birds of Ireland.
- Deppe, H. J. (1972). Einige Verhaltensbeobachtungen an einem Doppelhorst von Seeadler (Haliaeetus albicilla) und Wanderfalke (Falco peregrinus) in Mecklenburg. Journal für Ornithologie, 113(4), 440-444.
- Witherby, H. F., Jourdain, F. C. R., Ticehurst, N. F., & Tucker, B. W. (1943). Handbook of British birds.
- Fentzloff, C. (1977). Successful breeding and adoption of sea eagles (Haliaeetus albicilla). Papers on the veterinary medicine and domestic breeding of diurnal birds of prey, 71-91.
- Simmons, R. (1988). Offspring quality and the evolution of cainism. Ibis, 130(4), 339-357.
- Meyburg, B. U. (1974). Sibling aggression and mortality among nestling eagles. Ibis, 116(2), 224-228.
- Arnold, E., & Maclaren, P. (1938). NOTES ON THE HABITS AND DISTRIBUTION OF THE WHITE-TAILED EAGLE IN NW ICELAND. British Birds, 34: 4-10.
- Meyburg, B. U. (1975). Protective management of eagles by reduction of nestling mortality. World Confer. Birds of Prey, Vienna, 387-391.
- Helander, B. (1975). Havsörnen i Sverige. Fören.
- Hansen, K. (1979). Population status for the Greenland White-tailed Eagle Haliaeetus albicilla groenlandicus Brehm covering the years 1972-74. Dansk orn. Foren. Tidsskr., 73, 107-130.
- "Merikotkien määrä lisääntyy" [Eagles are increasing] (in Finnish). MTV3.fi. 10 July 2008. Retrieved 30 May 2011.
- McNicoll, G. (2001). Longevity Records: Life Spans of Mammals, Birds, Amphibians, Reptiles, and Fish. Population and Development Review, 27(2), 381 pp.
- Maurer, G., Russell, D. G., Woog, F., & Cassey, P. The eggs of the extinct Egyptian population of White-tailed Eagle Haliaeetus albicilla. Bull. B.O.C. 2010 130(3). 204-210.
- Murton, R. K. (1971). Man and birds (Vol. 51). HarperCollins UK.
- Hudson, W.S. (1906). British Birds. Harper Collins.
- Newton, I. (2010). Population ecology of raptors. A&C Black.
- Jensen, S., Johnels, A. G., Olsson, M. & Westermark, T. (1972). The avifauna of Sweden as indicators of environmental contamination with mercury and chlorinated hydrocarbons . -Proc . XV Int. Ornithol . Congr., Leiden : 455-465
- Joutsamo, E., & Koivusaari, J. (1976). White-tailed Eagle in Finland 1970-1976. In Proceedings from the World Wildlife Fund Sea Eagle Symposium, Norway, Sept. l976.
- Borg, K. , Wanntorp, H., Erne, K. & Hanko, E. (1965). Kvicksilverförgiftningar bland vilt i Sverige. State Veterinary Medical Institute. Stockholm.
- Oehme, G. (1969). Population trends in the white-tailed sea eagle in North Germany. Peregrine Falcon Populations: Their Biology and Decline, 351-352.
- Koeman, J. H., Hadderingh, R. H., & Bijleveld, M. F. I. J. (1972). Persistent pollutants in the white-tailed eagle (Haliaeetus albicilla) in the Federal Republic of Germany. Biological Conservation, 4(5), 373-377.
- Kalisńska, E., Salicki, W., & Jackowski, A. (2006). Six Trace Metals in White-Tailed Eagle from Northwestern Poland. Polish Journal of Environmental Studies, 15(5).
- Kim, E. Y., Goto, R., Iwata, H., Masuda, Y., Tanabe, S., & Fujita, S. (1999). Preliminary survey of lead poisoning of Steller's sea eagle (Haliaeetus pelagicus) and white‐tailed sea eagle (Haliaeetus albicilla) in Hokkaido, Japan. Environmental Toxicology and Chemistry, 18(3), 448-451.
- Iwata, H., Watanabe, M., Kim, E. Y., Gotoh, R., Yasunaga, G., Tanabe, S., Masuda, Y. & Fujita, S. (2000). Contamination by chlorinated hydrocarbons and lead in Steller’s Sea Eagle and White-tailed Sea Eagle from Hokkaido, Japan. In First Symposium on Steller’s and White-tailed Sea Eagles in East Asia. Wild Bird Society of Japan, Tokyo (pp. 91-106).
- Kenntner, N., Tataruch, F., & Krone, O. (2001). Heavy metals in soft tissue of white‐tailed eagles found dead or moribund in Germany and Austria from 1993 to 2000. Environmental Toxicology and Chemistry, 20(8), 1831-1837.
- Helander, B. (1985). Winter feeding as a management tool for white-tailed sea eagles in Sweden. Conservation studies on raptors. ICBP Technical Publication, (5), 421-427.
- Hario, M. (1981). Vinterufodring av Havsorn I Finland. In Projekt Hasvorn I Finland och Sverige. T. Stjernberg (ed.)
- Helander, B., Bignert, A., & Asplund, L. (2008). Using raptors as environmental sentinels: monitoring the white-tailed sea eagle Haliaeetus albicilla in Sweden. AMBIO: A Journal of the Human Environment, 37(6), 425-431.
- Movalli, P., Dekker, R., Koschorreck, J., & Treu, G. (2017). Bringing together raptor collections in Europe for contaminant research and monitoring in relation to chemicals regulations. Environmental Science and Pollution Research, 24(31), 24057-24060.
- Gómez-Ramírez, P., Shore, R. F., Van Den Brink, N. W., Van Hattum, B., Bustnes, J. O., Duke, G., & Krone, O. (2014). An overview of existing raptor contaminant monitoring activities in Europe. Environment international, 67, 12-21.
- Thomas, V. G., & Guitart, R. (2010). Limitations of European Union policy and law for regulating use of lead shot and sinkers: Comparisons with North American regulation. Environmental Policy and Governance, 20(1), 57-72.
- Guynup, S., & Safina, B. C. (2012). Mercury: Sources in the environment, health effects, and politics. Blue Oceans Institute, 1-54.
- Green, R. E., Pienkowski, M. W., & Love, J. A. (1996). Long-term viability of the re-introduced population of the white-tailed eagle Haliaeetus albicilla in Scotland. Journal of Applied Ecology, 357-368.
- "Birds released in secret location". BBC News. 13 August 2008. Retrieved 13 August 2008.
- Evans, R. J., Wilson, J. D., Amar, A., Douse, A., Maclennan, A., Ratcliffe, N., & Whitfield, D. P. (2009). Growth and demography of a re‐introduced population of White‐tailed Eagles Haliaeetus albicilla. Ibis, 151(2), 244-254.
- Snow & Perrins 1998, p. 48.
- "Birds of prey: Which birds are threatened?". RSPB. 23 January 2008.
- Ševčík, J. (1987). Hnízdění orla mořského (Haliaeetus albicilla) na Třeboňsku.[Nesting of the White-tailed Eagle (Haliaeetus albicilla) in the Třeboň region (south Bohemia)]. Buteo, 2, 41-50.
- Rajchard, J., Procházka, J., & Šmahel, L. (2010). Nest sites and reproductive success of a restored population of White-tailed Eagles in the Czech Republic. Journal of Raptor Research, 44(3), 243-246.
- "Rare eagle reintroduced to Ireland". RTÉ News. 16 August 2007. External link in
- "White-tailed Eagle". BirdWatch Ireland. External link in
- "Farmers protest at the arrival of the Eagles in 2007". Drimnagh Birdwatch. 4 March 2010. Archived from the original on 14 November 2012. Retrieved 30 May 2011.
- Lucey, Anne (4 May 2010). "Sea eagle death in Kerry park brings total to 13". The Irish Times. Retrieved 30 May 2011. External link in
- Siggins, Lorna (30 April 2012). "Sea eagles return to Irish nest". The Irish Times. Retrieved 30 April 2012. External link in
- "First white-tailed eagles born in Ireland in over 100 years". Rte.ie. 9 May 2013. Retrieved 20 May 2013.
- "White-tailed eagle chicks hatch in five nests". The Irish Times. 2 Jun 2015.
- The Proceedings of the Somerset Archaeological and Natural History Society. XXV1: Page 86. 1881. Missing or empty
- "Polish Birds Directory". birds.poland.pl. Archived from the original on 19 October 2011. Retrieved 30 May 2011. External link in
- Literák, I., Mrlík, V., Hovorková, A., Mikulíček, P., Lengyel, J., Št’astný, K., & Dubská, L. (2007). Origin and genetic structure of white-tailed sea eagles (Haliaeetus albicilla) in the Czech Republic: an analysis of breeding distribution, ringing data and DNA microsatellites. European Journal of Wildlife Research, 53(3), 195-203.
- "Wind farm causes eagle deaths". BirdLife International. 3 February 2006. Archived from the original on 22 September 2013.
- Unwin, Brian (4 July 2014). "Arrivals & Alarms: White-tailed Eagle Imports Endangered by Windfarms". fatbirder.com. External link in
- Nygård, T., Bevanger, K., Dahl, E. L., Flagstad, Ø., Follestad, A., Hoel, P. L., & Reitan, O. (2010). A study of White-tailed Eagle Haliaeetus albicilla movements and mortality at a wind farm in Norway. BOU Proceedings-Climate Change and Birds. British Ornithologists’ Union.
- Dahl, E. L., Bevanger, K., Nygård, T., Røskaft, E., & Stokke, B. G. (2012). Reduced breeding success in white-tailed eagles at Smøla windfarm, western Norway, is caused by mortality and displacement. Biological Conservation, 145(1), 79-85.
- Dahl, E. L., May, R., Hoel, P. L., Bevanger, K., Pedersen, H. C., Røskaft, E., & Stokke, B. G. (2013). White‐tailed eagles (Haliaeetus albicilla) at the Smøla wind‐power plant, Central Norway, lack behavioral flight responses to wind turbines. Wildlife Society Bulletin, 37(1), 66-74.
- Heuck, C.; Herrmann, C.; Schabo, D. G.; Brandl, R.; Albrecht, J. (2017). "Density-dependent effects on reproductive performance in a recovering population of White-tailed Eagles Haliaeetus albicilla". Ibis. 159 (2): 297–310. doi:10.1111/ibi.12444.
- Horváth, Z. (2009). White-tailed Eagle (Haliaeetus albicilla) populations in Hungary between 1987–2007. Denisia, 27, 85-95.
- Dementavičius, D. (2007). White-tailed Eagle (Haliaeetus albicilla) in Lithuania: population numbers and trends 1900-2007. Acta Zoologica Lituanica, 17(4), 281-285.
- The Dutch national forestry, which owns the reserve, has put up a webcam trained on the nesting eagles  Archived March 10, 2007, at the Wayback Machine
- Janssen, Caspar (24 March 2010). "Zeearend nestelt zich in Nederland" [White-tailed eagle nests in the Netherlands] (in Dutch). Volkskrant.nl. Retrieved 30 May 2011. External link in
- Hailer et al. 2006.
- Hailer 2006.
- Hailer, Gautschi & Helander 2005.
- Radovčić, D.; Sršen, A.O.; Radovčić, J.; Frayer, D.W. (2015). "Evidence for Neandertal Jewelry: Modified White-Tailed Eagle Claws at Krapina". PLoS ONE. 10 (3 e0119802): e0119802. doi:10.1371/journal.pone.0119802. PMC 4356571. PMID 25760648.
- Hailer, Frank (2006). Conservation genetics of the white-tailed eagle (Haliaeetus albicilla). PhD thesis. Sweden: Uppsala University. ISBN 978-91-554-6581-0. OCLC 185328184. Retrieved 2011-05-30.
- Hailer, Frank; Gautschi, Barbara; Helander, Björn (2005). "Development and multiplex PCR amplification of novel microsatellite markers in the White-tailed Sea Eagle, Haliaeetus albicilla (Aves: Falconiformes, Accipitridae)". Molecular Ecology Notes. 5 (4): 938–940. doi:10.1111/j.1471-8286.2005.01122.x.
- Hailer, F.; Helander, B.; Folkestad, A. O.; Ganusevich, S. A.; Garstad, S.; Hauff, P.; Koren, C.; Nygard, T.; Volke, V.; Vilà, C.; Ellegren, H. (2006). "Bottlenecked but long-lived: High genetic diversity retained in white-tailed eagles upon recovery from population decline". Biology Letters. 2 (2): 316–319. doi:10.1098/rsbl.2006.0453. PMC 1618921. PMID 17148392. Electronic appendix
- Hailer, F.; Helander, B.; Folkestad, A. O.; Ganusevich, S. A.; Garstad, S.; Hauff, P.; Koren, C.; Masterov, V. B.; Nygård, T.; Rudnick, J. A.; Saiko, S.; Skarphedinsson, K.; Volke, V.; Wille, F.; Vilà, C. (2007). "Phylogeography of the white-tailed eagle, a generalist with large dispersal capacity". Journal of Biogeography. 34 (7): 1193–1206. doi:10.1111/j.1365-2699.2007.01697.x.
- Helander, Björn; Hailer, Frank; Vilà, Carles (2007). "Morphological and genetic sex identification of white-tailed eagle Haliaeetus albicilla nestlings". Journal of Ornithology. 148 (4): 435–442. doi:10.1007/s10336-007-0156-y.
- Scottish Natural Heritage (Spring 2009). "The Nature of Scotland". OCLC 310094759.
- Snow, David W.; Perrins, Christopher M. (1998). The Birds of the Western Palearctic (Concise ed.). Oxford University Press. ISBN 978-0-19-854099-1.
- Wink, M.; Heidrich, P.; Fentzloff, C. (1996). "A mtDNA phylogeny of sea eagles (genus Haliaeetus) based on nucleotide sequences of the cytochrome b gene" (PDF). Biochemical Systematics and Ecology. 24 (7–8): 783–791. doi:10.1016/S0305-1978(96)00049-X.. The authors' reservations about using the generalised "2%" rate of molecular evolution have since proven to be well founded.
- Grant, Peter J. (1988). "The Co. Kerry Bald Eagle". Twitching. 1 (12): 379–380.
describes plumage differences between Bald Eagle and White-tailed Eagle in juvenile plumage
- Extinction in Scotland
- Harvie-Brown, J.A.; Buckley, T.E. (1892). A Vertebrate Fauna of Argyll and the Inner Hebrides. Edinburgh: David Douglas. pp. 104–107.
- Harvie-Brown, J.A.; Buckley, T.E. (1888). A Vertebrate Fauna of the Outer Hebrides. Edinburgh: David Douglas. pp. 84–87.
|Wikimedia Commons has media related to Haliaeetus albicilla.|
|Wikispecies has information related to Haliaeetus albicilla|
- White-tailed Eagle Webcam - Smøla, Norway
- White-tailed Eagle at RSPB: Birds by Name
- Live webcam nest White-tailed Eagle, Oostvaardersplassen, Netherlands.
- Fieldguide page on Flickr
- White-tailed Eagles in Scotland. BBC website.
- BirdLife species factsheet for Haliaeetus albicilla
- "Haliaeetus albicilla". Avibase.
- "White-tailed Sea-eagle media". Internet Bird Collection.
- White-tailed eagle photo gallery at VIREO (Drexel University)
- Audio recordings of White-tailed eagle on Xeno-canto.